Environmental and Social Impact Assessment Addendum – Supplement Studies including Biodiversity and Critical Habitat Assessment

Project Number: 49222-001 October 2016

INO: Tangguh LNG Expansion Project

Prepared by BP Berau Ltd. for the Asian Development Bank

The environmental and social impact assessment is a document of the project sponsor. The views expressed herein do not necessarily represent those of ADB’s Board of Directors, Management, or staff, and may be preliminary in nature. Your attention is directed to the “Term of Use” section of this website.

In preparing any country program or strategy, financing any project, or by making any designation of or reference to a particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of or any territory or area.

SUPPLEMENTARY INFORMATION TO SUPPORT THE IMPACT ASSESSMENT

BP Berau Ltd. (“BP”) is the operator of Tangguh LNG, which comprises of two gas treatment and liquefaction Trains located in Teluk Bintuni Regency, Papua Barat Province, Indonesia. The onshore plant produces Liquefied Natural Gas (LNG) and stabilized hydrocarbon condensate as export products with the first LNG cargo shipment in July 2009. Natural gas from two offshore platforms is delivered to onshore receiving facilities via subsea pipeline. BP and its partners plan to expand the Tangguh LNG facilities to increase Tangguh LNG production capacity by developing LNG Train 3 and additional supporting facilities, referred hereafter as the Tangguh Expansion Project (TEP). Initial expansion is to include LNG Train 3, two platforms (ROA and WDA), 13 new development wells, two subsea pipelines, a combined LNG and Condensate Jetty and other supporting facilities. TEP aims to optimize LNG production of existing reserves that cannot be produced within the existing two train development prior to Production Sharing Contract (PSC) expiry. TEP will provide benefits to the Government of Indonesia and local communities, which include a contribution to fulfilling domestic gas needs, supporting local livelihoods, strengthening partnership and continuing investment in economic and social development of the region. BP and its partners are seeking external financing to support the onshore components of the project. TEP aims are to comply with the environmental requirements of the Government of Indonesia and respective local government regulations, to conform to ADB's Safeguard Policy Statement 2009 (ADB, 2009), and to align with IFC Performance Standards (IFC, 2012), as well as the Equator Principle III (2013) standards.

This document provides additional information required to fulfill lenders requirements, to supplement the impacts assessment discussed in the AMDAL. The additional information requirements are:

- Impact assessment of LNG tankers operation; - Residual impact management, i.e. Acid Sulfate Soil (ASS) management, landfill and hydrostatic test water pond closure framework; - Water management; - Green House Gas (GHG) management; - Drilling mud and cuttings management; - Tangguh waste management facilities; and - Critical Habitat Assessment and Biodiversity Action Plan.

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1. LNG Tankers

LNG Tankers shall operate according to applicable Indonesian regulations and the International Requirement, i.e. International Maritime Organization (IMO), International Convention for the Safety of Life at Sea (SOLAS) and International Convention for the Prevention of Pollution from Ship (MARPOL). The requirement to follow those applicable international standards is stated in the Master Time Charter Party Agreement between Tangguh LNG and the Ship Owner(s).

According to the agreement, BP will act as Commercial Operator/Charterer, with main responsibility to provide assurance that the LNG Tankers will fully comply with applicable requirements, e.g. SOLAS, MARPOL, while the full accountability to conduct the environmental management of the LNG Tankers belongs to the Ship Owner(s).

It is clearly stated in the Master Time Charter Party Agreement that the Ship Owner(s) shall ensure that no pollution of any description shall be discharged from the LNG tankers. The LNG tankers shall be fully compliant with all applicable international, national and state oil and air pollution laws, conventions and regulations. In case of any non-conformance of the requirement, the LNG tanker shall be ‘Off-Hire’ until it is in state to resume the normal service and operation required under the agreement.

1.1 Impact Description

Similar with the general sea transportation activities, LNG tanker movements within Bintuni bay area may generate the following impacts which need to be managed:

1. Disturbance to Marine Mammal and Marine Biota due to LNG Tanker Movement. Marine mammals (dolphins and whales) are sensitive to direct disturbance from waves caused by vessel movements, and the possibility of vessels colliding with marine mammals. In addition, acoustic energy caused by transportation activities may also disrupt marine mammals’ communication and navigation systems, so that they avoid the area.

2. Potential Pollution from LNG Tankers Waste Disposal and Wastewater Discharge. Waste disposal and wastewater discharge from LNG tankers will be mainly sourced from organic material, such as sewage and food waste. Although the disposal of both, waste and wastewater from LNG tankers, may have impact to the sea water quality, but considering the treatment facility on board to treat the waste and wastewater prior to discharge and the fulfillment of MARPOL (and/or other applicable international requirement), the impact from disposal of waste and wastewater from the LNG tankers may be deemed insignificant.

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3. Potential Invasive Alien Species Invasive alien species may occur due to ballast water change and/or barnacles on ship body. Proper management of ballast water exchange and use of anti-fouling agent have been implemented, to minimize the impact of invasive alien species.

4. Potential Collision with Community and Other Boats Passing in Bintuni bay Area Tankers operating within Bintuni bay have the potential risk of colliding with community/other boats passing the area. Although a shipping lane has been determined for tanker’s operation, additional measures such as the presence of patrol boat and security boat as described in Section 1.2 below have been put in place to prevent collision between LNG tanker and community/other boats in the Bintuni Bay area.

For this assessment, the scope of impact and management will be limited within the project area of influence, i.e. within Bintuni Bay area, considering also limitations of the influence of the project to the tanker operation.

Greenhouse gases (GHG) generated from LNG tanker operation is not considered as GHG impact from Tangguh activity. Therefore, there will be no trans-boundary impact from Tangguh generated from the LNG tanker operation.

1.2 Impact Management

To minimize the impact from LNG Tankers operation within Bintuni Bay, the following mitigation measures have been implemented by Tangguh through inclusion into LNG Tankers Charter Agreement, Operational Procedure and Work Instruction. The operational procedure that is relevant for LNG tankers operation is Marine Mammals and Sea Reptiles Protection Procedure (900-PRC-EN-2329) and provided in Attachment 1.

1. Disturbance to Marine Mammal and Marine Biota due to LNG Tanker Movement - Tanker route shall consider the presence of endangered species and their calving grounds; and - Ensure compliance on Tangguh Policy to route LNG tankers along established international sea lanes through Halmahera (Maluku) waters and avoid travel through Raja Ampat, which features high biodiversity value and whale migration corridors. 2. Potential Pollution from LNG Tankers Waste Disposal and Wastewater Discharge Selective collection and management of wastes according to the criteria of MARPOL 73/78 Annex V Prevention Pollution Garbage Disposal of Garbage Outside of Special Area, as shown in Figure 1 below. - Disposal into the sea of all plastics, including but not limited to synthetic ropes, synthetic fishing nets, and plastic garbage bags is prohibited;

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- Disposal into the sea of the following garbage will be made as far as practical from the nearest land, but in any case is prohibited if distance from the nearest land is less than 25 nautical miles (nmi) (46.3 km) for dunnage, lining and packing material that will float; 12 nmi (22.2 km) for food wastes and all other garbage, including paper products, rags, glass, metal, bottles, crockery and similar refuse; - Disposal into the sea of garbage specified in sub-paragraph (b)(ii) of Annex V may be permitted when it has passed through a comminute or grinder and made as far as practicable from the nearest land, but in any case is prohibited if the distance from the nearest land, is less than 3 nmi (5.6 km). Such comminute or ground garbage will be capable of passing through a screen with openings no greater than 25 mm; and - When garbage is mixed with other discharges having different disposal or discharge requirements, the more stringent requirements will apply.

Table 1. Simplified Overview of the Discharge Provisions of the Revised MARPOL Annex V

Offshore platforms (more than 12 nm from Ships outside special Sh ips within special Type of Garbage land) and all ships areas areas within 500 m of such platforms Discharge permitted Discharge permitted Food waste comminuted ≥3 nm from the nearest ≥12 nm from the nearest Discharge permitted or ground land, en route and as far land, en route and as far as practicable as practicable Discharge permitted food waste not ≥12 nm from the nearest Discharge prohibited Discharge prohibited comminuted or ground land, en route and as far as practicable Cargo residues not Discharge prohibited Discharge prohibited contained in wash water Discharge permitted Discharge permitted ≥12 nm from the nearest ≥12 nm from the nearest Cargo residues land, en route and as far land, en route and as far Discharge prohibited contained in wash water as practicable as practicable and subject to two additional conditions Discharge permitted ≥12 nm from the nearest Cleaning agents and land, en route and as far additives contained in Discharge prohibited as practicable and subject cargo hold wash water to two additional Discharge permitted conditions Cleaning agents and additives in deck and Discharge permitted Discharge prohibited external surfaces wash water

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Offshore platforms (more than 12 nm from Ships outside special Sh ips within special Type of Garbage land) and all ships areas areas within 500 m of such platforms Carcasses of animals Discharge permitted carried on board as cargo as far from the nearest Discharge prohibited Discharge prohibited and which died during land as possible and en the voyage route All other garbage including plastics, synthetic ropes, fishing gear, plastic garbage, bags, incinerator ashes, clinkers, cooking oil, Discharge prohibited Discharge prohibited Discharge prohibited floating dunnage, lining and packing materials, paper, rags, glass, metal, bottles, crockery and similar refuse When garbage is mixed with or contaminated by other substances prohibited from Mixed garbage discharge or having different discharge requirement, the more stringent requirements shall apply

3. Potential Invasive Alien Species For potential invasive alien species due to ballast water exchange, a ballast management has been in place to ensure the ballast water exchange activity complies with local and international regulations as applicable. Under Regulation B-4 Ballast Water Exchange (International Convention for the Control and Management of Ships Ballast Water and Sediments – IMO 2004), all ships using ballast water exchange should: - Whenever possible, conduct ballast water exchange at least 200 nmi from the nearest land and in water at least 200 meters in depth, taking into account guidelines developed by IMO; - If the ship is unable to conduct ballast water exchange as above, this should be as far from the nearest land as possible, and in all cases at least 50 nmi from the nearest land and at least 200 meters in depth in water; - Where practicable, efforts should be made to reduce sound by ballasting unladen tankers (with consideration to the potential for relocation of invasive species in ballast water) and adjusting vessel speed; - Ballast water exchange shall be recorded for verification at Tangguh LNG sea port; and - A ballast handling plan for a ballast voyage, where ballast water exchange is intended to take place, should be prepared in advance. This pre-planning is necessary in order to maintain safety and stability of the vessels during any ballast water exchange or other ballast water treatment or control option as required. Ballast water exchange is an area of concern in certain ports of the

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world. Vessel must at all times comply with local and international regulations as applicable.

Another potential invasive alien species from tanker operation is from the presence of barnacles on the ship body. This impact can be prevented by the use of anti-fouling systems.

The International Convention on the Control of Harmful Anti-Fouling System on Ships (AFS) was adopted by the IMO in October 2001 and entered into force on 17 September 2008. The AFS regulations and guidelines were adopted to prohibit the application of anti-fouling systems containing organotin compounds.

The implementation of AFS will be certified with an International Anti-Fouling System Certificate (IAFS) – see Attachment 1. The IAFS Certificate will be supplemented by a Record of Anti-Fouling Systems. Compliance of the convention have also been touched up with a TBT-free AFS. An inspection of anti-fouling systems may be carried out by Port State Control (PSC) to verify compliance with the conventions.

In order to ensure compliance with the convention, the following steps are being implemented by the Ship Owner:

a. Checking of ship’s documentation and reporting the availability of the followings: o International Anti-Fouling System Certificate; o Supplement to IAFS Certificate – Record of Anti-Fouling Systems; o Statement of Compliance; and o Paint Specification and/or a paint record issued by the paint manufacturer. b. Re-validation of IAFS Certificate if one of the following actions takes place: o Change of vessel owner; o Change of name of the vessel; o Replacement of more than 25% of the existing AFS; o Complete removal of existing AFS; and o Change of flag.

4. Potential Collision with Community/Other Boats Passing in Bintuni Bay Area To prevent collision between LNG tankers with community/other boats during transport within Bintuni Bay, the following measures are in place and implemented: a. Dedicated Access Channel to Approach Tangguh Terminal LNG tanker approach to Tangguh area has been provided with a dedicated existing channel as shown in Figure 1. LNG Tankers entering and exit Tangguh port shall pass through this channel and will be escorted by pilot boat and security boat.

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b. Escort Duties Procedure Escort duties guidelines for LNG tanker entering Tangguh is provided in Marine Security Patrol Boat Operating Guidelines for Tangguh LNG (920-PRC-OP-7019). The escort duties responsibilities are: o Prior to LNG tanker entering the Tangguh access channel, the boat skipper is responsible to determine whether weather conditions have deteriorated sufficiently to suspend marine security patrol boat escort activities; o The pilot shall be informed of the weather and sea condition and is responsible for deciding if the scheduled LNG tanker movement can continue; o The pilot plus one security patrol boat shall escort LNG tanker from the pilot boarding position to their respective berth(s) and vice versa; o The pilot boat and patrol boat shall ensure the designated tanker route and jetty approaches are clear of all fishing boats and associated nets, buoys and equipment, and maintain an exclusion zone surrounding the vessel. Vessel underway in designated tanker route is shown in Figure 2; and o Security patrol boat and pilot boat will conduct channel clearance along the passage of LNG tanker inward and outward from Tangguh Terminal until Pilot Boarding Ground (PBG) to ensure the mandatory pilotage tanker route is clear from fisherman’s boat and other fishing equipment.

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Figure 1 – Dedicated Access Channel to Approach Tangguh Terminal SUPPLEMENTARY DOCUMENT TO LENDER 8

Port

Ahead Astern

Starboard

Figure 2 - Vessel Underway in Designated Tanker Route

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2. Residual Impact

2.1. Acid Sulfate Soil (ASS) Management

Acid Sulfate Soil (ASS) is naturally occurring within Tangguh LNG site. The high sulfate contents and acid conditions are probably results of the oxidation of pyrite that is present in a disseminated form within the Steenkool formation. In a normal undisturbed condition, the ASS is benign. However, if the soils are exposed to air, then the sulfides will react with oxygen and form sulfuric acid.

Acid sulfate soils were initially encountered during Train 1 and 2 (T1/2) constructions, where the excavations on site are exposing ASS. A pH snapshot map was made during T1/2 construction that illustrates the existing condition as earthworks progress at that time; it is shown in Figure 3. It is expected that during the earthwork activity of TEP, ASS will be also encountered.

If not managed properly, ASS may result negative impact to the environment, e.g. may affect the vegetation, seeping into and acidifying groundwater, flown to surface water and impact on fish and other aquatic organisms. Therefore, in the Invitation To Tender (ITT) document for Engineering Procurement Construction (EPC) Contractor, TEP has set the following management and monitoring plan to minimize and control the impact of ASS during construction. o Management and Mitigation Measures  Where ground-disturbing work is proposed, the EPC Contractor is required to assess the soil in advance of any construction activities for ASS potential and map the area at risk;  Where ASS is excavated, the ASS needs to be covered (or re-buried) to exclude oxygen at the designated area proposed by the EPC Contractor and approved by BP (as the appointed operator on behalf of Tangguh);  Where Acid Runoff Drainage (ARD) occurs, it is to be collected into neutralization pond and neutralized (e.g. with hydrated lime or crushed limestone) to ensure its pH meet the requirement before releasing it to the environment; and  Exposed ASS is to be treated and neutralized with materials such as hydrated lime or crushed limestone before final disposal to prevent ARD. o Monitoring  Record of Soil Assessment by the EPC Contractor;  Record of Soil Management including ASS Management by EPC Contractor;  Weekly pH monitoring at effluent of settlement/treatment pond to be conducted by the EPC Contractor;

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 Surface water monitoring, including pH at upstream and downstream (50-100 m from effluent) to be conducted on a monthly basis by the EPC Contractor and to be checked quarterly by External Laboratory appointed by the EPC Contractor;  Surface water monitoring at upstream and downstream (50-100 m from effluent) to be conducted every 6 months as per RPL requirement by External Laboratory appointed by the EPC Contractor; and  Surface water monitoring at upstream and downstream (50-100 m from effluent) to be conducted every 3 months as per RPL requirement by EPC Contractor Internal Laboratory.

The above requirements are also included in the EPC contract. The EPC Contractor is required to develop an Acid Sulfate Soil Management Procedure, prior to construction.

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Figure 3 - pH Snapshot Map

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2.2. Landfill Closure

Currently in Tangguh site, there are three existing landfills; inert landfill, organic waste landfill and new sanitary landfill (for combined organic and inert waste). The existing inert landfill and organic waste landfill are considered to be decommissioned, as it is nearly reach its full capacity. The inert landfill and organic waste landfill are shown in Figure 4 below.

Figure 4 - Inert and Organic Waste Landfills

At the time of closure, it is important to ensure that any potential environmental contamination resulting from the landfill is minimized through a proper closure and rehabilitation. To achieve that objective, the following framework will be implemented for landfill closure and post monitoring activity:

1. Final Cleaning Up Prior to closure, the landfill and surrounding area should be cleaned up, so that any waste pile, debris or other windblown waste are consolidated and placed in final disposal cell for final covering.

2. Landfill Sloping Landfill sloping is important to prevent any water ponding occur and seeping into the closed landfill areas, while at the same time prevent any erosion. The final slopes of the landfill site should be at least 2%-4% in grade to prevent ponding and ensure proper water flow, with vertical to horizontal ratio of less than 1 : 3 (see Figure 5 below). Safety factor for permanent slope is 1.5. Following the sloping of the landfill, compaction needs to be done to ensure stabilization of the landfill.

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Figure 5 - Slope Grade and Vertical Horizontal Ratio

3. Landfill Capping Main purposes of landfill capping are: o Ensure the integrity of the waste pile in longer term o Ensure the growth of vegetation during rehabilitation program o Ensure stability of slope o Reducing water infiltration, release of gas and odor from the landfill o Prevent animal nesting on the landfill Landfill capping will consist of the following: . Soil cover for compaction layer . Clay layer . Drainage layer . Topsoil material layer An additional layer of gravel between soil and clay layer is normally be added, if gas control piping is added to the system. Typical landfill capping layer is shown in Figure 6.

Figure 6 - Typical Landfill Capping Layer

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4. Re-vegetation Re-vegetation is included as part of landfill closure to prevent surface erosion by rain water runoff, protect final capping layer, improve visual amenity and maintain stability of the landfill slopes. Re-vegetation will be conducted upon completion of topsoil placement and will be using native species.

5. Drainage System Drainage system shall be designed to reduce infiltration into the closed landfill. The final surface is shaped so that any rain water runoff will flow away from the landfill and not ponding. Main drainage channel will be provided in around the landfill site. The landfill slope shall be designed to be directed to the main drainage channel. Volume of drainage channel shall be determined based on the total catchment area and rainfall intensity.

6. Leachate Collection System A leachate collection system has been installed during operations to collect leachate generated in the landfill and convey the collected leachate to the sewage treatment facility. The leachate collection system will be maintained and monitored, although the volume of leachate water should be reduced significantly if the landfill closure was conducted properly.

7. Gas Control System Gas control system is required to control the methane and other gasses generated from biodegradation process in the landfill. Collected gas must be released into atmosphere, normally using vertical venting pipe. If required, the additional venting pipe for gas control system shall be provided during the closure to release the gas.

8. Post Landfill Closure Monitoring Post landfill closure monitoring is required to ensure the effectiveness of landfill closure in terms of minimizing the environmental impact. The monitoring activity will include the following aspects: - Groundwater quality monitoring; - Nearest surface water monitoring – for any surface water located in less than 200m from the landfill site; - Leachate water quality monitoring; and - Regular inspection of vegetation, drainage system and leachate system.

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2.3. Hydrostatic Test Water Pond Closure

Similar with landfill, existing hydrostatic test water pond closure if not conducted properly may have potential negative impact to the environment. Hydrostatic test water pond is shown in Figure 7.

During T1/2 development, the hydrostatic test water pond was a temporary facility built during the construction phase to hold the hydrostatic water. It was planned to be decommissioned prior to operations; however it has become an integral part of the wastewater treatment system, as it is used as the effluent holding pond for off-spec waste water, particularly from Produced Water Treatment (PWT) unit.

Figure 7 - Hydrostatic Test Water Pond

For TEP, an additional produced water tank will be provided to collect the off-spec effluent to be transferred back to the system. Once Train 3 is in operation, the hydrostatic test water pond will be demolished.

To ensure the demolition of the hydrostatic test water pond is conducted properly and its potential impact to environment is managed, the following framework will be implemented:

1. Water Quality Testing and Draining Prior to draining, the water quality needs to be tested to determine proper handling method and treatment. Once the water quality is tested and proper treatment method is selected, the water draining process can be started. If the water will be treated in on-site facility, it is important to ensure the water draining rate is equal with the treatment unit available capacity and rate.

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2. Demolition of High Density Poly Ethylene (HDPE) Liner Once the pond is drained, the HDPE liner can be demolished. The disposal of the liner will also be determined from the water quality testing result, if there is any hazardous contaminant found in the water sample, the HDPE liner will need to be managed as hazardous waste.

3. Filling, Compaction and Re-vegetation Following the demolition of HDPE liner, the soil pit can be filled with soil material and compacted. The re-vegetation will be done in the area to stabilize the soil and also prevent any soil erosion.

4. Post Closure Monitoring Post closure monitoring will include the monitoring of groundwater and soil quality in the hydrostatic pond location to ensure the environmental impact has been properly managed.

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3. Water Management Plan

3.1. Wastewater Management Plan

The addition of a third train at Tangguh and the associated increase in gas production will require additional facilities to handle additional volumes of produced and waste water. The management and monitoring plan of the produced water and other waste water discharges has also been described in detail in AMDAL.

The existing Produced Water Treatment (PWT) and other waste water treatment and disposal system need to be expanded to collect and treat the additional waste water from TEP facilities. These new facilities will be an extension of the existing treatment plant to process the wastewater to meet the quality standard for final disposal to the sea.

To handle the anticipated increase in produced water from the TEP facilities, a treatment plant facility similar design to the two existing units (1 x 25 m3/hr) will be added to increase the total PWT plant capacity to 75 m3/hr for 3 LNG Trains. Similar systems to the current produced water treatment process will be utilized with a new treatment plant being installed. The new PWT will include a new Dissolved Air Floatation (DAF) unit, biological treatment and a new filtration train. Design of the integrated system shall address flow distribution between the new and existing PWT plants in addition to addressing lessons learned from existing PWT plant, to be incorporated in the design of TEP PWT unit.

A produced water buffer tank with a minimum working volume of 8,580 m³ will be installed, in order to provide sufficient supply during scenario of LNG Train shutdown, PWT Plant upset, PWT Plant under maintenance and also to collect any off-spec effluent to be re-routed back to the system. Interconnecting line shall be provided between existing and new PWT system.

All new areas of the TEP facilities will be provided with drainage/sewer as required. The waste water streams from these areas will also be routed to specific area of wastewater treatment.

The intent for TEP facilities is to strictly segregate the waste water streams for the PWT plant and oily water treatment system. A separate oily water treatment will be provided (i.e. a properly designed corrugated plate interceptor (CPI), similar with the existing one). All new oily water sump pits throughout the TEP facilities will flow to this new CPI which will be located in the new utility area. The discharge line from new CPI will be routed directly to common effluent header, as oily water has a different discharge specification to produced water. The discharge line to the produced / waste water handling is still provided as back-up in case downtime of the oily water treatment package. There will be no integration between existing and TEP oily water system, considering in the existing oily water system (in Onshore Receiving Facilities (ORF) area) is still combined with produced water system.

A new chemical neutralization pit will be provided where all chemical contaminated waste water is routed to be further neutralized to effluent specification. New neutralization pit will be

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located in new utility area together with associated acid/caustic storage and pumps. The capacity of the new neutralization pit will cover TEP requirements and there will be no integration with existing neutralization pit.

A new permanent integrated Sewage Treatment Plant (STP) will be built to handle sewage from TEP for both the construction and operational phases. Sewage treatment capacity will be based on peak activities during the project construction phase and will provide for treatment of the sewage from TEP dormitory / camp with increased personnel on site. Aerobic biological treatment with a disinfectant unit will be used for TEP. The sludge generated will be disposed to landfill.

Option to install a new desalination plant will produce a rejected brine stream that will be part of wastewater sources.

All of above wastewater sources will be tied-in to a new common wastewater discharge line to sea. A connection with the existing common wastewater discharge line may be implemented, in order to allow sparing to minimize potential risk due to blockage or maintenance at the existing discharge line. The discharge point to the sea will be at -6 LAT at the new LNG-Condensate jetty (LNG Jetty 2), with reference to the waste water discharge modelling stated in the AMDAL.

Each of the wastewater streams shall be monitored against applicable standard and its discharge permit. Therefore provision of sampling facility and/or online analyzer and flow meter is required at each of effluent pipe prior to tie-in to the common waste water discharge line to sea.

To finalize the option of produced water and wastewater treatment for TEP, a study has been conducted prior to Front End Engineering Design (FEED) to assess all the potential option and determine the final method to be used for TEP. The summary of analysis done in the study and its conclusion are provided in the following sections.

3.1.1. Analysis Basis

The overall project strategy for TEP is to standardize upon the existing design and ensure lessons learnt are incorporated within the design of future trains. Five main concern / strategy will be implemented for the produced / waste water management for the TEP:

1. Produced /waste water minimization – reduce the quantity of waste water if possible and segregate between the surface drainage run-off/oily water and produced / waste water stream which have different discharge standard. 2. Water polishing and re-use – further treat the water to be re-used as utility water in the plant. 3. Produced water mass balance strategy – produced water mass balance shall be maintained during one LNG trip or shutdown and upset in biological process.

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Existing hydrostatic test water pond shall be de-commissioned and its function will be replaced by produced water tank / buffer tank with sufficient capacity. 4. Provision of facilities in Train 3 to recover water in dehydration unit and re-use the water in Acid Gas Removal Unit (AGRU) will reduce the amount of waste-water to be treated with potential contamination of the PWT Plant with traces of amine solvent. 5. Waste water treatment and disposal – treat the waste water suitable for the respective discharge specification, and standardize on the treatment technologies / system and disposal method.

3.1.2. Produced Water Reinjection

Water re-injection into the subsurface formation is a proven method for waste water disposal. However, alternative disposal options may be implemented if they are demonstrated to have significant environmental and business benefit relative to preferred method.

Attachment 2 describes the sub-surface perspective regarding the feasibility of water disposal well in the vicinity of the Tangguh plant. The study completed in 2005 and a more recent study was conducted in 2013. In summary, two storage formations and seven options for well location have been identified. Each option has pros and cons, but onshore options have proved to be unviable, since the onshore area part of the Kasuri PSC is not owned by Tangguh and therefore it is not possible for Tangguh to drill the produced water reinjection well on other PSC’s area. The only potential option for disposal underground would involve drilling a disposal well to the south of Roabiba field.

The storage formation options are Faumai Formation and/or Roabiba Sandstone. Based on the information available, Roabiba Sandstone would be technically the best solution but is also significantly more expensive. The qualitative advantages and disadvantages of water re-injection are described below.

Qualitative Advantages

 Lowest impact to the environment and minimum social risk due to no discharge to the sea.  Less stringent, in terms of quality of the discharge specification compared to the discharge to the sea option, resulting in potentially less cost for the treatment system.

Qualitative Disadvantages

 Currently there is no access to the onshore subsurface formation for water re- injection, since the area bordering the Tangguh LNG plant belongs to another PSC. This requires injection to be sent to offshore formation resulting in a significantly increased CAPEX requirement, while also add technical complexity as the produced

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water separation process takes place in onshore and the separated produced water will need to be re-sent to offshore for reinjection.  A very stringent permitting process and require a more detail technical requirement.  Redundancy would be required in case of failure or problem at the injection well - provision of a spare injection well would further increase the overall CAPEX.  Capacity is limited by the selected size of the water re-injection pipeline.

The water re-injection system can be viewed as two distinct sections, which are the water treatment facility for re-injection and the water pipeline & water injection well. The cost component of the injection well is approximately of 60-75% of the total installed cost, hence is greatly influencing the economics of the system compared with the treatment for disposal to sea.

The typical treatment system is the removal of dispersed oil & grease using dissolved gas flotation system in the ORF, followed by additional filtration and chemical injection (for biocide, oxygen scavenger, etc.). The cost of this system will be lower than the treatment system for disposal to sea, however this cost differential will be negated by the high cost of the injection well and pipeline.

Considering the questions on feasibility and also cost, water re-injection will not be used as a method of produced water disposal for TEP.

3.1.3. Offshore Water Separation

Water separation & treatment in the offshore facilities, either for discharge/disposal to sea or for re-injection, is a common and proven design worldwide. The system typically consists of gravity separation, followed by further separation either using hydro cyclone or flotation unit. For re-injection, further treatment would be typically required such as filtration, chemical injection or de-oxygenation. The advantages and disadvantages of this system for the Tangguh facilities are listed below.

Qualitative Advantages

 Compared with discharges from onshore facilities, there is potentially less stringent water discharge specification for disposal to sea from an offshore facility, hence less processing /treatment equipment is required.  Reduction of water rate in the pipeline, thus reducing the pressure drop and slug volume, with potential to increase the gas production.  Direct re-injection from the offshore facilities removes the requirement for an additional water reinjection pipeline from onshore.

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Qualitative Disadvantages

 Additional equipment on the platform topsides. This will increase the topsides weight and potential the jacket weight and size. Additional equipment not aligned with the Normally Unattended Installation (NUI) philosophy adopted for the wellhead platforms, which aims for minimum equipment offshore in order to minimize the requirement for visits.  Additional engineering and longer schedule to design the separation system since it cannot be copied from the existing VRA/VRB platforms design (no standardization).  Although at smaller capacity, an onshore produced water treatment facility would still be required to treat the condensed water which forms along the pipeline.

Based on the above comparison, it is considered that the benefits of maintaining the NUI philosophy, design standardization and faster project delivery far outweigh the potential benefits of water disposal offshore. No increased production would result as the constraint on production is the LNG Train capacity, nor it would result a significant environmental benefit. Therefore, the offshore water separation system will not be utilized for TEP.

3.1.4. Produced Water Treatment Plant

The existing PWT plant at the Tangguh facilities was constructed at the end of the T1/2 construction after the LNG plant itself was operational, to fix the deficiencies in the original ORF design. For TEP, a similar process to the existing PWT plant is recommended based on current performance. However, there is also essential change that needs to be implemented to improve the overall system and capture the lesson learned from existing PWT plant, as shown in Table 2 below.

Interconnecting inlet lines and outlet lines to be provided to the existing PWT, and there shall be a provision to treat the off-spec effluent from the existing PWT to TEP PWT.

Qualitative Advantages

 Proven system using the bio-treatment and incorporation of lessons for the expansion design, to meet the discharge specification.  Experience and familiarity of Operation personnel to operate the similar system.  High availability / operating efficiency by proper specification and sparing philosophy.

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Qualitative Disadvantages

 Large plot area is required for the waste water treatment system (bio-treatment). This is also due to the potential increase in equipment sizes to accommodate the more stringent discharge specification.  Different waste stream is still generated from the PWT Plant, which is the solid bio- sludge from the bio-treatment system, requiring operating cost to handle and dispose it in the sanitary landfill area within Tangguh area. DAF-sludge from primary treatment is considered as hazardous waste and requires proper hazardous waste treatment. However, benefit from TEP is that provision of the Liquid/liquid Coalescing Package in ORF will reduce the hydrocarbon content in produced water; therefore it will reduce the amount of solid hazardous waste disposal.  Biological process relies on microorganism/bug activities, these microorganisms can be poisoned if conditions are not stable.

The proposed location for TEP produced water treatment is on the east side of the existing Main Control Building (MCB).

Table 2 - Waste Water Treatment Design for Tangguh Expansion

No Phase-1 Design Expansion Design 1 Primary treatment in PWT - removal of Primary separation at the ORF. Then dispersed oil & grease using Dissolved further dispersed oil flotation treatment Air Flotation (DAF) system at the PWT.

2 Secondary treatment in PWT - removal Similar design, adjusted for more of dissolved contaminants using bio- stringent discharge specification treatment / activated sludge system

3 Tertiary treatment in PWT - sand Similar design, with addition of ion filtration to remove TSS and activated exchange or reverse osmosis to remove carbon to remove residual dissolved TDS (higher than existing when contaminants formation water starts being produced)

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3.1.5. Water Polishing and Re-Use

The existing facility requires utility water (fresh water) for the process, utilities and personnel uses, which is supplied from the seawater desalination system. For TEP, the potential to use ground water from the aquifer to supply the water needs, instead of installing a new desalination plant was also considered. The estimated continuous demand of utility water, including for personnel use, is 141 m3/h for three trains operation.

The quality specification of utility water is shown in Table 3 below, compared with the quality of treated water from existing PWT plant, as proven during the performance test. It is identified that the effluent water from the PWT plant has the potential to be further treated / polished to reach the quality of utility water. The flow rate of the effluent water is not sufficient to meet all demand of the utility water, but there is still benefit envisaged if the effluent water is re-used as utility water.

Qualitative Advantages

 (If utility water is provided by desalination unit) – Reduction of energy use and minimizing waste stream (brine) from the desalination unit thus minimizing environmental impact to the environment / Bintuni Bay.  (If utility water is provided from ground water source) – Conservation of ground water resource.

Qualitative Disadvantages

 Utility water demand exceeds the flow rate of the treated produced water (from condensed water), hence water supplied from either desalination or ground water would still be required.  Higher capital expenditures which is not driven by environmental compliance.

The envisaged system for the water polishing is primarily for removal of dissolved solids (TDS), utilizing either reverse osmosis (RO) or an ion exchange system. Other equipment would be required for pH adjustment and water de-chlorination. Design of a water polishing system would need to consider formation water breakthrough which is predicted to result in total dissolved solids (TDS) increasing above 4000 mg/l. The polishing unit would not completely remove the requirement for effluent discharges to sea but the volumetric flowrate would be reduced.

Technically there are clear advantages of meeting some of the water demand by recycling and reusing the produced water streams. However, this system introduces more risk to the users of water as the inlet specification could vary. Furthermore, although smaller in scale, other water sources would still be required, hence no costs could be fully eliminated and will add operational complexity by having more types of water treatment package.

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Table 3 – Comparison of Required Quality of Utility Water and Typical Effluent from Existing PWT Plant

Quality / Specification Effluent from existing No Parameter (Note 1) PWT Plant (Note 2) 1 pH 6.5 – 7.5 8.2 – 8.4

2 TDS < 10 mg/l < 600 mg/l

3 Residual Chlorine 0.20 – 0.50 mg/l N/A

4 Turbidity < 5 NTU < 10 NTU

5 Iron (Fe) < 0.2 mg/l < 0.5 mg/l

Notes: 1. The utility water specification is derived from the existing requirements for Tangguh plant 2. The quality of effluent from existing PWT Plant is based on early operation and performance test, which needs to be re-confirmed based on long term monitoring of the existing PWT Plant.

3.1.6. Other Wastewater Management and Discharge to Sea

Other sources of wastewater from Tangguh LNG are: oily contaminated wastewater, chemically contaminated wastewater, sanitary waste, and brine waste discharge.

 Oily Contaminated Wastewater The sources of oily contaminated wastewater are from oily water sump pits during normal operation and maintenance activity. Different with current practice in existing operation, skimmed hydrocarbon from produced water tank shall not be routed to this system. A separate oily waste water treatment will be provided (i.e. a properly designed corrugated plate interceptor (CPI), similar with the existing one). All new oily water sump pits throughout the TEP facilities will flow to this new CPI which will be located in new utility area. The discharge line from new CPI to be routed directly to common effluent header, as oily water has a different discharge specification to produced water. The discharge line to the produced / waste water handling is still provided as back-up in case downtime of the oily water treatment package. There will be no integration between existing and TEP oily water system, considering in the existing oily water system (in ORF area) is still combined with produced water system.

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 Chemically Contaminated Wastewater A new chemical neutralization pit will be provided where all chemical contaminated waste water i.e. from Boilers and Heat Recovery Steam Generator (HRSGs) blowdown, Demineralization Package regeneration waste and Amine Carbon Filter backwash water is routed to be further neutralized to effluent specification. New neutralization pit will be located in new utility area together with associated acid/caustic storage and pumps. The capacity of new neutralization pit will cover TEP requirement and there will be no integration with existing neutralization pit.

 Sanitary Waste and Leachate Water A new permanent integrated STP will be built to handle sewage from TEP for both the construction and operational phases. Sewage treatment capacity will be based on peak activities during the project construction phase and will provide for treatment of the sewage from TEP dormitory / camp with increased personnel on site. Aerobic biological treatment with a disinfectant unit shall be used for TEP. The sludge generated will be disposed to landfill.

 Brine waste discharge flowrates will be produced when new TEP desalination unit is installed and operated to cover utility water requirement.

All of above sources, together with effluent from PWT Plant, will be tied-in to a new common wastewater discharge line to sea. A new discharge line with interconnection with the existing line is recommended, in order to allow sparing to minimize potential risk due to blockage or maintenance at the existing discharge line. The discharge point is to the sea -6 LAT at the new LNG-Condensate Jetty (LNG Jetty 2) refer to waste water discharge modelling stated in the proposed AMDAL study. Summary of TEP wastewater management is shown in Figure 8 below.

Each of the wastewater streams shall be monitored against applicable standard. Therefore provision of sampling facility and/or online analyzer and flow meter is required at each of effluent pipe prior to tie-in to the common waste water discharge line to sea.

An ecological risk assessment of the mixing zone1 found that the potential environmental impact to the marine flora and fauna within the effluent discharge zones is very low. Nontheless, the mixing zones will be monitored on a regular six-monthly basis

1 Greencap 2016, Tangguh Expansion Project Ecological Risk Assessment In The Mixing Zone

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Produced Water Produced Water Treatment Plant

Oily LNG Production Corrugated Plate Contaminated Process Interceptor (CPI) Water

Chemically Contaminated Neutralization Pit Water

LNG Jetty 1 & 2 at Desalination Unit Reject Brine -6m LAT

Domestic Sewage Sewage Activities Treatment Plant

Figure 8 – Summary of Tangguh Wastewater Management Plan

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3.1.7. Conclusion

Based on the qualitative evaluations described above, the recommended strategy for produced water / waste water management and handling of the TEP is as follows.

1. Expansion of the existing waste water treatment facilities to accommodate TEP as described below:  An additional PWT comprising Dissolved Air Flotation (DAF), Biological treatment and Filtration units to process the produced water from the produced water buffer tank and also sludge handling facility.  A new separate oily water treatment will be provided (i.e. a properly designed corrugated plate interceptor (CPI), similar with the existing one). All new oily water sump pits throughout the TEP facilities will flow to this new CPI which will be located in new utility area. The discharge line from new CPI to be routed directly to common effluent header as oily water has a different discharge specification to produced water. The discharge line to the produced / waste water handling is still provided as back-up in case downtime of the oily water treatment package. There will be no integration between existing and TEP oily water system, considering in the existing oily water system (in ORF area) is still combined with produced water system.  A new chemical neutralization pit will be provided where all chemical contaminated waste water can be treated. All new chemically contaminated waste water will be routed to this pit.  A new permanent integrated Sewage Treatment Plant (STP) will be built to handle sewage from TEP for both the construction and operational phases. Sewage treatment capacity will be based on peak activities during the project construction phase and will provide for treatment of the sewage from TEP dormitory / camp with increased personnel on site.  Rejected brine from the new desalinization plant will be comingled with all other effluent streams prior to discharge to sea.

A new common wastewater discharge line to sea will be provided for discharge off all treated waste water streams. A connection with the existing common wastewater discharge line may be implemented, in order to allow sparing to minimize potential risk due to blockage or maintenance at the existing discharge line. The discharge point is to the sea -6 LAT at the new LNG-Condensate Jetty (LNG Jetty 2) refer to result of waste water discharge modelling stated in the AMDAL. Each of the wastewater streams shall be monitored against applicable standard. Therefore provision of sampling facility and/or online analyzer and flow meter is required at each effluent pipe prior to tie-in to the common waste water discharge line to sea. The potential environmental impact to the marine flora and fauna within the effluent discharge zones is very low.

.

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3.2. Water Supply

The water supply is used as make-up for the potable water system, demineralized water system, closed cooling water (CCW) system and firewater system, as well as supplying service water to the utility hose stations in the plant and raw water to the loading berths. There will be an additional water supply demand for the Tangguh Expansion Project.

Water supply for the existing facilities is produced by the desalination of seawater via the mechanical vapor compression process, as the original AMDAL prohibited the extraction of groundwater. The existing facilities consist of Sea Water Supply Pumps, an Electro-Chlorination Package, Desalination Packages and Desalinated Water Tank, Corrosion Inhibitor Injection Package, and Desalinated Water Pumps.

In the new AMDAL, the option to use groundwater as water supply was considered as it was deemed to have several advantages, namely a significant reduction in volume of wastewater discharge into Bintuni Bay, greater energy efficiency and reduction in emission of GHG. However, before proceeding with a plan to utilize groundwater at Tangguh, further work would be required, among others to confirm the groundwater reserves, to assess the reduction of capital and operating expenditures compared to operational complexity, and how to manage the presence of shallow gas hazards beneath the Tangguh site.

To finalize the option of water supply for TEP, a thorough assessment was conducted prior to and during Front End Engineering Design (FEED) for both possible options; desalination and groundwater. The summary of the assessment and its conclusion are provided in the following sections.

3.2.1. Water Demand

The water demand for the water supply expansion study is estimated from the water demand of the existing T1/2 operations. The following Table 4 summarizes the water demand for TEP scope.

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Table 4 - Estimated Water Demand and Supply

No Parameter Units Requirements Water Demand

1 Normal Operation

Trains 1 and 2

1.1 Process Area m 3/hr 43

1.2 Non – Process Area m 3/hr 27

Train 3

1.3 Process Area (Note 1) m 3/hr 35

1.4 Non – Process Area m 3/hr 27

1.5 Modification Project – TAR m 3/hr 9

Water Supply

3 Tangguh Trains 1 and 2

3.1 MVC (Note 5) m 3/hr 48.5

3.2 Temporary Reverse Osmosis (RO) (Note 2) m 3/hr 62.5

4 Tangguh Expansion

4.1 Permanent Treatment (Note 3) m 3/hr 172

4.2 Temporary Treatment for Hydro-test m 3/hr 340

4.3 Re -used from PWT (Note 4) m 3/hr 30

Notes:

1. 15 m3/h + additional 3 m3/h demineralization for Train 3 vs 27m3/hr for Trains 1 & 2. 2. Assumption that the NPF RO Plant Refurbishment Program, for 3 +1 availability with new RO Unit 6 installed, figure represents the nameplate capacity (1500 m3/day) available. It is proposed to demolish this unit at the end of the Tangguh Expansion Project. 3. The permanent water supply treatment will be used for both the construction phase and for water supply for Train 3. This shall be a modular system and incorporated in the polishing unit for effluent PWT.

4. For 3T operation, total PWT effluent is approx. 60 m3/hr for which 30 m3/hr is re-used.

5. Design Nameplate Capacity for each Desalination Package (MVC) is 28m3/hr supplied from 2+1 available units.

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3.2.2. Firewater Demand

The existing plant (Trains 1 & 2) is divided into 15 fire risk areas and the design capacity of the firewater system is based on supplying the largest risk area, 1040 m3/hr. TEP will add fire risk areas. The current design assumption is that as none of these fire areas are any greater than the existing largest fire risk area, the firewater design capacity will remain at 1040 m3/hr. Therefore, based on the design philosophy that once a fire occurs within a fire risk area it will not spread out of that area, no additional firewater supply capacity will be required by TEP. However, TEP fire water design capacity need to be verified in Detail Engineering Design based on the likely plant layout, potential fire cases and the ability for some incidents to potentially escalate into adjacent areas. This may result in a larger maximum fire water demand and therefore potentially modifications to the existing pumps or new fire water pumps. Since the water demand for fire water case is significantly higher than water demand for normal operation, sizing of equipment will be based on provision of 100% firewater demand. Sparing concept of N+1 shall also be considered. Therefore, in existing facility, the provision of seawater intake pump/desalination systems is 3 x 50% (of firewater demand), with consideration that in normal condition 1 pump is operated to fulfill the normal operation water demand, while in case of fire water case emergency 2 pumps will be operated to fulfill fire water demand. Another 1 pump is provided as spare, in case any failure of one of the pump during fire water case. Full capacity of the pump shall be operated even in normal condition, to maintain the efficiency and performance of the pump, the excess sea water produced by the pump is re-routed to the common outfall for discharges.

3.2.3. Desalination Option

In this option, the water supply is supplied from a new seawater desalination system, as per the existing water supply. The new water supply system design would be segregated from the existing system, with provision for crossover lines between the existing and the new water supply system to provide operational flexibility. The existing seawater intake/desalination system consists of 3 x 50% seawater supply pumps, an electro-chlorination unit, 3 x 50% desalination plants and 1 x 100% fresh water tank. The seawater supply pumps feed the electro-chlorination unit where the seawater is dosed 20 minutes every 4 hours. The normal dose is 1.5 ppm in 1040 m3/hr water and the shock dose 3.0 ppm in 1040 m3/hr water. One of the three supply pumps is diesel engine driven

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to ensure system availability, as these pumps provide backup for the firewater system. The other two pumps are motor driven. The dosed seawater is then fed to the desalination plants which produce fresh water from seawater by the mechanical vapor compression (MVC) process. The desalinated water is stored in the desalinated water tank. The design capacity of the storage tank is four hours firewater plus one week’s plant use, excluding potable water demand. Since the desalinated water tank is commonly used as a source for other services, the pumps for such services take their suctions above the required fire water storage level so that the required amount of fire water is reserved at all times. The desalination system will standardize existing system; however a more optimized approach has been assessed during FEED, which instead of duplicating the provision of 3 x 50% sea water supply pump, an option to design an integrated system for three trains operation is being considered. Therefore, for TEP, the provision of additional sea water supply pump will be based delta of water volume required to cover the water need for total three train operation; rather than directly provide a single capacity for one additional train. A concept of pre-treatment system for desalination was also assessed during FEED. The objective of adding pre-treatment system is to increase the efficiency of the desalination unit and minimize the volume of brine reject discharged to sea. Qualitative advantages of using Desalination:  Familiarity of operations on site.  Lower schedule risk.  Less risk of project and operations disruption due to the sensitivity of groundwater usage (e.g. local community villages complain that their water usage is being disrupted or Regent wants to change price).  Less implications to Partners, Government of Indonesia (GOI) or stakeholder.  Less uncertainties, in terms of permit, reserve and potential social issue. Qualitative disadvantages of using Desalination:  Increase of brine discharge into Bintuni Bay.  High in capital and operating expenditures.

3.2.4. Groundwater Option

For TEP, the potential to use of groundwater as a replacement or supplement to desalination system was assessed. The estimated continuous demand of utility water, including for personnel use, is approx. 65 m3/h for three trains operation.

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However, it should be noted that the actual amount of abstraction will be subject to determination and approval by the Ministry of Environment and Forestry (MoEF), based on their technical assessment of the results of the proposed investigation program. If the approved amount is less than TEP requirements, then groundwater would be used as a supplement to, rather than a replacement for desalination. In addition, TEP would still need to construct, install and operate desalination system to mitigate against the potential of having to stop groundwater extraction in case of concerns from the local community of perceived impact to their won groundwater supply.

Based on existing groundwater analyses from the Tangguh LNG area, groundwater from 150 – 300 m depth may need treatment to remove dissolved iron and manganese, and possibly ammonia.

The presence of iron and manganese concentrations in water is not known to cause health problems. These elements are primarily associated with aesthetic factors, such as unpleasant taste and odor, and domestic problems, such as staining of laundry and fixtures, and can potentially be a serious problem for industrial uses. Another potential problem is the growth of iron bacteria within distribution mains.

The selected method for the removal of iron and manganese is oxidation by aeration continued by rapid sand filter and then disinfection by addition of chlorine.

Qualitative advantages of groundwater supply  Significant reduction in the volume of brine wastewater discharge into Bintuni Bay.  Better energy efficiency.  Reduction in emission of greenhouse gases.  Considerably lower capital and operating expenditures.

Potential risk in the development and use of groundwater supply  Potential seawater intrusion.  Potential adverse effect on nearby community water supply.  Potential ground subsidence.  Uncertainty of groundwater reserves.  Water-table decline.  Potential construction problems leading to well collapse or failure.  Refusal or delay of permit approval.  Management of potential shallow gas.

A comprehensive study has been done to assess potential seawater intrusion, impacts to community water supply and ground subsidence. The study result confirms that the impacts will not be significant as long as the groundwater supply system is designed as recommended, such as extraction from more than 150 meter depth and install steel casing for protection at water depth of over 150 m.

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Although groundwater offers advantages for water supply, the desalination water plant would need to be kept as back-up during normal conditions. It would be necessary to maintain at least one of the pumps and the electro-chlorinator in operation to ensure that the intake channel and outfall are kept flushed in order to:

 Avoid build-up of sediments;  Inhibit marine growth;  Maintain readiness of the pumps as backup to the firewater system; and  Control effluent temperature to be <2ºC above intake temperature.

As required in the AMDAL, to confirm the groundwater reserves and to submit the groundwater extraction permit at some point in the future, the pumping test need to be conducted. Pumping test will be done in one production well with depth of 400 m and one monitoring well with depth of 150 m for 10 days pumping test will need to be drilled. Should the test indicate the positive result and groundwater option is confirmed to be feasible, Tangguh would drill additional production wells up to 400 m depth and additional two monitoring wells up to 300 m depth, to monitor potential impact of seawater intrusion and land subsidence, also to monitor the availability of groundwater resource for the community.

However, during the preparation of pumping test, shallow gas issue was encountered in the area where the test well will be drilled. This discovery added additional risks and uncertainty for the groundwater option, which are drilling uncertainty and HSSE risk of a blowout. To mitigate the drilling and blowout risk, the type of drilling rig for testing and later on for drilling of groundwater well would need to be changed. This change however, results in significantly higher capital expenditures which erodes significantly the CAPEX savings when compared with the desalination option. Due to the shallow gas issue and other uncertainties, including potential high capital expenditures it is unlikely that groundwater supply will be used for TEP.

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4. GHG Management Plan

4.1. CO2 Emission from Tangguh LNG Plant Operation

CO2 emissions from existing T1/2 operation are generated from flaring, fuel gas, gas to Acid

Gas Incinerator (AGI)/flare, vehicle fuel, diesel and aviation fuel (<1%) with total CO2 emission as shown in Table 5 below.

Table 5 – CO2 from LNG T1/2 Operation

Year CO 2 (million tons) 2013 5.15 2012 4.66 2011 4.51 2010 4.56 2009 2.50

Based on above data, it is estimated that CO2 emissions which will be generated from LNG Train 3 (one train) operation are as follow:  Flare = 0.25 million tons/year (8.1% of total);

 Fuel gas = 0.79 million tons/year (25.5% of total);

 Gas to AGI/flare (CO2 from wellhead) = 1.96 million tons/year (63.2% of total);

 Fuel consumption and CH4 emission (converted to CO2) = 0.097 million tons/year (3.2% of total); and

 Total CO2 from Train 3 operation = 3.1 million tons/year. GHG generated from drilling reinjection and landfill can be considered as negligible compare to total GHG generated from other sources listed above, particularly the AGI (CO2 from feed gas) which contribute 63.2% of total CO2 from Train 3 activity.

4.2. Tangguh Operation and TEP GHG Management Plan

Tangguh commitment for GHG management as listed in this section is already included in the AMDAL. Hence the implementation of the following commitments is mandatory as it is already committed under the AMDAL, a legally binding document. A. Flare Based on current Tangguh LNG normal operation (T1/2), the amount of flared gas is less than 3% of feed gas amount. According to Ministry of Energy Resources and Mineral (ESDM) Regulation No. 31 Year 2012, flared gas optimization study and approval from

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related department are required if the amount of flared gas is more than 3% of feed gas amount.

T3 is designed with improvements by incorporating lesson learned from existing T1/2 operation in the efforts of reducing flare. Management efforts that will be done to maintain air quality from flaring emission are as follows:

 Minimizing flaring emissions by: - Implementing BOG (Boil of Gas) recovery from LNG storage facility and loading system; - Designing plant facility that will enable the transfer of process gas to a flaring system for safe burning and emergency conditions including relief valves, blowdown valves and operation/maintenance vent; - Optimizing Turnaround (TAR – LNG Plant major maintenance activity) frequency and minimizing numbers of plant shut downs, whether planned (gas turbine inspection) or unplanned; and - Maintaining the balance of the fuel management system as a whole (supply and demand) to reduce flaring emission by calculating fuel balance from whole system (existing plant and new plant).  Conducting calculation and recording of flaring amount.

Flaring reduction effort has been in place for existing operation, Figure 9 shown the flaring reduction since 2010-2015.

Figure 9 – Flaring from LNG T1/2 Operation

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B. Air Emission from Process Activity

Activities which will be conducted to manage air emission from process activities are:  Utilizing energy efficient design, such as Heat Recovery Steam Generator (HRSG) to recover excess heat from gas turbines to produce high pressure steam;

 Utilizing more efficient gas turbines;

 Utilizing Dry Low NOx burner for gas turbines;

 Installing and operating Continuous Emission Monitoring System (CEMS) at stacks with reference to applicable regulations;

 Conducting CEMS monitoring recording;

 Providing adequate facilities for safe monitoring and/or sampling; and

 Conducting calibration and CEMS maintenance to ensure CEMS is working properly.

C. Green House Gas Emission LNG production has the potential to reduce GHG emission on the consumer side, compared to other commonly used energy sources such as coal and oil.

Theoretical offsets by displacing coal-fired generation

It is important to note that if the T3 gas output displaces coal-fired generation, there should be a net CO2 reduction or offset of more than nine million tons carbon dioxide equivalent per year

(tCO2e/y) as set out below.

Assumptions and estimates: 1 billion m3 (Bm3) per year of natural gas is sufficient to run 1 GW of CCGT capacity at 7000 hours per year (h/y) 730,000 tons LNG = 1 Bm3 natural gas 3,800,000 tons LNG / 730,000 tons/Bm3 = 5.2 Bm3 natural gas Round down to 5 GW CCGT capacity 5 GW x 7000 h/y = 35,000 GWh/y Power generation emissions factors: Coal : 900 tCO2e/GWh Gas : 550 tCO2e/GWh

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Emissions for 5 GW running 7000 h/y Coal : 35,000 x 9001 = 31.5 Million tCO2e/y Gas : 35,000 x 550 = 19.25 Million tCO2e/y Reduction = 12.25 Million tCO2e/y Total emissions from T3 operations = 3.1 million tCO2/y (BP estimate) Net reduction or offset = 9.15 Million tCO2e/y

On the other hand, the low fuel emission on the consumer side means a concentrated GHG

emission on the LNG processing side. 10% to 15% CO2 produced by Tangguh operational

activities is from the feed gas. The higher the production rate of LNG, the higher CO2 level produced.

Tangguh LNG has conducted a study to evaluate a number of alternatives to significantly reduce the GHG emission produced by LNG plant through increasing energy efficiency, excess heat utilization and re-utilization of hydrocarbon that is usually emitted to the air, to be processed in the plant. A few examples are listed in the flare and air emission from process activity management above.

Actions to be taken to monitor GHG emission are as follow:

 Conducting calculation and recording the amount of GHG emission (CO2 and CH4) from all activities in LNG plant and its supporting facility; and  Conducting recording of fuel consumption, including diesel and aviation fuel.

Tangguh will continue to monitor the development of Indonesian regulations and new

technology on CO2 and GHG management.

4.3. Other GHG Management Options

During its operation, Tangguh has assessed other management options for GHG, such as offset and sequestration. Follow up action on those other options has also been taken by Tangguh. However, the final conclusion that generated from those studies is, both options are not feasible to be conducted.

4.3.1. Sequestration

- Tangguh had completed a comprehensive desktop study based on the available information on potential options for sequestration in 2002 – 2003 involving university experts and consultants. The reports were presented to MOE and the study indicated that the sequestration may technically feasible, but a series of field test is required to confirm the assessment.

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- The desktop study need to be confirmed with a series of field test including seismic program, which cost around $30M (at that time – c.a. 2003). Tangguh had proposed the field test study to SKKMIGAS at that time, but was rejected. - There is no mandatory requirement from Indonesian regulation and international standards, nor approval from SKKMIGAS for carbon sequestration. Therefore it is found to be challenging to implement the option as there is no strong basis of reinforcement, particularly in the PSC scheme where Tangguh LNG is currently operated. - Government permits would be required for sequestration and there is no regulatory basis in Indonesia to support this permit application. - Sequestration is economically not feasible; the estimated cost in 2002 is >$200 M, it would be 3 to 4 times higher now. Therefore it is concluded that the sequestration options is not a feasible option for Tangguh.

4.3.2. Offset

A study has been conducted by Forestry Consultant to review the feasibility of the offset option. The result of the study is summarized as follow: - During T1/2 development, the study considered an initial offset approximately 5- 10% of Tangguh’s emissions from venting by applying a similar mechanism like the Reducing Emissions from Deforestation and Forest Degradation (REDD) program on about 50,000 to 100,000 ha of forest, but did not make it as commercial project. Based on this proposed mechanism, Tangguh will allocate budget and resources required

to preserve the forest and use the forest carbon to offset of CO2 emission. - The calculation used for the assessment at that time was based on example from a forest location in Bintuni Bay, it is concluded that the project’s carbon stock over 24 years is 4.1 million tons CO2, with a carbon flow of approximately 225,000 tons CO2/year starting in 2016. If compared to Tangguh emission of 5 million tons CO2/year of venting emissions from existing Train 1 & 2, this represents about 5%. - The estimated cost at that time are as shown in Table 6, but with this budget and

efforts, the delivered offset will be only 3 to 5 million tons CO2 (over 20 years), while

Tangguh is generating about 5 million tons CO2/year.

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Table 6 – Estimated Cost of Offset Program (at that time)

Feasibility Costs $150,000

Project Development Costs $3 million

Ongoing Costs $7.6 million (over 20 years)

Trust Fund Contributions $2/tons CO2 (for example)

Delivered Offsets 3-5 million tons CO2 (over 20 years)

Estimated Price / tons $4-6/tons CO2

Considering that this offset strategy will only contribute to 5-10 % of Tangguh existing CO2 emission, while it requires a huge efforts and a dedicated team to develop detail plan, get all the stakeholders engagement and alignment, secure all required permits and approval from government, develop and maintain it over the 20 years period, then the carbon offset option is also deemed not feasible, as it will only represent a very small percentage of the CO2 generated.

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5. Additional Information to AMDAL

5.1. Residual Impact Management

The following table lists those environmental components for which the impact significance was assessed as Moderate and Major, and how the residual impacts will be managed.

Environmental Significance Short-term Management and Monitoring of Impacts Residual Impact No Parameter of Impact Source of Impact Component of Impact GAS EXPLOITATION 1 Noise Increase in Underwater Noise Production Well Drilling Moderate Sighting of marine mammal around production well drilling No residual impact is expected, considering the impact will location and recorded; only occur of short period of time and occur only in localized Fishery and marine mammal survey to be conducted once area around the drilling site. In addition, based on existing during drilling sighting data, marine mammals (e.g. dolphin) are still sighted swimming around the production well drilling area. 3 Marine Biota Changes in Nekton Diversity Dire ct Impact of: Moderate Sediment quality monitoring to be conducted one time after No residual impact is expected for changes in nekton (Including Marine Mammals) - • Overboard Discharge of Drilling Mud activity completion, at one sampling location at discharge diversity as the result of drilling activity (See explanation Construction Phase and Drill Cuttings site and one at control site. No. 1 above). Derivative Impact of : However, for overboard discharge, a post monitoring • Increase in Noise from Production activity has been set to check the sediment quality around Well Drilling activities discharge area for any residual impact as the result of overboard activity. Changes in Nekton Diversity Existence of Offshore Platform Moderate Not required as the platforms have a positive impact on The impact of existence of offshore platform is categorized as (Including Marine Mammals) - Nekton diversity. positive impact as it becomes a new habitat for nekton. Construction Phase - Operation Hence, although it may have residual impact, but since the Phase impact type is positive, no management step is required. LNG PLANT & MARINE FACILITIES

1 Greenhouse Gas Increase in CO2 Emissions • Flaring Major Management efforts that could be done to maintain air The CO2 emission generated from Tangguh LNG activity is • Electrical Power Generator (Gas quality from flaring emission are as follows: deemed as significant due to its long term duration, global Turbine)  Minimizing flaring emissions by: impact extent and sensitive receptor. Tangguh has already Boiler implemented GHG reducing processes and procedures in its •  Implementing BOG (Boil of Gas) recovery from LNG • Acid Gas Incinerator (AGI) existing operations and will ensure that the new operation is storage facility and loading system; managed in a similar way.  Designing plant facility that will enable the transfer of However it should be noted the T3 gas output displaces process gas to a flaring system for safe burning and coal-fired generation, there should be a net CO reduction or emergency conditions including relief valves, blowdown 2 offset of more than nine million tons carbon dioxide valves and operation/maintenance vent; equivalent per year.  Optimizing Turnaround (TAR – LNG Plant major maintenance activity) frequency and minimizing numbers of plant shut downs, whether planned (gas turbine inspection) or unplanned;  Maintaining the balance of the fuel management system as a whole (supply and demand) to reduce flaring emission by calculating fuel balance from whole system (existing plant and new plant); and  Conducting calculation and recording of flaring amount.

Activities which will be conducted to manage air emission from process activities are:  Utilizing energy efficient design, such as Heat Recovery Steam Generator (HRSG) to recover excess heat from gas turbines to produce high pressure steam;  Utilizing more efficient gas turbines;  Utilizing Dry Low Nox burner for gas turbines;  Installing and operating Continuous Emission Monitoring System (CEMS) at stacks with reference to applicable regulations;  Conducting CEMS monitoring recording;

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Environmental Significance Short-term Management and Monitoring of Impacts Residual Impact No Parameter of Impact Source of Impact Component of Impact  Providing adequate facilities for safe monitoring and/or sampling; and  Conducting calibration and CEMS maintenance to ensure CEMS is working properly. 2 Noise Increase in Noise Level • Land clearing Major The EPC contractor will be required to develop detailed The high noise impact will only be generated from • Construction of LNG Plant and its mitigation plans in order to implement the noise construction activity, which will occur for a finite period of Supporting Facilities requirement specified in Appendix 1 of the RKL-RPL which time (max. 5 years). Once the activity is completed, the high is to ensure noise levels at neighbouring communities will noise impact will be eliminated and there will be no residual not exceed 55 dBA during the daytime and not exceed 45 impact. dB(A) at nightime 3 Hydrology Changes in Creek Morphology Site Preparation Moderate As per the RKL-RPL: The impact is predicted as short-term; mainly occur during a. an earthwork plan map will be developed which will construction period (i.e. site preparation activity). It is also provide information about: predicted that after site preparation activities are completed, 1) Land clearing plan; drainage ditches are able to replace the natural drainage 2) Cut and fill plan including amount of excavated flows that disappeared. Hence, no significant residual and stockpiled soil; impact is expected. 3) Initial and final topography from site preparation; Visual monitoring will be carried out post construction to and ensure that the impact is short-term as predicted. 4) Natural drainage pattern and drainage management plan during Earthwork including erosion control. b. Conduct land clearing and site preparation only at designated area. c. Maintain riparian area with the minimum of 100 meters for large river and minimum 50 meters for small river in accordance with Government Regulation No. 38 Year 2011 d. Minimise natural flow pattern change of Ephemeral. e. If Earthwork at creek is inevitable then culverts, bridges and artificial drainage or other method will be installed. f. Ensure culverts, bridges, drainage or other facility can accommodate peak flow of creek/river. g. Design drainage pattern at affected area to transfer surface run off to natural flow. h. Construct sedimentation pond in the downstream affected area before receiving water body to minimise impact. i. Build facilities to reduce run off flow rate hence minimizing river morphological change. j. Conduct revegetation (grass/cover crop) at cleared area which will not be used yet for construction activity. Increase in Creek Water Flow Increase in Surface Water Runoff, Moderate As above Increase in creek flow rate is derivative impact of changes in

Rate Changes in Drainage Pattern and Creek creek morphology, increase surface run-off and changes in Morphology drainage pattern. The change may occur permanently, however the artificial drainage channel will immediately replace the natural drainage flow, hence no residual impact is expected. Visual monitoring will be carried out post construction to ensure that the impact is short-term as predicted. Increase in Surface Water • Land clearing Major Refer to increase in soil erosion below. The impact is predicted as short-term; mainly occur during Runoff • Site Preparation construction period (i.e. site preparation activity). It is also Cut and fill predicted that after site preparation activities are completed, drainage ditches are able to replace the natural drainage flows that disappeared. Hence, no significant residual impact is expected. Visual monitoring will be carried out post construction to ensure that the impact is short-term as predicted.

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Environmental Significance Short-term Management and Monitoring of Impacts Residual Impact No Parameter of Impact Source of Impact Component of Impact Changes in Drainage Pattern Site Preparation Moderate Not required The impact type is categorized as permanent, however the artificial drainage channel will immediately replace the natural drainage flow, hence no residual impact is expected. 5 Soil Increase in Soil Erosion Increase in Surface Water Runoff Major a. Develop land clearing and site preparation activity plan The potential impact will be major during construction by considering erosion mitigation factor. period, particularly during land clearing and earthwork. b. Earthwork activity will start after main facility of erosion However, re-vegetation effort and proper drainage system and sedimentation control is available. installation will be implemented in disturbed areas. c. Manage drainage pattern and sediment control by: Therefore, although the impact is major, but it will only 1) Create temporary or permanent drainage and construct occur in short term, hence no residual impact is expected. dike and water channel; 2) Ensure water channel and/or creek is not blocked; 3) Provide Retaining Wall with wall slope more than 2:1; 4) Install jute net or plant cover crop to maintain wall stability especially in the area with wall slope ratio more than 3:1 or wall/slope height more than 3 meters; 5) Install Sediment Trap in various drainage locations; 6) Provision of Sedimentation Pond at downstream of drainage before entering receiving water body; 7) Conduct routine clean-up for trapped sediment in Sediment Trap and Sediment pond; 8) Sediment pond volume shall be able to control TSS during peak rain condition (hour); 9) If sediment pond volume is ineffective then other control efforts need to be done; and 10) Conduct revegetation (grass/cover crop) at cleared area which will not be used yet for construction activity in the period of minimum 3 months. Using local Papua plants. d. Conduct routine inspection to erosion and sedimentation control facility to ensure those facilities in maximum function, especially after rain. 6 Surface Water Increase in Content of Total Increase in Soil Erosion Major See above. The impact will heavily occur during construction period, Quality Suspended Solids (TSS) particularly during land clearing and earthwork. However, re-vegetation effort and proper drainage system installation will be implemented in disturbed areas to manage the erosion issue. Therefore, although the impact is major, but it will only occur in short term, hence no residual impact is expected. 7 Terrestrial flora Changes in Land Cover Land clearing Moderate Mitigation measures are detailed in the Biodiversity Action The impact will only occur in limited area to be cleared, but Plan. may occur permanently due to the permanent changes made Changes in Structure and Changes in Land Cover Moderate Mitigation measures are detailed in the Biodiversity Action for permanent building. Therefore, residual impact may be Composition of Flora Species Plan. expected for flora species, such as change in structure, composition and diversity of flora species. However, these Changes in Flora Species Changes in Structure and Composition of Moderate Mitigation measures are detailed in the Biodiversity Action impacts will be mitigated as set out in the Biodiversity Diversity Flora Species Plan. Action to ensure that the ADB SPS requirements for Biodiversity Conservation and Sustainable Natural Resource Management are achieved. 8 Terrestrial Fauna Changes in Wildlife Habitat Land clearing Moderate Mitigation measures are detailed in the Biodiversity Action Impact to fauna species during construction period may Plan. occur due to increase of noise level from the use of equipment and habitat reduction due to land clearing. Changes in Fauna Species • Changes in Wildlife Habitat Moderate Mitigation measures are detailed in the Biodiversity Action Distribution • Increase in Noise Levels Plan. The impact due to increase of noise level will only occur during construction period (short-term) and considering the Changes in Fauna Species • Changes in Fauna Species Distribution Moderate Mitigation measures are detailed in the Biodiversity Action ability of animal to move to other area to avoid disturbance, Diversity • Changes in Structure and Composition Plan. no residual impact is expected. of Flora Species The impact of changes of fauna species in distribution and diversity may occur due to land clearing activity, considering the changes of the land clearing will occur permanently, the impact may also occur permanently.

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Environmental Significance Short-term Management and Monitoring of Impacts Residual Impact No Parameter of Impact Source of Impact Component of Impact However, considering the surrounding forest also has similar forest type with the area to be cleared, the animal can move to the similar area with their habitat and hence no significant residual impact is expected. Nonetheless, these impacts will be mitigated as set out in the Biodiversity Action to ensure that the ADB SPS requirements for Biodiversity Conservation and Sustainable Natural Resource Management are achieved. 9 Marine Biota Changes in Nekton Diversity Direct Impact of: Moderate The RKL-RPL provides detailed information on the Impact to nekton and marine mammal species due to the (Including Marine Mammals) • Sea Transportation for Workforce, management measures that will be taken to mitigate vessel activity will be potentially significant during Equipment and Materials impacts. construction period. The impact will still occur during • Loading and Transportation of LNG operation, but the frequency is decreased compare to the and Condensate short term construction period. In addition, the discharge of Derivative Impact : wastewater may also have impact to the nekton and marine • Increase in Ammonia Concentration mammal. However, considering the ability of nekton and Decrease in Benthos Abundance Dredge Material Disposal (Construction Major The RKL-RPL provides detailed information on the marine mammal to move away to avoid disturbance and Phase) and Maintenance Dredging in the management measures that will be taken to mitigate based on the sighting and survey that were conducted by Operations Phase impacts. current operation, marine mammal and nekton are still found to be swimming near the vessels and also shown consistent presence in Bintuni Bay, then no significant residual impact is expected. In addition, these impacts will be mitigated as set out in the Biodiversity Action to ensure that the ADB SPS requirements for Biodiversity Conservation and Sustainable Natural Resource Management are achieved.

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5.2. Potential Risks to the Project from Climate Change Impacts

In general, the Indonesian territory lies along the equator and this is a key factor that contributes to the weather and climate condition in the country. Indonesian geography along the equator has an increased threat of tropical cyclones. Basically tropical cyclones are formed in the area with the position of 10° south latitude and 10° north latitude and rarely occur in equatorial regions. The impact to the Indonesian region is fairly low, however strong winds, high waves, and changes in rainfall patterns do occur during the cyclones in the north and south part of the equatorial margins.

The climate in Indonesia is divided into three climatic patterns, which are generally illustrated as shown in the picture below (Figure 2). Region A experiences the Australian monsoon and occurs in most parts of southern Indonesia, region B shows the semi-monsoon condition, while region C (indicated with dashed red line) has the anti-monsoon climate / Indonesia through flow.

Figure 10 Map of the Indonesian Climate Region (Edvin A. et al 2003 in LAPAN/National Aviation and Astronomical Agency, 2009 : www.dirgantara-lapan.or.id/apklimatling/Artikel1/artikel1.pdf)

It has recently been alleged that there has been a major change in climate and weather conditions, with impacts to human life such as a decrease in food production, more polluted areas, outbreaks of disease, rising of sea level, longer dry seasons, and a shorter rainy season but with higher intensity. These conditions are suspected to occur in most parts of Indonesia, including eastern Indonesia/Papua.

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Papua’s forest area accounts for 30% of total forests in Indonesia (Forestry Dept., 2011). Approximately 85% of Papua and West Papua is still covered with intact forest. Deforestation in Papua over the last decade has totaled 1% of the national total. Significantly, over 47% of Papua forest is classified as lowland rainforest, making Papua province home to the largest remaining tracts of lowland forest in Indonesia. 20% of Papua’s forest estate has been designated for conservation and protection. This is much greater than any other province in Indonesia (USAID/Indonesia, 2009). The region is known to have a very rich biodiversity. It hosts 223 species of mammals, 602 species of birds, 223 species of reptile, 11 species of amphibian, 400 species of fishes, and 1030 species of plant. Form all those entire identified species, 41 species among of them are listed as threatened species (source: BKSDA Papua/Conservation of Natural Resources Agency). Freshwater resources per capita are abundant compared to the other island in the country.

According to recent studies, Papua is also fairly highly exposed to climate variability and climate change and has regularly experienced extreme weather conditions. For example, rains do not arrive when they should, islands are being flooded, the reduction of ice concentration in the Puncak Jayawijaya (Jayawijaya Mountain) and malaria is appearing in highland valleys where the temperature was previously too cool for mosquitoes. Weather- and climate-related disasters that have severe adverse effects on the lives of people, and on the economy, include: (i) landslides and erosion, especially at the highlands; (ii) flooding in most parts of the island, especially in the lowland; (iv) droughts in some parts of the island which often associated with El Niño conditions. Recent observations are consistent with those expected to result from global warming. In the future, sea levels are expected to rise steadily.

Climate projections for 2050 are shown below. The temperature is expected to rise steadily through to the middle of the 21st Century. Precipitation changes are less certain but floods and droughts may increase in intensity between current dates and the middle of the century.

The vulnerability and risk profile from natural disasters in Indonesia region is presented in the Figure 10 below.

The characteristic most applicable to Tangguh Expansion due to the climate change impact are potential land/coastal erosion, landslide, flooding and moderate freshwater availability. Those aspects are indicated to be the characteristics which relate to the Papuan environment.

Potential impact of climate change on the Tangguh LNG facilities and operations have been studied as part of the project technical design and development. This includes considerations of 100 year Tsunami events in the marine facilities design, high rainfall in most of the area, tidal waves and coastal abrasion due to natural phenomena in the area.

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Table 7 Climate Variability scenario for 2050 using MAGICC/Model for the Assessment of Greenhouse-gas Induced Climate Change, and SCENGEN/Scenario Generator model from IPCC. (Source: LAPAN/National Aviation and Astronomical Agency)

Temperature Sea level Precipitation increasing (°C) increasing(cm)

0.9 - 1.45 12.5 - 16 Variability : 5.20 - 8.63%

Changes probability : 0.68 - 1.0 (potentially cause floods and or droughts)

Figure 11 Indonesia Disaster Risk Profile (Source : UNISDR http://www.preventionweb.net/english/countries/statistics/risk.php?cid=80)

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5.3. Environmental Baseline

Environmental baseline data that were used for the AMDAL are combination of the older data and the most recent data. The use of those data combination is expected to provide a high quality baseline. The following list provides the information of the data source and timing of the baseline data that are acquired to be used for the AMDAL:

Table 8 – Environmental Baseline Data Source and Year Obtained

Data Data Source (Year Obtained)

Rainfall Tropical Rainfall Measuring Mission (TRMM) radar data and observation meteorology station (1998-2012)

Air Temperature AERMET MM5 Worldwide Meteorological Data (2002- 2011)

Relative Air Humidity AERMET MM5 Worldwide Meteorological Data (2002- 2011)

Air Pressure AERMET MM5 Worldwide Meteorological Data (2002- 2011)

Wind MM5 data by Lakes Environmental (2002-2011)

Evapotranspiration - TRMM (1998-2012) - Lister (2002) - AERMET MM5 Worldwide Meteorological Data (2002-2011)

Ambient Air Quality Baseline Sampling Dry and Wet Season (Aug and Oct 2012)

Noise Baseline Sampling Dry and Wet Season (Aug and Oct 2012)

Hydrogeology - Community Well Groundwater Quality Analysis Survey (2012-2013) - Tangguh LNG Groundwater Quality Monitoring (Oct-Dec 2010 to Jan-Sept 2011)

Soil Primary Data of Analysis of Soil Physical Properties by Soil Physics Laboratory Analysis, Soil Research Center- Bogor (July 2013)

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Data Data Source (Year Obtained)

Surface Water Quality Baseline Sampling Dry and Wet Season (Jul-Aug 2012 and Mar-Apr 2013)

Groundwater Quality Baseline Sampling Dry and Wet Season (Jul 2012 and Mar 2013)

Seawater Quality Baseline Sampling Dry and Wet Season (Jul-Aug 2012 and Mar-Apr 2013)

Wastewater Quality of Tangguh LNG Monitoring Data (2011-2013) Existing Tangguh Operation Sediment Baseline Sampling Dry and Wet Season (Aug-Oct 2012 and Mar-Apr 2013)

Oceanography PT EHI and PT Calmarine MetOcean Data Analysis (2001)

Terrestrial Biology - Environmental Baseline Study for AMDAL (2002) - Flora Fauna Survey in Tangguh Site (2007) - Flora Fauna Survey in Tangguh Site (2011)

Aquatic Biology Baseline Sampling Dry and Wet Season (Jul-Aug 2012 and Mar-Apr 2013)

5.4. Cumulative Impact Assessment for Nekton Diversity

Changes in nekton diversity (in particular marine mammals) sourced from various activities for each of the Gas Exploitation (Offshore Platform and Production Wells Drilling), LNG Plant and Marine Facilities activities as well as between activities that take place either in the same space-different time, in different space-at the same time or at different time and different space.

Some parameters of the direct impacts and derivative impacts that potentially cause change in nekton diversity (in particular marine mammals), among others are sea transportation for workforce, equipment and materials of all TEP activities (Gas Exploitation, Gas Transmission, LNG Plant and Marine Facilities); increase in underwater noise level from production well drilling activities; existence of offshore platforms; overboard discharge of drilling mud and drill cuttings; loading and transportation of LNG and condensate.

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5.5. Monitoring and Reporting

Implementation of the Environmental Management and Monitoring Plan will be monitored against the parameter provided in RKL-RPL document (Chapter III Environmental Monitoring Plan). In addition to recording information to track performance, inspections will also be undertaken to verify compliance with the EMMP and progress toward the expected outcomes.

The monitoring result will be documented; necessary corrective actions will be identified and will be reflected in a corrective action plan. The corrective action plan will be implemented and followed up to ensure its effectiveness.

Periodical monitoring report that describe progress with implementation of Environmental Management and Monitoring Plan, including compliance issue and corrective actions (if any) will be developed. The report will be submitted semi- annually, which will be posted in a location accessible to the public (e.g. ADB’s website).

5.6. Additional Information on Air Emission

- Monitoring for flares will be conducted only for opacity parameter. - Fugitive emission to air will be monitored using LDAR. LDAR procedure is already in place for existing operation and regularly conducted as part of integrity checking. Similar approach will be applied for Train 3 operation. - Open burning of waste is prohibited. - Air emission from vessel will be managed according to MARPOL requirement. - With regards to Ozone Depletion Substances, compliance to Indonesian regulation is being implemented.

5.7. Roles and Responsibilities in Environmental Management and Monitoring Plan Implementation

Vice President (VP) Project The VP Project has overall accountability for project environmental performance and is responsible for: • Providing leadership by clearly defining environmental goals and expectations; • Ensuring that the Project environmental requirements are met at all times; and

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• Ensuring that adequate resources within both BP and contractors are in place to implement planned Project environmental management and monitoring programs. Development Project Risk Manager The Development Project Risk Manager has two key roles: line support and verifying conformance to BP HSSE requirements. Development Project Risk Manager is responsible for:  Developing a project HSSE management plan that clearly articulates how HSSE risks will be systematically identified, assessed and mitigated.  Providing HSSE resources for implementation of the project HSSE management plan.  Providing the project leadership team and functional leaders with HSSE advice, guidance and assistance.  Promoting standardization and simplification of HSSE plans, processes and procedures.  Verifying that adequate HSSE training is provided.  Developing a budget for the HSSE team and ensure that HSSE team activities are conducted within the constraints of the budget. Environmental and Social Lead The Environmental and Social Lead provides assurance process and day to day environmental and social support to TEP activity. Environmental and Social Lead is responsible for: • Providing assurance that Tangguh Expansion Project is executed in compliance with applicable regulation, AMDAL and environmental requirement. • Providing advice to Project leaders in abnormal and emergency situations related to environmental requirements and regulations. • Providing supervision to Contractor’s management, especially the Contractor’s Environmental and Social Lead in managing environmental aspects during construction activities. • Ensuring the environmental requirement in the contract is implemented by Contractors • Developing all environmental report to internal BP and Government Environmental Site Lead The Environmental Site Lead will provide day to day site environmental support to TEP activity. Environmental Advisor is responsible for: • Ensuring the daily site construction activity comply with environmental requirement as stipulated in contract.

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• Providing day to day supervision and advice to Contractors related to environmental issues and permit compliance during construction activity • Reviewing environmental monitoring performance and provide advice to improve the performance • Act as Single Point Responsible (SPR) during external environmental audit and/or visit conducted by BP and external Parties (Lenders and Government official) • Providing administrative support for development of environmental report • Supporting Environmental and Social Lead to ensure the environmental requirement is implemented

VICE PRESIDENT PROJECT

DEVELOPMENT PROJECT RISK MANAGER

HEALTH AND SAFETY HEALTH AND SAFETY PROJECT HSE TEAM REGULATORY ENVIRONMENTAL TEAM LEADER - TEAM LEADER - LEADER COMPLIANCE LEAD AND SOCIAL LEAD ONSHORE OFFSHORE

ENVIRONMENTAL SITE LEAD

Figure 12 (Tentative) Project HSE Organization Chart

5.8. Stakeholder Engagement Process

National Level Upon agreed by BPMIGAS, Ministry of Environmental (MoE) and BP issued an announcement through national and local media on 14 May 2012.

Province and Regency Level The local environmental department from Bintuni and Fakfak regencies are expected to “own” the activities by formally inform the designated villages and districts. Prior to the consultation/meeting, Environmental and Community Affairs team from BP will

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be working closely with these regencies to make all necessary preparation e.g. to prepare the notification letter and send them to designated villages/districts. Also, to be prepared in responding community concerns and aspirations.

Village and District Level Formal notification from local environmental department will be sent to all respective villages/districts and followed by the meeting/consultation on the agreed day/date. The head of village, community leaders, youth leaders and all level of community may involve in the consultation, aiming to explain about the Tangguh Expansion and it impacts as well as to listed to community concern and demand. In the certain villages/district, the meeting may take 2 days (meeting will be subject to community readiness). In this case the team will stay over-night. The aim of public consultation is not to instantly answer or response to all community concerns and aspiration, but to compile them and to be included in the AMDAL Term of Reference for further discuss in AMDAL commission. Community Affairs team will identify issues and concern in some villages.

5.9. Project Decommissioning Plan

The Tangguh Expansion Project includes the Abandonment & Site Restoration (ASR) Plan (the ASR Plan) with the main objective being to prepare a conceptual program and cost estimate for abandonment and site restoration of the production & processing facilities consisting of the offshore facilities such as platforms, wells, conductors, risers, subsea pipelines, subsea cables and the onshore facilities such as LNG plant, Onshore Receiving Facilities, storage tanks and other supporting facilities. BP Berau Ltd. operates the Tangguh facilities on behalf of the Tangguh Production Sharing Contract Contractors.

The abandonment and site restoration of the facilities under the ASR Plan would be implemented following the end of the field commercial production period (Field Production Cessation). In line with SKKMIGAS Regulation PTK no.040/PTK/XI/2010 the process is commenced by the Production Sharing Contract (PSC) Contractor submitting an ASR implementation plan to SKKMIGAS 2 (two) years prior to actual ASR implementation.

The conceptual ASR Plan for the LNG Plant aims to ensure:

 Protection of human health and safety;  Elimination or significant reduction in environmental impact caused by gas extraction and processing activities;  Sustainable economic development in the region; and  Avoidance of social conflict.

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The ASR conceptual plans for the offshore and onshore facilities are as follows:

1. Gas Exploitation Facilities These include production wells and offshore platforms. Production wells will be properly closed and offshore platforms will be removed.

2. Gas & Power Transmission Facilities These include subsea pipelines and subsea cables. The pipelines will carry production gas to the ORF and subsea cables will transmit electric power from shore base to platforms.

Pursuant to Clause 12 Minister of Energy and Mineral Resources Regulation No. 01/2011, the subsea pipelines and subsea cables will be flushed and abandoned in place.

3. LNG Plant Facilities. Most of LNG Plant and supporting facilities will be removed. However, discussion with stakeholders, especially traditional land owners and government, will be ongoing to determine if any of these facilities will be left behind to be used in the future. A clear plan and legal understanding of the transfer of responsibility for the facilities will be determined through this process. Some reclamation and replanting of the areas is expected and will be completed prior to release.

4. Sea Port Facilities These include LNG jetties, combo docks, construction jetties and marine shipping facilities. Similar to the LNG Plant and support facilities, these can be removed or remain for other future land uses. Discussion with stakeholders will determine this. A clear plan and legal understanding of the transfer of responsibilities to a responsible party for the facilities will be determined through this process.

5.10. Offsite Facility Requirement

For offsite supporting facilities that is outside the AMDAL study boundary, such as platform fabrication, pipeline fabrication and quarry source, Tangguh will ensure that the appointed facilities has proper environmental document to conduct their activity, including relevant license and approval.

5.11. List of Chemical Used in Tangguh Operation

List of chemical used in Tangguh operation is provided in Attachment 2.

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6. Drilling Mud and Cuttings Management

6.1. Background

ADB’s Safeguards Policy Statement requires that “During the design, construction, and operation of the project the borrower/client will apply pollution prevention and control technologies and practices consistent with international good practice, as reflected in internationally recognized standards such as the World Bank Group’s Environment, Health and Safety Guidelines.7 These standards contain performance levels and measures that are normally acceptable and applicable to projects. When host country regulations differ from these levels and measures, the borrower/client will achieve whichever is more stringent. If less stringent levels or measures are appropriate in view of specific project circumstances, the borrower/client will provide full and detailed justification for any proposed alternatives that are consistent with the requirements presented in this document.”

The IFC EHS Guidelines “contain the performance levels and measures that are generally considered to be achievable in new facilities by existing technology at reasonable costs. Application of the EHS Guidelines to existing facilities may involve the establishment of site- specific targets, with an appropriate timetable for achieving them.

The applicability of the EHS Guidelines should be tailored to the hazards and risks established for each project on the basis of the results of an environmental assessment in which site-specific variables, such as host country context, assimilative capacity of the environment, and other project factors, are taken into account. The applicability of specific technical recommendations should be based on the professional opinion of qualified and experienced persons.

When host country regulations differ from the levels and measures presented in the EHS Guidelines, projects are expected to achieve whichever are more stringent. If less stringent levels or measures than those provided in these EHS Guidelines are appropriate, in view of specific project circumstances, a full and detailed justification for any proposed alternatives is needed as part of the site-specific environmental assessment. This justification should demonstrate that the choice for any alternate performance levels is protective of human health and the environment.

6.2. Synthetic Based Muds

The synthetic based muds (SBM) associated with discharged cuttings are not present in the water column and rapidly reach bottom sediments adsorbed onto the drill cuttings. SBM do not present a risk to other aquatic fauna including the endangered species that could be near drilling operations, although experience demonstrates that such fauna are not likely to remain near the rigs during drilling operations in any case. The NADF criteria established in the IFC guidelines is a historic catch-all approach which does not take into account the low toxicity of 3rd generation SBM which are demonstrably environmentally safe. For example the toxicity tests carried out for the SBM used during the Tangguh Development Drilling Project (TDDP) in 2007-2009 demonstrated

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the SBM was non-toxic (refer appendix C of drilling mud and cutting management). It follows that changes to benthic communities are more likely caused by smothering than by SBM toxicity. Further, BP’s modelling and monitoring exercises have demonstrated that bottom conditions rapidly return to baseline conditions.

6.3. BP Approach

BP has applied a best practice approach to assessing the risk and establishing the mitigation measures for potential impacts from drilled cuttings and fluids waste through a BPEO (Best Practicable Environmental Option) assessment prepared by qualified, experienced, and multidisciplinary personnel for the Tangguh Expansion Project (TEP). The BPEO identifies all possible offshore and onshore options to manage the drilled cuttings and fluids waste such as tubular injection, annulus injection, discharge overboard, using Thermal Desorption Unit (TDU), or sent to 3rd party certified landfill facility. Based on the prescreening, BPEO determined 11 (eleven) potential options which could proceed to full assessment. The full assessment considered certain criteria and scoring matrices including the weighting. Such criteria comprises of elements such as safety, cost, reputation, practicability, environmental, economic, societal, and regulation. Each of the criteria has its own sub-criteria which then contributed to the final score. Therefore, a multidisciplinary team was consulted on the scoring and potential impacts from each scenario. Based on the final scoring, a ranking was established. The BPEO found that the top 3 options were onsite annular injection, overboard discharge using cuttings dryer, and onsite tubular injection. Since TEP has several drilling location which could have different restriction (water depth, development vs exploration drilling), all of those 3 options were chosen accordingly.

As discussed in the AMDAL, BP’s preferred management of drill cuttings is drill cutting reinjection (DCRI) and BP is committed to applying this technology wherever feasible. DCRI will result in minimizing the volume of cutting discharge. SBMs are expensive and only used when WBM is ineffective. The hierarchy in principle is:

1. Use of WBM with reinjection; 2. Use of WBM with treatment prior to overboard discharge; 3. Use of SBM with reinjection; and lastly 4. Use SBM with treatment prior to overboard discharge of cuttings containing residual SBM.

This hierarchy depends on the specific well, drilling conditions and permit requirements. Overboard discharge will be considered especially for the top section of the well; when the target formation for the reinjection is not yet available; and when reinjection is not technically feasible. DCRI and overboard discharge have been performed safely by BP during the TDDP in 2007-2009 which drilled 15 offshore wells.

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Permit was obtained from Ministry of Environment and Forestry (MoEF) with strict monitoring requirements.

6.4. Drill Cuttings Management

The drill cutting management plan, which includes the Indonesian Ministry of Environment and Forestry (MOEF) regulatory requirements, provides a more comprehensive site specific framework of environmental protection measures and extends well beyond the relatively simplistic guidance provided in the IFC EHS Guidelines for Offshore Oil & Gas Facilities. Notably, the MOEF takes a load-based approach to regulation of discharges, which is widely regarded as a best practice approach resulting in better environmental outcomes than concentration-only criteria. The plan includes rigorous monitoring and management of potential environment impacts and ensures compliance with the MOEF permit which includes the following conditions and monitoring requirements:

 Location specific controls to ensure environmental protection objectives are met;  Use of environmentally safe drilling fluids (Synthetic Based Mud and Water Based Mud);  Conduct LC50 toxicity, TCLP, oil content, and heavy metals test to the drilling mud and cuttings;  Use of solid control unit such as cuttings dryer, shale shaker, and centrifuge;  Discharge flowrate restrictions for each drilling section to prevent shock loading;  Total discharge volume restrictions;  Cuttings discharge line of 5 meters below sea level;  Periodical monitoring of seawater (using national standards) and sediment (using ANZECC interim sediment quality guidelines) including benthic abundance (prior, in the duration, and after the project has concluded) using 3rd party certified laboratory facility;  Conduct dispersion modeling to observe potential impact;  Conduct fishery study after the project has concluded; and  Provide baseline environmental data.

6.5. Assessment of Impacts

Modelling results indicate that the mud and cuttings from drilling will have negligible to minor impacts during drilling and disperse rapidly following cessation of the drilling activities due to the hydrodynamic conditions in Bintuni Bay.

Importantly, assessment of cutting discharge impacts have been the subject of a 2013 - 2014 Tangguh Exploration and Appraisal Project (TEAP) campaign, in which BP drilled

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2 wells in offshore Bintuni Bay using a jack up rig. A drilling cuttings dumping permit was obtained from MOEF with strict controls and monitoring requirements. Monitoring and testing of the cuttings, seawater and sediment during and after the campaign was conducted and the results show that all parameters were in compliance with the relevant permit requirements including the stringent ANZECC interim sediment quality guidelines which are considered to meet international good practice requirements, consistent with the modeling result. Examples of the results can be found in the appendix below.

The modelling results were updated with the actual drilling discharge data to confirmed that the TEAP campaign clearly demonstrate that performance levels are protective of human health and the environment and that BP’s cuttings management and the national requirements imposed on the project represent good international practice, are appropriate in view of the specific project circumstances, which primarily include the commitment to applying DCRI and the naturally high dispersing hydrodynamic conditions in Batumi Bay.

Not only do the drill cuttings have a negligible short term impact on the benthic community, which can recover rapidly, long term increases in biodiversity impacts around well infrastructure are expected.

6.6. Conclusion

The BP assessments have demonstrated that its cuttings management practices and the stringent national requirements are appropriate in the Tangguh project specific circumstances and are protective of human health and the environment. Therefore, the requirements of ADB’s SPS are met. Notwithstanding that it is worth noting that it is neither technically not financially feasible to meet the requirements of new facilities as detailed in appendix A.

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Appendix

A. Financial and technical feasibility of achieving 1% discharge requirement

Techniques to achieve the 1% discharge requirement involve complex engineering operations, high energy consumption, slow processes, and in BP’s experience is unproven technology which could jeopardize drilling operations, requires large space, and increases HSE concern. It would require additional $20 million increase in the cost of the capital cost of the current option. In addition, the technologies can result in unnecessarily higher operational costs. The result of BPEO confirmed that the treatment options included in the AMDAL are the most feasible practicable options on all aspects including achievement of the international good practice requirements of protecting human health and the environment. To change it from the current state will result in additional cost and delay for the project.

Detailed explanation for the TDU Offshore Thermal Desorption Unit, Offshore Discharge.

This unit requires significant deck space and is similar to a process plant. In addition to the space requirements of the TDU, ISO tanks are needed to take the process off critical path. This is because the system does not process at a large rate and is prone to shut down. Rather than attempting to drill and process concurrently, the cuttings are stored and the processing continues offline. There will be significant operational issues with this installation due to engineering complexity.

Key points of this option are: • Large space requirement; • Large energy consumption (2.5MW); • Unproven technology; and • Expensive

Offshore: • Big footprint; • Very heavy deck loading; • Slow process; • Storage of unprocessed cuttings required; and • Very expensive.

Onshore: • Very Expensive; and • Ship & Skip required which adds: - More boats – 2 to 4 boats increase depending on distance to shore; and

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- More lifts & handling – Safety risk increased. Note: the impact of the Bintuni Bay’s tidal currents should not be underestimated in the ability to efficiently and safely carry out a major Skip & Ship operation.

B. Modeling

Modeling result example from TEAP campaign which shows Total Suspended Solid (TSS) value within 500 m zone is between 1-7 ppm, far below national standard of 80 ppm.

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C. LC50 toxicity test for Synthetic Based Mud from TDDP campaign

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D. Sediment quarterly sampling from TEAP Campaign

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E. Seawater quarterly sampling from TEAP Campaign

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7. Tangguh Waste Management Facilities

7.1. Summary

Tangguh waste management practices are required by ADB to be consistent with international good practice. The existing facilities at Tangguh provide a good example on the amounts and types of wastes generated; the adoption of the waste hierarchy particularly in the reduction and recycling of wastes; and the implementation of stringent standard operating procedures to minimise risk to environment. High standards of occupational health and safety are rigorously applied. These practices will be continued into TEP.

Volumes of wastes generated by Tangguh are relatively small. The volumes of non-hazardous and hazardous waste generated during TEP Operations will increase by about 50% over that being generated for T1/2. The volume of non-hazardous waste will increase to 43 t/day and hazardous waste to 12 t/day. Two non-hazardous waste incinerators similar to those being used for T1/2 will be installed each with a capacity of 2 t/day and the existing landfill will be expanded. Approximately 40% of non-hazardous waste will be directed to the landfill, the remainder will be either incinerated (30%) or reused (30%). A single hazardous waste incinerator with capacity of 3 t/day will be installed for TEP. It is estimated that about 1.8 t/day of the hazardous waste, mainly liquid, will be directed to this incinerator the remainder to a 3rd party licensed contractor.

The IFC EHS Guidelines for Waste Management facilities, which sets out good international practice, also refers to USEPA and European Council Directives for Waste Management. Certain elements of these guidelines are relevant to Tangguh, and as such, a full review of these Guidelines has been made against the Tangguh and TEP waste management practices to demonstrate Tangguh applies practices consistent with good international practice. It is noted that in Indonesia there is no industrial waste classification therefore the review refers to those aspects of Municipal Solid Waste (MSW) and Industrial Hazardous waste in the context of the very small volumes and predictable waste streams generated by Tangguh. This review is presented in section 7.3 to this report and summarised in Table 9.

The conclusion is that existing and proposed Tangguh waste management practices are consistent with international good practice, as reflected in internationally recognized standards such as the IFC Guidelines.

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Table 9 Conformance to International Good Practice

International Good Practice Conformance Hazardous Waste - Waste Collection and Transport yes - Waste Receipt, Unloading , Processing And yes Storage - Hazardous Waste Incineration yes Non – Hazardous Waste - Waste Collection and Transport yes - Waste Receipt, Unloading, Processing And yes Storage - Biological and Physico– Chemical Treatment yes - Incineration yes - Landfilling yes Performance Indicators and Industry Benchmarks - Environmental Monitoring yes - Occupational Health and Safety yes - Accident And Fatality Rates yes - Occupational Health and Safety Monitoring yes

7.2. Introduction

7.2.1. Study Rationale

ADB has requested BP Tangguh to demonstrate that the Tangguh waste management facilities are consistent with international good practice, as reflected in internationally recognized standards such as the IFC EHS Guidelines for Waste Management Facilities.

The accepted standards for International Good Waste Management Practice are those presented in the IFC EHS Guidelines as discussed below.

7.2.1.1. General EHS Guidelines

The IFC EHS Guidelines are technical reference documents with general and industry- specific examples of Good International Industry Practice (GIIP), as defined in IFC’s Performance Standard 3: Resource Efficiency and Pollution Prevention. The General EHS Guidelines contain information on cross-cutting environmental, health, and safety issues potentially applicable to all industry sectors. The General EHS Guidelines are to be used

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together with the relevant Industry Sector Guidelines and state that for complex projects, use of multiple industry-sector guidelines may be necessary.

7.2.1.2. Industry Sector Guidelines for LNG Facilities

Hazardous Materials and Waste Management are described in the EHS Guidelines for Liquefied Natural Gas (LNG) Facilities under Industry Specific Impacts and Management. The LNG Guideline states that waste materials should be segregated into non-hazardous and hazardous wastes and considered for re-use/recycling prior to disposal. A waste management plan should be developed that contains a waste tracking mechanism from the originating location to the final waste reception location.

The LNG Guideline further states that storage, handling and disposal of hazardous and non-hazardous waste should be conducted in a way consistent with good EHS practice for waste management as described in the General EHS Guidelines.

7.2.1.3. Industries Sector Guidelines for Waste Management

The industry sector EHS Guidelines for Waste Management cover facilities or projects dedicated to the management of municipal solid waste (MSW) and industrial waste, including waste collection and transport; waste receipt, unloading, processing, and storage; landfill disposal; physico-chemical and biological treatment; and incineration projects. Although the scale and predictable nature of the TEP waste is very different to those of the much larger and diverse waste streams of MSW, a number of aspects of MWS management are considered relevant to Tangguh when taken into context, the industrial waste component of the guidelines has been used to assess conformance with International Good Practice.

Referral to the EHS Guidelines for Waste Management state that incineration facilities to which the Guideline applies refers to MWS which Tangguh is demonstrably not, and to Industrial Waste managed in commercial facilities or within complex projects. It is the latter reference which is being applied for this Tangguh review. The context is that the Tangguh facilities are small scale, with a predictable waste stream in terms of type and composition, remote, securely fenced and situated at some distance from communities. The Guidelines typically apply to incineration facilities in the range between 15,000 to 500,000 tons per year, approximately 20 to 750 times larger than the 650 t/yr proposed for TEP hazardous waste incinerator). Reference can also be made to European Union Directive 2010/75/EU for Industrial Emissions. The Directive applies to disposal or recovery of waste in waste incineration plants or in waste co-incineration plants for non- hazardous waste with a capacity exceeding 3 t/hour; and for hazardous waste with a capacity exceeding 10 t/day. Given that the capacity of the non-hazardous waste and hazardous waste incinerators for TEP are 4 t/day and 3 t/day respectively they classify as small facilities not covered by the EU Directive. Also US Federal Regulations Title 40

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Protection of Environment Part 60 Standards of Performance for New Stationary Sources defines "very small municipal combustion units as those which have the capacity to combust less than 35 t/day of municipal solid waste. And a small remote incinerator is one that combusts 3 t/day or less of solid waste and is more than 25 miles (40 km) driving distance to the nearest municipal solid waste landfill. Very small incinerators are regulated at the local level and practices are generally not uniformly normative with the risks considers as insignifcant. Nonetheless, the performance specifications for the Tangguh incinerators are stringent, and Indonesian Government permits for the incinerators as discussed below.

7.3. Waste Management Overview

Tangguh waste management facilities conformance status against the IFC Health & Safety Guidelines for Waste Management is presented in below table.

Table 10 Waste Management Facility Conformance Status

No. IFC Health & Safety Guidelines for Waste Conformance Status Management i. Introduction i.a The Environmental, Health, and Safety (EHS) This review of Tangguh waste management has Guidelines are technical reference documents been prepared in the context of the applicability with general and industry specific examples of of these Waste Management Guidelines which Good International Industry Practice (GIIP) 1. incorporate the specific requirements of the When one or more members of the World Bank General EHS Guidelines and the sector specific Group are involved in a project, these EHS LNG facility EHS Guidelines. Guidelines are applied as required by their respective policies and standards. These industry sector EHS guidelines are designed to be used together with the General EHS Guidelines document, which provides guidance to users on common EHS issues potentially applicable to all industry sectors.

The EHS Guidelines contain the performance levels and measures that are generally considered to be achievable in new facilities by existing technology at reasonable costs. Application of the EHS Guidelines to existing facilities may involve the establishment of site- specific targets, with an appropriate timetable for achieving them.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management i.b The applicability of the EHS Guidelines should The applicability of these guidelines is assessed be tailored to the hazards and risks established in the context of the hazards and risks presented for each project on the basis of the results of an by the small scale Tangguh waste facilities. The environmental assessment in which site specific applicability of specific technical variables, such as host country context, recommendations has been based on the assimilative capacity of the environment, and professional opinion of qualified and other project factors, are taken into account. The experienced persons. applicability of specific technical recommendations should be based on the professional opinion of qualified and experienced persons. i.c When host country regulations differ from the Hazard assessment and risks for Tangguh waste levels and measures presented in the EHS management facilities have been undertaken for Guidelines, projects are expected to achieve the existing T1/2 facilities commencing with the whichever is more stringent. If less stringent approved T1/2 AMDAL of 2002 and more levels or measures than those provided in these recently with the TEP AMDAL of 2014. The EHS Guidelines are appropriate, in view of existing waste management facilities consist of specific project circumstances, a full and an inert waste landfill and two non-hazardous detailed justification for any proposed waste incinerators which will be replicated in alternatives is needed as part of the site-specific TEP. The main change will be the addition of a environmental assessment. This justification small hazardous waste incinerator. should demonstrate that the choice for any alternate performance levels is protective of human health and the environment ii. Applicability The EHS Guidelines for Waste Management These Guidelines are generally applied to cover facilities or projects dedicated to the dedicated municipal and industrial waste management of municipal solid waste and facilities of much larger scale and for the industrial waste, including waste collection and management of a significantly greater diversity transport; waste receipt, unloading, processing, of waste types than the waste facilities at and storage; landfill disposal; physico-chemical Tangguh. Nevertheless the relevant aspects of and biological treatment; and incineration these waste management guidelines are already projects. Industry-specific waste management practiced at Tangguh T1/2. Waste collection and activities applicable, for example, to medical transport, waste receipt, processing and storage, waste, municipal sewage, cement kilns, and landfill disposal, physico-chemical and others are covered in the relevant industry- biological treatment and incineration at sector EHS Guidelines, as is the minimization Tangguh have been subject to risk and hazard and reuse of waste at the source. assessment, preparation and approval of management and monitoring plans (reported to GoI six-monthly), EMS accredited to ISO14001 and detailed SOPs. These will all apply to TEP with the exception of the addition of a small hazardous waste incinerator which will be installed during Construction and used for

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management Operations commencing 2020. This incinerator will require the preparation of an SOP for inclusion in the EMS and will for the most part comply with the requirements of these Guidelines as they apply to industrial waste. ii.a This document is organized according to the following sections: Section 1.0 — Industry-Specific Impacts and Management Section 2.0 — Performance Indicators and Monitoring Section 3.0 — References and Additional Sources Annex A — General Description of Industry Activities 1.0 Industry-Specific Impacts and Management The following section provides a summary of the most significant EHS issues associated with Waste Management, which occur during the operational and decommissioning phases, along with recommendations for mitigating these impacts. Recommendations for the management of EHS impacts common to most large industrial facilities during the construction phase are provided in the General EHS Guidelines, as are other operational phase issues, such as noise, common to many industrial activities 1.1 Environment 1.1.1 Municipal Solid Waste Municipal solid waste (MSW) is generally The waste stream for Tangguh is well defined as the wastes (other than sewage and air understood and is not MSW as per accepted emissions) generated in and usually collected by definitions. The volumes are generally low and a municipality. MSW is extremely variable in relatively constant for normal operations composition, depending on the income and increasing by about 60% during Turnarounds lifestyle of the generators. As shown in Table 1, (TAR). Therefore, our review addresses MSW includes household refuse, institutional industrial waste specifically with general wastes, street sweepings, commercial wastes, as comments on MSW. well as construction and demolition debris. MSW may include paper and packaging materials; foodstuffs; vegetable matter such as yard debris; metal; rubber; textiles; and potentially hazardous materials such as batteries, electrical components, paint, bleach,

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management and medicines. MSW may also contain varying amounts of industrial wastes from small industries, as well as dead animals and fecal matter. Environmental impacts and associated mitigation measures applicable to MSW collection and transport; waste receipt, unloading, processing, and storage; biological treatment; incineration; and landfilling are described below. 1.1.1.1 Waste Collection and Transport 1.1.1.1a Litter and clandestine dumping The causes of littering and clandestine dumping All Tangguh waste is generated on site and in urban areas occur because of inadequate transported to the Central Waste Accumulation availability of litter bins along walkways, Area in existing T1/2 operation and newly inadequate public awareness of their developed Integrated Waste Management responsibilities as urban dwellers, and Facility in T3 operation for treatment, recycling, inadequate refuse collection service. Littering landfill or incineration. occurs everywhere and often into drains, while clandestine dumping is commonly on vacant There is no litter or clandestine dumping at the lots, public spaces, or along waterways. Tangguh facility. Accumulated waste may attract disease vectors, contribute to clogging of drainage and sewerage networks, make waste readily accessible to neighborhood animals and birds, and pollute waterways. Recommended management strategies to minimize litter and clandestine dumping include:  Encourage use of containers or bags for waste at the point of collection for each household and establishment;  Implement a regular collection schedule with sufficient frequency to avoid accumulation of garbage;  Use vehicles appropriate for the geographic conditions and waste types to maximize reliability of collection (e.g.,compactor trucks may be appropriate for neighborhoods with wide streets and low-density trash, while smaller vehicles may be appropriate for neighborhoods with narrow streets and higher-density garbage);  Encourage separation of recyclable materials

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management at the point of generation, so that the collection points do not become sorting points for informal sector waste pickers;  Cover collection and transfer vehicles along the entire route of transport to avoid windblown litter;  Clean vehicles used for waste hauling before transportation of any goods, including compost;  Encourage residents to put waste out at designated times and locations;  Where possible, blocking off access to du mping sites and fining illegal dumpers. 1.1.1.1b Air Emissions Air emissions from MSW collection and As described in 1.1.1.2 below transport include, dust and bio-aerosols, odors, and vehicle emissions. 1.1.1.2 Dust, Bio-aerosols, and Odors Dust can include nuisance dust, hazardous dust Not applicable due to the small scale of the (e.g., containing asbestos or silica), and project no nusiance dusts are generated. No bioaerosols (i.e., particles in the air consisting hazardous dust will be introduced in the wholly or partially of microorganisms). temporary hazardous waste storage. Asbestos Bioaerosols are of particular concern to the material is prohibited at site. If any suspected health of waste workers and have been shown asbestos containing material is found, to be the source of reduced pulmonary function appropriate management arrangements will be and increased respiratory disease for those in implemented to contain the material safely prior immediate proximity to waste sweeping and to sending it to temporary hazardous waste collection activities. Recommended storage. management strategies to minimize dust, bio- aerosols, and odors include: Insiginficant bioaerosols and odors may be  Establishing frequent waste collection produced from the food waste in the landfill schedules; because food waste transported to the landfill is  Instituting a washing program for waste one trip per day with truck capacity of eight m3. collection vehicles and for company-owned waste collection and transfer containers;  Promoting the use of bags to reduce the odors from soiling of waste collection and transport equipment.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.1.3 Vehicle Emissions Emissions from on-road vehicles may be Not applicable as the project involves minimal regulated through national or regional waste transportation. Daily travel distance is no programs. In the absence of these, specific more than a few kilometers at maximum speed measures to prevent, minimize, and control of 20 km/hour. vehicle air emissions during waste collection and transport include the following:  Optimize waste collection routes to minimize distance travelled and overall fuel use and emissions  Implement transfer stations for small vehicles to consolidate waste into large vehicles for transportation to a treatment or disposal facility;  Waste collection and transport vehicle owners and operators should implement the equipment manufacturers’ recommended engine maintenance, along with the mechanical maintenance for the safe operation of the vehicle, including proper tire pressure.;  Drivers should also be instructed on the benefits of driving practices which reduce both the risk of accidents and fuel consumption, including measured acceleration and driving within safe speed limits (working with garbage truck drivers can save as much as 25% on fuel use and reduce maintenance by 15%).

Additional fleet management recommendations are presented in the General EHS Guidelines. 1.1.1.4 Waste Receipt, Unloading, Processing, and Storage Control of the incoming waste stream is Tangguh has developed a comprehensive Non necessary to ensure safe and effective Hazardous Solid Waste Procedure (900-PRC- processing, treatment, and disposal of the waste EN-2321) that sets out the requirements set forth and the quality of end products (e.g., compost). in the point 2.4. Wastes at Tangguh have been While procedures may vary depending on the identified and management requirements for the nature of the waste and necessary processing waste stream are detailed in the procedure methods, recommended measures include: appendix. All wastes shall be collected from the  Visually evaluate, weigh, and document collection points, stored in appropriate incoming waste loads; designated contrainers and recorded. Wastes are  Reject or, if the facility is equipped to segregated into categories i.e. food waste,

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management process the waste, segregate potentially recyclable waste, combustible waste and hazardous materials or wastes identified, hazardous waste. In the waste management including infectious waste, and manage as a facility, all incoming wastes will be inspected by hazardous or infectious waste, as applicable; the facility person in charge to ensure it is  Analyze suspected hazardous materials segregated. before acceptance so that they are segregated relative to compatibility and so that they can be adequately treated and disposed of;  If possible, isolate size reduction equipment (e.g., shredders or grinders) in an explosion- proof area with proper ventilation and pressure relief to reduce the impacts of potential explosions that could be caused by materials such as gas cylinders and ignitable liquids that may be present in MSW. Visual inspection of the incoming waste, along with sorting and removal procedures, can minimize this potential hazard;  Separate recoverable secondary materials for recycling and organic waste for composting to the extent practical. 1.1.1.4a Contaminated Runoff Leachate from waste piles caused by exposure to All waste in the waste management facility is precipitation and from residual liquids in the stored under roofed paved areas such that no waste itself may contain organic matter, precipation will have direct contact to the nutrients, metals, salts, pathogens, and wastes. hazardous chemicals. If allowed to migrate, leachate can contaminate soil, surface water, and Temporary hazardous waste storage is designed groundwater potentially causing additional to comply with secondary containment impacts such as eutrophication and acidification requirements. Any accidental leaks will be of surface water and contamination of water contained inside the temporary hazardous supplies. waste storage. Recommended contaminated runoff management strategies include: There remains negligible to no potential for soil  When siting, consider the proximity of waste and groundwater contamination. handling and storage areas to water supply wells for people and animals, irrigation canals, and surface water bodies that support aquatic life and the ability to prevent contaminated leachate and drainage from entering surface and ground water;  Use impermeable materials for roads, waste processing and storage areas, and vehicle washing areas, and install curbs to prevent

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management runoff to permeable areas;  Collect runoff and leachate from areas used for waste storage, and treat runoff to meet applicable environmental standards before discharge to surface water or the municipal sewage system (e.g., screen to remove large material, install silt traps to remove particulates, and remove separate-phase liquids with an oil/water separator).  Discharge to the municipal sewage system (via pipe or tanker truck), where available, is preferred for runoff from waste storage and handling areas;  Re-use collected water in on-site disposal processes to the extent practical or store with collected leachate awaiting treatment.

In addition, management strategies for contaminated runoff from vehicles include:  Cover containers during transport,  Ensure vehicle equipment is designed to collect drainage and that it is held in a sump container until the vehicle reaches a safe discharge location. 1.1.1.4b Litter The following measures are recommended to The amout of incoming wastes is minimal and prevent, minimize, and control litter and solid in most occassions will be immediately waste during waste receipt, unloading, processed for treatment therefore litter is not an processing, and storage: issue at Tangguh.  Provide adequate storage for waste not immediately treated or disposed of; Good housekeeping is practiced as observed  Implement good housekeeping procedures; during a number of independent audits.  Consider use of enclosed/covered areas for waste tipping, shredding, compacting, etc.;  Install catch fences and netting to trap windblown litter. 1.1.1.4c Air Emissions The following measures are recommended to These requirements are for facilities that receive prevent, minimize, and control vehicle large volumes of waste and are not applicable to emissions and emissions of dust, odors, and Tangguh. bioaerosols during waste receipt, unloading, processing, and storage:  Select vehicles and containers that minimize air emissions during waste loading and

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management unloading;  Design drop-off points to minimize queuing of vehicles;  Sweep waste management areas and roads frequently and use water spray for dust control where needed;  Pre-treat wastes as needed (e.g., solidification, encapsulation, or wetting sufficient to reduce dust but without forming leachate);  Use enclosed waste handling and storage areas for malodorous wastes or wastes that generate hazardous dust (e.g., asbestos). Enclosed waste storage and handling areas are preferred for all wastes;  Use extraction system to remove dust from working areas, buildings, and storage vessels, and treat as needed to control particulate emissions (e.g., bag filter);  Remove, treat, or dispose of all biological/malodorous wastes in an expeditious manner;  Use odor-neutralizing sprays where necessary;  Use negative pressure in processing buildings and appropriate air filtration (e.g., biofilter) to remove odor. 1.1.1.4d Noise and Vibration Principal sources of noise and vibration include The number of trucks transporting wastes are truck traffic; loading equipment (e.g., cranes, very minimal to the facility. Existing CWAA and wheeled loaders), stationary compactors, balers, the future IWMF are located far apart from the grinders, and other treatment and conveyance dwelling areas. systems. Recommended noise management strategies include:  Construct a buffer zone between the facility and the external environment or locate facilities away from sensitive receptors;  Include noise and vibration considerations during design, including use of models to predict noise levels at specified noise-sensitive locations, using standardized sound power levels for

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management construction plant;  Maintain site roads in good condition to reduce noise and vibration from vehicle movements;  Use acoustic screens around fixed/mobile plant and equipment;  Select equipment that has low noise emission levels;  Fit silencing equipment to plant, e.g. baffles/mufflers;  Use buildings to contain inherently noisy fixed plant equipment (e.g., locate waste shredder in the tipping hall, and enclose tipping hall on all sides) and consider use of sound-insulating materials in construction. 1.1.1.5 Biological Treatment Biological treatment includes composting with Composting on a small scale is undertaken for other organic materials for the preparation of organic waste at the waste management facility. soil products 4 (i.e., aerobic treatment), and Surplus organic waste is directed to the organic anaerobic digestion. To maximize the usability waste cell at the non-hazardous waste landfill. of end products, waste should not be accepted Wood chips are used as a bulking agent. The that contains organics that are contaminated by organic waste is food waste from the on-site potentially hazardous chemicals (e.g., PCBs, canteens and does not contain any chemicals or chlordane and other pesticides, heavy metals hazardous materials. and metalloids) and/or pathogenic substances and micro-organisms (e.g., prions, viruses, bacteria, and parasites) that will not be rendered harmless by the process or may constitute a health or environmental risk. This may include certain clinical waste and other related wastes of clinical origin, and diseased carcasses, or contaminants classified as hazardous or industrial wastes.5 1.1.1.5a Leachate and Runoff Leachate and runoff from waste storage and The only leachate generated is in the non- processing areas may contain organic material hazardous waste landfill. This is drained to a (biochemical oxygen demand (BOD)), phenols, leachate pond and treated before disposal. This nitrates, phosphorous, dissolved metals, and leachate is monitored regularly according to the other contaminants. If treated wood is permit requirements against the agreed TEP processed, wood preservative chemicals, such as numerical standards which are approved in the creosote and chromated copper arsenate, and AMDAL. their degradation products may be present. Municipal waste may contain human and

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management animal fecal matter and blood which have a wide range of disease microorganisms. Some household chemicals can possess hazardous properties; examples include pesticides, solvents, paints, batteries, used oils, pharmaceuticals, etc. The following measures are recommended to prevent, minimize, and control leachate generation and discharge from biological treatment operations:  Install a drainage layer underneath the A drainage layer is installed at the base of the processing area to provide adequate leachate landfill. drainage from composting organics. This may consist of a bed of coarse material such as wood chips, or alternatively the processing platform may permanently incorporate a drainage layer designed to withstand the loading, working and removal of material.  For small-scale compost facilities or in dry areas, an adsorbent material can be incorporated in the compost and at the base of the pile;  The material processing or storage areas of The landfill is lined with HDPE. the facility should have a leachate barrier system that forms a secure barrier between the groundwater, soil, and substrata and the composting or stored organics, as well as systems for collecting and treating leachate;  Design and maintain the slope and There is no windrowing at Tangguh. orientation of windrows and/or leachate drains such that free drainage of leachate to a collection drain is facilitated and ponding of leachate is avoided; shape the piles and windrows to maximize run-off and hence reduce infiltration;  Store leachate in a lined earthen basin or in As above. Engineered leachate pond. aboveground storage tanks;  For anaerobic digestion, maximize recycling of wastewater to the reactor;  Measure total organic carbon (TOC), chemical oxygen demand (COD), nitrogen (N), phosphorus (P) and chlorine (Cl) levels in the inlet and outlet flows from an

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management anaerobic digester. When a better control of the process is required, or a better quality of the waste output, monitoring of additional parameters may be necessary;  Operate an anaerobic digester under A purpose built small capacity composter is thermophilic digestion conditions, in order used. to increase the pathogen destruction, biogas production rate (hence higher energy recovery) and the retention time  Maintain ideal composting conditions such as: o Carbon: nitrogen (C:N) ratio between 25:1 and 35:1 o Moisture content of 50 to 60 percent of total weight during treatment (and less than 50 percent for marketing following screening) o Balance between particle size and void space to promote rapid decomposition. Void space should be sufficient to achieve a 10 to 15 percent oxygen level within the pile in aerobic systems o Optimum temperature levels which can range between 32 and 60 degrees Celsius. Pathogen destruction can be achieved by attaining and maintaining a temperature of 55 degrees Celsius for three days in a vessel composting system or 15 days in a windrow system o pH of between 6 and 8.

1.1.1.5b Air Emissions Releases to the air can include direct stack No biological substace incinerates as well as no emissions and fugitive emissions associated burning of biogas use in the incinerator. with biological processes, as well as emissions from burning of biogas. Direct air emissions can include bioaerosols, particulate matter/dust, ammonia, amines, volatile organic compounds (VOCs), sulfides, odors, etc. The following measures are recommended to prevent, minimize, and control air emissions from biological treatment:

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Use mist spray to keep down dusts, especially during and prior to loading or other handling procedures.  Use windrow turning equipment that is specially designed to minimize air emissions, as opposed to wheeled loaders or conveyor loaders that drop wastes into piles.  For highly odorous wastes, use closed feed bunkers constructed with a vehicle sluice; for less odor-intensive wastes, use automated and rapid action doors (opening times of the doors being kept to a minimum) in combination with an appropriate exhaust air collection device resulting in an under pressure in the treatment hall.  Enclose leachate drains to reduce the emission of odors.  Minimize the amount of water added to compost (e.g., by covering compost material) to avoid anaerobic conditions that can cause hydrogen sulfide odors if the compost mixture contains sulfur- containing materials. Biomass and biogas combustion emissions depend on the type of biomass material and combustion method and can include particulate matter, nitrogen oxide (NOX), sulfur oxide (SOX), carbon monoxide (CO), hydrogen sulfide (H2S), and VOCs. When using biomass or biogas as a fuel source for power generation, reference should be made to the General EHS Guidelines for emissions guideline values and the selection of appropriate emissions prevention and control techniques. 1.1.1.5c Fire Biodegradable wastes can be combustible and Due to the limited operation and nature of the aerobic degradation can produce sufficient heat waste stream spontaneous combustion will be to cause spontaneous combustion in certain most unlikely from the landfill and composter, circumstances. Wastes can, in some instances, and methane generation will be limited. also contain ashes and other readily ignitable materials that burst into flame under wind

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management conditions, or when contacting flammables. In landfills, methane is generated by anaerobic digestion and can potentially ignite if it encounters an ignition source within or external to the landfill. Methane in landfill gas can become trapped in underground cavities, and even move along geologic discontinuities, to pose a risk of explosion. Recommended fire prevention and control strategies include:  For composting, avoid conditions that can lead to spontaneous combustion (e.g., moisture between 25 – 45 percent and temperatures above about 93ºC. This can be achieved for example by keeping windrows less than about 3m high and turning them when the temperature exceeds 60ºC);  Collect biogas for use or treatment (e.g. energy recovery or flaring);  Provide a fire alarm system, including temperature sensors in the waste being treated;  Design the facility for access by firefighting equipment, including clear aisles among windrows and access to an adequate water supply. 1.1.1.6 MSW Incineration Facilities 1.1.1.6a Air Emissions Air emissions from incineration depend on the The facility does not operate a MSW specific waste composition and the presence and incineration facility, however it does operate effectiveness of air pollution control systems. small scale non-hazardous waste incinerators Polluting emissions may include carbon dioxide with limited and well characterised waste (CO2), CO, NOX, sulfur dioxide (SO2), streams. Internatioanl best practice guidelines particulate matter, ammonia, amines, acids are available for large scale facilities. Small scale (HCL, HF), VOCs, dioxins/furans, facilities are regulated at the local level. polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs), metals (Hg), and sulfides, etc., depending on the waste content and combustion conditions.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management The following measures are recommended to prevent, minimize, and control air emissions:  Conduct waste segregation and/or pre- Waste segregation is practiced at Tangguh sorting to avoid incineration of wastes that contain metals and metalloids that may volatilize during combustion and be difficult to control through air emission technology (e.g., mercury and arsenic);  Follow applicable national requirements and The incinerator specifications follow national internationally recognized standards for requirements. Internationally recognized incinerator design and operating conditions, standards for facilities of this scale are not mainly rapid quenching of the flue gas after available. leaving all combustion chambers and before entering any dry particulate matter air pollution control device but also combustion temperature, residence time, and turbulence. Standards for stationary incinerators which include temperature and afterburner exit gas quenching (i.e. rapid temperature reduction) requirements are preferred in order to nearly eliminate dioxins and furans;  Introduce wastes into the incinerator only The incinerators are operated in a manually fed after the optimum temperature is reached in in 20 to 40kg loads over a 10 hour period and the final combustion chamber. operating temperatures must be reached before the waste is introduced into the incinerator. This is not necessary for a batch operating system as described above.  The waste charging system should be This is not applicable for incinerators of this interlocked with the temperature monitoring scale. and control system to prevent waste additions if the operating temperature falls below the required limits;  Minimize the uncontrolled ingress of air into Uncontrolled ingress of air can be controlled. the combustion chamber via waste loading or other routes;  Optimize furnace and boiler geometry, This is not applicable for incinerators of this combustion air injection, and, if used, NOX scale. control devices using flow modeling;  Optimize and control combustion conditions Air supply is controlled as per design by the control of air (oxygen) supply, specification. distribution and temperature, including gas and oxidant mixing; the control of combustion temperature level and distribution; and the control of raw gas

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management residence time;  Implement maintenance and other A maintenance program is in place but this procedures to minimize planned and requirement relates to large incinerator facilities unplanned shutdowns; which may have storage limitations.  Avoid operating conditions in excess of This is not applicable for incinerators of this those that are required for efficient scale. destruction of the waste;  Use auxiliary burner(s) for start-up and Not practical for a facility of this scale. shut-down and for maintaining the required operational combustion temperatures (according to the waste concerned) at all times when unburned waste is in the combustion chamber.  Use a boiler to transfer the flue-gas energy Not necessary for an incinerator of this scale. for the production of electricity and/or supply of steam/heat, if practical;

 Use primary (combustion-related) NOX Not necessary for an incinerator of this scale. control measures and/or selective catalytic reduction (SCR) or selective noncatalytic reduction (SNCR) systems, depending on the emissions levels required;  Use flue gas treatment system for control of Not necessary for an incinerator of this scale. acid gases, particulate matter, and other air pollutants;  Minimize formation of dioxins and furans Insignificant quantities of chlorinated or by ensuring that particulate control systems fluorinated materials are present in the waste do not operate in the 200 to 400 degrees stream, therefore there is an extremely low Celsius temperature range; identifying and likelihood of the formation of dioxins and controlling incoming waste composition; furans. using primary (combustion-related) controls; using designs and operation conditions that limit the formation of dioxins, furans, and their precursors; and using flue gas controls;  Consider the application of waste- to-energy This is not feasible for the scale of the or anaerobic digestion technologies to help incinerator. off-set emissions associated with fossil fuel based power generation 1.1.1.6b Ash and Other Residuals Combustion of solid wastes generates ash and Ash from non-hazardous waste incinerator is other material remaining after incineration. disposed of to inert waste landfill. The Solid wastes may also be generated from incinerators only generate about 0.1 cubic treatment of wastewater from flue gas treatment metres of ash per day. (FGT).

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management The following measures are recommended to prevent, minimize, and control solid waste from incineration:  Design the furnace to, as far as possible, Ash from the future hazardous waste physically retain the waste within the incinerator is classified as hazardous waste and combustion chamber (e.g. narrow grate bar is to be disposed by licensed 3rd party spacing for grates, rotary or static kilns for contractor. The ash is collected in a chamber appreciably liquid wastes), and use a waste prior to disposal in the landfill. throughput rate that provides sufficient agitation and residence time of the waste in the furnace at sufficiently high temperatures, including any ash burn-out areas, in order to achieve a total organic carbon (TOC) value in the ash residues of below 3 wt percent and typically between 1 and 2 wt percent.  Manage bottom ash separately from fly ash The incinerators do not generate fly ash. and other flue gas treatment residues to avoid contamination of the bottom ash for its potential recovery;  Separate remaining ferrous and non- ferrous Ferrous metals are not present in the ash as the metals from bottom ash as far as practicably waste is segregared before incineration. and economically viable, for their recovery;  Treat bottom ash on or off-site (e.g., by The incinerators only generate about 0.1 cubic screening and crushing) to the extent that is metres of ash per day. required to meet the specifications set for its use or at the receiving treatment or disposal site (e.g., to achieve a leaching level for metals and salts that is in compliance with the local environmental conditions at the place of use);  Bottom ash and residuals should be The bottom ash for the non-hazardous waste managed based on their classification as incinerators is classified as non-hazardous hazardous or non-hazardous materials. waste. Hazardous ash should be managed and disposed of as hazardous waste. Non- hazardous ash may be disposed of in an MSW landfill or considered for recycling in construction materials.9 1.1.1.6c Water Effluents Cooling systems generate cooling tower Due to the small scale of the incinerators they do blowdown, which is addressed in the General not have cooling systems. EHS Guidelines. In addition, flue gas treatment generates wastewaters requiring treatment and disposal.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management To prevent, minimize, and control water effluents, wastewater from flue gas treatment should be treated as necessary, e.g., using filtration coagulation, precipitation, and filtration to remove heavy metals, and neutralization. 1.1.1.6d Noise Principal sources include exhaust fans and The incinerators are not significant sources of resulting in noise from the outlet of the stack; noise and Occupational noise exposure is cooling system (for evaporation cooling and managed by existing systems especially for air cooling); and turbine generators. Measures to address noise impacts are addressed in the General EHS Guidelines. Additional recommended measures to prevent, minimize, and control noise from incineration include use of silencers on air coolers and chimneys, as necessary. 1.1.1.7 Landfilling A sanitary landfill is a carefully engineered, The non-hazardous waste landfill is designed to structurally stable formation of segregated meet international good practice. waste cells separated by soil cover material, with base and side slopes designed to minimize The landfill is design to meet below minimum infiltration and facilitate collection of leachate. requirements: Landfills are sited, designed and operated to 1. Soil permeability less than 1x10-7 isolate the wastes from the surrounding cm/second environment, particularly groundwater. Even 2. Adequate leachate drainage and collection after closure, landfills required long-term care, system, where on this project the leachate including maintenance of the cap system, pipe drain system and Leachate Pond are collection and treatment of leachate, collection functioning as leachate collection system. and flaring or utilization of landfill gas, and Leachate shall be treated before discharge monitoring of groundwater so that the waste 3. Leachate collection pond remains isolated. Thus, the EHS impacts of 4. Equipped with HDPE geomembrane liner eventual decommissioning or closure and long for both the non-Hazardous waste pits and term operation and maintenance of a landfill the leachate pond. need to be considered in the system design. Specific closure procedures should focus on the preservation of the long- term integrity and security of the site, preferably with a minimum of maintenance. Landfill operators, working in coordination with local regulatory authorities, should explore and implement opportunities to minimize the landfill disposal of municipal wastes which

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management contain metals, such as mercury, which may be released due to crushing of waste materials. Segregation and presorting of these materials should be performed to the extent feasible. 1.1.1.7a Landfill Siting The location of the landfill should take into account potential impacts associated with releases of polluting substances including the following: 1.1.1.7a1 Proximity to residential, recreation, agricultural, The landfill is within the Tangguh Project Area natural protected areas, or wildlife habitat and inaccessible to community members and with areas prone to scavenging wildlife, as well as limited access to site personnel. The nearest other potentially incompatible land uses: community is Tanah Merah several km to the o Residential development should be typically west. The landfill is sited within a valley which further than 250 meters from the perimeter is east of the Tangguh plant site and not visible of the proposed landfill cell development to from the accommodation units. minimize the potential for migration of underground gaseous emissions The nearest airport is Babo which is about 20 km o Visual impacts should be minimized by east of Tangguh. evaluating locational alternatives o Siting should be further than 3 km of a turbojet airport and 1.6 km of a piston-type airport or as permitted by the aviation authority fully considering potential threats to air safety due to attraction and presence of birds 1.1.1.7a2 Proximity and use of groundwater and surface water resources; o Private or public drinking, irrigation, or There are no communities downstream of the livestock water supply wells located down landfill and no use of groundwater on site. gradient of the landfill boundaries should be further than 500 meters from the site perimeter, unless alternative water supply sources are readily and economically available and their development is acceptable to regulatory authorities and local communities o Areas within the landfill boundaries should Not applicable be located outside of the 10-year groundwater recharge area for existing or pending water supply development. o Perennial stream should not be located There are no perennial streams near the landfill within 300 meters downgradient of the site. proposed landfill cell development, unless

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management diversion, culverting or channeling is economically and environmentally feasible to protect the stream from potential contamination. 1.1.1.7a3 Site geology and hydrogeology; o Landfills should be located in gently sloped Existing non-hazardous waste landfill is located topography, amenable to development using in gently sloped topography, containing 4 cells the cell (bund) method), with slopes which with slope directing to the leachate collection minimize the need for earthmoving to obtain pond. the correct leachate drainage slope of about 2% o Groundwater's seasonally high table level The base of the landfill is 4 m above water table (i.e., 10 year high) should be at least 1.5 to meet Indonesian landfill design requirements. meters below the proposed base of any excavation or site preparation to enable landfill cell development o Suitable soil cover material should be Soil cover material is stockpiled adjacent to the available on-site to meet the needs for landfill. intermediate (minimum of 30 cm depth) and final cover (minimum of 60 cm depth), as well as bund construction (for the cell method of landfill operation). Preferably, the site would have adequate soil to also meet required cover needs (usually a minimum of 15 cm depth of soil)

1.1.1.7a4 Potential threats to landfill site integrity from natural hazards such as floods, landslides, and earthquakes: o Landfills should be sited outside of a Landfill is sited outside of a floodplain that floodplain subject to 10-year floods and, if subject to 10-years floods. within areas subject to a 100- year flood, amenable to an economic design which would eliminate the potential for washout o There should be no significant seismic risk Detailed seismic risk assessment undertaken for within the region of the landfill which could the LNG facility. cause destruction of berms, drains or other civil works, or require unnecessarily costly engineering measures; otherwise, side slopes should be adjusted accordingly to prevent failure in the event of seismic activity No fault lines or significantly fractured geologic structure should be present within 500 meters of the perimeter of the proposed

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management landfill cell development which would allow unpredictable movement of gas or leachate o There should be no underlying limestone, The landfill is underlain by a sticky black low carbonate, fissured or other porous rock permeability claystone with thin sandstone formations which would be incompetent as intercalations. barriers to leachate and gas migration, where the formations are more than 1.5 meter in thickness and present as the uppermost geologic unit above sensitive groundwater. 1.1.1.7b Leachate Generation Landfill leachate contains dissolved constituents A leachate collection system is installed at the derived from the interstitial waters of the landfill and is directed to the leachate collection disposed waste as well as its degradation pond. Leachate is treated to meet the efluent products. It also may contain some suspended discharge standard. solids, including pathogens. If not collected and treated, leachate can migrate from the landfill and contaminate soil, groundwater, and surface water. Leachate and site monitoring are used to confirm that the engineered landfill systems effectively isolate the waste, both during operation of the landfill and after closure. Leachate from a MSW landfill typically is very high in nitrogen (as ammonium), chloride, and potassium, as well as dissolved biological oxygen demand and chemical oxygen demand organics. The following measures are recommended to prevent, minimize, and control leachate generation from MSW landfills: 1.1.1.7b1  Site landfills in areas with stable geology The landfill is located in stable geology and in and avoid siting near particularly vulnerable an area away from vulnerable or sensitive or sensitive ecosystems and groundwater ecosystems. and surface water resources;  Design and operate the landfill in The landfill is designed with low permeability accordance with applicable national liners to prevent migration of leachate and the requirements and internationally recognized small quantities of landfill gas that are standards to minimize leachate generation, generated. including the use of low-permeability landfill liners to prevent migration of leachate as well as landfill gas, a leachate drainage and collection system, and landfill cover (daily, intermediate, and final) to minimize infiltration;

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Treat leachate onsite and/or discharge to Leachate drains to a leachate pond and is then municipal wastewater system. Potential treated to meet discharge limits. treatment methods include aerated lagoons, activated sludge, anaerobic digestion, artificial wetlands, re-circulation, membrane filtration, ozone treatment, peat beds, sand filters, and methane stripping;  Minimize the daily exposed working face The small working face is minimized and is and use perimeter drains and landfill cell covered daily with woodchips and compaction compaction, slopes and daily cover materials is carried out. to reduce infiltration of rainfall into the deposited waste;  Prevent run-on of precipitation into the Water diversion structures are in place. active area of the landfill (e.g., by use of berms or other diversions); systems should be designed to handle the peak discharge from a 25-year storm;  Collect and control run-off from the active The active area of the landfill is properly area of the landfill; the system should be drained the only significant waste contaminated designed to handle the discharge from a 24- water is the leachate. hour, 25-year storm. Runoff is typically treated together with leachate from the site. 1.1.1.7c Groundwater and Leachate Monitoring Recommended measures for groundwater and leachate monitoring include the following:  Measure and record the quantity and quality Leachate quantity and quality is recorded in of leachate generated. Changes in leachate regular basis. quantity or quality not attributable to weather or other factors may indicate changes in the liner, leachate collection, or landfill cover systems;  Install groundwater monitoring wells One upstream and three downstream monitor outside the landfill perimeter at locations wells plus three additional shallow downstream and depths sufficient to evaluate whether monitor wells. leachate is migrating from the landfill into the uppermost groundwater unit. This groundwater monitoring network should usually include, at a minimum, one monitoring well located in the upgradient groundwater flow direction from the landfill and two monitoring wells located in the down gradient direction. The groundwater monitoring system should be consistent with applicable national regulations and

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management internationally recognized standards.14  Regularly sample the monitoring wells and Baseline groundwater quality has been analyze for constituents, selected based on: established and both internal and external o The types, quantities, and groundwater monitoring is undertaken on a concentrations of constituents in regular basis and reported to Government on a wastes managed in the landfill six-monthly basis. Also subject to external o The mobility, stability, and independent audit. persistence of waste constituents their reaction products in the unsaturated zone beneath the waste management area o The detectability of indicator parameters, waste constituents, and reaction products in ground water; The constituent concentrations in the groundwater background. 1.1.1.7d Landfill Gas Emissions MSW contains significant portions of organic Landfill gas generation will be very minimum. materials that produce a variety of gaseous The landfill is designed to ventilate landfill gas. products when dumped, compacted, and Gas vent pipes will be installed in the final closure of the landfill. covered in landfills. Oxygen in a landfill is quickly depleted, resulting in anaerobic bacterial decomposition of the organic materials and the production of primarily carbon dioxide and methane. Carbon dioxide is soluble in water and tends to dissolve in the leachate. Methane, which is less soluble in water and lighter than air, tends to migrate out of the landfill, resulting in landfill gas that is typically about 60 percent methane and 40 percent CO2, with trace amounts of other gases. Some MSW landfills are designed to maximize anaerobic degradation and production of landfill gas, which can be burned for energy. In addition, operation of landfills can generate dust and odors. Landfill gas is not generated, or in lesser quantities, if the waste material is primarily inert, such as construction debris.

Recommended methods to control and monitor landfill gas emissions include the following:

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Include landfill gas collection system designed and operated in accordance with applicable national requirements and recognized international standards including recovery and pre-use processing or thermal destruction through an efficient flaring facility. Prevent condensation from accumulating in extraction systems by arranging the pipe work to fall to a removal point such as a knock out-pot.  Use landfill gas as fuel if practical, or treat before discharge (e.g., by using enclosed flare or thermal oxidation if methane content is less than about 3 percent by volume).  Use gas blowers (boosters) of sufficient capacity for the predicted gas yield and constructed of materials appropriate for landfill gas duty; blowers should be protected by flame arrestors at both gas inlet and outlet.  Install and regularly sample boreholes surrounding the landfill to monitor for migration of landfill gas.

Carbon financing may also be considered, including opportunities implemented through the host- country Joint Implementation of the United Nations Network Convention on Climate Change.

Recommended methods to control dust and odor emissions include the following:  Compact and cover waste promptly after discharge from the vehicle delivering the waste  Minimize open tipping face area  Dispose of odorous sludge in covered trenches  Restrict acceptance of loads known to be particularly odorous  Restrict tipping activities during periods of adverse weather (e.g., wind toward sensitive receptors)

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Seal sump covers  Aerate leachate storage areas 1.1.1.7e Litter Wind, vehicles, and vermin can disperse MSW, potentially attracting vermin, contributing to transmission of diseases, and adversely affecting wildlife and neighboring communities.

The following measures are recommended to prevent, minimize, and control dispersal of litter:  Avoid siting of facilities in particularly Landfill is located in a well covered location exposed, windy areas; surrounding by trees.  Provide perimeter planting, landscaping, or As above. fences to reduce wind  Pin waste by use of dozers and landfill Compaction is carried out excavator. compactors immediately after discharge from the vehicles delivering the waste;  Use soil or artificial cover materials so that Woodchips is used to cover the deposited waste. deposited waste is held in place. More frequent application of cover may be required during high winds or in exposed areas;  Use scaring techniques or natural predators Not applicable. to control scavenging birds;  Provide an emergency tipping area/foul Not applicable. weather cell for lightweight wastes such as paper;  Construct temporary banks and bunds Not applicable. immediately adjacent to the tipping area, install strategically placed mobile catch fences close to the tipping area or on the nearest downwind crest, and/or fully enclose of the tipping area within a mobile litter net system;  Install wind fencing upwind of the tipping Not applicable. area to reduce the wind strength as it crosses the facility;  Temporarily close the facility to specific or Landfill will be closed if the weather condition all waste or vehicle types when weather is unsafe. conditions are particularly adverse.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.1.7f Closure and Post-Closure Landfill facility operators should plan for the Landfill closure and post-closure is described in closure and postclosure care of the facility. Such the Supplementary Information Section 2.2 planning should take place as early as possible in the project cycle so that potential closure and post-closure issues are incorporated in the financial and technical planning. Closure and post-closure planning activities should include the following elements:  Development of a closure plan which specifies the necessary environmental objectives and controls (including technical specifications), future landuse (as defined in consultation with local communities and government agencies), closure schedule, financial resources, and monitoring arrangements;  Evaluation, selection, and application of closure methods consistent with post- closure use and which should include the placement of a final cover to prevent further impacts to human health and the environment;  Application of final cover components that are consistent with post closure use and local climatic conditions. The final cover should provide long term environmental protection by preventing direct or indirect contact of living organisms with the waste materials and their constituents; minimize infiltration of precipitation into the waste and the subsequent generation of leachate; control landfill gas migration; and minimize long term maintenance needs.  Financial instruments in place to cover the costs of closure and post-closure care and monitoring. 1.1.2 Industrial Hazardous Waste 1.1.2.1 Waste Collection and Transport Transportation of industrial hazardous waste is a specialized activity requiring appropriate equipment and suitably trained staff. Recommended measures to prevent spills and

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management releases during waste transport and to facilitate emergency response if an accident should occur are provided in the General EHS Guidelines. Additional recommendations specifically applicable to hazardous waste collection and transport operations include:  Follow applicable national regulations and Tangguh is in conformance with applicable internationally accepted standards for national regulation and international standard packaging, labeling, and transport of for packaging, lebeling and transported of hazardous materials and wastes; hazardous material and wastes.  Use tanks and containers specially designed Tangguh uses tanks and containers as specified and manufactured to incorporate features in the MSDS. appropriate for the wastes they are intended to carry;  If drums or other containers are used to Drums and other containers are inspected to transport waste, containers should be in ensure its condition and compatibility good condition and compatible with the compliant, as well as safely transported. waste and are adequately secured in the transport vehicle;  Adequately label all transport tanks and Tanks and containers are labeled to indentify containers to identify the contents, hazards, the content, volume, and hazard. and actions required in various emergency situations. 1.1.2.2 Waste Receipt, Unloading, Processing, and Storage Because of the potential inherent hazards of the Generate hazardous wastes at Tangguh are from waste, it is especially important for industrial processed plant, maintenance shops, and offices, hazardous waste management facilities to which are well-understood. The hazardous understand and control the nature of the waste waste management procedure is place. that is accepted for storage, treatment, or disposal. Failure to adequately identify and classify incoming waste could result in inadequate treatment or disposal or unintended reactions that could release hazardous substances or cause fires or explosions. Therefore, recommended measures to control waste receipts and general measures to mitigate risks at industrial hazardous waste management facilities include:  Establish and maintain a close relationship with the waste generator to understand the process generating the waste and to monitor any changes in the process or waste

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management characteristics;  Sufficient personnel with the requisite qualifications should be available and on duty at all times. All personnel should undergo specific job training;  Obtain a thorough understanding of the incoming waste. Such knowledge needs to take into account the waste characteristics and variability, the origin of the waste, the tr eatment and disposal under consideration, the nature of the waste residuals, if any, that may be generated during treatment, and potential risks associated with waste treatment and disposal;  Implement a pre-acceptance procedure that includes, as applicable, tests of the incoming waste and documentation of the waste source (e.g., the processes producing the waste, including the variability of the process), and identifying the appropriate treatment/disposal;  Implement an acceptance procedure that includes, as applicable, procedures that limit the acceptance of waste to only that which can be effectively managed including effective disposal or recovery of residuals from waste treatment. Only accept waste if the necessary storage, treatment capacity, and disposition of any treatment residuals (e.g. acceptance criteria of the output by another treatment or disposal facility) are assured. The reception facility should include a laboratory to analyze incoming waste samples at the speed required by facility operations to determine if the waste is acceptable; In the case of treatment, analyze the waste out according to the relevant parameters important for the receiving facility (e.g. landfill or incinerator).

SUPPLEMENTARY DOCUMENT TO LENDER 94

No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.2.2a Spills and Releases Overfills, vehicle accidents, and tank and piping failures can lead to releases during waste storage and handling. Mitigation measures, including physical protection, overfill protection, tank integrity, and secondary containment for tanks are addressed in the General EHS Guidelines. Additional recommended measures include:  Segregate hazardous wastes and materials Hazardous wastes are collected in designated from non-hazardous wastes and materials; drums or containers, and well segregrated from the non hazardous waste  Separate incompatible wastes, such as certain Wastes are segregated to its compatibity refers alkaline and acidic wastes that would release to Hazardous Waste Procedure (900-PRC-EN- toxic gases if mixed; keep records of testing; 2322) store waste in separate drums or vessels based on their hazard classification;  Lock out valves controlling material and Lock out valve is in place. waste transfer when not in use  Waste containers should be suitably labeled Waste containers are labeled according to waste to include details of their contents and that characteristics. Color coding of wastes are their locations are recorded in a tracking implemented to distinguish the waste. Refer to system; non hazardous and hazardous waste procedures.  Transfer or decant only one type of material Risk of decanting of hazardous waste of at any one time; material is assessed and will be assessed for a new type of material.  Conduct regular training and exercises for Regular training and exercices are conducted as site staff regarding emergency procedures; per emergency response procedure.  Provide sufficient firewater containment to Firewater system is in place. prevent uncontrolled discharge of water off site in the event of a fire. 1.1.2.2b Fires and Explosions Industrial hazardous wastes can be flammable and reactive; therefore, special precautions are needed when handling these wastes to prevent accidents. Recommended measures to prevent and prepare for fires and explosions are presented in the General EHS Guidelines. Additional recommended measures include:  Fire fighting equipment appropriate to the Firewater system is in place. type of waste received at the site should be available;

SUPPLEMENTARY DOCUMENT TO LENDER 95

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Minimize the storage of flammable liquids on Flammable liquids are stored at a dedicated site (e.g. fuel, flammable wastes); licensed storage.  Use of a nitrogen atmosphere for organic Low flashpoint organic waste liquids are not waste liquid with a low flashpoint stored in present. tanks;  Perform crushing and shredding operations No flammable or highly volatile substances are under full encapsulation and under an inert crushed nor shredded. or exhausted atmosphere for drums and containers containing flammable or highly volatile substances;  Provide an emergency tipping area for waste It is very unlikely that flammable liquid will be loads identified to be on fire or otherwise on fire. Emergency fire system is in place in case deemed to be an immediate risk; of fire event.  Prepare and annually review a fire risk Fire risks are assessed in regular basis. assessment

1.1.2.2c Air Emissions Air emissions may include releases of Leak detection and repair undertaken on a particulate matter and VOCs from storage routine basis. vessels and waste processing equipment. Hazardous waste incineration facilities should minimize leaks from hazardous waste transfer equipment (e.g. pumps, piping, etc) through the implementation of leak detection and repair program. Additional guidance on VOC emissions prevention and control is addressed in the General EHS Guidelines. Guidance on emissions prevention and control is also addressed above under the MSW section. 1.1.2.2d Water Effluents Storage and processing operations may generate Refer to discussion on water and runoff above. wash water and runoff from waste management areas. General measures for runoff control are addressed under MSW above and in the General EHS Guidelines. In addition, the following methods are recommended for prevention, minimization, and control of water effluents:  Collect and treat wash water and runoff from waste storage and handling areas as potentially hazardous, unless analytical tests determine otherwise;  Segregate runoff from areas storing incompatible wastes.

SUPPLEMENTARY DOCUMENT TO LENDER 96

No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.2.3 Biological and Physico-Chemical Treatment Biological and physico-chemical treatment All wastewaters are treated to meet the processes destroy, separate, concentrate, or international standards. contain waste materials to minimize potential environmental, health, and safety hazards and to facilitate environmentally sound management of the wastes. These treatments are usually applied to aqueous solutions or sludge. Many of the treatment processes are effective only for specific waste types, and can be compromised by constituents from other waste streams; therefore, waste acceptance procedures discussed above are especially important. Many of the processes in this sector incorporate sophisticated equipment technology requiring highly-trained staff. General recommended procedures for biological Not applicable. treatment are addressed under MSW, above. General recommended procedures to prevent, minimize, and control potential environmental impacts from chemical treatment include:  Design and operate facilities in accordance Facilities are designed and operated in with applicable national requirements and accordance with national requirements and internationally accepted standards; international standards.  Prepare a quality control plan, which may Not applicable, generate hazardous wastes are include a definition of personnel rolls, well understood. responsibilities, and qualifications, inspection procedures, and documentation etc.;

 Clearly define the objectives and the expected Not applicable, generate hazardous wastes are reaction chemistry for each treatment well understood. process;  Assess each new set of reactions and Not applicable, as above. proposed mixes of wastes and reagents in a laboratory-scale test prior to waste treatment;  Specifically design and operate the reactor No reactor vessels vessel so that it is fit for its intended purpose;  Monitor the reaction so that it is under Not applicable, as above. control and proceeding towards the anticipated result.

SUPPLEMENTARY DOCUMENT TO LENDER 97

No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.2.3a Air Emissions Air emissions associated with storage and Not applicable, generate hazardous wastes are transfer operations are discussed above. well understood. Wastes are stored in a proper Additional recommended measures to prevent, containers and in a well ventilated area. minimize, and control air emissions include:  Enclose treatment and reaction vessels so that Not applicable, as above. they are vented to the air via an appropriate scrubbing or other air emission abatement system;  Install gas detectors (e.g. suitable for Not applicable, as above. detecting HCN, H2S, and NOX) and implement safety measures to prevent releases of potentially toxic gases;  Link the air space above filtration and Not applicable, as above. dewatering processes to the main air pollution abatement system of the plant, if such a system is in place. 1.1.2.3b Water Effluents Waste water from biological and chemical The five effluent streams are treated to agreed processes includes runoff and leachate TEP effluent standards (the more stringent of (addressed above), pollution control residuals, Indonesian and international standards) before and waste residuals (e.g., separated aqueous discharge. fractions of waste s). General measures for runoff control are addressed under MSW above and in the General EHS Guidelines. Recommended measures to prevent, minimize, and control water effluents include:  Add flocculation agents to the sludge and Floccution agent is added to PWT sludge. wa ste water to be treated to accelerate the sedimentation process and to facilitate the further separation of solids or, where practical, use evaporation (which avoids the use of flocculation agents);  Preventing the mixing of wastes or other No mixing od waste containing metal or streams that contain metals and complexing complexing agents. agents. 1.1.2.3c Waste Residuals Biological and chemical treatments typically Tangguh is moving forward to implement generate solid waste residuals that must be improved initiatives following the 3Rs principle. disposed of. Recommended measures to Trial is underway of reutilizing biosludge and prevent, minimize, and control solid wastes oily sludge for soil improvement. Approval is include: being sought for reutilizing oily sludge as it is categorized as hazardous waste.

SUPPLEMENTARY DOCUMENT TO LENDER 98

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Restrict the acceptance of wastes to be treated Not applicable by solidification/immobilization to those not containing high levels of VOCs, odorous components, solid cyanides, oxidizing agents, chelating agents, high TOC wastes, and compressed gas cylinders.

 Minimize the solubility of metals and reduce Not applicable the leaching of toxic soluble salts by a suitable combination of water washing, evaporation, re-crystallization, and acid extraction when immobilization is used to treat solid waste containing hazardous compounds prior to landfilling.  Based on the waste residual’s physical and Not applicable chemical characteristics, solidify, vitrify, melt, or fuse wastes as required/necessary prior to landfill disposal.  Test the leachability of inorganic compounds USEPA TCLP tests have been undertaken for (e.g., by using the standardized European biosludge as well as LD50 (which is over and Committee for Standardization (CEN) or U.S. above international best practice) and EPA leaching procedures) for waste to be conformance is achieved. landfilled. 1.1.2.4 Hazardous Waste Incineration Incineration involves several integrated process Note that the incinerator is not a typical operations, including feed control and hazardous waste incinerator, in that the waste preparation, combustion, and management of stream does not include the typical range of combustion products (e.g., flue gases and ash). hazardous wastes that hazardous waste Incineration reduces the volume and weight of incinerators normally receive. The incinerator is waste and destroys nearly all of the organic in essence a simple hydrocarbon incinerator and compounds in the waste, but also generate s air the emissions characteristics are more akin to emissions and waste residues that must be small combustion energy systems than to the appropriately managed. operations of hazardous waste incinerators for which these guidelines are intended. To minimize potential environmental, health, and safety impacts, the following general measures should be considered:  Design and operate incinerators in The combustion efficiency for the hazardous accordance with applicable national waste incinerator is at least 99.99% which is requirements and internationally accepted appropriate for the destruction of the wastes standards. These standards typically require being incinerated. destruction efficiencies of 99.99 percent to 99.9999 percent, depending on the hazard characteristics of the waste;

SUPPLEMENTARY DOCUMENT TO LENDER 99

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Implement stringent waste selection A very narrow types is incinerated. A summary procedures so that only wastes that can be of waste procedures. The wastes comprise used effectively managed are accepted; oil (0.15 t/day); amine (0.22 t/day); and hydrocarbon sludge (1.33 t/day). The sludge comes from produced water treatment and small plant spills. The produced water has been tested for metals and the results are below the limits of detection. Therefore the sludge does not contain metals. Small volumes of non chlorine-containing thin plastic (LDPE) will also be incinerated.  Continuously monitor incinerator parameters Stack monitoring is not undertaken including waste feed rate, total continuously given the low volume and the hydrocarbons, temperature (measured at the constant nature of the waste stream. The end of the residence zone), and CO and emissions will not vary significantly and three oxygen (measured at the stack); monthly monitoring by an external contractor has been agreed in the EMPP, Appendix B. Waste feed rate and waste types are measured and recorded daily. The wastes are fed in batch process and the incinerator is not operated continuously.  Install an automatic system to prevent Not applicable given the low volume of the feeding of hazardous waste to the incinerator waste. The liquid waste is fed into the when operating conditions deviate from the incinerator manually and procedures are in acceptable range (e.g., during startup and place to ensure the incinerator is operating shutdown or upset conditions). normally. 1.1.2.4a Air Emissions Air emissions depend on the waste-feed composition and may include NOX, SO2, CO2, metals, acids, and products of incomplete combustion, most notably polychlorinated dibenzo-p-dioxins and -furans (PCDDs and PCDFs). Recommended measures to prevent, minimize, and control air emissions include:  Continuously monitor CO and O2 to evaluate As above, continuous monitoring is not proper combustion conditions; applicable.  Closely track chlorine content of the waste The waste stream does not include chlorine feed and the feed rates of these and other containing materials potential pollutants;  Periodically monitor concentrations of No chlorine and fluorine content wastes are PCDDs, PCDFs, other combustion products, incinerated. and heavy metals in flue gas;

SUPPLEMENTARY DOCUMENT TO LENDER 100

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Reduce the generation and emission of Not applicable PCDDs and PCDFs, if/when chlorine See above. containing wastes are incinerated, by ensuring rapid cooling of flue gas as well as good turbulence of the combustion gas, high temperature, adequate oxygen content, and adequate residence time. De-NOX systems can also reduce PCDD and PCDF emissions;

 Additional emission controls (e.g., activated Not applicable carbon) should be installed if necessary;

 Treat combustion gases to remove metals and Not applicable. No metals and acid gases will be acid gases (e.g., by wet scrubbers); generated.

 Control fugitive emissions from the The combustion zone is sealed. combustion zone (e.g., by sealing the combustion zone or maintaining the combustion zone pressure below atmospheric pressure);

 Minimize fugitive emissions of ash (e.g., use Specific handling procedures are in place to of closed systems to handle fine dry material manage the ash as hazardous waste, however and use of closed containers for transfer to note that the waste stream is in liquid form and the disposal site). ash formation will be limite  Consider the application of waste-to-energy Not feasible for an incinerator of this scale. technologies to help conserve resources and off-set emissions associated with fossil fuel based power generation. 1.1.2.4b Water Effluents Many air pollution control devices use water for Water is not used in the hazardous waste gas cleaning, and generate wastewater that incinerator facility. contains the pollutants removed from the flue gas. Recommended measures to prevent, minimize, and control water effluents include:

 Periodically monitor concentrations of Not applicable PCDDs and PCDFs if/when chlorine containing wastes are incinerated, and other combustion products and heavy metals in wastewater;  Minimize discharge of process wastewater to Not applicable the extent possible while maintaining required air emission control;

SUPPLEMENTARY DOCUMENT TO LENDER 101

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Treat wastewater before discharge (e.g., Not applicable using settling, precipitation of metals, and neutralization). 1.1.2.4c Ash and Residues Incinerator bottom ash contains metal oxides See above regarding ash generation. and halides, which can have significant water solubility (halides) and can potentially constitute a hazardous waste. Fly ash can absorb water-soluble incomplete combustion products from the flue gas. Thus, contaminants may readily leach from untreated incinerator waste residuals. Recommended measures to prevent, minimize, and control solid wastes include:  Treat ash and other solid residue from Hazardous waste Incinerator ash is a designated incineration of industrial hazardous wastes hazardous waste and the very low volumes as hazardous unless it can be demonstrated generated during TEP are to be disposed to a that they are not hazardous; licensed 3rd party contractor.  Periodically monitor concentrations of Not applicable PCDDs, PCDFs, other combustion products, and heavy metals in pollution control residues, and ash or slag;  Reduce the potential for leaching from ash Not applicable residues (e.g., by solidification or verification) prior to final disposition. 1.1.2.5 Landfilling Hazardous constituents in landfilled industrial There is no hazardous waste landfill at site. hazardous wastes can potentially migrate from the landfill as leachate or in the gas phase. Therefore, design and operation criteria are particularly important for landfills that accept industrial hazardous waste so that the waste remains contained during the operating life of the landfill, including after closure of the landfill.

General recommended measures to prevent, minimize, and control potential environmental impacts from landfilling of industrial hazardous wastes include:  Design and operate the landfill in accordance with applicable national requirements and internationally accepted standards;

SUPPLEMENTARY DOCUMENT TO LENDER 102

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Divide the landfill into different cells to separate wastes with different properties;  Maintain records of the wastes received, including sources, analytical results, and quantity;  Record on a map the location and dimensions of each landfill cell and the approximate location of each hazardous waste type within the landfill cell. 1.1.2.5a Leachate Generation Not applicable Storm water controls are addressed under MSW landfills, above, and in the General EHS Guidelines. In addition, recommended measures to prevent, minimize, and control leachate generation include:  Install a liner system, preferably consisting of two or more liners with a leachate collection system above and between the liners, to prevent migration of wastes out of the landfill to the adjacent subsurface soil or ground water or surface water at anytime during the active life of the landfill and after closure, as long as the wastes remain hazardous. The liners should be: o Constructed of low-permeability materials that have appropriate chemical properties and sufficient strength and thickness to prevent failure due to pressure gradients, physical contact with the waste or leachate to which they are exposed, climatic conditions, the stress of installation, and the stress of daily operation; o Placed upon a foundation or base capable of providing support to the liner and resistance to pressure gradients above and below the liner to prevent failure of the liner due to settlement, compression, or uplift; o Installed to cover all surrounding earth likely to be in contact with the waste or leachate.  Install a leachate collection and removal system immediately above the upper liner to

SUPPLEMENTARY DOCUMENT TO LENDER 103

No. IFC Health & Safety Guidelines for Waste Conformance Status Management collect and remove leachate from the landfill so that leachate depth over the liner does not exceed 30 cm. The leachate collection and removal system should be: o Constructed of materials that are chemically resistant to the waste managed in the landfill and the leachate expected to be generated and of sufficient strength and thickness to prevent collapse under the pressures exerted by overlying wastes, waste cover materials, and by any equipment used at the landfill; o Designed and operated to function without clogging through the scheduled closure of the landfill.  In a two-liner system, install a leak detection system between the liners. This leak detection system should be capable of detecting, collecting, and removing leaks of hazardous constituents at the earliest practicable time through all areas of the top liner likely to be exposed to waste or leachate;  At final closure of the landfill or upon closure of any cell, cover the landfill or cell with a final cover designed and constructed to: o Provide long-term minimization of migration of liquids through the closed landfill; o Function with minimum maintenance; o Promote drainage and minimize erosion or abrasion of the cover; o Accommodate settling and subsidence so that the cover's integrity is maintained; and o Have a permeability less than or equal to the permeability of any bottom liner system or natural subsoils. 1.1.2.5b Groundwater and Leachate Monitoring Not applicable Groundwater monitoring is addressed under MSW landfills, above. In addition, recommended measures for leachate and site

SUPPLEMENTARY DOCUMENT TO LENDER 104

No. IFC Health & Safety Guidelines for Waste Conformance Status Management inspections and monitoring include:  During construction, inspect the liners for uniformity, damage, and imperfections.  Inspect the landfill regularly (e.g., after storms and weekly during operation and quarterly after closure) to detect evidence of any of deterioration, malfunctions, or improper operation of run-on and run-off control systems, such as erosion of the final cover; proper functioning of wind dispersal control systems, where present; and the presence of leachate in and proper functioning of leachate collection and removal systems. 1.1.2.5c Landfill Gas If biodegradable wastes are disposed of, landfill Not applicable gas can be generated and should be controlled and monitored, as described for MSW landfills, above. 1.1.2.5d Closure and Post-Closure Landfill facility operators should plan for the Not applicable closure and postclosure care of the facility as described previously (see Municipal Solid Waste – Landfills). 1.1.3 Industrial Non-Hazardous Waste Solid industrial non-hazardous wastes are defined through national legislation as they originate from industrial sources but do not meet the definition of hazardous waste with regards to their specific origin with in the industrial process or its characteristics. Examples of non-hazardous industrial wastes include any garbage, refuse, or sludge from a waste treatment plant, water supply treatment plant, or air pollution control facility, and other discarded material, including solid, liquid, semisolid, or contained gaseous material resulting from industrial operations; inert construction / demolition materials; refuse, such as metal scrap and empty containers; and residual waste from industrial operations, such as boiler slag, clinker, and fly ash.

SUPPLEMENTARY DOCUMENT TO LENDER 105

No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.1.3.1 Waste Collection and Transport Transportation of industrial non-hazardous Refer to the discusions in 1.1.1.1 waste requires appropriate equipment and suitably trained staff, and mitigation measures described above for hazardous waste can be generally applicable to industrial non-hazardous waste. Additional recommended measures to prevent, minimize, and control potential environmental risks associated with waste collection and transport include:  Vehicles and other equipment used for collection industrial non-hazardous wastes should not be used for collection of MSW without prior cleaning to remove waste residues.  Vehicles and other equipment used for collection industrial non-hazardous wastes should not be used for distribution of goods (e.g., mulch). 1.1.3.2 Waste Receipt, Unloading, Processing, and Storage As with MSW and industrial hazardous waste, Refer to the discusions in 1.1.1.1 facilities managing industrial non-hazardous waste should understand and control the nature of the waste that is accepted for storage, treatment, or disposal so that the waste can be managed safely and effectively. Waste acceptance and analysis procedures should be implemented considering the nature and expected variability of the incoming waste streams, and generally should be similar to measures suggested for industrial hazardous waste management facilities, described above. 1.1.3.3 Biological and Physico-Chemical Treatment Treatment of non-hazardous industrial waste Not applicable as the non-hazardous industrial can help to reduce the volume and toxicity of wastes are either re-used or disposed to landfill. waste prior to disposal. Treatment can also make a waste amenable for reuse or recycling. Consequently, a facility managing non- hazardous industrial waste might elect to apply treatment. For example, treatment might be incorporated to address small quantity VOC emissions from a waste management unit, or a facility might elect to treat a waste so that a less

SUPPLEMENTARY DOCUMENT TO LENDER 106

No. IFC Health & Safety Guidelines for Waste Conformance Status Management stringent waste management system design could be used. Treatment and post- treatment waste management methods can be selected to minimize environmental impact, keeping in mind that treatment residuals, such as sludge, are wastes themselves that will need to be managed. In general, recommended mitigation measures are similar to those for industrial hazardous waste treatment facilities, discussed above. 1.1.3.4 Incineration Incineration might be considered for industrial Not applicable, as above non-hazardous wastes, including solids, and especially liquids, with heat value that can be recovered during incineration. Recommended mitigation measures for industrial hazardous waste incineration facilities, discussed above, should be considered and adopted for industrial non-hazardous incineration facilities as appropriate, based on the nature of the incoming waste stream. 1.1.3.5 Landfilling Industrial non-hazardous waste landfills, like Refer to the discussions in 1.1.1.7 other landfill facilities, depend on waste containment, including leachate collection and treatment (and where appropriate, gas management) to control potential hazards associated with the waste. Industrial non- hazardous waste landfills might accept only one type of waste (i.e., monofills), or a variety of wastes. The nature of the incoming wastes will determine whether the design and controls are more similar to MSW or industrial hazardous waste landfills. In addition to measures discussed for MSW and industrial hazardous waste landfills, the following measures are recommended to prevent, minimize, and control potential environmental impacts associated with industrial nonhazardous waste landfills.  Comply with applicable national and local requirements and internationally accepted standards for industrial non-hazardous waste landfills, including provisions for

SUPPLEMENTARY DOCUMENT TO LENDER 107

No. IFC Health & Safety Guidelines for Waste Conformance Status Management monitoring;  Do not dispose of putrescible wastes, unless the facility is equipped to manage these types of wastes, with landfill gas collection and treatment systems and degradation products will not interact with the other industrial wastes in a manner that would increase their toxicity or mobility;  Do not dispose of liquids, explosive wastes, radioactive or nuclear materials, or medical wastes together with non-hazardous industrial wastes or by landfilling;  Design the landfill systems, including selection of liner and cover materials, so that industrial wastes and degradation products are contained;  Monitor groundwater and surface water quality in the vicinity of the facility in a manner similar to that recommended for industrial hazardous waste management facilities;  Develop and follow a written schedule for inspecting monitoring equipment, safety and emergency equipment, and operating and structural equipment (such as dikes and sump pumps) that are important to preventing, detecting, or responding to potential environmental or human health hazards;  Implement a training program so that facility personnel are able to respond effectively to emergencies by familiarizing them with emergency procedures, emergency equipment, and emergency systems.

1.2 Occupational Health and Safety Occupational health and safety impacts during Tangguh has rigorous and documented OH&S the construction and decommissioning of waste procedures supported by internal and external management facilities are common to other audits, training programs and key performance large industrial projects and are addressed in indicators. Tangguh performs very well against the General EHS Guidelines. The most BP global performance indicators, significant occupational health and safety impacts typically associated with workers at

SUPPLEMENTARY DOCUMENT TO LENDER 108

No. IFC Health & Safety Guidelines for Waste Conformance Status Management waste management facilities occur during the operational phase and include:  Accidents and injuries  Chemical exposure  Exposure to pathogens and vectors 1.2.1 Accidents and Injuries Physical hazards encountered at waste management facilities are similar to those at other large industrial projects and are addressed in the General EHS Guidelines. Solid waste workers are particularly prone to accidents involving trucks and other moving equipment, so traffic management systems and traffic controllers are recommended. Accidents include slides from unstable disposal piles, cave-ins of disposal site surfaces, fires, explosions, being caught in processing equipment, and being run over by mobile equipment. Other injuries occur from heavy lifting, contact with sharps, chemical burns, and infectious agents. Smoke, dusts, and bioaerosols can lead to injuries to eyes, ears, and respiratory systems. Mitigation measures for accidents and injuries This requirement is not applicable for a landfill are partially addressed in the General EHS of this scale. Guidelines. In addition, the following procedures are recommended to prevent, minimize, and control accidents and injuries at waste management facilities:  In landfills, conduct compaction of wastes The landfill is designed to ventilate landfill gas. in thin layers using heavy equipment and Underground fires is very unlikely. place regular cover material over each compacted layer of waste, so that any underground fires within a waste cell are not able to spread throughout the landfill and lead to significant cave-ins;  Ventilate landfill gas so that underground As above fires and explosions do not occur;  Use maximum side slopes of 3:1 in non- Slope ratio is followed seismic areas and lower slopes (e.g., 5:1) in seismic areas, with regular drainage of water so that saturated conditions do not develop and lead to slope subsidence; Workers are provided with appropriate PPE  Provide workers with appropriate based on specific hazards and risks at the protective clothing, gloves, respiratory face

SUPPLEMENTARY DOCUMENT TO LENDER 109

No. IFC Health & Safety Guidelines for Waste Conformance Status Management masks and slip-resistant shoes for waste workplace transport workers and hard-soled safety shoes for all workers to avoid puncture wounds to the feet. For workers near loud equipment, include noise protection. For workers near heavy mobile equipment, buckets, cranes, and at the discharge location for collection trucks, include provision of hard hats;  Provide all landfill equipment with Not applicable enclosed air conditioned cabs and roll-over protection;  Provide refuse collection vehicles and Not applicable landfill equipment with audible reversing alarms and visible reversing lights; Not applicable  Improve the storage of solid wastes at the

source so that the loads to be collected are

well contained and not too heavy; Not applicable  Locate exhaust pipes on waste collection

vehicles so that exhaust does not discharge

into the breathing zone of workers on the

riding steps; Not applicable  Design collection routes to minimize, or possibly eliminate, crossing traffic that is going in the opposite direction; Not applicable  Provide two-hand constant-pressure co ntrols for collection vehicles with compaction mechanisms;  Restrict access to disposal sites such that Only authorized personnel only permitted in the only safety - trained personnel with vicinity protective gear are permitted to high-risk areas;  Segregate people from operating trucks in As above recycling and transfer stations;  Use automated systems to sort and transfer Not applicable waste to the extent practical in order to minimize contact with the waste;  Provide workers with communications Handheld radio is provided tools, such as radios. Special signaling codes have been developed for communications on landfill sites;  Minimize sorting from the ground by Not applicable providing conveyor belts and/or tables that facilitate sorting;

SUPPLEMENTARY DOCUMENT TO LENDER 110

No. IFC Health & Safety Guidelines for Waste Conformance Status Management  Establish engineering and materials norms Not applicable for special facility and stationary equipment design requirements that minimize exposure to hazards (e.g., ventilation, air conditioning, enclosed conveyor belts, low loading and sorting heights, non- skid flooring, safety rails on stairs and walkways, spill protection and containment, noise control, dust suppression, gas alarm systems, fire alarm and control systems, and evacuation facilities). 1.2.2 Chemical Exposure Chemical hazards encountered at waste The full composition of wastes and their management facilities are similar to those at potential hazards are identified and known. other large industrial facilities, such as toxic and Risks have been assessed and mitigated. asphyxiating gases, and are addressed in the General EHS Guidelines. However, the full composition of wastes and their potential hazards is often unknown. Even municipal solid waste (MSW) often contains hazardous chemicals, such as heavy metals from discarded batteries, lighting fixtures, paints, and inks. The following procedures are recommended to prevent, minimize, and control chemical exposure at waste management projects:  Control and characterize incoming waste The wastes characteristic is well-understood. (see waste receipt, unloading, processing and storage);  Provide adequate personnel facilities, Personnel facilities are provided in the waste including washing areas and areas to management facility change clothes before and after work;  Ventilate enclosed processing areas (e.g., Not applicable dust in waste size reduction areas, VOCs driven off by high temperatures during composting);  Monitor breathing zone air quality in work Not applicable areas at processing, transfer and disposal facilities. Direct-reading instruments that measure methane and oxygen deficiency are of primary importance; these include combustible gas indicators, flame ionization detectors, and oxygen meters. At waste treatment/disposal facilities, volatile

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management organics should also be analyzed in the biodegradation gases being collected and/or vented. In waste handling, sorting, and composting facilities, monitoring for organic dust is needed;  Prohibit eating, smoking, and drinking Designated areas are provided in the waste except in designated areas; management facility  Provide air filtered and air conditioned cabs Not applicable for heavy mobile equipment used at landfills as necessary. 1.2.3 Dust Waste processing can generate nuisance and Tangguh does not generate much dust. hazardous dust, including organic dust. Dust control measures discussed in Section 1.1 above, will also help to reduce worker exposure to dusts. General mitigation measures for dust are also addressed in the General EHS Guidelines. 1.2.4 Pathogens and Vectors Workers can be exposed to pathogens contained Pathogens-contaminated wastes are managed in in manure and animal excreta found in MSW separate operations. The wastes are categorized from the disposal of sludge, carcasses, diapers, as medical wastes and sent to licensed 3 rd party and yard trimmings containing domestic animal offsite. waste. Uncontrolled dumping of MSW attracts rats, flies, and other insects that can transmit diseases. Processing of MSW can also generate bioaerosols, suspensions of particles in the air consisting partially or wholly of microorganisms, such as bacteria, viruses, molds, and fungi. These microorganisms can remain suspended in the air for long periods of time, retaining viability or infectivity. Workers may also be exposed to endotoxins, which are produced within a microorganism and released upon destruction of the cell and which can be carried by airborne dust particles. The following measures are recommended to prevent, minimize, and control pathogens and vectors:  Provide and require use of suitable personal Suitable PPEs are provided. protective clothing and equipment;  Provide worker immunization and health Routine Medical Check Up is performed to monitoring (e.g. for Hepatitis B and every workers. tetanus);  Maintain good housekeeping in waste Housekeeping is maintained in the waste

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management processing and storage areas; management facility  Use automatic (non- manual) waste Not applicable handling methods if practical;  For landfills, promptly emplace, compact Not applicable and cover of wastes in defined cells, especially for waste with the potential to attract vermin and flies, such as food wastes (especially animal by-products if accepted at the facility) and tannery wastes;  Clean and wash with disinfectant the cabins Not applicable of heavy mobile equipment used at regular intervals;  For composting, maintain aerobic Not applicable conditions and proper temperatures in the windrows. Isolate workers from spore dispersing components of the composting process such as mechanical turning (e.g., by using tractors or front-end loaders with enclosed air-conditioned or heated cabs). Aeration systems are preferred over manual turning;  Maintain adequate temperature and Not applicable retention time in biological treatment systems to achieve pathogen destruction (e.g., 55ºC for at least 3 consecutive days in most compost situations and 55ºC for 15 days in windrows);  Grade the area properly to prevent ponding Grading is performed (to minimize insect breeding areas);  Use integrated pest-control approaches to Pest control is undertaken control vermin levels, treating infested areas, such as exposed faces and flanks with insecticide, if necessary;  Provide and require use of dust masks or Dust masks or respirators are provided respirators under dry and dusty conditions (e.g., when compost is being turned). Charcoal-filled respirators also reduce odor perception;  Provide prompt medical attention for cuts and bruises. Cover open wounds to prevent First aid kit is provided at the waste contact with the incoming loads or management facility. Clinic is open 24 hours. feedstock;  Fully enclose the waste management site with fencing so that no livestock or wildlife The waste stream does not originate from

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management is able to come in contact with the waste, sources that would include livestock or zoonotic which contains significant potential to disease risks. enable the spread of livestock and zoonotic disease, as well as spillover disease to wildlife. Provide daily cover of wastes to minimize the attraction to birds, which can become infected with avian influenza and other bird diseases that can then be carried off-site. 1.3 Community Health and Safety Community health and safety issues related to No access to communities. Nearest community the construction of waste management projects of Tanah Merah several km to the west. may include emissions from the solid wastes and construction site issues which are addressed in the General EHS Guidelines.

Community health and safety impacts which occur during the operational and decommissioning phases of waste management facilities may include:  General occupational and environmental health issues associated with waste scavenging  Physical, chemical, and biological hazards  Litter  Noise  Dust and odors 1.3.1 General Occupational and Environmental Not applicable, as above Health Issues Associated with Waste Scavenging The presence of informal sector workers laboring in municipal or mixed waste disposal sites in search of commercially valuable materials is a common place occurrence in developing countries. The causes and dynamics are the result of complex social, cultural, labor, and economic factors that are clearly outside of the scope of this guidance document. However, the following principles should be considered in managing the occupational, health, and safety risks of informal laborers:  Waste scavenging should not be allowed under any circumstances in hazardous and non-hazardous industrial waste

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management management facilities;  Facilities dedicated to the management of MSW should work with government entities in the development of simple infrastructure that can allow for the sorting of waste, helping groups of scavengers form cooperatives or other forms of micro- enterprises, or formally contracting them to provide this function. The outright displacement of scavenging workers as an occupational health and safety management strategy, without the provision of viable alternatives, should be avoided;  Operators of existing facilities with scavenging workers should exercise commercially viable means of formalizing their work through the creation of management programs that include: o Allowing only registered adults on the site, excluding children and domestic animals. Striving to provide alternatives to access to childcare and education to children; o Providing protective gear, such as shoes. face masks, and gloves; o Arranging the disposal layout and provide sorting facilities to improve access to recyclables while reducing their contact with other operations, thus minimizing potential hazards; o Providing water supply for washing and areas for changing clothes; o Implementing education campaigns regarding sanitation, hygiene, and care of domestic animals; o Providing a worker health surveillance program including regular vaccination and health examinations. 1.3.2 Physical, Chemical, and Biological Hazards Not applicable, as above Visitors and trespassers at waste management facilities may be subject to many of the hazards described for site workers. In particular, waste pickers, looking for recyclable materials and food scraps for animal feeding, often work

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management informally at waste transfer and disposal sites, especially MSW facilities, typically living adjacent to the site in poor housing conditions, with minimal basic infrastructure for clean water and sanitation. Waste pickers may be encounter numerous risks, including contact with human fecal matter, paper that may have become saturated with toxic materials, bottles with chemical residues, metal containers with residue pesticides and solvents, needles and bandages (containing pathogenic organisms) from hospitals, and batteries containing heavy metals. Exhaust fumes of waste collection trucks traveling to and from disposal sites, dust from disposal operations, and open burning of waste all contribute to potential occupational health problems.

Recommended measures to prevent, minimize, and control physical, chemical, and biological hazards to the community include:  Restrict access to waste management facilities by implementing security procedures, such as: o Perimeter fencing of adequate height and suitable material, e.g. chain link, stock proof palisade; o Lockable site access gate and buildings; o Security cameras at key access points linked to recording equipment and remote access CCTV, where required; o Security alarms fitted to buildings and storage areas; o Review of site security measures annually or whenever a security breach is reported o Use of a site visitor register; o Immediate repair of fencing/access points if damaged; and o Lighting of site during night time where necessary. As this may cause light nuisance to neighbors, the lighting installations should be selected to minimize ambient light pollution.

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management 1.3.3 Litter Not applicable, as above Uncollected garbage and litter spread beyond the waste management facility boundaries by wind, vermin, and vehicles can directly spread disease; attract rats, flies, and other vectors; and expose the community to hazardous substances. Scavenging birds, such as gulls and crows, commonly congregate on landfill sites accepting household waste. They disturb newly tipped and partially covered waste whilst searching for food, and lead to complaints from adjoining residents and landowners about food scraps, excreta and other waste dropped away from the landfill. Litter control is addressed in Section 1.1, above. 1.3.4 Noise Not applicable, as above Noise is typically generated by waste processing and treatment equipment as well as vehicular traffic on the site and bringing waste and materials to and from the facility. Sources of noise and abatement measures are addressed in Section 1.1, above, and the General EHS Guideline. In addition, facility operators should coordinate hours of operation with adjacent land uses. 1.3.5 Dust and Odors Not applicable, as above Dust and odors from waste management facilities can be a nuisance to the neighboring community. Organic dust can also carry disease- causing microorganisms. Dust and odor controls are addressed in Section 1.1 and in the General EHS Guidelines. In addition, the following measures are recommended to prevent, minimize, and control community exposure to dust and odors from waste management facilities:  Provide adequate buffer area, such as hills, trees, or fences, between processing areas and potential receptors.  Avoid siting facilities near densely populated neighborhoods and installations with potentially sensitive receptors, such as hospitals and schools. Site facilities downwind from

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management potential receptors, if possible. 2.0 Performance Indicators and Industry Benchmarks 2.1 Environmental Performance 2.1.1 Emissions and Effluents Tables 1 through 4 present examples of In conformance with Indonesian Regulations emissions and effluent standards for waste management facilities from the European Union Refer TEP AMDAL approval of 2014. and the United States for this sector. These emissions and effluent values are assumed to be Only partly applicable to International achievable under normal operating conditions standards given the small capacity, remoteness in appropriately designed and operated facilities and security of the facilities through the application of pollution prevention and control techniques discussed in the The EU and US emissions and effluent preceding sections of this document. These standards apply to MWS and large industrial levels should be achieved at all times as facilities. They do not apply to hazardous waste described in the above-referenced standards. incinerators with capacity <10t/day (EU) or to Deviation from these levels in consideration of 15,000 t/yr and more (EHS Waste Management specific, local project conditions should be Guidelines) or to small remote incinerator more justified in the environmental assessment. than 40 km driving distance to nearest municipal solid waste landfill (US). Effluent guidelines are applicable for direct Meet international standards discharges of treated effluents to surface waters for general use. Site-specific discharge levels may be established based on the availability and conditions in the use of publicly operated sewage collection and treatment systems or, if discharged directly to surface waters, on the receiving water use classification as described in the General EHS Guideline. These levels should be achieved, without dilution, at least 95 percent of the time that the plant or unit is operating, to be calculated as a proportion of annual operating hours. Deviation from these levels in consideration of specific, local project conditions should be justified in the environmental assessment. 2.1.2 Environmental Monitoring 2.1.2.1 Environmental monitoring programs for this Monitoring at agreed frequency as per AMDAL sector should be implemented to address all RPL (Environmental Monitoring Plan) by activities that have been identified to have external accredited contractor and reported six- potentially significant impacts on the monthly to GoI. environment, during normal operations and upset conditions. Environmental monitoring External audits by Lenders Independent activities should be based on direct or indirect Environmental and Social Consultant and by

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management indicators of emissions, effluents, and resource GOI (PROPER audit process whose results are use applicable to the particular project. published). 2.1.2.2 Monitoring frequency should be sufficient to The monitoring frequency is sufficient to provide representative data for the parameter provide representative data. Monitoring is being monitored. Monitoring should be conducted by trained individuals and record conducted by trained individuals following keeping and calibration and maintenance monitoring and record-keeping procedures and procedures are in place. using properly calibrated and maintained equipment. Monitoring data should be analyzed and reviewed at regular intervals and compared with the operating standards so that any necessary corrective actions can be taken. Additional guidance on applicable sampling and analytical methods for emissions and effluents is provided in the General EHS Guidelines. 2.2 Occupational Health and Safety Performance 2.2.1 Occupational Health and Safety Guidelines Occupational health and safety performance Risk assesments indicate there are very limited should be evaluated against internationally circumstances in which workers would be published exposure guidelines, of which occupationally exposed to hazards at levels examples include the Threshold Limit Value which would require monitoirng of TLV and (TLV®) occupational exposure guidelines and BEI levels. Biological Exposure Indices (BEIs®) published by American Conference of Governmental Industrial Hygienists (ACGIH), the United States National Institute for Occupational Health and Safety (NIOSH), Permissible Exposure Limits (PELs) published by the Occupational Safety and Health Administration of the United States (OSHA), Indicative Occupational Exposure Limit Values published by European Union member states, or other similar sources. 2.2.2 Accident and Fatality Rates Projects should try to reduce the number of Tangguh sets safety targets each year and aims accidents among project workers (whether for continuous improvement. All targets have directly employed or subcontracted) to a rate of been exceeded to date for T1/2. zero, especially accidents that could result in lost work time, different levels of disability, or even fatalities. Facility rates may be benchmarked against the performance of facilities in this sector in developed countries through consultation with published sources

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No. IFC Health & Safety Guidelines for Waste Conformance Status Management (e.g. US Bureau of Labor Statistics and UK Health and Safety Executive). 2.2.3 Occupational Health and Safety Monitoring The working environment should be monitored Full records of occupational incidents, diseases, for occupational hazards relevant to the specific dangerous occurrences and accidents are project. Monitoring should be designed and maintained. implemented by credentialed professionals as part of an occupational health and safety monitoring program. Facilities should also maintain a record of occupational accidents and diseases and dangerous occurrences and accidents. Additional guidance on occupational health and safety monitoring programs is provided in the General EHS Guidelines

7.3.1. Existing Waste Management Facilities

T1/2 are supported by a non-hazardous waste landfill and two non-hazardous waste incinerators. Hazardous waste is temporarily stored in permitted storage facilities on site before transfer to a licensed 3rd party hazardous waste contractor

Figure 13 T1/2 Waste Management Facilities

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Figure 14 T1/2 Waste Management Flow Chart

7.3.2. Waste Hierarchy

International Good Practice requires the adoption of a waste hierarchy designed to minimize the generation of waste and maximize its use and recycling. At Tangguh current operations, continuing through into TEP, the Waste Hierarchy is actively practiced with a commitment to continuous improvement through programs to reduce waste and introduce new methods of waste recycling and re-use.

As described in the following sections the generation of hazardous waste has been progressively reduced on an annual basis partly by replacement with alternative products such as mercury waste catalysts and by incineration of non-hazardous wastes; plastics and metals are recycled, organic waste is composted and wood waste is chipped and used as a bulking agent for the compost. Used oil is processed into biodiesel fuel in a pilot plant and a larger scale production plant is proposed. The low volumes of hazardous waste generated which are currently disposed to 3rd party contractor’s hazardous waste facility will be reduced by incineration of the liquid component on site, a reduction of about 25% which enhances the

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hazardous waste landfill capacity and reduces the risk associated with land and sea transport of liquid wastes over a distance of 3,500 km.

. Landfills, the existing non-hazardous waste landfill has four cells with a total capacity of 60,000 m3 supported by an engineered leachate collection system and leachate pond. Leachate is treated prior to discharge to ensure that discharge criteria is met.

Waste types disposed to landfill: Food waste (excess waste which cannot be composted due to limited composter capacity); Non-hazardous inert waste (i.e. furniture, tarpaulin, HDPE liner, and expired PPE); Sewage Treatment Plant sludge; and Produced Water Treatment Plant bio-sludge (trial is underway for reusing the sludge as soil ameliorant, which will reduce future bio-sludge disposed to landfill).

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100000 90000 80000 70000 60000 Food Waste 50000 40000 STP Sludge 30000 Grease 20000 10000 Inert Waste 0

Figure 15 T1/2 Generated landfill waste (kg) in 2015

. Incinerators - Two units (1 unit as spare) each of 2 tons/day capacity for non- hazardous combustible waste such as papers, cardboard boxes and thin plastic. . Wood Chipper - One unit of wood chipper for chipping used planks. Woodchips are used as composting media, landscaping and landfill cover. . Can Compactor and Plastic Shredder - Recyclable wastes i.e. aluminium cans are compacted, plastic bottles are chipped and shipped to 3rd party contractor in Sorong.

9000 8000 7000 6000 5000 Can 4000 Plastic 3000 Glass 2000 Plastic Jerry Can 1000 0

Figure 16 T1/2 generated recyclable waste (kg) in 2015

. Composter - One unit of composter with capacity 1.5 tons/day mainly for food waste with added woodchips to provide structure for good aeration. Compost product is

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used for landscaping at site and sometimes is donated to local communities for their horticultural program supported by BP CRP Team.

16000.00 14000.00 12000.00 10000.00 8000.00 6000.00 Food Waste 4000.00 Wood Chip 2000.00 0.00 July May June April March August January October February December November September

Figure 17 T1/2 generated food waste and woodchips (kg) to composter in 2015

. Hazardous Waste - All hazardous waste produced from existing T1/2 activities are temporarily stored in two licensed temporary hazardous waste storage facilities and shipped out to the Tangguh facility at Lamongan in Java where the wastes are handed over to licensed third party hazardous waste treatment and disposal facility) Wastes are then transported by land to the licensed third party hazardous waste treatment and disposal facility in Cileungsi, West Java. It can be seen from Figure 6 below that the tonnage of T1/2 hazardous waste has been decreasing annually from about 2,800 tons in 2012 to about 1,300 tons in 2015.

3000

2500

2000

1500

1000

500

0 2012 2013 2014 2015

Figure 18 T1/2 Annual generated hazardous waste (tons) between 2012 and 2015

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7.3.3. TEP Proposed Facilities

7.3.3.1. Construction

TEP Contractor will establish a Temporary Waste Management Facility (TWMF). The complex will be stand-alone from the existing T1/2 facility and will serve all generated wastes during T3 construction phase. The complex comprises temporary hazardous waste storage and non-hazardous waste treatment equipment i.e incinerator, wood chipper, plastic shredder, can compactor and laydown area.

 Landfill. Two cells of the existing operations landfill (30,000 m3 capacity) will be utilized by TEP Contractors for their generated non-hazardous waste which cannot be reuse, recycled, and incinerated.  Non-Hazardous Waste Incinerator. TEP Contractor plans to install 2 units of 4 t/day incinerators for non-hazardous combustible wastes.  Wood chipper, 2 unit with a capacity 5 m3/day.  Plastic shredder, 1 unit with a capacity of 4 m3/day.  Can compactor, 1 unit with a capacity of 2 m3/day for non-hazardous waste and 1 unit with a capacity of 5 m3/day for hazardous waste.  Hazardous Waste Management. All wastes will be temporarily stored in newly built temporary hazardous waste storage before shipping offsite to licensed hazardous waste treatment and disposal facility.

7.3.3.2. Operation

TEP Contractor, as part of deliverables, will establish an Integrated Waste Management Facility (IWMF) for operations phase replacing current equipment. The facility will consist of:

 Temporary Hazardous Waste Storage;  Hazardous Waste Laydown for ISO Tanks and Open Top Container;  unit of 3 t/day capacity non-hazardous waste incinerator;  1 unit of 3 t/day capacity hazardous waste incinerator;  1 unit of composter;  1 unit of can compactor;  1 unit of plastic shredder; and  An additional two cells with 30,000 m3 total capacity to be added to existing landfill.

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7.4. Description of Non-Hazardous Waste

Estimated volumes of Non-Hazardous Waste during T1 – T3 operations are given below. The projected annual volume of non-hazardous waste is about 12,800 m3 (10,700 t equivalent at average density of 1.2) of which about 3,000 tons goes to landfill, up to 1,500 tons goes to incinerator and the remainder is either recycled or composted.

Table 11 Estimated Volumes of Non-Hazardous Wastes during T1-3 Operations

Non-Hazardous Waste Estimation of Quantity m3/month Category Minimum Maximum Average

Organic 143 340 240

Recyclable 40 170 94

Combustible 470 650 530

Inert 22 180 90

Wood 25 240 110

TOTAL 700 1,580 1,064

. To Landfill -furniture, tarpaulin, rockwool, PVC pipe, HDPE, LDPE plastics and expired PPE. . To Incinerator -paper, thin plastic. . Recycle -aluminium cans, plastic bottles, glass. . Reuse -used tyres, cooking oil for bio-diesel (trial), bio-sludge for soil ameliorant (trial), food waste as compost.

Non-Hazardous Waste Incinerator

The specification for the Non-Hazardous waste incinerators is for emission standards to conform with the standards given in Table 13 with the following operating parameters.

. Capacity 2 x 2 t/day . Maximum operating incineration period 10 hrs/day . Operating temperature chamber 1 >800 OC . Operating temperature chamber 2 >1,000 OC

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. O2 content in flue gas 2% by wet volume . Residence time in incinerator chamber 2 seconds with complete combustion to be considered . Waste Volumes o Minimum 41.36 t/month o Average 46.64 t/month o Maximum 57.2 t/month . Waste Characteristics o Paper/cardboard 70% o Plastic (LDPE or similar) 20% o Food waste with 70% water content 10% The incinerator operating at 10 hrs/day has the capacity to accept about 90 t/month of paper, plastic and food waste (surplus to composting capacity).

7.5. Description of Hazardous Waste

Hazardous waste to be generated during T1-3 Operations comprises the following.

Table 12 Description of hazardous waste generated during T1 – T3 Operations Liquid Hazardous Waste Solid Hazardous Waste

Used oil Used filters

Used diesel fuel Ex carbon filters

Hydrocarbon and DAF sludge Dry and wet battery

Chemical Waste (amine) Oily rags, absorbents, gloves

Empty cans, drums, containers

Used toner, cartridges

Clinical waste

Pressurised cans

Fluorescent lights

Mercury contaminated filters

Incinerator ash

. To Incinerator -amine wax, oily sludge, used fuel, used oil

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. To Third Party Contractor -all other hazardous wastes including hazardous incinerator ash. Note that mercury waste catalysts are recovered and disposed only during Turn Around (TAR) activities which occur annually. Others are generated during routine maintenance and account for the differential between minimum and maximum monthly tonnages.

Hazardous Waste Incinerator The specification for the hazardous waste incinerator is for emission standards to conform with the standards given in Table 14 with the following operating parameters.

. Capacity 3 t/day . Maximum operating incineration period 10 hrs/day . Operating temperature Chamber 1 >1,000 OC . Operating temperature Chamber 2 >1,200 OC

. O2 content in flue gas 2% by wet volume . Waste Characteristics o Used oil, liquid 0.15 t/day o Used diesel and jet fuel, liquid 0.07 t/day o Amine, liquid 0.22 t/day o Hydrocarbon sludge 1.33 t/day The total normal daily hazardous waste volume for incineration is therefore specified as 1.78 t/day with a 60% increase during Turnaround.

7.6. Indonesian Requirements

The Indonesian Regulatory Requirements for Landfills are specified under Decrees 225/1996 and 128/2003. However the international good practice USEPA landfill design requirements* and those of the Geosynthetic Research Institute** (for HDPE liner) are more applicable and form the basis for the landfill specifications.

*EPA 600-R-93-182 QA/QC for waste containment facilities

**EPA 530-R-93-017 Solid waste disposal facility criteria – Technical Manual for Leachate Drainage

The Indonesian Regulatory Requirements for Incinerators are as follows:

. Minister of Environment Decree No. 13 Year 1995 regarding Emission Standard for Stationary Source; and . Head of Environmental Impact Management Agency Decree KEP- 03/BAPEDAL/09/1995 regarding Technical Guidelines for Hazardous Waste Management

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Subsequent to the TEP AMDAL approval a new Hazardous Waste Regulation PP101/2014 was released. It is obligatory for Tangguh to conform to the requirements of new regulations. It is recognized in the industry that B3 waste management requirements of PP101/2014 meet a very high international standard and will be adopted for TEP. The numerical standards specified for TEP are derived from the Indonesian regulatory standards as tabulated below.

Table 13 Numerical Standard for Non-Hazardous Waste Incinerator

TEP Standard 1 No Parameter (mg/Nm 3)

1 Nitrogen Oxide as NO2 1000

2 Sulphur Dioxide (SO2) 800 3 Total Reduced Sulphur 35 (H2S) 1 Tangguh Expansion Project Standard refers to Minister of Environment Decree no. 13 Year 1995 regarding Emission Standard for Stationary Source

Table 14 Numerical Standard for Hazardous Waste Incinerator

Indonesian No Parameter Standard 1 (mg/m 3) 1 Particulate 50

2 Sulphur Dioxide(SO2) 250

3 Nitrogen Dioxide (NO2) 300 4 Hydrogen Fluoride (HF) 10 5 Hydrogen Chloride (HCl) 70 6 Carbon Monoxide (CO) 100 7 Total Hydrocarbon (as 35

CH4) 8 Arsenic (As) 1 9 Cadmium (Cd) 0,2 10 Chromium (Cr) 1 11 Lead (Pb) 5 12 Mercury (Hg) 0,2 13 Thallium (Ti) 0,2 14 Opacity 10

1 Decree KEP-03/BAPEDAL/09/1995 regarding Technical Guidelines for Hazardous Waste Management

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The hazardous waste emission standards in Table 14 require individual heavy metals to be analysed which is more stringent than international requirements which only require total metals.

The Tangguh project is sited in a remote sparsely populated area and is closed off to access by the general public. The greatest risk currently is in the transportation of hazardous waste by sea and land to the licensed third party hazardous waste treatment and disposal facility near Bogor in West Java some 3,500 km to the west. The construction of a hazardous waste incinerator for TEP Operations will remove the transportation risk for liquid hazardous waste. The incinerator facilities proposed are of limited capacity. Hazardous waste generation is about 12 tonnes/day on average of which up to 3 t/day will be directed to the hazardous waste incinerator.

Non-hazardous waste will be about 43 m3 per day in average. Total landfill storage capacity for non-hazardous waste will be 90,000 m3 after construction of two additional cells; and the two non-hazardous waste incinerators each have a capacity of 2 t/day.

The existing waste facilities have been designed consistent with International Good Industry Practice and to meet Indonesian Regulatory requirements.

7.7. Occupational Health and Safety

Tangguh has a very strong and over-riding commitment to Occupational Health and Safety subject to frequent internal and external audits. Safety is monitored against key performance indicators. There have been no reportable incidents, accidents or days away from work recorded at the VWAA, the landfill and all other waste management activities related to transport, storage, handling and processing.

7.8. Conclusions

The existing Tangguh T1/2 facility operate a non-hazardous waste landfill and two non- hazardous waste incinerators. In any context they can be considered as small facilities. They are also remote. They are contained within the Tangguh LNG site and are inaccessible to the nearest community of Tanah Merah which is several km to the west. The Standard Operating Procedures for both facilities follow closely the requirements outlined in the IFC EHS General Guidelines including OH&S, waste reduction, reuse, recycling, risk assessment and mitigation, monitoring and auditing. Hazardous waste is all stored temporarily on site before disposal to a licensed hazardous waste contractor whose facilities are near Bogor, West Java some 3,500 km to the west of Tangguh. All the waste management facilities operated currently will be replicated in TEP

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During TEP Operations the non-hazardous waste landfill and incinerators will adopt the existing SOPs and will continue to be classified as small remote facilities. A small capacity hazardous waste incinerator will also be installed. The hazardous waste incinerator will be required to follow the updated Indonesian hazardous waste regulation (PP101/2014), which was released after TEP AMDAL approval. PP101/2014 meets all the requirements of the IFC General EHS Guidelines. The SOP to be prepared for the hazardous waste incinerator will adopt the requirements of PP101/2014 and will represent Best International Industry Practice.

Under EU and IFC Waste Management Guidelines the TEP hazard waste incinerator can be considered as a small facility for which no emission guidelines have been nominated. The EU emission guidelines are for hazardous waste incinerators with greater than 10 t/day capacity. Given the remoteness and very small capacity of the TEP hazardous waste incinerator the emission standards proposed under the Indonesian regulations are therefore considered appropriate. A further benefit is that all liquid hazardous wastes which are currently transported long distance by sea and land for disposal to a licensed facility will be incinerated thereby reducing the risks associated with transporting hazardous wastes over long distances.

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8. Critical Habitat Assessment and Biodiversity Action Plan – refer to Tangguh CHA and BAP Documents

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References

1. 087-TDN-PS-0001 Technical Decision Note – Produced/Waste Water Management

2. 900-TDN-PS-0008 Technical Decision Note – Water Supply

3. 900-DBS-EM-BP2-0002 Basis of Design for Onshore Facilities

4. Tangguh LNG Train 1 and 2 Independent Environmental Compliance Audit Report – Greencap, 2016

5. Tangguh LNG Project Engineering Geology Assessment Consolidated Report Volume 1 of 2 – Text, Figures & Appendices – Baynes Geologic, 2006

6. Suntown Landfill Closure – Closure and Post Closure Management Plan – Aecom Gold Coast, 2011

7. Lampiran III Peraturan Menteri Pekerjaan Umum No. 03 Tahun 2013 Tentang Penyelenggaraan Prasarana dan Sarana Persampahan dalam Penanganan Sampah Rumah Tangga dan Sampah Sejenis Sampah Rumah Tangga

8. Tangguh Non-Hazardous Solid Waste Management (900-PRC-EN-2321)

9. Tangguh Hazardous Waste Management Procedure (900-PRC-EN-2322)

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ATTACHMENT 1

MARINE MAMMALS AND SEA REPTILES PROTECTION PROCEDURE

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BP Berau Ltd Marine Mammals And Sea Reptiles Protection

PREFACE PENDAHULUAN

Review and Update Tinjauan dan Pembaruan This document will be subject to 24- Dokumen ini akan ditinjau dan diperbarui monthly review and update, when setiap 24-bulan, dimana pemegang document holders will have the dokumen memiliki kesempatan untuk opportunity to express opinions and menyampaikan pendapat dan suggest improvements. menyarankan perbaikan.

However, the document control system Namun, sistem pengendalian dokumen allows for continuous update of this memungkinkan untuk melakukan document. pembaruan dari dokumen ini.

As such, any user may at any time Dengan demikian, setiap pengguna dapat identify an error or suggest an setiap saat mengidentifikasi kesalahan improvement using the Document atau menunjukkan perbaikan Request Form which is provided in 920- menggunakan Formulir Permintaan PRC-HE-2750 HSE Document and Dokumen yang disediakan di 920-PRC- Record Control Procedure. HE-2750 Prosedur Pengendalian Dokumen dan Catatan HSE.

All holders of this document are Semua pemegang dokumen ini terdaftar registered so that they can be sent sehingga mereka dapat dikirimkan updates and be kept informed of pembaruan dan selalu diberi informasi changes or reviews. perubahan atau tinjauan.

Responsibility of Copyholders Tanggung Jawab Pemegang Salinan It is the responsibility of the registered copyholder of controlled hard copy Adalah tanggung jawab pemegang versions to maintain the accuracy of the salinan yang terdaftar untuk menjaga document by ensuring that all updates keakuratan dokumen dengan are promptly incorporated and memastikan bahwa semua pembaruan acknowledged. segera dimasukkan dan diketahui.

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TABLE OF CONTENTS

AMENDMENT SUMMARY...... 2 PREFACE ...... 4 TABLE OF CONTENTS ...... 5 1.0 INTRODUCTION ...... 9 2.0 PURPOSE ...... 9 3.0 SCOPE ...... 9 4.0 DEFINITIONS AND ABBREVIATIONS ...... 9 4.1 Definitions ...... 9 4.2 Abbreviations ...... 12 5.0 ROLES AND RESPONSIBILITIES ...... 13 5.1 Site Manager ...... 13 5.2 Department Managers ...... 13 5.3 H&M Manager ...... 13 4 5. LNG Shipping Operations Manager ...... 14 5 5. Security Team Leader ...... 14 5.6 Site Environmental Team Leader ...... 14 5.7 Site Environmental Advisor ...... 15 6.0 PROCEDURES ...... 16 6.1 Identification ...... 16 Identification of Marine Mammal and Sea Reptiles 6.1.1 16 Species ...... 6.1.2 Type of Disturbance ...... 19 6.2 Protection Activity ...... 20 6.2.1 Seismic Survey Management ...... 22 6.2.2 Vessel Movement Management ...... 22 6.2.3 Waste Disposal at Sea Management ...... 24 6.2.4 Ballast Management ...... 26 2.5 6. Coastal Sedimentation Management...... 27 6.2.6 General Management Protection...... 29 6.3 Monitoring ...... 30 6.4 Nonconformity ...... 30 6.5 Reporting ...... 31 7.0 REGULATORY AND STANDARD REFERENCES ...... 32 7.1 Government of RI Regulation ...... 32 7.2 BP Standards and Policies ...... 32 7.3 Industrial Standards ...... 33

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DAFTAR ISI

RINGKASAN PERUBAHAN ...... 2 PENDAHULUAN ...... 4 DAFTAR ISI ...... 7 1.0 PENDAHULUAN ...... 9 2.0 TUJUAN ...... 9 3.0 RUANG LINGKUP ...... 9 4.0 DEFINISI DAN SINGKATAN ...... 9 4.1 Definisi ...... 9 4.2 Singkatan ...... 12 5.0 PERAN DAN TANGGUNG JAWAB ...... 13 5.1 Manajer Site ...... 13 5.2 Manajer Departemen ...... 13 5.3 Mana jer H&M ...... 13 4 5. Manajer Operasional Shipping LNG ...... 14 5.5 Team Leader Keamanan ...... 14 5.6 Site Environmental Team Leader ...... 14 5.7 Site Environmental Advisor ...... 15 6.0 PROSEDUR...... 16 6.1 Identifikasi ...... 16 6.1.1 Identifikasi Spesies Mamalia Laut dan Reptil Laut ...... 16 6.1.2 Jenis Gangguan...... 19 6.2 Kegiatan Perlindungan ...... 20 6.2.1 Manajemen Survei Seismik ...... 22 6.2.2 Manajemen Gerakan Kapal ...... 22 6.2.3 Manajemen Pembuangan Limbah di Laut ...... 24 6.2.4 Manajemen Ballast ...... 26 6.2.5 Pengelolaan Sedimentasi Pesisir...... 27 6.2.6 Manajemen Perlindungan Umum...... 29 6.3 Pemantauan ...... 30 6.4 Ketidaksesuaian ...... 30 6.5 Pelaporan...... 31 7.0 REFERENSI PERATURAN DAN STANDAR ...... 32 7.1 Peraturan Pemerintah RI ...... 32 7.2 Standar dan Kebijakan BP ...... 32 7.3 Standar Industri ...... 33

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1.0 INTRODUCTION 1.0 PENDAHULUAN OMS Element 3.0 Risk, Sub- OMS Elemen 3.0 Risiko, Sub-Elemen Element 3.6 Environment stipulates 3.6 Lingkungan menetapkan bahwa that BP identifies and systematically BP secara sistematis manages the impact of its activities mengidentifikasi dan mengelola on the environment and integrates dampak dari kegiatan terhadap environmental requirements into the lingkungan dan mengintegrasikan local OMS, Environmental persyaratan lingkungan ke dalam compliance and sustainability is OMS lokal, kepatuhan dan prominent to the success of keberlanjutan Lingkungan adalah Tangguh LNG Operation. penting untuk keberhasilan Operasi LNG Tangguh.

Our Goals are simply stated – no Tujuan kami dinyatakan secara accidents, no harm to people, and sederhana – tidak ada kecelakaan, no damage to the environment tidak membahayakan orang, dan tidak ada kerusakan lingkungan

This procedure is part of the Prosedur ini merupakan bagian dari Environmental Management System Sistem Manajemen Lingkungan to guide the management and untuk mengarahkan manajemen dan workforce towards the goals. tenaga kerja dalam mencapai tujuan.

2.0 PURPOSE 2.0 TUJUAN To prevent any potential impacts or Untuk mencegah dampak potensial disturbance to marine mammals and atau gangguan terhadap mamalia laut sea reptiles in Berau/Bintuni Bay dan reptil laut di Berau/Teluk Bintuni area caused by Tangguh LNG yang disebabkan oleh operasi LNG operation and be in accordance with Tangguh dan sesuai dengan the requirements of AMDAL, persyaratan AMDAL, peraturan yang applicable Indonesian regulations, berlaku di Indonesia, izin, permits, Tangguh Lenders Groups Persyaratan Grup Pemberi Pinjaman Requirements and BP Group Dana Tangguh dan Praktek Grup BP. Practices.

3.0 SCOPE 3.0 RUANG LINGKUP This Marine Mammals and Sea Prosedur Mamalia Laut dan Reptil Reptiles Procedure apply to Tangguh Laut ini berlaku untuk operasi LNG LNG operation (including Babo) Tangguh (termasuk Babo) dalam under normal, abnormal and situasi normal, abnormal dan darurat. emergency situation.

4.0 DEFINITIONS AND 4.0 DEFINISI DAN SINGKATAN ABBREVIATIONS 4.1 Definitions 4.1 Definisi Abnormal Condition Kondisi abnormal Beyond normal operation Kondisi operasi yang melampaui condition but still controllable parameter operasi normal yang

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which covering start-up, shut- masih dapat dikontrol, meliputi: down and upset. start up, shut-down dan upset.

Ballast water Air Ballast (air pemberat) Water added to a vessel in Air yang ditambahkan ke kapal order to maintain stability. untuk menjaga stabilitas.

Biodiversity Keanekaragaman Hayati Refers to the number of Mengacu kepada jumlah spesies different species and the yang berbeda dan jumlah associated number of individu yang hidup terkait dalam individuals living within a suatu komunitas. community.

Dredge Pengeruk A ship designed to remove Sebuah kapal yang dirancang sediment from a channel or untuk mengupas sedimen dari dock region to maintain draft saluran atau daerah dermaga depths. untuk menjaga kedalaman draft.

Emergency conditions Kondisi darurat Uncontrollable operation Kondisi operasi di luar parameter conditions beyond normal operasi normal yang tidak operation parameters. terkendali

ISO ISO International Organisation for International Organisation for Standardization. Standardization.

Mammal Mamalia Any of various warm-blooded Setiap hewan vertebrata vertebrate animals of the class berdarah panas dari kelas Mammalia, including humans, Mamalia, termasuk manusia, characterized by a covering of ditandai dengan penutup rambut hair on the skin and, in the di kulit, dan pada betina terdapat female, milk-producing kelenjar penghasil susu untuk mammary glands for nourishing memberi makan anaknya. the young. Mamalia laut Marine Mammals Suatu mamalia laut terutama A mammal that is primarily yang tinggal atau tergantung ocean -dwelling or depends on pada laut untuk makanannya. the ocean for its food. Mamalia yang awalnya Mammals originally evolved on berkembang di darat, tapi land, but later marine mammals kemudian mamalia laut evolved to live back in the berevolusi untuk hidup kembali ocean. di laut.

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Nonconformity Ketidaksesuaian Non-fulfilment of AMDAL, Tidak terpenuhinya AMDAL, applicable Indonesian peraturan yang berlaku di regulations, permits, Tangguh Indonesia, izin, Persyaratan Grup Lenders Groups Requirements Pemberi Pinjaman Dana and BP Group Practices. Tangguh dan Petunjuk Praktis Grup BP.

Reptile Reptil Any of various cold-blooded, Setiap hewan berdarah dingin, usually egg-laying vertebrates of biasanya vertebrata bertelur dari the class Reptilia, having an kelas Reptilia, memiliki sisik external covering of scales or eksternal atau horny plate dan horny plates and breathing by bernapas dengan paru-paru. means of lungs.

Sedimentation Pengendapan The process of break up and Proses pemecahan dan separation of particles from memisahnya partikel dari batuan their parent rocks, their induknya, selama transportasi, transportation, deposition and deposisi dan berkonsolidasi ke consolidation into another rock. batuan lain.

Tangguh LNG Operation Operasi LNG Tangguh All activities under Tangguh Semua kegiatan di bawah Phase I LNG operations operasi LNG Tangguh Tahap I excluding all activities under tidak termasuk semua kegiatan Tangguh Development. di bawah Pengembangan Tangguh.

Uncontrolled releases/ events Kejadian/ pelepasan yang Any uncontrolled event where tidak terkendali process fluids are released from Setiap peristiwa yang tidak primary containment and which terkendali di mana cairan proses results in the need for dibebaskan dari wadah primer immediate corrective action dan yang mengakibatkan (e.g. shutdown, evacuation or perlunya tindakan perbaikan isolation) to mitigate the effects segera (misalnya penghentian, of loss of containment. Fugitive evakuasi atau isolasi) untuk emissions and minor flange, mengurangi efek dari hilangnya hose joint or seal liquid leaks penahanan. Emisi fugitive dan which can be contained by minor flange, sambungan selang capturing the fluid for safe atau kebocoran seal liquid yang disposal should not be included. dapat ditahan dengan menangkap cairan untuk pembuangan yang aman tidak harus dimasukkan disini.

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4.2 Abbreviation 4.2 Singkatan

AMDAL Analisa Mengenai Dampak Lingkungan

BAPEDAL Badan Pengendalian Dampak Lingkungan CAR Corrective Action Request CITES Convention on International Trade on Endangered Species of Wild Fauna and Flora ERNP Environment Requirements for New Projects EPR Environment Performance Requirements HSE Health Safety & Environment HSEMS Health, Safety & Environmental Management System IUCN International Union for the Conservation of Nature and Natural Resources JNCC Joint Nature Conservation Committee LNG Liquefied Natural Gas MoE Ministry of Environment PP Peraturan Pemerintah RI Republik Indonesia SOP Standard Operating Procedures

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5.0R OLES AND 5.0 PERAN DAN TANGGUNG RESPONSIBILITIES JAWAB

5.1 Site Managers 5.1 Manajer Site • Overall assurance of the • Jaminan menyeluruh untuk implementation to this pelaksanaan prosedur ini. procedure. • Menyediakan sumber daya yang • Provide resources required for dibutuhkan untuk pelaksanaan the implementation of this Prosedur Perlindungan Mamalia M arine Mammals and Sea Laut dan Reptil Laut ini. Reptiles Protection Procedures.

5.2 Department Managers 5.2 Manajer Departemen Ensure that every personnel in Memastikan bahwa personel di respective department masing-masing departemen (including contractors) (termasuk kontraktor) understand the importance of memahami pentingnya marine mammals and sea perlindungan mamalia laut dan reptile protection and follow reptil laut dan memenuhi this procedures requirements. persyaratan prosedur ini.

5.3 H&M Manager 5.3 Manajer H&M • Ensure that marine mammal • Memastikan bahwa kegiatan and sea reptiles sighting perekaman pengamatan recording activity is conducted mamalia laut dan reptile laut in accordance to this dilaksanakan sesuai dengan procedure. prosedur ini. • Ensure that all waste • Memastikan bahwa semua generated from the vessel and limbah yang dihasilkan dari kapal hazardous chemical on board dan bahan kimia berbahaya dari are not discharged to the sea. kapal tidak dibuang ke laut. • Ensure no disturbance, • Memastikan tidak ada including boat collision, to gangguan, termasuk tabrakan marine mammals and sea kapal, terhadap mamalia laut dan reptiles during vessel reptil laut dari pergerakan kapal. movement. • Menetapkan langkah-langkah • Establish adequate measures yang memadai tentang regarding vessel speed, routing kecepatan kapal, rute dan jarak and distance from potential or dari lokasi tempat atau potensial known turtle nesting sites. tempat penyu bersarang. • Ensure the marine operations • Memastikan operasi laut follows the guideline under the mengikuti pedoman Mamalia Marine Mammals and Sea Laut dan Penyu Laut di Berau- Turtle in Berau-Bintuni Bay - A Teluk Bintuni – Panduan untuk guide to Reducing Impacts Mengurangi Dampak.

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• Ensure that condensate carrier • Memastikan bahwa rute route is following established pembawa kondensat mengikuti international sea lanes through alur laut internasional melalui Halmahera waters, avoiding perairan Halmahera, Raja Ampat area. menghindari daerah Raja Ampat

5.4 LNG Shipping Operations 5.4 Manajer Operasional Shipping Manager LNG • Ensure that LNG carrier route • Memastikan bahwa rute kapal is following established LNG mengikuti alur laut international sea lanes through internasional yang ditetapkan Halmahera waters, avoiding yaitu melalui perairan Raja Ampat area. Ensure Halmahera, menghindari daerah that ballast water exchange Raja Ampat. Memastikan bahwa follows the IMO requirements pertukaran air ballast mengikuti and recorded as required by persyaratan IMO dan dicatat AMDAL. seperti yang dipersyaratkan oleh AMDAL. • Monitor the evolving research • Memonitor perkembangan on ballast water treatment. penelitian pada pengolahan air ballast.

5.5 Security Team Leader 5.5 Team Leader Keamanan Ensure that all personnel, Memastikan bahwa semua contractors and visitors do not personil, kontraktor dan carry in and/or out protected pengunjung tidak membawa wildlife and wildlife parts. masuk dan / atau keluar satwa dan bagian satwa liar dilindungi.

5.6 Site Environmental Team 5.6 Site Environmental Team Leader Leader • Ensure the compliance of • Memastikan kepatuhan dari Tangguh LNG commitment to komitmen Tangguh LNG the AMDAL, Indonesian terhadap peraturan AMDAL applicable regulations, permits, yang berlaku di Indonesia, izin, BP Lenders Groups Persyaratan Pemberi Pinjaman Requirements and BP Group Dana BP Grup dan Praktek Grup Practices. BP. • Provide assurance of marine • Memberikan jaminan program mammals and sea reptiles perlindungan mamalia dan reptil protection program, laut, kepatuhan proses dan compliance of process and kepatuhan terhadap peraturan regulatory compliance. • Ensure that marine mammals • Memberikan jaminan kualitas and sea reptile studies and dan ketepatan waktu program are implemented as penyampaian laporan. per requirements.

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• Use the marine mammals and • Memastikan bahwa studi dan sea reptile studies to develop program mamalia laut dan reptil and/or update the guideline for laut diimplementasikan sesuai reducing Tangguh potential kebutuhan. impacts on marine mammals and sea reptiles in the Berau Bintuni Bay • Ensure the socialization of this • Memastikan sosialisasi guideline to Tangguh pedoman ini kepada tenaga kerja workforce. Tangguh.

5.7 Site Environmental Advisor 5.7 Site Environmental Advisor • Coordinate and monitor as well • Mengkoordinasikan dan as provide assurance of marine memantau serta memberikan mammals and sea reptile jaminan perlindungan mamalia protection, compliance of laut dan reptil laut, kepatuhan process and regulatory proses dan kepatuhan terhadap compliance. peraturan. • To compile and analyse the • Mengkompilasi dan result of the marine mammals menganalisis hasil dari rekaman and sea reptiles sighting penampakan mamalia laut dan record. reptil laut.

• Ensure that all marine • Memastikan bahwa semua mammals and sea reptiles are mamalia laut dan reptil laut protected against disturbance dilindungi dari gangguan dari from LNG operation daily kegiatan operasi LNG sehari- activity. hari.

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6.0 PROCEDURES 6.0 PROSEDUR Marine mammals and sea reptiles A liran proses prosedur perlindungan protection procedure process flow mamalia laut dan reptil laut dapat can be seen in Appendix 1 - dilihat pada Lampiran 1 - Flowchart Marine Mammals and Sea Prosedur Mamalia Laut dan Laut Reptiles Procedure Flowchart. Reptil.

6.1 Identification 6.1 Identifikasi 6.1.1 Identification of Marine 6.1.1 Identifikasi Spesies Mammal and Sea Mamalia Laut dan Reptil Reptiles Species Laut The identified species of Mengidentifikasi spesies ma rine mammals and sea mamalia laut dan reptil laut reptiles and their dan lokasi penampakan sighting location in mereka di Teluk Berau Berau/Bintuni Bay is /Bintuni diberikan dalam provided in the following tabel berikut table

Table 1 – Identification of Marine Mammal and Sea Reptile Species SPECIES MOST FREQUENT SIGHTING LOCATION a. Dolphins Coastal mangroves, channels, sand banks and 1. Indo Pacific nearshore waters throughout the Bay, in particular Humpback the coastal strip between Babo and Saengga. Dolphins (Sousa Sousas frequently approach Tangguh marine Dolphin) facili ties such as the LNG Jetty, Combo Dock, navigation and anchor buoys. Deep open waters of the Berau-Bintuni Bay.

2. Spinner Dolphins A large group of spinner dolphins are long-term residents in the central section of the bay, and can often be found near the offshore platforms. 3. Indo Pacific Bottlenose Arguni Islands and open waters of the bay. Dolphins 4. Common Open and coastal waters of Bintuni Bay, with Bottlenose occasional sightings near the platform areas. Dolphin

b. Whales

Have been observed in the western section of the 1. Bryde’s Whale bay.

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SPECIES MOST FREQUENT SIGHTING LOCATION c. Turtle Nesting and sea grass grazing in outer Bay, especially the Arguni Islands. Possibly feeding on 1. Green turtle mangrove fruits in inner Bay. (chelonia mydas) Pristine sandy beaches for nesting, especially Kokas and Arguni Islands, Pisang Island, Ogar Island and beaches along the Onin Peninsula. Feeding along reefs, nesting in outer bay and likely mating and resting near nest sites. Activities in mangrove areas of the innermost bay remain mysterious. 2. Hawksbill Turtle Pristine sandy beaches for nesting, especially Kokas and Arguni Islands, Pisang Island, Ogar Island and beaches along the Onin Peninsula. Hawksbills show a particular preference for small, narrow beaches. The bay’s highly productive benthic environment would seem to serve as an ideal feeding ground. 3. Olive Ridley Turtle More research is needed to confirm the significance of this habitat. Outer waters, possibly throughout the Bay. 4. Leatherback Additional research is needed on this species’ Turtle habitat use. d. Crocodiles Frequent sightings by community members as well as prime habitat characteristics indicate that Berau Saltwater Crocodile Bintuni Bay is a stronghold for this endangered species. Occasional sightings of medium to large crocodiles near the LNG Plant Site.

Tabel 1 – Identifikasi Mamalia Laut dan Reptil Laut SPESIES LOKASI PENGAMATAN YANG PALING SERING a. Lumba – Lumba Bakau , saluran-saluran, gumuk pasir dan perairan 1. Lumba - Lumba dekat pantai di sepanjang teluk, khususnya jalur Indo Pacific pantai antara Babo dan Saengga. Humpback Sousa sering kali mendekati fasiltas Tangguh Marine (Sousa Dolphin) seperti LNG Jetty, Combo Dock, navigasi dan anchor buoys. Perairan terbuka dalam di Berau –Teluk Bintuni S ekumpulan besar lumba-lumba spinner adalah 2. Lumba - Lumba penghuni jangka panjang di bagian tengah teluk, dan Spinner seringkali ditemukan di dekat platform lepas pantai

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SPESIES LOKASI PENGAMATAN YANG PALING SERING 3. Lumba – Lumba Indo Pacific Pulau Arguni dan perairan terbuka di Teluk Bottlenose 4. Lumba – Lumba Perairan terbuka dan pesisir di Teluk Bintuni, dengan Common beberapa kali pengamatan di dekat area platform Bo ttlenose b. Paus Pernah teramati di bagian barat Teluk 1. Paus Bryde’s

c. Penyu Bersarang dan memakan rumput laut di area luar Teluk, khususnya di Pulau Arguni. Mungkin 1. Penyu Hijau memakan buah bakau di sebelah dalam teluk (chelonia mydas) Pantai berpasir yang belum tersentuh untuk bersarang terutama Kokas dan Arguni, Pulau Pisang, Pulau Ogar dan pantai sepanjang semenanjung Onin. Mencari makan sepanjang area batu karang, bersarang di sebelah luar Teluk, dan kemungkinan besar kawin dan beristirahat di area sekitar sarang. Aktivitas di dalam area bakau dan bagian dalam 2. Penyu Hawksbill Teluk masih belum diketahui. Pantai berpasir yang belum tersentuh untuk bersarang terutama Kokas dan Arguni, Pulau Pisang, Pulau Ogar dan pantai sepanjang semenanjung Onin. Hawksbills menunjukkan preferensi di pantai kecil dan sempit. Keanekaragaman benthic yang tinggi di Teluk merupakan area pencarian makan yang 3. Penyu Olive ideal.Penelitian lebih lanjut diperlukan untuk Ridley membenarkan signifikansi dari habitat ini. Perairan sebelah luar, mungkin di keseluruhan 4. Penyu Teluk. Penelitian tambahan mengenai habitat yang Leatherback digunakan spesies ini diperlukan.

d. Crocodiles Seringkali teramati oleh penduduk dan juga karakteristik habitat mengindikasikan bahwa Berau Saltwater Crocodile Teluk Bintuni adalah area yang cocok untuk spesies yang terancam punah ini. Pengamatan sesekali terjadi untuk buaya berukuran sedang hingga besar di dekat Plant LNG SIte

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The pictures of the Gambar- gambar dari species can be seen in spesies dapat dilihat Appendix 4 - Marine pada Lampiran 4 - Mammals and Sea Gambar Mamalia Laut Reptiles Pictures. dan Reptil Laut.

6.1.2 Type of Disturbance 6.1.2 Jenis Gangguan Identification of type of Identifikasi jenis disturbance for marine gangguan bagi mamalia mammals and sea laut dan reptil laut dapat reptiles can be seen in dilihat pada tabel berikut. the following table.

Table 2 – Type of Disturbance NO. ACTIVITY TYPE OF DISTURBANCE

1 Seismic survey A coustic disturbance Boat collision 2 Vessel movement Water current change Acoustic disturbance Waste disposal at sea: a. Inorganic solid a. Potential to be swallowed by 3 waste marine mammal and sea turtles b. Waste water b. Reduction of sea water quality c. Chemical and/or c. Toxic fuel spill d. Chemical spill d. Toxic during platform and shipping maintenance Platform and pipeline Acoustic disturbance 4 maintenance Reduction of sea water quality 5 Ballast Introduction of invasive species 6 Coastal sedimentation Habitat loss Specific disturbance to sea turtles: 7 a. Hunting and egg harvest b. Coastal development and artificial lighting disturbance

Tabel 2 – Jenis Gangguan NO. A KTIVITAS JENIS GANGGUAN

1 S urvey Seismik Gangguan Akustik • Tabrakan boat 2 Pergerakan Kapal • Perubahan Arus Laut • Gangguan Akustik

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NO. A KTIVITAS JENIS GANGGUAN Pembuangan Limbah di Laut 3 a. Limbah Padat a. Potensi untuk tertelan oleh Anorganik mamalia laut dan penyu laut b. Air Limbah b. Penurunan kualitas air laut c. Bahan Kimia c. Beracun dan/atau Tumpahan Bahan Bakar d. Tumpahan Bahan d. Beracun Kimia selama Kegiatan Perawatan Platform dan Perkapalan Perawatan Platform dan Gangguan Akustik 4 Perpipaan 5 Ballast • Penurunan kualitas air laut • Spesies Invasif 6 Sedimentasi Area Pantai Berkurangnya Habitat Gangguan Spesifik Penyu Laut: 7 a. Perburuan b. Pengembangan Area Pantai dan Gangguan Pencahayaan Buatan

6.2 Protection Activity 6.2 Kegiatan Perlindungan The following protection shall Perlindungan berikut harus be conducted to avoid and/or dilakukan untuk menghindari minimise the disturbance to dan /atau meminimalkan marine mammals and sea gangguan terhadap mamalia reptiles. laut dan reptil laut.

General Protection Perlindungan Umum All BP personnel Semua personel BP • All personnel including • Semua personel termasuk contractors working in kontraktor yang bekerja di LNG Tangguh LNG Site and Babo Tangguh Site dan Operasi Babo operation must respect and harus menghormati dan report violations of laws and melaporkan pelanggaran treaties on protected wildlife. terhadap hukum dan perjanjian Collection and transport of terhadap satwa liar dilindungi. protected wildlife and wildlife Pengumpulan dan parts including cetaceans, pengangkutan satwa liar dan turtles, turtle shells, turtle bagian satwa liar yang eggs, crocodiles and crocodile dilindungi termasuk cetacean, skins is prohibited by kura-kura, karapas penyu, telur Indonesian law and CITES penyu, buaya dan kulit buaya - treaties (Convention on adalah dilarang oleh hukum International Trade of Indonesia dan perjanjian CITES

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Endangered Species). (Konvensi Perdagangan Offenders can be charged with Internasional Spesies Langka). high fines and jail sentences in Pelanggar dapat dkenakan line with applicable denda yang tinggi dan regulations. hukuman penjara sesuai dengan peraturan yang berlaku. • All personnel including • Semua personel termasuk contractors working in kontraktor yang bekerja di Tangguh LNG Site and Babo Tangguh LNG Site dan operasi operation are not allowed to Babo tidak diperbolehkan untuk hunt or feed marine life. memburu atau memberi makan binatang laut • Fishing in the sea or river is • Dilarang memancing di laut dan prohibited. sungai. • All personnel are encouraged • Semua personel dianjurkan to support monitor marine untuk membantu memantau mammals and sea reptiles in mamalia laut dan reptil laut di Berau -Bintuni Bay waters by perairan Teluk Bintuni-Berau observing, recording and dengan mengamati, mencatat reporting on marine life in dan melaporkan kehidupan laut Berau/Bintuni Bay and di Teluk Berau/ Bintuni dan surrounding waters. Marine perairan sekitarnya. Logbooks mammals and sea reptiles memantau mamalia laut dan Logbooks are available for reptil laut tersedia untuk staf interested staff. Learn more by yang tertarik. Untuk contacting the Tangguh mempe lajari lebih lanjut dapat Environmental Team. menghubungi Tim Lingkungan Tangguh. • During induction training, • Selama pelatihan induksi, information regarding the informasi tentang larangan prohibition of collection and pengumpulan dan transport of protected wildlife pengangkutan satwa liar dan and wildlife parts shall be bagian-bagian satwa liar yang delivered to personnel, dilindungi harus disampaikan contractors and/or visitors. kepada personel, kontraktor dan / atau pengunjung

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6.2.1 Seismic Survey Management 6.2.1 Manajemen Survei Seismik Seismic survey may be conducted Survei seismik dapat dilakukan every 5 years. Where appropriate, setiap 5 tahun. Bila sesuai, employ JNCC guidelines for seismic menggunakan pedoman JNCC surveys to ensure minimal acoustic untuk survei seismik untuk impact to marine mammals. Refer memastikan dampak akustik to Guidelines for Minimising minimal terhadap mamalia laut. Acoustic Disturbance to Marine Merujuk pada Pedoman untuk Mammals from Seismic Surveys - Meminimalkan Gangguan Akustik JNCC 2010. untuk Mamalia Laut dari Survei Marine mammal sighting & Airgun Seismik - JNCC 2010. operation should be recorded. See Penampakan Mamalia Laut & Appendix 3 – Marine Mammals Operasi Air Gun harus dicatat. Lihat Recording Form – Record of Lampiran 3 – Formulir Rekaman Operation. Mamalia Laut – Rekaman Operasi.

6.2.2 Vessel Movement Management 6.2.2 Manajemen Gerakan Kapal Where practicable, new vessels and Apabila memungkinkan, kapal baru major vessel modifications shall be dan modifikasi kapal besar harus designed to minimise sound dirancang untuk meminimalkan generation. suara yang dihasilkan. A. Routing A. Routing Boat Route Rute Kapal • Establish a boat-free “dolphin • Menetapkan "zona habitat lumba- habitat zone” by re-routing lumba bebas-kapal" dengan speedboats between Babo and merubah rute speedboat antara the LNG Plant Site to deeper Babo dan Lapangan Kilang LNG ke (>12m) waters, during all perairan lebih dalam (>12m), pada months with calm sea semua bulan dengan kondisi laut conditions (due to safety yang tenang (untuk alasan concerns on rough sea days, this keamanan pada hari-hari kondisi action is limited to the dry laut buruk, tindakan ini terbatas season and other calm months). pada musim kemarau dan bulan- Exercise particular vigilance at bulan tenang lainnya). Melatih the mouth of the bay, around usaha kewaspadaan ini di daerah Kokas and Arguni islands, near mulut teluk, sekitar Kokas dan the Tangguh platform, LNG Plant pulau-pulau Arguni, dekat Site, Babo and other sites that anjungan Tangguh, Lapangan marine mammals are known to Kilang LNG, Babo dan area lain frequent. dimana mamalia laut diketahui sering terlihat. • A monitoring system is • Sebuah sistem pemantauan recommended to gauge this dianjurkan untuk menguji measure’s effectiveness. The efektivitas pengukuran ini. Zona speedboat exclusion zone adds eksklusif speedboat menambah minimal time and operational waktu minimal dan biaya costs and will be enforced operasional dan akan diberlakukan seasonally based on bay musiman didasarkan pada kondisi teluk dan keselamatan.

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conditions and safety. • Small boat shall be completed • Boat kecil harus dilengkapi dengan with water jet to make water jet untuk memastikan operations safer to aquatic life. operasi yang lebih aman bagi While bigger vessel shall be kehidupan aquatic Sedangkan completed with Kort Nozzle. kapal yang lebih besar seperti LCT dan tug boat harus dilengkapi dengan Kort Nozzle. • During rough seas the off-shore • Selama kondisi laut buruk rute route will be avoided and lepas pantai akan dihindari dan vessels will revert to the channel kapal akan kembali ke rute route. In such circumstances channel. Dalam keadaan seperti during bad weather, a reduced selama cuaca buruk, pengurangan vessel speed is recommended. kecepatan kapal dianjurkan.

Tanker Route Rute Tanker • For tanker route, routing shall • Untuk rute kapal tanker, routing consider the presence of harus mempertimbangkan endangered species and their keberadaan spesies langka dan calving grounds, and sound perkembangbiakan mereka, dan reduction measures shall be tindakan-tindakan pengurangan taken where practicable (noise, suara harus diambil bila water current change). memungkinkan (kebisingan, perubahan arus air). • Ensure compliance on Tangguh • Memastikan kepatuhan pada Policy to route LNG tankers Kebijakan Tangguh terhadap rute along established international tanker LNG di sepanjang alur laut sea lanes through Halmahera internasional yang ditetapkan (Maluku) waters. Avoid travel melalui perairan Halmahera through Raja Ampat, possibly (Maluku). Hindari perjalanan the world’s epicenter of marine melalui Raja Ampat, yang mungkin biodiversity and crucial whale sebagai pusat keanekaragaman migration corridors. hayati laut dan koridor penting migrasi paus.

B. Speed Limit and Distance B. Batas Kecepatan dan Jarak • Speedboat approaches and • Kedatangan dan keberangkatan departures from Babo jetty are also st peedboa dan dari dermaga Babo required to control the speed on a juga diperlukan untuk mengontrol day-to-day basis as this area has a kecepatan boat sehari-hari dimana high proportion of Sousa dolphin daerah ini memiliki proporsi yang sightings. The route usage will be tinggi dari penampakan lumba- monitored to assess the lumba Sousa. Penggunaan rute akan effectiveness. dipantau untuk menilai efektivitasnya.

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• If approached by a marine mammal, • Jika didekati oleh mamalia laut, put the vessel’s engine in neutral netralkan posisi mesin kapal dan and allow the animal to pass. Any biarkan hewan untuk lewat. Setiap vessel movement should be from gerakan kapal harus dari bagian the rear of the animal. Certain belakang hewan. Spesies lumba- species of dolphin may choose to lumba tertentu dapat memilih untuk bo- w ride a vessel’s pressure wave. membungkuk-menaiki gelombang If so, keep a steady course and kapal. Jika demikian, pertahankan speed, let the dolphins come near. kestabilan dan kecepatan, biarkan Don’t turn and run over nearby lumba-lumba mendekati. Jangan dolphins and expect them to bow- berbalik dan melintasi lumba-lumba ride. terdekat dan biarkan mereka membungkuk-naik. • If possible, allow a passing distance • Jika memungkinkan, berikan jarak of 50 meters or more for dolphins lewat 50 meter atau lebih untuk and at least 100 meters for whales. lumba-lumba dan setidaknya 100 Upon sighting, reduce speed and meter untuk ikan paus. Jika terlihat, alter course as necessary. Never kurangi kecepatan dan ubah arah intentionally approach a marine seperlunya. Jangan pernah sengaja mammal for a closer look. mendekati mamalia laut untuk melihat lebih dekat. • Use care to not encircle or trap • Berhati-hati agar tidak mengepung marine mammals and reptiles atau memerangkap mamalia laut between various vessels or dan reptil diantara berbagai kapal between vessel and shore. Always atau antara kapal dan darat. Selalu leave them a generous exit. berikan mereka jalan keluar yang Refer to Table 1 – Identification of mudah . Lihat Tabel 1 – Identifikasi Marine Mammal and Sea Reptile Spesies Mamalia Laut dan Reptil Species for specific area of the Laut untuk daerah tertentu dari marine mammal and sea reptiles. mamalia laut dan reptil laut.

6.2.3 Waste Disposal at Sea 6.2.3 Manajemen Pembuangan Management Limbah di Laut A. Boat A. Perahu (Boat) Food waste, recyclable waste, and Limbah sisa makanan, daur ulang, hazardous waste generated on boat bisa dibakar, dan limbah B3 yang are not allowed to be disposed to dihasilkan di perahu tidak boleh the sea. All waste shall be collected dibuang ke laut. Semua limbah returned to the onshore facilities for tersebut harus dikumpulkan dan further handling.While waste water dikembalikan ke fasilitas darat shall be patched and discharge untuk penanganan lebih lanjut. outside of exclusive zone. Sedangkan untuk air limbah saniter ditampung dan dibuang ke laut di luar area exclusive zone. B. LNG Carrier and Condensate B. LNG Carrier dan Tanker Tanker Kondensat Selective collection and Pengelolaan dan pengumpulan management of wastes according limbah secara selektif sesuai

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to the criteria of MARPOL 73/78 dengan kriteria MARPOL 73/78 revisi Annex V Prevention of Lampiran V Pencegahan Polusi Pollution Garbage Disposal of Sampah Pembuangan Sampah Garbage Outside of Special Area. luar Area Khusus. (Ketentuan (Provision can be seen in dapat dilihat pada Appendix 5 – Simplified Overview Lampiran 5 – Gambaran yang of the Discharge Provisions of the Disederhanakan untuk Revised MARPOL Annex V) Ketentuan Pembuangan di • Disposal into the sea of all revisi MARPOL Annex V) plastics, including but not limited • Pembuangan ke laut dari to synthetic ropes, synthetic semua plastik, tidak terbatas fishing nets, and plastic garbage pada tali sintetis, jaring ikan bags is prohibited. sintetis, dan kantong sampah • Disposal into the sea of the plastik adalah dilarang. following garbage will be made as • Pembuangan ke laut dari far as practicable from the nearest sampah berikut akan dilakukan land, but in any case is prohibited sejauh mungkin dari daratan if the distance from the nearest terdekat, tetapi dalam hal land is less than 25 nmi (46.3 km) apapun adalah dilarang jika jarak for dunnage, lining and packing dari daratan terdekat kurang material that will float; 12 nmi dari 25 NMI (46,3 km) untuk (22.2 km) for food wastes and all dunnage, lapisan dan bahan other garbage, including paper kemasan yang mengapung; 12 products, rags, glass, metal, NMI (22,2 km) untuk limbah bottles, crockery and similar makanan dan semua sampah refuse. lainnya, termasuk produk kertas, kain, logam, kaca, botol, periuk dan yang serupa. • Disposal into the sea of garbage • Pembuangan sampah ke laut specified in sub-paragraph (b)(ii) of yang ditentukan dalam sub-ayat Annex V may be permitted when (b) (ii) Lampiran V dapat it has passed through a diizinkan apabila telah comminute or grinder and made ditumbuk atau digiling dan as far as practicable from the dibuang sejauh mungkin dari nearest land, but in any case is daratan terdekat, tetapi dalam prohibited if the distance from the hal apapun dilarang jika jarak nearest land, is less than 3 nmi dari daratan terdekat, kurang (5.6) km. Such comminute or dari 3 NMI (5,6) km. Tumbukan/ ground garbage will be capable of gilingan sampah harus mampu passing through a screen with melewati saringan dengan openings no greater than 25 mm. ukuran diameter tidak lebih besar dari 25 mm.

• Jika sampah tercampur dengan • When garbage is mixed with other kotoran lain yang memiliki discharges having different persyaratan pembuangan yang disposal or discharge berbeda, maka persyaratan requirements, the more stringent yang lebih ketat akan requirements will apply. diberlakukan.

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For generated solid waste record, Untuk catatan limbah padat yang see Appendix 3 - Non Hazardous dihasilkan, lihat Lampiran 3 - Solid Waste Record) - in 900 – Rekaman Limbah Padat Tidak PRC-EN 2322 Non Hazardous Berbahaya - dalam 900–PRC-EN- Solid Waste Procedure. 2322 Prosedur Limbah Padat - Tidak Berbahaya. Wastewater including sanitary Air limbah termasuk limbah waste generated on Tangguh LNG saniter yang dihasilkan di LNG Site is managed and controlled Tangguh Site dikelola dan under 900-PRC-EN-2324 Waste dikendalikan di bawah Prosedur Water Management Procedure. Pengelolaan Air Limbah 900-RRC- For record, refer to the Appendix 2 EN-2324. Sebagai catatan, lihat – Maritime Sanitary Wastewater Lampiran 2 – Rekaman Air Record. Limbah Sanitary Maritim.

6.2. 4 Ballast Management 6.2.4 Manajemen Ballast Under Regulation B-4 Ballast Water Berdasarkan Regulasi B-4 Ballast Exchange (International Convention Water Exchange (Konvensi for the Control and Management of Internasional untuk Pengendalian Ships' Ballast Water and Sediments dan Pengelolaan Air Ballast dan - IMO 2004), all ships using ballast Sedimen Kapal - IMO 2004), semua water exchange should: kapal yang melakukan pertukaran air ballast harus: • Whenever possible, conduct • Bila mungkin, melakukan ballast water exchange at least pertukaran air ballast setidaknya 200 nautical miles from the 200 mil laut dari daratan terdekat nearest land and in water at least dan di perairan setidaknya pada 200 metres in depth, taking into kedalaman 200 meter, dengan account Guidelines developed by mempertimbangkan Pedoman IMO; yang dikeluarkan oleh IMO; • In case where the ship is unable • Dalam kasus di mana kapal tidak to conduct ballast water exchange dapat melakukan pertukaran air as above, this should be as far ballast seperti di atas, maka harus from the nearest land as possible, sejauh mungkin dari daratan and in all cases at least 50 nautical terdekat, dan dalam semua kasus miles from the nearest land and in setidaknya harus 50 mil laut dari water at least 200 metres in daratan terdekat dan di perairan depth. setidaknya pada kedalaman 200 meter • Tangguh project personnel • Personil proyek Tangguh yang responsible for shipping will bertanggung jawab untuk monitor the evolving research on perkapalan akan memantau ballast water treatment. perkembangan penelitian pada Where practicable, efforts should pengolahan air ballast. be made to reduce sound by Apabila memungkinkan, upaya

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ballasting unladen tankers (with harus dilakukan untuk mengurangi consideration to the potential for suara dengan melakukan ballast relocation of invasive species in pada kapal yang tidak bermuatan ballast water) and adjusting vessel (dengan pertimbangan potensi speed. untuk relokasi spesies invasif dalam air ballast) dan menyesuaikan kecepatan kapal. Ballast water exchange shall be Pertukaran air ballast harus dicatat recorded for verification at the untuk verifikasi di pelabuhan Proyek Tangguh LNG Project seaport. For LNG Tangguh. Untuk rekaman, lihat recording, see Appendix 3 – Lampiran 3 – Catatan Pertukaran Ballast Water Exchange Record in Air Ballast pada 900-RRC-EN 2324 900-PRC-EN 2324 Wastewater Prosedur Pengelolaan Air Limbah. Management Procedure.

6.2. 5 Coastal Sedimentation 6.2. 5 Pengelolaan Sedimentasi Pesisir Management Maintenance Dredging may be Pengerukan pemeliharaan dapat conducted every 2 (two) years, dilakukan setiap 2 (dua) tahun, depends on the amount or number tergantung pada jumlah of repeated natural sedimentation sedimentasi alami yang terjadi occurs near jetty Tangguh LNG berulang-ulang di dekat dermaga Site. Management effort will be Site LNG Tangguh. Upaya conducted at the mangrove area pengelolaan akan dilakukan di along the nearshore pipeline kawasan mangrove sepanjang construction corridor, other koridor konstruksi pipa dekat pantai, d redging areas, and at the dredged pengerukan daerah lain, dan di material disposal location. Two lokasi pembuangan material keruk. potential deep water areas of the Dua area potensial peraian dalam Bay have been identified for dari Teluk telah diidentifikasi untuk dredged material disposal. They are pembuangan material keruk. Yaitu the West Disposal Site Lokasi Pembuangan Barat (02º26’46.40” S latitude, (02 º26'46.40" LS; 132º52'06,56" 132 º52’06.56” E longitude and bujur timur dan kedalaman 50 m) depth 50 m) and East Disposal Site dan Timur Site Pembuangan (02º19’31.97” S latitude, (02 º19'31,97" LS, 133º07'15,99" 133º07’15.99” E longitude, and bujur timur, dan kedalaman 60 m). depth 60 m). Menurut AMDAL, langkah-langkah According to AMDAL, the following berikut ini akan dipertimbangkan measures will be considered during selama operasi pengerukan dan dredging operations and the pembuangan material keruk: disposal of dredged materials: • Design dredging operations to • Desain operasi pengerukan untuk retain as much existing natural mempertahankan sebanyak aquatic and marginal vegetation mungkin lingkungan perairan alami as possible. dan vegetasi marjinal yang ada. • Dredges spoil (except for that • Sedimen kerukan (kecuali yang used for bund walls) will not be digunakan untuk dinding penahan)

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deposited on surrounding tidak akan ditumpuk pada vegetasi vegetation, inclusive of sekitarnya, termasuk mangrove, mangroves, or in the directly atau di daerah yang berbatasan adjacent areas as the sediment langsung yang mana sedimen can disrupt the natural hydrology dapat mengganggu area hidrologi of the area and make it vulnerable alam dan membuatnya rentan to erosion. terhadap erosi. • Dredging operations and design • Operasi dan desain pengerukan will take into consideration the harus mempertimbangkan flora dan site flora and fauna in coastal fauna di wilayah pesisir dengan areas by including an inventory of memasukkan inventarisasi total total area and flora (type and size) area dan flora (jenis dan ukuran) cleared, as well as conducting dengan jelas, serta melakukan feasible replanting efforts using upaya penanaman kembali vegetasi indigenous vegetation. asli yang layak ditanam.

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6.2. 6 General Management Protection 6.2.6 Manajemen Perlindungan Umum • Launch environmental awareness • Peluncuran program kesadaran programs for Tangguh personnel, lingkungan untuk personil Tangguh, maritime contractors, support vessel kontraktor maritim, operator kapal operators and local communities (in pendukung dan masyarakat lokal coordination with CRP) on the (dalam koordinasi dengan CRP) importance of Berau-Bintuni Bay as a tentang pentingnya Teluk Berau- habitat for marine mammals and Bintuni sebagai habitat mamalia laut reptiles. Materials such as related dan reptil. Bahan-bahan seperti posters and brochures will highlight poster dan brosur terkait akan the protected status of whales, menyoroti status perlindungan paus, dolphins, turtles and crocodiles lumba-lumba, kura-kura dan buaya di under Indonesian law as well as bawah hukum Indonesia serta Tangguh Marine Mammals and Sea Pedoman Mamalia dan Penyu Laut Turtles guidelines. Community Tangguh. Edukasi masyarakat terkait education on these species and their spesies dan habitat laut ini dapat marine habitats may be integrated diintegrasikan dengan program CRP with the ongoing CRP program. yang sedang berlangsung. • Conduct conservation education • Melakukan kegiatan pendidikan activities for the Tangguh LNG Site, konservasi untuk Lokasi LNG including workshops and seminars Tangguh, termasuk lokakarya dan for key personnel and local seminar untuk personil kunci dan communities. masyarakat lokal. • Conduct further survey on the • Melakukan survei lebih lanjut abundance, distribution and mengenai populasi, penyebaran, dan movements of marine reptiles in the pergerakan reptil laut di teluk untuk bay to determine the best strategies menentukan strategi terbaik dalam for impact mitigation. mitigasi dampak. • Report all found dead marine • Melaporkan jika ditemukan mamalia mammals and sea reptiles using dan reptil laut yang mati sighting report, Appendix 2. Sighting menggunakan rekaman Report. penampakan, Lampiran 2. Rekaman Penampakan. • Continue strong enforcement of • Melanjutkan penegakan kuat AMDAL requirements relating to terhadap persyaratan AMDAL yang marine habitat protection, pollution berkaitan dengan perlindungan and water quality management. If habitat laut, polusi, dan pengelolaan any future activities include the kualitas air. Jika ada kegiatan di masa Kokas and Arguni areas (such as mendatang termasuk Kokas dan increased crew, personnel and/or daerah Arguni (seperti personil kru supply vessel movements to/from meningkat, dan/atau gerakan kapal the Project site), then adequate pasok dari/ke lokasi proyek), maka measures, including SOPs, will be langkah-langkah yang memadai, established regarding vessel speed, termasuk SOP, akan ditetapkan routing and distance from potential terkait kecepatan kapal, jalur dan or known turtle nesting sites. jarak dari lokasi potensial atau yang telah diketahui sebagai tempat ber sarang penyu.

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6.3 Monitoring 6.3 Pemantauan • Monitoring of marine mammals • Pemantauan mamalia laut dan and sea turtle throughout the penyu laut di seluruh Wilayah Tangguh Marine Facilities Area Fasilitas Laut Tangguh (yaitu, (i.e. LNG jetty, combo dock and dermaga LNG, dermaga combo platforms). Marine mammals and dan anjungan). Penampakan sea reptiles sighting from several Mamalia laut dan reptil laut dari locations, including vessel, beberapa lokasi, termasuk kapal, platform, combo dock and jetty platform dermaga, combo dan will be recorded. For recording, dermaga akan direkam. Untuk refer Appendix 2 - Sighting rekaman, lihat Lampiran 2 - Record. Rekaman Penampakan. • Consider to conduct further • Pertimbangkan untuk melakukan monitoring and survey with aims pemantauan dan survei lebih to identify, implement and assess lanjut dengan tujuan untuk the performance of additional mengidentifikasi, melaksanakan mitigation measures and dan menilai kinerja langkah- appropriate education campaigns. langkah mitigasi tambahan dan kampanye pendidikan yang tepat

6.4 Nonconformity 6.4 Ketidaksesuaian Incident covers uncontrolled Insiden mencakup pelepasan/ releases/events and/or spills. kejadian tidak terkendali dan/atau As per Group HSSE Reporting tumpahan Requirements, all uncontrolled Sesuai Persyaratan Pelaporan Grup releases/events and/or spills shall be HSSE, semua pelepasan/ kejadian reported in Traction. tidak terkendali dan/atau tumpahan Any waste chemical spill shall be harus dilaporkan dalam Traction. reported. Refer to 900-PRC-EN-2328 Setiap tumpahan limbah bahan Environmental Communication kimia harus dilaporkan. Lihat 900- Procedure. PRC-EN-2328 Prosedur Komunikasi Lingkungan. Abnormal and emergency condition K ondisi abnormal dan darurat dapat could cover but not limited to the mencakup namun tidak terbatas following: pada berikut ini: a. Abnormal condition: a. Kondisi abnormal: • Noise caused by seismic • Kebisingan disebabkan oleh activity. aktivitas seismik. • LNG tanker takes the Raja • LNG tanker mengambil rute Ampat route. Raja Ampat. • Untreated waste discharge • Pembuangan limbah yang from Tangguh vessels and tida k diolah dari kapal dan boat. perahu Tangguh

Abnormal situation arise shall be Situasi abnormal yang timbul recorded in CAR and corrective dicatat dalam CAR dan tindakan action shall be conducted. perbaikan harus dilakukan.

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b. Emergency: b. Kondisi darurat: Chemical or fuel spill from Tumpahan bahan kimia atau Tangguh vessel. minyak dari Kapal Tangguh. . 6.5 Reporting 6.5 Pelaporan The performance of marine Kinerja perlindungan mamalia laut mammal and sea reptile’s dan laut reptil akan dilaporkan protection will be reported as part sebagai bagian dari kinerja of overall environmental pengelolaan dan pemantauan management and lingkungan secara keseluruhan. monitoring performance. For detail Untuk pelaporan rinci, lihat 900- reporting, refer to 900-PRC-EN- RRC-EN-2328 Prosedur 2328 Environmental Komunikasi Lingkungan. Communication Procedure.

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7.0 REGULATORY AND 7.0 REFERENSI PERATURAN DAN STANDARD REFERENCES STANDAR 7.1 Government of RI Regulation 7.1 Peraturan Pemerintah RI • Tangguh Integrated AMDAL • Tangguh AMDAL Terpadu (Surat (AMDAL Approval Letter of The Persetujuan AMDAL Menteri State Minister of Environment Negara Lingkungan Hidup Decree No. 85 of 2002). Keputusan No 85 Tahun 2002). • Law No. 5 year 1990 regarding • UU No. 5 tahun 1990 tentang Conservation of Biological Konservasi Sumber Daya Alam resources & its ecosystem. Hayati dan Ekosistemnya. • Government of Indonesia • Peraturan Pemerintah Indonesia regulation PP no. 7 year 1999 PP no. 7 tahun 1999 tentang regarding Flora and Fauna Pelest arian Flora dan Fauna. Preservation. • Presidential Regulation of • Peraturan Presiden Nomor 29 Republic of Indonesia Number Tahun 2012 tentang 29 Year 2012 regarding Pengesahan Annex III, Annex IV, Ratification of Annex III, Annex Annex V, and Annex VI dari IV, Annex V, and Annex VI of Konvensi Internasional Tahun The International Convention for 1973 tentang Pencegahan the Prevention of Pollution from Pencemaran dari Kapal Ships 1973 as modified by the sebagaimana diubah dengan Proto col of 1978 relating to Protokol tahun 1978 yang terkait there. dari padanya. • International Union for the • International Union untuk Conservation of Nature and Konservasi Alam dan Sumber Natural Resources (IUCN). Daya Alam (IUCN). • Convention on International • Konvensi Perdagangan Trade on Endangered Species of Internasional tentang Spesies Wild Fauna and Flora (CITES). Fauna dan Flora Liar yang Terancam Punah (CITES).

7.2 BP Standards and Policies 7.2 Standar dan Kebijakan BP • OMS Element 3.0 Risk, Sub- • OMS Elemen 3.0 Risiko, Sub- Element 3.6 Environment. Elemen 3.6 Lingkungan. • Group Defined Practice • Group Defined Practice Environment for Access, Major Lingkungan untuk Akses, Proyek Projects, Non Major Projects in Major, Proyek Non-Major di sensitive areas and Acquisition d aerah sensitif dan Kegiatan Activities GDP 3.6-0001 EPR - 8: Akuisisi GDP 3,6-0001 EPR - 8: Marine mammals. mamalia Laut.

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7.3 Industrial Standards 7.3 Standar Industri • ISO 14001: 2004 – • ISO 14001: 2004 - Sistem Environmental Management Manajemen Lingkungan - Systems – Requirements with Persyaratan dengan Guidance for use. Clause petunjuk penggunaan. 4.4.6 Operational Control. Klausul 4.4.6 Pengendalian Operasional. • Marine Mammals and Sea • Mamalia Laut dan Penyu di Turtles in Berau-Bintuni Bay. Teluk Berau-Bintuni. Proyek Tangguh LNG Project. A LNG Tangguh. Sebuah Guide to Reducing Impacts. Panduan untuk Mengurangi Tangguh LNG Project. BP Dampak. Proyek LNG Indonesia. September 2007. Tangguh. BP Indonesia. September 2007. • Guidelines for Minimising • Pedoman untuk Acoustic Disturbance to Meminimalkan Gangguan Marine Mammals from Akustik untuk Mamalia Laut Seismic Surveys – JNCC dari Survei Seismik - JNCC 2010. 2010. • IMO Resolution A/868 (20) – • Resolusi IMO A/868 (20) - Guideline for the Control and Pedoman Pengendalian dan Management of Ship’s Ballast Pengelolaan Air Ballast Water to Minimise the Kapal untuk Meminimalkan Transfer of Harmful Aquatic Pergantian Organisme Organisms and Pathogens. Perairan Berbahaya dan Patogen. • International Convention for • Konvensi Internasional the Control and Management untuk Pengendalian dan of Ships' Ballast Water and Pengelolaan Air Ballast dan Sediments Sedimen Kapal • MARPOL 73/78 Annex V • MARPOL 73/78 Annex V Prevention of Pollution Pencegahan Polusi Sampah Garbage . 8.0 RELATED STANDARD / 8.0 PROSEDUR/STANDAR PROCEDURE TERKAIT • 900-PRC-EN 2321 Non Hazardous • 900-PRC-EN 2321 Prosedur Solid Waste Procedure. Limbah Padat Non Berbahaya. • 900-PRC-EN-2324 Wastewater • 900-PRC-EN-2324 Prosedur Management Procedure. Pengelolaan Air Limbah. • 900-PRC-EN-2328 Environmental • 900-PRC-EN-2328 Prosedur Communication Procedure. Komunikasi Lingkungan.

9.0 APPENDICES 9.0 LAMPIRAN • Appendix 1 Marine Mammals • Lampiran 1 Bagan Alir Prosedur and Sea Reptile Protection Perlindungan Mamalia Laut dan Procedure Flowchart. Reptil Laut.

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• Appendix 2 Sighting Record. • Lampiran 2 Rekaman • Appendix 3 Marine Mammals Penampakan. Recording Form – Record of • Lampiran 3 Formulir Catatan Operations. O perasi Mamalia Laut. • Appendix 4 Marine Mammals • Lampiran 4 Gambar Mamalia Laut and Sea Reptile Pictures. dan Reptil Laut. • Appendix 5 Simplified Overview • Lampiran 5 Gambaran yang of the Discharge Provisions of the Disederhanakan untuk Ketentuan Revised MARPOL Annex V. Pembuangan di revisi MARPOL Annex V.

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Appendix 1 - Marine Mammals and Sea Reptiles Protection Procedure Flowchart

START

6.1 IDENTIFICATION

6.2. PROTECTION ACTIVITY

SEISMIC VESSEL WASTE PLATFORM AND SURVEY MOVEMENT DISPOSAL AT PIPLINEE MANAGEMENT MANAGEMENT SEA MAINTENANCE M ANAGEMENT

BALLAST COASTAL GENERAL MANAGEMENT SEDIMENTATION MANAGEMENT MANAGEMENT

6.3 MONITORING

RAISE CAR AND 6.4 Yes CONDUCT NO NC O NFORMITY CORRECTIVE no ACTION

No REFER TO 900-PRC- EN-2328 ENVIRONMENTAL 6.5 REPORTING COMMUNICATION PROCEDURE

FINISH

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Appendix 2 – Sighting Record

MARINE MAMMALS AND SEA REPTILES SIGHTINGS FORM FORMULIR PENGAMATAN MAMALIA dan REPTIL LAUT

DISTANCE DATE TIME LATITUDE LONGITUDE SPECIES SIZE (cm) NUMBER DIRECTION COMMENTS OBSERVER (m)

Tanggal Waktu Jenis Ukuran Jumlah Jarak Arah Komentar Pengamat

Note:

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Appendix 3 – Marine Mammals Recording Form – Record Of Operations

MARINE MAMMAL RECORDING FORM - RECORD OF OPERATIONS

DTI ref. no. ………………………… Client ……………….. Type of survey (site, 2D, 3D, 4C, OBC, VSP etc.) ……………… Ship ………………………… Seismic contractor ……………….. Total airgun volume (cu. in.) ……………… Method of soft start (if site survey/ VSP) Increase no. guns Increase pressure Increase shotpoint interval

Complete this form every time the airguns are used, including overnight, whether for shooting a line or for testing or for any purpose. Times should be in GMT.

Airgun activity Pre -shooting search for marine mammals Action necessary Date Reason Time Time Time Time Time Time Who Time Time Reasons Were Were If What action for soft of full of of end output airguns carried pre- search why hydro- animals yes, was taken firing start power start of line reduced stopped out shooting ended animals phones present when (e.g. delay (line/ began of line to 160 search? search may have used? in the were shooting) test, dB (if (Job began been 30 they etc.) relevant) title) missed? mins last (e.g. dark, before seen? fog, swell, firing? etc.)

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Appendix 4 – Marine Mammals And Sea Reptiles Pictures

PICTURES SPECIES Reference Tangguh Appearance a. Dolphins 1. Indo Pacific Humpback Dolphins (Sousa Dolphin)

Sousa chinensis http://en.wikipedia.org/ (Wibowo N; Bintuni, 2011) 2. Spinner Dolphins

Stenella longirostris (Wibowo N; Bintuni, 2010)

http://en.wikipedia.org/ 3. Indo Pacific Bottlenose Dolphins

http://en.wikipedia.org/ (Benjamin Kahn/ APEX Environmental; Bintuni, 2006) 4. Common Bottlenose Dolphin

Tursiops truncatus (Drilling Env. Engineer; Bintuni, 2013) http://en.wikipedia.org/

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Bryde’s Whale

http://www.dailymail.co.uk/ Balaenoptera brydei (Kahn; Bintuni, 2006) c. Turtles

1. Green turtle (chelonia mydas)

http://en.wikipedia.org/ Chelonia mydas (Kahn; Bintuni, 2006) 2. Hawksbill Turtle

Eretmochelys imbricata http://en.wikipedia.org/ (Wibowo N; Bintuni, 2010) 3. Olive Ridley Turtle

Lepidochelys olivacea (IPB; Bintuni, 2013)

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Printed from Tangguh Documentum on 08-Jan-2015 BP Berau Ltd Marine Mammals And Sea Reptiles Protection http://en.wikipedia.org/ 4. Leatherback Turtle

Dermochelyscoreacea (WibowoN; Bintuni,2010) http://en.wikipedia.orp/ Crocodiles

Saltwater Crocodile

Crocodylusporosus (MeivyA.; Bintuni,2009) http://en.wikipedia.org/

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ATTACHMENT 2

LIST OF HAZARDOUS MATERIAL AND CHEMICAL USE IN TANGGUH

SUPPLEMENTARY DOCUMENT TO LENDER 135

CHEMICAL INVENTORY Tangguh LNG Operations

Updated: 8/1/2015 Document Number Ingredient Quantity Associated Health Hazards User Other Hazards (Safety & No. Product Name Purpose / Usage / Application Manufacturer / Supplier Form Amount Incompatibilities Hazard Identification Remark (Langua TLV Order Environment) Dept./Section/Contracto (MSDS) (Number) Doc Number File Name Chemical Name Synonyms Symbol / Formula CAS No. Weight% Per Unit Eye Exposure Respiratory (Inhaled) Digestive (Swallowed) Skin Exposure Person In-Charge Phone ge) (mg/m3) Period r Order 1 MSDS 001 EN 0.1mol/l Silver nitrate solution(N/10) MSDS-001-EN 0.1mol - l Silver nitrate solution.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Silver nitrate Silver nitrate in water AgNO3 7761-88-8 1.7 0.01 (mg/m3) as silver 500 ml sunlight, heat, and combistible materials Inflammation Irritation Irritation, vomiting, and Sto Black colour Harmful to Aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to the human body. 2) 2 MSDS 002 EN 1,5-Diphenylcarbonohydrazide MSDS-002-EN 1,5-Diphenylcarbonohydrazide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder 1,5-Diphenylcarbonohydrazide 1,5-Diphenylcarbazide (C6H5NHNH)2CO 140-22-7 85 NA 2 25 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : Irritate English to skin, eyes and cause inflammation. If 1-Amino-2-naphthol-4-naphthalenesulf onic acid 3 MSDS 003 EN 1-Amino-2-naphthol-4-sulfonic acid MSDS-003-EN 1-amino-2-naphtol.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder 1-Amino-2-naphthol-4-sulfonic acid H 2NC10H5(OH)SO3H 116-63-2 97 NA 2 25 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : English irritation to skin, eyes and cause

4 MSDS 004 EN 2,2,4-Trimethylpentane MSDS-004-EN 2,2,4-Trimethylpentane.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid 2,2,4-Trimethylpentane Isooctane, iso-Octane (CH 3)3CCH2CH(CH3)2 540-84-1 98 NA 12 500 mL None Inflammation headache, dizzines No specific Irritation Flammable Operation Lab. Sr. Chemist 1) The most important danger and English hazard : flammable. 2) Adverse human 5 MSDS 005 EN 2,2'-Iminodiethanol MSDS-005-EN 2,2'-Iminodiethanol.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid 2,2'-Iminodiethanol Diethanolamine (HOCH2CH2)2NH 111-42-2 99 NA 10 500 mL Irritation Irritation Irritation Irritation Combustible Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to human body, and 6 MSDS 006 EN 2-Amino-2-hydroxymethyl-1,3-propanediol MSDS-006-EN 2-Amino-2-hydroxymethyl-1,3-propanediol.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder 2-Amino-2-hydroxymethyl-1,3-propanediol Aminomethylidine trimethanol (HOCH2)3CNH2 77-86-1 97 N/A 500 g Light, heat, oxidizing subtances Inflammation N/A Irritation, nausea, vomiting irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : English Irritate to skin, eyes and cause Ethanolamine, Monoethanolamine 7 MSDS 007 EN 2-Aminoethanol MSDS-007-EN 2-Aminoethanol.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid 2-Aminoethanol NH2CH2CH2OH 141-43-5 99 3 ppm 8 500 mL Oxidizers, acids Irritation Irritation No specific Irritation Combustible Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to human body and Isopropyl alcohol, iso-Propyl alcohol 8 MSDS 008 EN 2-Propanol - Kanto MSDS-008-EN 2-Propanol-KANTO.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid 2-Propanol (CH 3)2CHOH) 67-63-0 99 200 ppm 5 500 mL PVC resin, acrylic resin, polystyrene Inflammation Inflammation Inflammation Inflammation Substance is flammable and vapor Operation Lab. Sr. Chemist 1) The most important danger and English hazard : this substance is flammable and Isopropyl alcohol, iso-Propyl alcohol 9 MSDS 009 EN 2-Propanol - Merck MSDS-009-EN 2-Propanol-Merck.pdf Operation Lab. Analysis Merck KGaA Liquid 2-Propanol CH 3CH(OH)CH3 67-63-0 60.1 g/mol 200 ppm 29 2.5 L PVC resin, acrylic resin, polystyrene Inflammation Inflammation Inflammation Inflammation Substance is flammable and vapor Operation Lab. Sr. Chemist Highly flammable. Irritating to eyes. English Vapours may cause drowsiness and 10 MSDS 010 EN 3752 almagard Varl MSDS-010-EN 3752 almagard Varl.pdf Although there are no consistent primary English routes of entry, the product may cause 11 MSDS 011 EN 3M Scotch-Brite Hand Pads -7440 MSDS-011-EN 3M Scotch-Brite Hand Pads-7440.pdf 1) Eye contact :signs/symptoms may English include pain, redness, tearing and 12 MSDS 012 EN 3M Scotch-Brite Hand Pads-7445-Light Duty Pad MSDS-012-EN 3M Scotch-Brite Hand Pads-7445-Light Duty Pad.pdf 1) Eye contact : dust created by cutting, English grinding, sanding, or machining may 13 MSDS 013 EN 3M Scotch-Brite Hand Pads-7448-7448B-7468 MSDS-013-EN 3M Scotch-Brite Hand Pads-7448-7448B-7468.pdf 1) Eye contact :signs/symptoms may English include pain, redness, tearing and

14 MSDS 014 EN 4-Aminoantipyrine MSDS-014-EN 4-aminoantipyrine.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder 4-Aminoantipyrine NA C11H13N3O 83-07-8 99 NA 2 25 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : English irritation to skin, eyes and cause

15 MSDS 015 EN 4-Methyl-2-pentanone MSDS-015-EN 4-Methyl-2-pentanone.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid 4-Methyl-2-pentanone Methyl isobutyl ketone (CH 3)2CHCH2COCH3 108-10-1 95 205 2 500 mL None Inflammation Narcotic No specific Irritation Flammable Operation Lab. Sr. Chemist 1) The most important danger and English hazard : flammable. 2) Adverse human

16 MSDS 016 EN 8-Hydroxyquinoline MSDS-016-EN 8-Hydroxyquinoline.pdf Operation Lab. Analysis Merck KGaA Solid 8-Hydroxyquinoline Oxine, 8-Quinolinol C9H7NO 148-24-3 145.2 g/mol NA 2 50 g Strong oxidizers, strong acids and bases No specific Harmful Harmful No specific Combustible Operation Lab. Sr. Chemist Harmful by inhalation and if swallowed. English

17 MSDS 017 EN Accepta 3550 MSDS-017-EN Accepta 3550.pdf Not regarded as a health under current English legislation 18 MSDS 018 EN Accu-Lead Acid Storage Battery MSDS-018-EN Accu-Lead Acid Storage Battery.pdf Liquid sulfuric acid with its corrosive English property can cause skin irritation

19 MSDS 019 EN Acetic acid (glacial) MSDS-019-EN acetic acid (glacial).pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Liquid Acetic acid NA CH 3COOH 64-19-7 60.05 g/mol NA 2 1000 mL Various metals Burns Irritation Burns Burns Corrosive and Flammable Operation Lab. Sr. Chemist Flammable. Causes severe burn. English

20 MSDS 020 EN Acetone MSDS-020-EN acetone GR.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Aceton Domethyl ketone, 2-Propanone CH 3COCH3 67-64-1 99 500ppm 10 500 mL PVC resin, acrylic resin, polystyrene Inflammation headache, dizzines Inflammation Inflammation Highly Flammable Operation Lab. Sr. Chemist Flammable liquid, acute toxic English substances.

21 MSDS 021 EN Acetone GR MSDS-021-EN acetone.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Liquid Aceton Domethyl ketone, 2-Propanone CH 3COCH3 67-64-1 58.08 g/mol 500ppm 51 2.5 L Various plastics, rubber Irritation Irritation Irritation Irritation Highly flammable Operation Lab. Sr. Chemist Highly flammable. Irritating to eyes. English Repeated exposure may cause skin 22 MSDS 022 IN acetylene MSDS-022-IN acetylene.pdf Acetilene may cause asphyxianous, Bahasa exposured in the middle concentration 23 MSDS 023 EN Acid Digestion Vials for Low Range TOC MSDS-023-EN Acid Digestion Vials for Low Range TOC.pdf Cause eye burn, harmful if inhaled, may English cause skin irritation cancer hazard 24 MSDS 024 EN Acid Digestion Vials for Mid Range TOC MSDS-024-EN Acid Digestion Vials for Mid Range TOC.pdf Cause eye burn, harmful if inhaled, may English cause skin irritation cancer hazard 25 MSDS 025 EN Acidic Washing Solution MSDS-025-EN Acid Washing Solution.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Triglycerides Aqueous Solution NA NA NA NA N/A N/A None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English EMERGENCYexcluded. However, OVERVIEW: risks are in not the to fresh be 26 MSDS 026 EN Activated Alumina MSDS-026-EN Activated Alumina.pdf Utilities unused state, this product is not English dalamflammable. keadaan Repeated yang tidakor prolonged terpakai, MSDS 026 IN Activated Alumina MSDS-026-IN Activated Alumina B.Indo.pdf Operation Lab. Analysis Starborn Granule Activated Alumina 1344-28-1 Operation Marcelinus Haryanto 62-811-103739 produk ini tidak mudah terbakar. Bahasa Paparan berulang atau berkepanjangan 27 MSDS 027 EN Activated carbon MSDS-027-EN Activated carbon.pdf Ingestion; practically non toxic, eye English contact; irritation or mechanical injury, 28 MSDS 028 EN Agfa Fixer part-A MSDS-028-EN Agfa Fixer part-A.pdf Slight sulfur dioxide odor; may cause English eye, skin, and respiratory tractus 29 MSDS 029 EN agip alisma 32pv MSDS-029-EN Agip alisma 32 PV.pdf In the conditions specified for use and English for the intended services, the product 30 MSDS 030 EN Agip OTE MSDS-030-EN Agip OTE.pdf The product is not classified as English dangerous according to the criteria set 31 MSDS 031 EN Agip OTE 32GT MSDS-031-EN Agip OTE 32GT.pdf NA English

32 MSDS 032 EN Agip OTE GT MSDS-032-EN Agip OTE GT.pdf NA English

33 MSDS 033 EN Agip rustia 100/F MSDS-033-EN Agip Rustia 100-F.pdf In the conditions specified for use and English for the intended services, the product 34 MSDS 034 EN Agip Rustia C. MSDS-034-EN Agip Rustia C.pdf In the conditions specified for use and English for the intended services, the product 35 MSDS 035 EN ALAT/ALT (GPT) MSDS-035-EN ALAT-ALT GPT.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 36 MSDS 036 EN Albumin MSDS-036-EN albumin.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Albumin Aqueous Solution NA NA NA NA 1 kit/300ml Yearly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 37 MSDS 037 EN alkali solution for calcium and magnesium test MSDS-037-EN alkali solution for calcium and magnesium test.pdf Cause severe burns. May cause kidney English or liver damage based on animal data. 38 MSDS 038 EN Alkaline Phosphatase IFCC MSDS-038-EN Alkaline Phosphatase IFCC.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Alkaline Phosphatase Aqueous Solution NA NA NA NA 1 kit/300ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 39 MSDS 039 EN Alkaline Washing Solution MSDS-039-EN alkaline washing sol.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Triglycerides Aqueous Solution NA NA NA NA 1 bottle/500ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 40 MSDS 040 EN Alpha ZN 220 MSDS-040-EN Alpha ZN 220.pdf NA English

41 MSDS 041 EN Alpha-SMR-Heavy X MSDS-041-EN Alpha-SMR-Heavy X.pdf This preparation is not classified as English dangerous 42 MSDS 042 EN Alphasyn T-150 MSDS-042-EN Alphasyn T-150.pdf This preparation is not classified as English dangerous according to directive 43 MSDS 043 EN Alphasyn T-220 MSDS-043-EN Alphasyn T-220.pdf This preparation is not classified as English dangerous according to directive 44 MSDS 044 EN Alumunium Sulfate MSDS-044-EN Alumunium sulfate.pdf Avoid prolonged sufficient protective English apparatus and avoid contracting with the 45 MSDS 045 EN Amdea MSDS-045-EN Amdea.pdf Risk of serious damage to eyes. May English cause sensitization by inhalation and 46 MSDS 046 EN Amidosulfuric acid MSDS-046-EN Amidosulfuric acid.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Amidosulfuric acid Sulfamic acid HOSO2NH2 5329-14-6 99 N/A 500 g Alkaline substances, heat, sunlight Irritation Irritation N/A irritation N/A Operation Lab. Sr. Chemist 1) The most important danger and English hazard : Corrosive to human body. 2) 47 MSDS 047 EN amino acid f reagent MSDS-047-EN amino acid f reagent.pdf Causes eye irritation may cause English respiratory tract irritation may cause 48 MSDS 048 EN Amino acid reagent for Phosphate and Silica MSDS-048-EN Amino acid reagent for Phosphate and Silica.pdf Harmful if inhaled or absorbed through English skin causes eye irritation may cause 49 MSDS 049 EN Ammonia solution 25% GR MSDS-049-EN Ammonia solution 25% GR.pdf Operation Lab. Analysis Merck KGaA Liquid Ammonium hydroxide Aqueous ammoniacal solution 1336-21-6 25 NA 2 1000 mL Strong alkalis, merury, water, etc. Burns Irritation Irritation Burns Very toxic to aquatic organism Operation Lab. Sr. Chemist Causes burns. Very toxic to aquatic English organism.

50 MSDS 050 EN Ammonium chloride GR MSDS-050-EN Ammonium chloride GR.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Solid Ammonium chloride Sal ammoniac NH4Cl 12125-02-9 53.49 g/mol 10 2 500 g Alkali hydroxides Irritation Harmful Harmful Harmful Operation Lab. Sr. Chemist Harmful if swallowed. Irritating to eyes. English

51 MSDS 051 EN Ammonium monovanadate GR MSDS-051-EN Ammonium monovanadate GR.pdf Operation Lab. Analysis (Reag. Ph Merck KGaA Solid Ammonium monovanadate Ammonium vanadate NH4VO3 7803-55-6 116.98 g/mol NA 2 100 g Strong oxidizers, acids Irritation Harmful Toxic NA Operation Lab. Sr. Chemist Harmful by inhalation. Toxic if swallowed. English Irritating to eyes and respiratory system. 52 MSDS 052 EN Anion resin MSDS-052-EN Anion resin.pdf Hazard warning not required English

53 MSDS 053 EN Ansulex Low pH MSDS-053-EN Ansulex Low pH.pdf Not classified as hazardous English

54 MSDS 054 EN Ansulite-3% AFF MSDS-054-EN Ansulite-3% AFF.pdf Neither this preparation nor the English ingredients contained in it have been 55 MSDS 055 EN Ansul-PKW MSDS-055-EN Ansul-PKW.pdf This preparation is not classified as English dangerous according to directive 56 MSDS 056 EN anticorit 3 MSDS-056-EN anticorit 3.pdf 1) For man : frequent and/or prolonged English contact may give rise to skin irritation 57 MSDS 057 EN Antimony standard solution (Sb-1000) MSDS-057-EN Antimony standard solution (Sb-1000).pdf Operation Lab. Analysis Merck KGaA Liquid antimony (III)oxyde Sb2O3 1309-64-4 N/A 100 ml Unsuitable working materials: metal, metal alloys (generation of hydirritation irritation irritation irritation harmful to aquatic organisms Operation Lab. Sr. Chemist No Hazardous as specified English

58 MSDS 058 EN Aquamicron Water Standard, 0.2mg, for Karl Fisher MSDS-058-EN Aquamicron Water Standard, 0.2mg, for Karl Fisher.pdf Operation Lab. Analysis API Corporation Liquid Propylene carbonate NA 108-32-7 99.98 NA 2 5mLx10mL None Irritation Irritation Irritation Slight irritation Operation Lab. Sr. Chemist Irritating liquid. English

59 MSDS 059 EN Aquamicron Water Standard, 1mg, for Karl Fisher MSDS-059-EN Aquamicron Water Standard, 1mg, for Karl Fisher.pdf Operation Lab. Analysis API Corporation Liquid Propylene carbonate NA 108-32-7 99.98 NA 2 5mLx10mL None Irritation Irritation Irritation Slight irritation Operation Lab. Sr. Chemist Irritating liquid. English

60 MSDS 060 EN Aquaquick-2000sp MSDS-060-EN Aquaquick-2000sp.pdf NA English

61 MSDS 061 EN Arcus Cleaner 4443 MSDS-061-EN Arcus Cleaner 4443.pdf Clinic Lab. Diagon Ltd. Liquid Ammonium Salts NA NA NA 6.2 NA 1 pack/5 litre Yearly NA Irritation Irritation Irritation Irritation HSE MP Clinic Irritant English

62 MSDS 062 EN Arcus Diluent 44441 MSDS-062-EN Arcus Diluent 44441.pdf Clinic Lab. Diagon Ltd. Liquid Ammonium Salts NA NA NA 6.2 NA 1 pack/20 litre Bi-monthly NA Irritation Irritation Irritation Irritation HSE MP Clinic Irritant English

63 MSDS 063 EN Arcus Lyse 44442 MSDS-063-EN Arcus Lyse 44442.pdf Clinic Lab. Diagon Ltd. Liquid Ammonium Salts NA NA NA 4.2 NA 1 bottle/500ml Bi-monthly NA Irritation Irritation Irritation Irritation HSE MP Clinic Irritant English

64 MSDS 064 IN argon MSDS-064-IN argon.pdf Asphixiant Bahasa

65 MSDS 065 EN Arsenic standard solution (As-1000) MSDS-065-EN Arsenic standard solution (As-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Arsen As2O5 in H2O 7778-39-4 2.5-10% 0.01 mg/m3 100 mL Toxic cause cancer Toxic cause cancer toxic to aquatic organisms Operation Lab. Sr. Chemist May cause cancer. Also harmful by English inhalation and if swallowed.Toxic to 66 MSDS 066 EN ASAT/AST (GOT) MSDS-066-EN ASAT-AST (GOT).pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 67 MSDS 067 EN Bactron B1710 MSDS-067-EN Bactron B1710.pdf Biocide Champion Servo Liquid NA Phosphonium Salts Xn NA 20 - 60 NA Strong Bases Harmful Dizziness and nausea Irritation Burns GPF & ORF TBD Harmful if swallowed. Toxic by inhalation. English NA Proprietray Surfactants C NA 1 - 5 NA Risk of serious damage to eyes. May 68 MSDS 068 EN Barbituric acid MSDS-068-EN Barbituric acid.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Barbituric acid Malonylurea C4H4N2O3 67-52-7 98 NA 2 25 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : irritate English to skin, eyes and cause inflamation. If 69 MSDS 069 EN Barium chloride dihydrate MSDS-069-EN Barium chloride dihydrate.pdf Operation Lab. Analysis (Reagen) Kanto Chemical Co., Inc Powder Barium chloride dihydrate NA BaCl2-2H2O 10326-27-9 98.5 NA 15 500 g Strong oxidizers Irritation Irritation Irritation Irritation Harmful to aquatic organisms Operation Lab. Sr. Chemist 1) danger and hazard : toxic of the English human body 2) adverse human health 70 MSDS 070 EN Barium standard solution (Ba-1000) MSDS-070-EN Barium standard solution (Ba-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Barium Nitrate I0022-31-8 Nitric acid: 2.6 mg/m3, Barium:0.5 mg/mm3 100 mL Unsuitable working materials: metal, metal alloys (generation of hydIrritation Irritation Irritation, nausea, salvation Irritation Hazard for drinking water, toxic to Operation Lab. Sr. Chemist Irritating to eyes and skin English

71 MSDS 071 IN Barrier - comp A MSDS-071-IN Barier comp-a.pdf

72 MSDS 072 EN Barrier 77-comp.A MSDS-072-EN Barrier 77-comp.A.pdf This preparation is classified as English dangerous according to directive 73 MSDS 073 EN Basalt mineral wool MSDS-073-EN Basalt Mineral W0ol.pdf 1) Health hazards chronic : the risk of English respiratory or skin conditions that are 74 MSDS 074 EN Battery electolyte MSDS-074-EN Battery electolyte.pdf Corrosive. Causes severe burns. English

75 MSDS 075 EN Belgard EV2050 MSDS-075-EN Belgard EV2050.pdf Irritating to eyes English

76 MSDS 076 EN Belgard EVN MSDS-076-EN Belgard EVN.pdf Antiscalant Biolab Liquid Polycarboxylic Acid Sodium Salt NA 70247-90-4 NA NA NA Irritation Irritation Irritation Irritation Utilities James Lempoy Non hazardous for conveyor, non English hazardous for supply. Irritating to eyes 77 MSDS 077 EN Belite M8 MSDS-077-EN Belite M8.pdf Antifoam Biolab Liquid Polyglycols NA NA 67-63-0 0 - 8 TBD Strong oxidizer, heat, flame Irritation Irritation Irritation Irritation Flammable Utilities James Lempoy Flammable. Irritating to eyes. Vapours English Isopropanol may cause drowsiness and 78 MSDS 078 EN Belzona 1111 MSDS-078-EN Belzona 1111.pdf Harmful if swallowed. Causes burns. English May cause sensitization by skin contact. 79 MSDS 079 EN Belzona 1311 MSDS-079-EN Belzona 1311.pdf Harmful if swallowed. Causes burns. English May cause sensitization by skin contact. 80 MSDS 080 EN Belzona 1321 MSDS-080-EN Belzona 1321.pdf May cause sensitization by skin contact. English Iritating to eyes and skin. Toxic to 81 MSDS 081 EN Belzona 1341 MSDS-081-EN Belzona 1341 N.pdf Cause burns. May cause sensitization English by skin contact. Possible risk of 82 MSDS 082 EN Belzona 1341 N MSDS-082-EN Belzona 1341.pdf Harmful by inhalation, in contact with English skin and if swallowed. Causes burns. 83 MSDS 083 EN Belzona 1391 MSDS-083-EN Belzona 1391.pdf Harmful if swallowed. Causes burns. English Irritating to respiratory system. May 84 MSDS 084 EN Belzona 2211 MSDS-084-EN Belzona 2211.pdf Toxic to aquatic organism, may cause English long-term adverse effects in the aquatic 85 MSDS 085 EN Benzene GR MSDS-085-EN Benzene GR.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Liquid Benzene Cyclohexatriene C6H6 71-43-2 78.11 g/mol 0.5ppm 2 1000 mL Halogens, uranium hexafluoride Irritation Carcinogen Irritation Carcinogen Flammable Operation Lab. Sr. Chemist May cause cancer. May cause heritable English genetic damage. Highly flammable. 86 MSDS 086 EN Bilirubin Total MSDS-086-EN bilirubin total.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Bilirubin Aqueous Solution NA NA NA NA 1 kit/300ml Yearly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 87 MSDS 087 EN Biobor JF MSDS-087-EN Biobor JF.pdf Combustible liquid and vapor (flammable English if shipped by air/vessel). Inhalation may 88 MSDS 088 EN BioCal MSDS-088-EN biocal.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 vial/ 5 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 89 MSDS 089 EN BioNorm MSDS-089-EN bionorm.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 vial/ 5 ml Monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 90 MSDS 090 EN BioPath MSDS-090-EN BioPath.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA N/A N/A None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 91 MSDS 091 EN Bis (+)-tartrato diantimonate(III) dipotassium trihydrate MSDS-091-EN Bis (+)-tartrato diantimonate(III) dipotassium trihydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Bis (+)-tartrato diantimonate(III) dipotassium trihydra Antimony potassium tertrate trihydrate C8H4K2O12Sb2-3H2O 28300-74-5 98 NA 4 25 g Strong acids Irritation Irritation Irritation Irritation Harmful to aquatic organisms Operation Lab. Sr. Chemist 1) danger and hazard : toxic of the English human body 2) adverse human health 92 MSDS 092 EN Boricᇖ Acid GRᇗ MSDS-092-EN Boricᇖ acid GR.pdfᇗ ᇖ ᇗ

93 MSDS 093 EN Boiling stone, Big granule MSDS-093-EN Boiling stone, Big granule.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Aluminium oxide NA Al2O3 TBD 20-33 NA 2 500 g No specific No specific No specific No specific Operation Lab. Sr. Chemist 1) Adverse human health hazard : the English Silicon dioxide SiO2 60-75 product is ceramic and does not have 94 MSDS 094 EN Bromocresol green MSDS-094-EN Bromocresol green.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Bromocresol green 3',3',5',5'-Tetrabromo-m-cresoldulf onphthalein C21H14Br4O5S 76-60-8 80 NA 2 1 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : irritate English to skin, eyes and cause inflamation. If 3,3',5,5'-Tetrabromophenolsulf onphthalein, BBB 95 MSDS 095 EN Bromophenol blue MSDS-095-EN Bromophenol blue.pdf Operation Lab. Analysis Merck KGaA Solid Bromophenol blue C19H10Br4O5S 115-39-9 669.96 g/mol NA 2 5 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist not hazardous product as specified. English

96 MSDS 096 EN Buffer Solution, pH 2.0 MSDS-096-EN Buffer Solution pH-2,0.pdf Causes eye burns, may cause skin English irritations. 97 MSDS 097 EN Cadmium oxide MSDS-097-EN Cadmium oxide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Cadmium oxide NA CdO 1306-19-0 99 NA 4 25 g Oxidizer - gradually dust: irritation Long term: kedney damageGastroenteritis NA Operation Lab. Sr. Chemist 1) Danger and hazard : toxic to human English body. 2) Adverse human health hazard : 98 MSDS 098 EN Cadmium standard solution (Cd-1000) MSDS-098-EN Cadmium standard solution (Cd-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Cadmium nitrate 4-Hydrate Cd(NO3)2 in HNO3 1002-68-1 Nitric acid: 2.6 mg/m3, Cadmium: 0.01 mg/mm3 500 mL Unsuitable working materials: metal, metal alloys (generation of h:\ Irritation Irritation Irritation of mucous membr Irritation Hazard for drinking water, toxic to Operation Lab. Sr. Chemist Irritating to eyes and skin English

99 MSDS 099 EN Cadmium, Drops MSDS-099-EN Cadmium, Drops.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Granule Cadmium NA Cd 7440-43-9 99 0.002 4 25 g Oxidizer - gradually dust: irritation Long term: kedney damageGastroenteritis NA Operation Lab. Sr. Chemist 1) Adverse human health hazard : If English swallowed, may cause,vomitting, 100 MSDS 100 EN calcium and magnesium indicator solution MSDS-100-EN calcium and magnesium indicator solution.pdf May cause eye irritation. English

101 MSDS 101 EN Calcium carbonate - ScienceLab MSDS-101-EN Calcium Carbonate-Science Lab.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Calcium carbonate NA CaCO3 471-34-1 98 NA 2 500 g None No specific No specific No specific No specific Operation Lab. Sr. Chemist 1) Adverse human health hazard : As English calcium carbonate is permitted to be 102 MSDS 102 EN Calcium carbonate - Starborn MSDS-102-EN Calcium Carbonate-Starborn.pdf Starborn Calcium carbonate CaCO3 471-34-1 Hazardous in case of eye contact English (irritant), slightly hazardous in case of MSDS 102 IN Calcium carbonate - Starborn MSDS-102-IN Calcium Carbonate MSDS _B.Indo.pdf Operation Lab. Analysis Starborn Powder Calcium carbonate CaCO3 471-34-1 Hazardous in case of eye contact Bahasa (irritant), slightly hazardous in case of 103 MSDS 103 EN calcium chloride MSDS-103-EN calcium chloride.pdf NA English

104 MSDS 104 EN Calcium chloride dihydrate MSDS-104-EN Calcium chloride dihydrate.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Solid Calcium chloride dihydrate NA CaCl 2*2H2O 10035-04-8 147.02 g/mol NA 2 500 g Irritation No specific No specific No specific Operation Lab. Sr. Chemist Irritating to eyes English

105 MSDS 105 EN Calcium hydroxide MSDS-105-EN Calcium hydroxide.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Solid Calcium hydroxide NA Ca(OH)2 1305-62-0 74.1 g/mol NA 2 500 g Eye damage NA NA NA Operation Lab. Sr. Chemist Risk of serious damage to eyes. Harmfull English if swallowed or inhaled causes burn to 106 MSDS 106 EN Calcium Hypochlorite MSDS-106-EN Calcium Hyphoclorite.pdf Biocide, Algae Control Starborn Powder TCCA Trie chloro Cyanuric acid Bahan dapat iritasi yang keras pada Bahan berbahaya bila Bahan dapat Swallowed : Material is harmful if English menyebabkan sebagai hidung, tenggorokan dan tertelan menyebabkan berikut: swallowed. Eye: Material can cause the MSDS 106 IN Calcium Hypochlorite MSDS-106-IN Calcium hypochlorite B.Indo.pdf Biocide, Algae Control Starborn Powder TCCA Trie chloro Cyanuric acid Bahan dapat iritasi yang keras pada Bahan berbahaya bila Bahan dapat Swallowed : Material is harmful if Bahasa menyebabkan sebagai hidung, tenggorokan dan tertelan menyebabkan berikut: swallowed. Eye: Material can cause the 107 MSDS 107 EN Calcium oxide MSDS-107-EN Calcium oxide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Calcium oxide NA CaO 1305-78-8 97 NA 2 500 g Water --> generating heat Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Danger and hazard : corrosive to the English human body. 2) Adverse human health 108 MSDS 108 EN Calcium standard solution (Ca-1000) MSDS-108-EN Calcium standard solution (Ca-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Calcium nitrate 4-Hydrate Ca(NO3)2 in HNO3 13477-34-4 Nitric acid: 2.6 500 ml Unsuitable working materials: metal, metal alloys (generation of hydIrrittation Irrittation Mucosal Irrittation Irrittation Hazard for drinking water, toxic to Operation Lab. Sr. Chemist Irritating to eyes and skin English

109 MSDS 109 IN Calsium Sulfonate MSDS-109-IN calcium sulfonate.pdf

110 MSDS 110 EN carbocrylic 3359 MSDS-110-EN carbocrylic 3359.pdf May cause eye irritation, skin irritation. English CarbonHarmful Dioxideif inhaled, is amay colorless, affect theodorless brain 111 MSDS 111 EN Carbon Dioxide-Air Liquide MSDS-111-EN Carbon Dioxide-Air Liquide.pdf TBD Air Liquide Liquid Carbon dioxide Carbon anhydride CO2 124-38-9 99.5 5000 ppm Stable Frosbite Not specified Not specified Frosbite NA Utilities Asrory gas, or a colorless, odorless liquid in a English Carbonhigh-pressure Dioxide container. is a colorless, Over-exposure odorless MSDS 111 IN Carbon Dioxide-Air Liquide MSDS-111-IN MSDS CO2 B.Indo.pdf TBD Air Liquide Liquid Carbon dioxide Carbon anhydride CO2 124-38-9 99.5 5000 ppm Stable Frosbite Not specified Not specified Frosbite NA Utilities Asrory gas, or a colorless, odorless liquid in a Bahasa high-pressure container. Over-exposure 112 MSDS 112 EN Carbon Dioxide-Firenze MSDS-112-EN Carbon Dioxide-Firenze.pdf Firenze Not classified as dangerous substances English under the current regulations liquified 113 MSDS 113 EN Carbon Dioxide-Nova MSDS-113-EN Carbon Dioxide-Nova.pdf This product is imediately harmfull by English inhalation. Gas with not burn, hydrogen 114 MSDS 114 EN Carbon disulfide MSDS-114-EN Carbon disulfide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Carbon disulfide NA CS2 75-15-0 99 NA 2 500 mL PVC resin, acrylic resin, polystyrene --> Plastics Irritation Irritation Irritation Irritation Extremely flammable Operation Lab. Sr. Chemist 1) Danger and hazard : extremely English flammable, harmful to human. 2) Adverse 115 MSDS 115 IN Castrol Hyspin AWH M 100-INA MSDS-115-IN Castrol Hyspin AWH M 100-INA.pdf Pelumas Hydrolik Castrol Tidak diketahui efek signifikan atau bahaya Bahasa – bahaya kritis 116 MSDS 116 EN Castrol TQ Dextron III MSDS-116-EN Castrol TQ Dextron III.pdf This preparation is not classified as English dangerous according to directive 117 MSDS 117 EN castrol transaqua HT MSDS-117-EN castrol transaqua HT.pdf This preparation is not classified as English dangerous according to directive 118 MSDS 118 EN Caustic Soda - Omega Chemical MSDS-118-EN Caustic Soda-Omega Chemical.pdf Omega Chemical Its corrosive product, do not touch if English event change to be solution 119 MSDS 119 EN Caustic Soda (100%) - Alliance MSDS-119-EN Caustic Soda 100%-Alliance.pdf Drilling Mud Additive Alliance Energy Services, Ltd. Solid Sodium Hydroxide Caustic Soda NaOH 1310-73-2 100 2 (Ceiling) Strong acid, water, metals (Al, Zn), organohalogen compound Extremely corrosive Severe irritation secere burning of mouth, t Severe burning Logistic Tugu - Willy 1) Skin: Severe burning, frequently deep English ulcerations and ultimate scarring. 120 MSDS 120 EN caustic soda (40%) - Kurita MSDS-120-EN caustic soda (40%)-Kurita.pdf Poison, Danger, Corrosive, may be fatal English if swallowed. Harmfull if inhalled, causes 121 MSDS 121 EN Caustic Soda Flakes MSDS-121-EN Caustic Soda Flakes.pdf Poison ! Danger ! Corrosive. May be English fatal if swallowed. Harmful if inhaled. 122 MSDS 122 EN cecagel MSDS-122-EN cecagel.pdf Possible temporary irritation of eyes and English respiratory system 123 MSDS 123 EN cecagel c1/e1 MSDS-123-EN cecagel c1-e1.pdf Possible temporary irritation of eyes and English respiratory system 124 MSDS 124 EN ceramic ball MSDS-124-EN ceramic ball.pdf NA English

125 MSDS 125 EN CFR-6L MSDS-125-EN CFR-6L.pdf May cause eye irritation English

126 MSDS 126 EN Charcoal activated, Powder MSDS-126-EN Charcoal Activated, Powder.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Carbon Activated carbon, powder C 7440-44-0 95 NA 4 500 g None Irritation Irritation No specific No specific Combustible Operation Lab. Sr. Chemist 1) danger and hazard : combustible. 2) English adverse human health hazard : irritation

Tosylchloramide sodium, N-Chloro-4-toluenesulfonamide sodium salt, Chlrine leaching solution 127 MSDS 127 EN Chloramine T (Sodium p-toluenesulfonchloramide trihydrate) MSDS-127-EN Chloramine T (Sodium p-toluenesulfonchloramide trihydrate).pdf Operation Lab. Analysis Merck KGaA Solid Chloramine T CH3C6H4SO2NClNa*3H2O 7080-50-4 281.69 g/mol NA 2 250 g Strong oxidizers, acids Irritation Sensitization Harmful Burns Operation Lab. Sr. Chemist Harmful is swallowed. Contact with acids English liberates toxis gas. Causes burns. May 128 MSDS 128 EN Chlorinated lime MSDS-128-EN Chlorinated lime.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Chlorinated lime Calcium hypochlorite Ca(Ocl)2 7778-54-3 60 NA 2 500 g Irritation NA NA Light irritation Operation Lab. Sr. Chemist 1) Danger and hazard : this substance English has oxidizibility and increases 129 MSDS 129 EN Chloroform GR MSDS-129-EN Chloroform GR.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Liquid Chloroform GR Trichloromethane CHCl3 67-66-3 119.38 g/mol NA 2 2.5 L Strong alkalis, alkali metal Irritation Harmful Harmful Irritation Harmful to aquatic organisms Operation Lab. Sr. Chemist Harmful is swallowed. Irritating to skin. English Limited evidence of a carcinogenic 130 MSDS 130 EN Cholesterol MSDS-130-EN cholesterol.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Cholesterol Aqueous Solution NA NA NA NA 1 kit/300ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 131 MSDS 131 EN Chromium standard solution (Cr-1000) MSDS-131-EN Chromium standard solution (Cr-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Chromium ( III) Nitrate 9-Hydrate Cr(NO3)3 in HNO3 2/8/7789 Nitric acid: 2.6, chromium (III): 0.5 mg/mm3 500 ml Unsuitable working materials: metal, metal alloys (generation of hydIrrittation irritation Irritation of mucus membra Irrittation toxic to aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin English

132 MSDS 132 EN Citric acid f reagent MSDS-132-EN citric acid f reagent.pdf Causes eye irritation my cause skin English irritation.

133 MSDS 133 EN Citric acid monohydrate GR MSDS-133-EN Citric acid monohydrate GR.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Solid Citric acid monohydrate NA C6H8O7*H2O 5949-29-1 210.14 g/mol NA 2 500 g Metals, oxidizers, bases, reducing agents Irritation NA NA NA Operation Lab. Sr. Chemist Irritating to eyes English

134 MSDS 134 EN CK-MB MSDS-134-EN ck-mb.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Triglycerides Aqueous Solution NA NA NA NA 1 kit/ 62,5 ml Yearly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 135 MSDS 135 EN Cobalt standard solution (Co-1000) MSDS-135-EN Cobalt standard solution (Co-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Cobalt(II) Nitrate 6-Hydrate Co(NO3)2 10026-22-9 Nitric acid: 2.6 mg/m3, cobalt: 0.02 mg/m3 100 ml Unsuitable working materials: metal, metal alloys (generation of hydIrrittation Irrittation, coughing, dyspn Irrittation Irrittation Hazard for drinking water Operation Lab. Sr. Chemist Irritating to eyes and skin. Contains English cobalt (I) nitrate : may produce an 136 MSDS 136 EN condensate MSDS-136-EN condensate.pdf NA English

137 MSDS 137 EN condensate treatment MSDS-137-EN condensate treatment.pdf Corrosive to skin, corrosive to eyes. English Vapor, gas, mist and aerosol may cause 138 MSDS 138 EN Continous filament E-glass MSDS-138-EN continous filament E-glass.pdf Man made mineral fibres (MMMF) can English cause irritation to the skin and eyes. It 139 MSDS 139 IN Coolant, Low Conductivity MSDS-139-IN Coolant,Low Conductivity.pdf

140 MSDS 140 EN COPPER MASKING REAGANT MSDS-140-EN Copper Masking reagent.pdf May cause eye and respiratory tract English iritation 141 MSDS 141 EN Copper standard solution (Cu-1000) MSDS-141-EN Copper standard solution (Cu-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Copper (II) nitrate Cu(NO3)2 3251-23-8 Nitric acid: 2.6 mg/mm3, copper as Fume: 0.2 mg/mm3 and as Dust and Mists: 1 mg/m3 500 ml Unsuitable working materials: metal, metal alloys (generation of hydIrrittation Irritation in the mucus memIrrittation Irrittation toxic to aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin Harmful to English aquatic organism, may cause long - term 142 MSDS 142 EN Copper(I) chloride MSDS-142-EN Copper(I) chloride.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Copper(I) chloride NA CuCl 7758-89-6 93 NA 2 100 g Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Danger and hazard : Irritant to the English human body. 2) Adverse human health

143 MSDS 143 EN Copper(II) chloride dihydrate MSDS-143-EN Copper(II) chloride dihydrate.pdf Operation Lab. Analysis Merck KGaA Solid Copper(II) chloride dihydrate Copper dichloride dihydrate CuCl 2*2H2O 10125-13-0 170.48 g/mol NA 1 250 g Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist Harmful if swallowed. Irritating to eyes English and skin. Very toxic to aquatic organism,

144 MSDS 144 EN Copper(II) sulfate MSDS-144-EN Copper(II) sulfate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Copper(II) sulfate NA CuSO4 7758-98-7 97.5 NA 2 500 g Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Danger and hazard : Irritant to the English human body. 2) Adverse human health

145 MSDS 145 EN Copper(II) sulfate pentahydrate MSDS-145-EN Copper(II) sulfate pentahydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Copper(II) sulfate pentahydrate NA CuSO 4*5H2O 7758-99-8 99 NA 2 500 g Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Danger and hazard : Irritant to the English human body. 2) Adverse human health 146 MSDS 146 EN Copper, Turnings MSDS-146-EN Copper, Turnings.pdf Operation Lab. Analysis Sigma - Aldrich Solid Copper Allbri natural copper Cu 7440-50-8 NA NA 1 250 g Acetylene, ammonium nitrate, bromates, chlorates, iodates, chlorin No specific No specific No specific No specific Operation Lab. Sr. Chemist not identified English

147 MSDS 147 EN Creatinine MSDS-147-EN creatinine.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Triglycerides Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 148 MSDS 148 EN darina grease RL-1 MSDS-148-EN darina grease RL-1.pdf Health hazard: High pressure injection English under the skin may cause serious 149 MSDS 149 EN DECLEAN B-801 MSDS-149-EN diclean b-801.pdf Irritant. English

150 MSDS 150 EN delo silver SAE 40 MSDS-150-EN delo silver SAE 40.pdf Avoid prolonged or repeated contact with English used motor oil. If skin contact occurs, 151 MSDS 151 EN denso hotline tape MSDS-151-EN denso hotline tape.pdf This product is not classified as English dangerous for supply under the terms of 152 MSDS 152 EN denso paste s105 MSDS-152-EN denso paste s105.pdf This product is not classified as English dangerous for supply under the terms of 153 MSDS 153 EN densyl mastic MSDS-153-EN densyl mastic.pdf This product is not classified as English dangerous for supply under the terms of

154 MSDS 154 EN Dibenzothiophene MSDS-154-EN Dibenzothiophene.pdf Operation Lab. Analysis Merck KGaA Powder Dibenzothiophene NA C12H8S 132-65-0 184.26 g/mol NA 2 25 g Strong oxidizers No specific No specific No specific No specific Toxic for aquatic organisms Operation Lab. Sr. Chemist Very toxic to aquatic organism, may English cause long-term adverse effects in the 155 MSDS 155 EN diclean BH-327 MSDS-155-EN diclean BH-327.pdf NA English

156 MSDS 156 EN diclean f-601 MSDS-156-EN diclean f-601.pdf Avoid any direct contact with the English product. Never breath dust. Change

157 MSDS 157 EN Diethyl ether GR MSDS-157-EN Diethyl ether GR.pdf Operation Lab. Analysis Merck KGaA Liquid Diethyl ether GR Ethyl ether, Ether (C2H5)2O 60-29-7 74.12 g/mol NA 10 1 L Oxidizer NA Harmful NA Dryness / cracking Extremely flammable Operation Lab. Sr. Chemist Extremely flammable. May form explosive English peroxide. Harmful if swallowed. Repeated 158 MSDS 158 EN Di-n-butyl sulfide MSDS-158-EN Di-n-butyl sulfide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Di-n-butyl sulfide n-Butyl Sulfide [CH3(CH2)3]2S 544-40-1 98 NA 2 100 mL Irritation Irritation Irritation Irritation Combustible Operation Lab. Sr. Chemist 1) danger and hazard : combustible. 2) English adverse human health hazard : If inhaled 159 MSDS 159 EN Direct Bilirubin MSDS-159-EN Direct Bilirubin.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Bilirubin Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be

160 MSDS 160 EN Disodium dihydrogen ethylenediamine tetraacetate dihydrate MSDS-160-EN Disodium dihydrogen ethylenediamine tetraacetate dihydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Disodium dihydrogen ethylenediamine tetraacetate di Ethylenediamine tetraacetic a C10H14N2O8Na2*2H2O 6381-92-6 99.5 NA 2 500 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : Irritate English to skin, eyes and cause inflammation. If 161 MSDS 161 EN DNF-7 Switchgear MSDS-161-EN DNF-7 Switchgear.pdf 1) Eyes : the flame and explosive can English cause irritation and scald. 2) Skin : the 162 MSDS 162 EN dowex C-211 MSDS-162-EN dowex C-211.pdf Caution! May cause irritation English

163 MSDS 163 EN Drierite, with indicator 238961, 4 mesh MSDS-163-EN Drierite, with indicator 238961, 4 mesh.pdf Operation Lab. Analysis Sigma - Aldrich Solid Calcium sulfate anhydrous NA NA 7778-18-9 97 NA 2 454 g Strong oxidizers, alkali metals NA Sensitization NA Sensitization Operation Lab. Sr. Chemist Toxic. Dangerous for the environment. English Cobalt chloride 7646-79-9 3 May cause cancer by inhalation. May 164 MSDS 164 EN EDTA Solution 1 M MSDS-164-EN EDTA Solution 1 M.pdf Cause irritation may cause skin English irritation. 165 MSDS 165 EN EGTA solution MSDS-165-EN EGTA solution.pdf Causes burns. English

166 MSDS 166 IN elpiji campuran MSDS-166-IN elpiji campuran.pdf Berdasarkan OSHA 29 CFR 1910.1200 Bahasa dan bahan ini dianggap berbahaya. Efek 167 MSDS 167 EN emulsion paints MSDS-167-EN emulsion paints.pdf The product is not classified as English dangerous according to the CHP 168 MSDS 168 EN energol CS68 MSDS-168-EN energol CS68.pdf This preparation is not classified as English dangerous according to Dirrective 169 MSDS 169 EN energol GR-XP 220 MSDS-169-EN energol GR-XP 220.pdf This preparation is not classified as English dangerous according to Dirrective 170 MSDS 170 EN energol GR-XP 320 MSDS-170-EN energol GR-XP 320.pdf This preparation is not classified as English dangerous according to Dirrective 171 MSDS 171 EN energol HLP 68 MSDS-171-EN energol HLP 68.pdf This preparation is not classified as English dangerous. 172 MSDS 172 IN energol HLP-HM 68 MSDS-172-IN energol HLP-HM 68.pdf

173 MSDS 173 EN energol SHF-HV 46 MSDS-173-EN energol SHF-HV 46.pdf This preparation is not classified as English dangerous according to Dirrective 174 MSDS 174 EN energol THB 32 MSDS-174-EN energol THB 32.pdf No clear data English

175 MSDS 175 EN energol THB 46 MSDS-175-EN energol THB 46.pdf This preparation is not classified as English dangerous according to Dirrective 176 MSDS 176 EN energol THB 68 MSDS-176-EN energol THB 68.pdf NA English

177 MSDS 177 EN energol THB-turbine oil MSDS-177-EN energol THB-turbine oil.pdf NA English

178 MSDS 178 EN energol WM2 MSDS-178-EN energol WM2.pdf NA English

179 MSDS 179 EN energrease AS-11 MSDS-179-EN energrease AS-11.pdf This preparation is classified as English dangerous according to Dirrective 180 MSDS 180 EN energrease LC-2 MSDS-180-EN energrease LC-2.pdf This preparation is not classified as English dangerous. 181 MSDS 181 EN energrease LS-2 MSDS-181-EN energrease LS-2.pdf This preparation is not classified as English dangerous according to Dirrective 182 MSDS 182 EN energrease LS-EP2 MSDS-182-EN energrease LS-EP2.pdf This preparation is classified as English dangerous according to Dirrective 183 MSDS 183 EN enersyn SG-XP 320 MSDS-183-EN enersyn SG-XP 320.pdf This preparation is not classified as English dangerous according to Dirrective 184 MSDS 184 EN eponic-20 under coat MSDS-184-EN eponic-20 under coat.pdf Flamable liquid, acutely toxic substance. English May cause organic solvent poisoning. 185 MSDS 185 EN epoxy HR-Comp A MSDS-185-EN epoxy HR-Comp A.pdf This preparation is classified as English dangerous according to Dirrective 186 MSDS 186 EN Eriochrome black T MSDS-186-EN Eriochrome black T.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder 3-Hydroxy-4-[(1-hydroxy-2-naphthalenyl)azo]-7-nitro- Eriochrome black T C20H12N3O7SNa 1787-61-7 80 NA 2 25 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : irritate English to skin, eyes, and cause inflamation. If 187 MSDS 187 EN ethanol MSDS-187-EN Ethanol.pdf Flammableliquid and vapor, may cause English eye irritation, may cause respiratory Ethyl alcohol, Spirit, Spirit of wine 188 MSDS 188 EN Ethanol absolute GR MSDS-188-EN Ethanol absolute GR.pdf Operation Lab. Analysis (ACS, ISO, Merck KGaA Liquid Ethanol absolute C2H5OH 64-17-5 46.07 g/mol NA 10 1000 mL Oxidizers No specific No specific No specific No specific Highly Flammable Operation Lab. Sr. Chemist Highly flammable. English

189 MSDS 189 EN ethylene (refrigerated) MSDS-189-EN ethylene (refrigerated).pdf Refrigerated liquified gas. Contact with English product may cause cold burn or frosbite. 190 MSDS 190 EN ethylene glycol MSDS-190-EN ethylene glycol.pdf Hazardous in case of ingestion. Slightly English hazardous in case of skin contact 1,2-iaminoethane, 1,2-Ethanediamine 191 MSDS 191 EN Ethylenediamine MSDS-191-EN Ethylenediamine.pdf Operation Lab. Analysis Merck KGaA Liquid Ethylenediamine H 2NCH2CH2NH2 107-15-3 60.1 g/mol NA 2 500 mL Acids, oxidizers, perchlorates Burns Sensitization Harmful Harmful Flammable Operation Lab. Sr. Chemist Flammable. Harmful in contact with skin English and if swallowed. Cause burns. May 192 MSDS 192 EN Ethylenediaminetetraacetic acid MSDS-192-EN Ethylenediaminetetraacetic acid.pdf Operation Lab. Analysis Merck KGaA Powder Ethylenediaminetetraacetic acid (Ethylenedinitrilo)tetraacetic a[CH2N(CH2COOH)2]2 60-00-4 99 NA 2 500 g Strong oxidizers Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : Irritate English to skin, eyes and cause inflammation. If 193 MSDS 193 IN Ethylenediaminetetraacetic acid - Kanto MSDS-193-IN Ethylenediaminetetraacetic acid-Kanto.pdf Kanto Chemical Co., Inc

194 MSDS 194 EN Ethylenediaminetetraacetic acid disodium magnesium salt tetrahydrate MSDS-194-EN Ethylenediaminetetraacetic acid disodium magnesium salt tetrahydrate (ETA-Na2-Mg).pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Ethylenediaminetetraacetic acid disodium magnesium NA C10H12N2O8Na2Mg*4H2O 14402-88-1 96 NA 4 25 g None Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health : may cause English (ETA-Na2-Mg) irritation of skin and eyes. If swallowed, 195 MSDS 195 EN ezy-turn-3 Valve sealant MSDS-195-EN ezy-turn-3 Valve sealant.pdf Eye; may cause irritation, Ingestion; English may cause diarrhea, Inhalation: Viscous 196 MSDS 196 EN FERROZINE IRON REAGENT SOLUTION PILLOWS MSDS-196-EN Ferrozine Iron reagent solution.pdf Causes eye burns harmful if swallowed, English inhaled or absorbed through skin may 197 MSDS 197 EN filmtech-membrane wet 70031 MSDS-197-EN filmtech-membrane wet 70031.pdf Cause eye irritation. May cause skin English irritation. May be harmful if 198 MSDS 198 EN flake NaOH MSDS-198-EN flake NaOH.pdf Danger! Corrosive, toxic, harmfull if English swallowed. Causes eye and skin burn. 199 MSDS 199 EN flammable gas mixture MSDS-199-EN flammable gas mixture.pdf This product is collorless, flammable English gas with sweet odor (due to the 200 MSDS 200 EN gasmixture MSDS-200-EN gasmixture.pdf Extremly flammable, compressed gas. English

201 MSDS 201 EN GGT MSDS-201-EN GGT.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 202 MSDS 202 EN Giemsa Stain MSDS-202-EN Giemsa_Stain.pdf Clinic Lab. Sciencelab.com, Inc. Solid Azure II NA NA 37247-10-2 20.8 NA 1 bottle/500ml Yearly NA Irritation Irritation Irritation Irritation HSE MP Clinic Potential Acute Health Effects: English Azure II eosinate 53092-85-6 79.2 Hazardous in case of ingestion. Slightly 203 MSDS 203 EN Glucose GOD PAP MSDS-203-EN Glucose GOD PAP.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 bottle/500ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 204 MSDS 204 EN Glycerol (Glycerin) MSDS-204-EN Glycerol (Glycerin).pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Glycerol 1,2,3-Propanetriol (HO)CH2Cl(OH)CH2(OH) 56-81-5 99 10 2 500 mL PVC, polystyrene No specific No specific No specific No specific Combustible Operation Lab. Sr. Chemist 1) The most important danger and English hazard : combustible. 2) Adverse human 205 MSDS 205 EN glysantin G 48-00 MSDS-205-EN glysantin G 48-00.pdf Harmfull if swallowed English

206 MSDS 206 EN golest-series MSDS-206-EN golest-series.pdf Avoid brething oil mists English

207 MSDS 207 EN Gum tragacanth, Powder MSDS-207-EN Gum tragacanth, Powder.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Tragacanth Mixture of polysaccharide (L-Arabinose, D-Xylose, D-Focuse, D-Galactose, D-Galacturonic acid) 9000-65-1 NA NA 4 25 g None No specific No specific No specific No specific Operation Lab. Sr. Chemist 1) Adverse human health hazard : As English Poison!gum tragacanth Danger! is Corrosive. permitted Liquidto be used and 208 MSDS 208 EN H2SO4 - Starborn MSDS-208-EN H2SO4-starborn.pdf Desalination Process PT. Luas Birus Utama Liquid Sulfuric acid H2SO4 7664-93-9 98 - 100 0.2 Water, potassium chlorate, potassium perchlorate, potassium permSevere tissue burn Damaging effect Burns Severe burns Leach into ground water Utilities Asrory mist cause severe burns to all body English Poison!tissue. May Danger! be fatal Corrosive. if swallowed Liquid or and MSDS 208 IN H2SO4 - Starborn MSDS-208-IN H2SO4 B.Indo.pdf Desalination Process PT. Luas Birus Utama Liquid Sulfuric acid H2SO4 7664-93-9 98 - 100 0.2 Water, potassium chlorate, potassium perchlorate, potassium permSevere tissue burn Damaging effect Burns Severe burns Leach into ground water Utilities Asrory mist cause severe burns to all body Bahasa tissue. May be fatal if swallowed or 209 MSDS 209 EN Hardtop AS - Comp. A - Marine_Protective - English (uk) - United Kingdo MSDS-209-EN Hardtop AS - Comp. A - Marine_Protective - English (uk) - United Kingdom.pdf Coatings Jotun The preparation is classified English asdangerous according to dirrective MSDS 209 IN Hardtop AS - Comp. A - Marine_Protective - Indonesian (id) - Indonesia MSDS-209-IN Hardtop AS - Comp. A - Marine_Protective - Indonesian (id) - Indonesia.pdf Coatings Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 210 MSDS 210 EN Hardtop AS_HB - Comp. B - Marine_Protective - English (uk) - United Ki MSDS-210-EN Hardtop AS_HB - Comp. B - Marine_Protective - English (uk) - United Kingdom.pdf Coatings Jotun The preparation is classified English asdangerous according to dirrective MSDS 210 IN Hardtop AS_HB - Comp. B - Marine_Protective - Indonesian (id) - Indone MSDS-210-IN Hardtop AS_HB - Comp. B - Marine_Protective - Indonesian (id) - Indonesia.pdf Coatings Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 211 MSDS 211 EN HD developer part-a MSDS-211-EN HD developer part-a.pdf The product as a whole has not been English tested. This hazard information is for 212 MSDS 212 EN HDL Cholesterol MSDS-212-EN HDL Cholesterol.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid HDL Cholesterol Aqueous Solution NA NA NA NA 1 kit/ 300 ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 213 MSDS 213 EN helium MSDS-213-EN helium.pdf Compressed gas, in high concentration English may cause asphyxiation.

214 MSDS 214 EN Hexaammonium heptamolybdate tetrahydrate MSDS-214-EN Hexaammonium heptamolybdate tetrahydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Hexaammonium heptamolybdate tetrahydrate Hexaammonium molybdate te (NH 4)6Mo7O24-4H2O 12054-85-2 99 NA 2 500 g NA Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : may English irritation to skin, eyes. If inhaled dust,

215 MSDS 215 EN Hexachloroplatinic(IV) acid hexahydrate MSDS-215-EN Hexachloroplatinic(IV) acid hexahydrate.pdf Operation Lab. Analysis Merck KGaA Solid Hexachloroplatinic(IV) acid hexahydrate Chloroplatinic acid Cl 6H2Pt*6H2O 18497-13-7 517.92 g/mol NA 4 1 g Bases Burns Burns Toxic Burns Operation Lab. Sr. Chemist Toxic if swallowed. Cause burns. May English cause sensitization by inhalation and

216 MSDS 216 EN Hexane MSDS-216-EN Hexane.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Hexane NA C6H14 110-54-3 95 500 ppm 10 500 mL PVC resin, acrylic resin, polystyrene Inflammation Inflammation Inflammation Inflammation Substance is flammable and vapor Operation Lab. Sr. Chemist 1) The most important danger and English hazard : this substance is flammable and 217 MSDS 217 EN Hydranal Coulomat AG MSDS-217-EN Hydranal Coulomat AG.pdf Operation Lab. Analysis (Reagent fo Sigma - Aldrich Liquid Methanol Methyl alcohol NA 67-56-1 >60 200ppm 22 500 mL Strong oxidizer Toxic & irritative Toxic & irritative Toxic & irritative Toxic & irritative Highly Flammable Operation Lab. Sr. Chemist Highly flammable. Toxic by inhalation, in English Imidazole NA 288-32-4 5-15 NA contact with skin and if swallowed. Toxic 218 MSDS 218 EN Hydranal Coulomat CG MSDS-218-EN Hydranal Coulomat CG.pdf Operation Lab. Analysis (Reagent fo Sigma - Aldrich Liquid Diethanolamine Hydrochloride NA NA 14426-21-2 50-60 2 22 51mLx10mL Strong oxidizer Toxic & irritative Toxic & irritative Toxic & irritative Toxic & irritative Highly Flammable Operation Lab. Sr. Chemist Highly flammable. Toxic by inhalation, in English Methanol Methyl alcohol 67-56-1 30-60 200ppm contact with skin and if swallowed. Toxic 219 MSDS 219 EN hydrochloric acid 32% MSDS-219-EN hydrochloric acid 32%.pdf Harmfull vapor, causes burn, irritating English to respiratory system. 220 MSDS 220 EN hydrochloric acid 33-40% MSDS-220-EN hydrochloric acid 33-40%.pdf Poison, danger, corrosive. Liquid and English mist cause severe burns to all body 221 MSDS 221 EN Hydrochloric acid fuming 37% GR MSDS-221-EN Hydrochloric acid fuming 37% GR.pdf Operation Lab. Analysis Merck KGaA Liquid Hydrochloric acid NA HCl 7647-01-0 37 7.5 5 1000 mL Amines, potassium permanganate, salt of oxyhalogenic acids, sem Burns Irritation Burns Burns Operation Lab. Sr. Chemist Causes burns. Irritating to respiratory English system. 222 MSDS 222 EN Hydrochloric Acid-HCl MSDS-222-EN Hydrochloric Acid-HCl.pdf Metito Liquid Poison, danger, corrosive. Liquid and English mist cause severe burns to all body MSDS 222 IN Hydrochloric Acid-HCl Ind MSDS-222-IN Hydrochloric Acid-HCl Ind.pdf Metito Liquid Poison, danger, corrosive. Liquid and Bahasa mist cause severe burns to all body 223 MSDS 223 EN Hydrochloric acid-Kanto MSDS-223-EN Hydrochloric acid-kanto.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Hydrochloric acid NA HCl 7647-01-0 35-37 7.5 6 4 kg Amines, potassium permanganate, salt of oxyhalogenic acids, sem Burns Irritation Burns Burns Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to the human body. 2) 224 MSDS 224 EN hydrogen MSDS-224-EN hydrogen.pdf Compressed gas, extremly flammable English

225 MSDS 225 EN Hydrogen peroxide MSDS-225-EN Hydrogen peroxide.pdf Operation Lab. Analysis Merck KGaA Liquid Hydrogen peroxide NA H2O2 7722-84-1 30 1 ppm 3 250 mL Alkali metals, Alkali salts, alkali hydroxides, alkali earth metals, met Damage No specific Harmful No specific Operation Lab. Sr. Chemist Harmful if swallowed. Risk of serious English damage to eyes. 226 MSDS 226 EN hydrogen-compressed MSDS-226-EN hydrogen-compressed.pdf Hydrogen is flammable, colorless and English odorless, compressed gas packaged in

227 MSDS 227 EN Hydroxynaphthol blue(40 to 50 mesh) MSDS-227-EN Hydroxynaphthol blue(40 to 50 mesh).pdf Operation Lab. Analysis Merck KGaA Solid Hydroxynaphthol blue NA C20H11N2Na3O11S3 63451-35-4 620.5 g/mol NA 16 25 g None No specific No specific No specific No specific Combustible Operation Lab. Sr. Chemist Harmful if swallowed. Risk of serious English damage to eyes. 228 MSDS 228 EN hypogear EP-85W 140 MSDS-228-EN hypogear EP-85W 140.pdf This preparation is not classified as English dangerous. 229 MSDS 229 EN hypogear EP-90 MSDS-229-EN hypogear EP-90.pdf This preparation is not classified as English dangerous. 230 MSDS 230 EN hyspin AWH-M 68 MSDS-230-EN hyspin AWH-M 68.pdf This preparation is not classified as English dangerous. MSDS 230 IN Castrol Hyspin AWH-M 68 Ina MSDS-230-IN Castrol Hyspin AWH-M 68 Ina.pdf Pelumas Hydrolik Castrol Liquid Tidak Diklasifikasikan sebagai bahan Bahasa berbahaya 231 MSDS 231 EN icon 100cs MSDS-231-EN icon 100cs.pdf Berbahaya bila terhirup. Kontak dengan English kulit mungkin dapat menyebabkan 232 MSDS 232 EN industrial gear lubricant MSDS-232-EN industrial gear lubricant.pdf May be harmfull if swallowed. May English irritate eyes, skin, digestive/intestinal 233 MSDS 233 EN IPS weld-on MSDS-233-EN IPS weld-on.pdf Effect of over exposure: iNhalation; English Severe overexposure may result in 234 MSDS 234 EN Iron standard solution (Fe-1000) MSDS-234-EN Iron standard solution (Fe-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Iron (III) Nitrate-9 Hydrate Fe(NO3)3 in HNO3 7782-61-8 Nitric acid:2.6 mg/mm3, as Iron salts: 1 mg/m3 500 ml Unsuitable working materials: metal, metal alloys (generation of hydIrrittation irritation Irritation of mucus membra Irritation Damage in aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin English

235 MSDS 235 EN Iron(III) chloride hexahydrate MSDS-235-EN Iron(III) chloride hexahydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Iron(III) chloride hexahydrate NA FeCl 3-6H2O 10025-77-1 97 NA 2 500 g None Irritation Irritation Irritation Irritation Harmful to aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to human body. 2) 236 MSDS 236 EN Jet-x foam concentrate MSDS-236-EN jet-x foam concentrate.pdf Flammable; Keep away from sources English of ignition - No smoking. 237 MSDS 237 EN KALGEN 314 MSDS-237-EN Kalgen 314.pdf harmful vapours. English

238 MSDS 238 EN kalgen 351-Boiler compound MSDS-238-EN kalgen 351-Boiler compound.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 239 MSDS 239 EN Kalgen 358 MSDS-239-EN Kalgen 358.pdf Boiler Compound PT. Kurita Indonesia Powder Phosphate Formulation NA NA NA NA 10 (TWA) Strong Acid Irritation Irritation Irritation Irritation Utilities James Lempoy Do not eat, drink or smoke at the English working place. Avoid any direct contact 240 MSDS 240 IN Karbon Dioksida MSDS-240-IN Karbon Dioksida.pdf Tyra Gas Pernafasan: Karbon dioksida Bahasa merupakan zat penyebab sesak nafas. 241 MSDS 241 EN kendex OCTG MSDS-241-EN kendex OCTG.pdf None considered hazardous English

242 MSDS 242 IN Klerat RMB MSDS-242-IN KLERAT RMB.pdf Insecticide Sygenta Solid Brodifacoum NA TBD 56073-10-0 0.005 0.002 None Slightly irritating Significant inhalation expos The active ingredient is desunlikely to cause any discomfort in normal use. Logistic Indocater Pada kondisi normal tidak akan Bahasa berbahaya, bila digunakan dan ditangani 243 MSDS 243 EN kuriflock PA-322 MSDS-243-EN kuriflock PA-322.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 244 MSDS 244 IN kuriless S-115 MSDS-244-IN kuriless S-115.pdf Do not eat, drink or smoke at the Bahasa working place. Avoid any direct 245 MSDS 245 EN Kurilex L-111 MSDS-245-EN kurilex L-111.pdf Corrosion Inhibitor PT. Kurita Indonesia Liquid Nitrite Formulation NA NA NA NA NA Strong Acid Irritation Irritation Irritation Irritation Utilities James Lempoy Do not eat, drink or smoke at the English working place. Avoid any direct contact 246 MSDS 246 EN kurinstar SP MSDS-246-EN kurinstar SP.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 247 MSDS 247 EN Kurita H-6060 MSDS-247-EN kurita H-6060.pdf Oxygen Scavenger PT. Kurita Indonesia Liquid Deoxide Amine NA NA NA NA NA None Irritation Irritation Irritation Irritation Utilities James Lempoy Do not eat, drink or smoke at the English Alcohol Amine working place. Avoid any direct contact 248 MSDS 248 EN kurita H-6060L MSDS-248-EN kurita H-6060L.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 249 MSDS 249 EN kurita P-3700 MSDS-249-EN kurita P-3700.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 250 MSDS 250 EN kurita T-7800 MSDS-250-EN kurita T-7800.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 251 MSDS 251 EN L(+)-Ascorbic acid MSDS-251-EN L(+)-Ascorbic acid.pdf Operation Lab. Analysis (ACS, ISO, Sigma - Aldrich Solid Ascorbic acid Vitamin C C6H8O6 50-81-7 NA NA 2 1000 g Strong oxidizers None None None None Operation Lab. Sr. Chemist not hazardous. English

252 MSDS 252 EN Lanthanum oxide MSDS-252-EN Lanthanum oxide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Lanthanum oxide NA La2O3 1312-81-8 98 NA 20 25 g None Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health : irritate to English eyes, if inhaled the dust, nose, throat, or 253 MSDS 253 EN LDL Cholesterol MSDS-253-EN LDL Cholesterol.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid HDL Cholesterol Aqueous Solution NA NA NA NA 1 kit/ 300 ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be

254 MSDS 254 EN Lead (II) carbonate MSDS-254-EN Lead (II) carbonate.pdf Operation Lab. Analysis Merck KGaA Solid Lead carbonate NA PbCO3 598-63-0 267.21 g/mol NA 2 250 g Strong oxidizers, strong acids and bases No specific No specific No specific No specific Very toxic to aquatic organism Operation Lab. Sr. Chemist May cause harm to the unborn child. English Danger of cumulative effects. Also 255 MSDS 255 EN MSDS-255-EN lead acid battery.pdf NA English lead acid battery 256 MSDS 256 EN Lead standard solution(Pb-1000) MSDS-256-EN Lead standard solution(Pb-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Lead (II) Nitrate Pb(NO3)2 10099-74-8 0.05 mg/m3 500 ml Unsuitable working materials: metal, metal alloys (generation of hydrogen), to be avoided: heat Irritation Irritation Irritation Hazard for drinking water Operation Lab. Sr. Chemist Irritating to eyes and skin English

257 MSDS 257 EN Lead(II) acetate trihydrate MSDS-257-EN Lead(II) acetate trihydrate.pdf Operation Lab. Analysis Merck KGaA Solid Lead(II) acetate trihydrate NA (CH 3COO)2Pb*3H2O 6080-56-4 379.34 g/mol NA 4 250 g Strong oxidizers, strong acids and bases No specific No specific No specific No specific Very toxic to aquatic organism Operation Lab. Sr. Chemist May cause harm to the unborn child. English Danger of cumulative effects. Also

258 MSDS 258 EN Lead(II) nitrate MSDS-258-EN Lead(II) nitrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Lead(II) nitrate NA Pb(NO3)2 10099-74-8 99.3 NA 2 500 g None Irritation No specific Lead poisoning Irritation Harmful to aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : toxic to the human body. 2)

259 MSDS 259 EN Lead(II) perchlorate trihydrate MSDS-259-EN Lead(II) perchlorate trihydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Lead(II) perchlorate trihydrate NA Pb(ClO 4)2*3H2O 13453-62-8 97 NA 2 500 g None Irritation No specific Lead poisoning Irritation Operation Lab. Sr. Chemist 1) The most important danger and English hazard : toxic human,oxidizable. 2) Lead dioxide, Lead oxide, brown, Lead peroxide 260 MSDS 260 EN Lead(IV) oxide MSDS-260-EN Lead(IV) oxide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Lead(IV) oxide PbO2 1309-60-0 95 NA 2 500 g Oxidizers Irritation No specific Lead poisoning Irritation Operation Lab. Sr. Chemist 1) The most important danger and English hazard : toxic to the human body. 2) 261 MSDS 261 IN Lewatit Monoplus M500 MSDS-261-IN LEWATIT MonoPlus M500.pdf Lewatit

262 MSDS 262 IN Lewatit Monoplus S100 MSDS-262-IN LEWATIT MonoPlus S100.pdf Lewatit

263 MSDS 263 EN MSDS-263-EN LGEP 2.pdf Potential to cause cancer; lead has English LGEP 2 been tested for ability to cause cancer. 264 MSDS 264 EN MSDS-264-EN lghp 2.pdf May be irritating to eyes. Prolonged or English lghp 2 frequently recurrent contact will 265 MSDS 265 EN MSDS-265-EN Limestone-CaCO3.pdf NA English limestone-CaCO3 266 MSDS 266 EN Linde Adsorbent LA MSDS-266-EN Linde Absorbent LA.pdf Repeated or prolonged exposure may English irritate eyes, skin and respiratory 267 MSDS 267 EN Linde Adsorbent LMC MSDS-267-EN Linde Absorbent LMC.pdf Contach with strong oxidizer such as English ozone, liquid oxygen, chlorine, 268 MSDS 268 EN MSDS-268-EN LMX Grease.pdf Non hazardous substance. Non English LMX Grease dangerous good. 269 MSDS 269 EN MSDS-269-EN LMX Grease2.pdf NA English LMX Grease2 270 MSDS 270 EN MSDS-270-EN low range TOC indicator ampules.pdf This product does NOT contain any English low range TOC indicator ampules OSHA listed carcinogen. This product 271 MSDS 271 EN MSDS-271-EN Lubricant oil.pdf NA English Lubricant oil 272 MSDS 272 EN MSDS-272-EN lubricant-769.pdf NA English lubricant-769 273 MSDS 273 EN m-78 MSDS-273-EN m-78.pdf This product, and concentrated English solutions of it are corricive to skin, MSDS 273 IN M-78 in Bahasa MSDS-273-IN M-78 in Bahasa.pdf Pembersih membran Metito Liquid NA Bahasa

274 MSDS 274 EN Magnaflux 7HF MSDS-274-EN Magnaflux 7HF.pdf Magnetic Particle Inspection Magnaflux Liquid TBD White mineral oil TBD 64742-47-8 60 - 100 5 None Irritation Dizziness and nausea No significant Irritation Flammable Maintenance Wisnugroho Extremely flammable aerosol. Bland oily English LPG 68476-86-8 30 NA liquid which may irritate the skin. 275 MSDS 275 EN Magnaflux WCP-2 MSDS-275-EN Magnaflux WCP-2.pdf Magnetic Particle Inspection Aid Magnaflux Liquid 2-propanone NA TBD 67-64-1 60 - 100 750 ppm None Irritation Dizziness and nausea No significant Irritation Flammable Maintenance Wisnugroho Extremely flammable aerosol. Fast English Titanium oxide 13463-67-7 10 - 30 10 evaporating vapors can reach hazardous

276 MSDS 276 EN Magnesium chloride hexahydrate MSDS-276-EN Magnesium chloride hexahydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Magnesium chloride hexahydrate NA MgCl 2*6H2O 7791-18-6 95 NA 2 500 g None No specific No specific No specific No specific Operation Lab. Sr. Chemist 1) Adverse human health : As English magnesium chloride is permitted to be 277 MSDS 277 EN Magnesium standard solution (Mg-1000) MSDS-277-EN Magnesium standard solution (Mg-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Magnesium Nitrate 6 Hydrate Mg(NO3)2 13446-18-9 nitric acid: 2.6 mg/m3, 500 ml Unsuitable working materials: metal, metal alloys (generation of hydrogen), to be avoided: heat Irritation Irritation Irritation Hazard for drinking water Operation Lab. Sr. Chemist Irritating to eyes and skin English

278 MSDS 278 EN Magnesium sulfate heptahydrate MSDS-278-EN Magnesium sulfate heptahydrate.pdf Operation Lab. Analysis Merck KGaA Solid Magnesium sulfate heptahydrate NA MgO 4S*7H2O 10034-99-8 246.48 g/mol NA 2 500 g None No specific No specific No specific No specific Operation Lab. Sr. Chemist No hazardous as specified English

279 MSDS 279 EN Manganese standard solution (Mn-1000) MSDS-279-EN Manganese standard solution (Mn-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Manganase-(II)Nitrate-6-Hydrate Mn (NO3)2 17141-63-8 nitric acid: 2.6 mg/m3, Mangan: 0.2 mg/m3 500 ml Unsuitable working materials: metal, metal alloys (generation of hydIrritation Irritation Irritation Irritation Hazard for drinking water,toxic to Operation Lab. Sr. Chemist Irritating to eyes and skin English

280 MSDS 280 IN masri RG 220 ISO VG220 MSDS-280-IN masri RG 220 ISO VG220.pdf The product and concentrated solution Bahasa of it are irritating to skin, eyes, and 281 MSDS 281 IN meditran 40-SAE MSDS-281-IN meditran 40-SAE.pdf Cairan berwarna coklat, tidak ada Bahasa pengaruh yang berarti dalam jangka 282 MSDS 282 IN meditran SC SAE 15W-40 MSDS-282-IN meditran SC SAE 15W-40.pdf NA Bahasa

283 MSDS 283 IN meditran SMX SAE 40 MSDS-283-IN meditran SMX SAE 40.pdf Cairan berwarna coklat, tidak ad Bahasa pengaruh yang berarti dalam jangka 284 MSDS 284 EN Mercury standard solution (Hg-1000) MSDS-284-EN Mercury standard solution (Hg-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Mercury (II) Nitrate-1-Hydrat Hg(NO3)2 in HNO3 7697-37-2 nitric acid:2.6, as Mercury alkyl compounds: 0.01 mg/m3, as elemental and inorganic forms: 0.025 mg/m3 100 ml Unsuitable working materials: metal, metal alloys (generation of hydBurn irritation Burns in mouth, throat, eso Burns Mechanical damage to aquatic org Operation Lab. Sr. Chemist causes burn English

285 MSDS 285 EN Mercury(II) oxide, red MSDS-285-EN Mercury(II) oxide, red.pdf Operation Lab. Analysis Merck KGaA Solid Mercury(II) oxide, red NA HgO 21908-53-2 216.59 g/mol NA 2 50 g Alcohol, nitrates, halogens, semimetallic halides, hydrazine and de Irritation Very toxic Very toxic Very toxic Very toxic to aquatic organism Operation Lab. Sr. Chemist Very toxic by inhalation, in contact with English skin and if swallowed. Danger of 286 MSDS 286 IN mesrania 2T Super MSDS-286-IN mesrania 2T Super.pdf Efek pemaparan: Tidak ada pengaruh Bahasa yang berarti, dalam jangka pendek. 287 MSDS 287 EN Methanol MSDS-287-EN Methanol 3.pdf Kurita Efek pemaparan: Tidak ada pengaruh English yang berarti, dalam jangka pendek. 288 MSDS 288 EN Methanol (2) MSDS-288-EN Methanol.pdf Functional fluids BJ Services Liquid Methyl Alcohol Methanol TBD 67-56-1 100 200 ppm Strong oxidizers Toxic Toxic Toxic Toxic Highly flammable GPF & ORF TBD Methanol burns with a colorless flame. English May form flammable vapour-air mixture.

289 MSDS 289 EN Methanol (3) MSDS-289-EN Methanol2.pdf Clinic Lab. Methanex Corp. Liquid Methyl Alcohol Methyl Hydroxide CH3OH 67-56-1 99-100 200ppm 1 bottle/1000ml Very Rare Stong oxidizers, srong acid & base, strong mineral Mild-Moderate Irritation Irritation Blindness Moderate Irritation HSE MP Clinic 1) Inhalation : can also irritate mucous English membranes, cause headaches,

290 MSDS 290 EN Methyl orange MSDS-290-EN Methyl orange solution (Methyl orange).pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Methyl orange Orange III C 14H14N3NaO3S 547-58-0 90 NA 2 25 g None Inflammation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health : irritate to English skin, eyes and may cause inflamation. If

291 MSDS 291 EN Methyl orange solution (Methyl orange) 0.1% MSDS-291-EN Methyl orange.pdf Operation Lab. Analysis Merck KGaA Liquid Methyl orange solution (Methyl orange) NA C 14H14N3NaO3S 547-58-0 90 NA 1 1000 mL None Inflammation Irritation Irritation Irritation Operation Lab. Sr. Chemist No hazardous as specified English

292 MSDS 292 EN Methyl purple solution MSDS-292-EN Methyl purple solution.pdf Operation Lab. Analysis Sigma - Aldrich Liquid Methyl purple solution NA C67H62N8Na4O14S3 1340-02-9 NA NA 1 1000 mL Strong oxidizers No specific No specific No specific No specific Operation Lab. Sr. Chemist Avoid contact and inhalation English

293 MSDS 293 EN Methyl red MSDS-293-EN Methyl red.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Methyl red 2-[[4-(Dimethy lamino)pheny l]azo]benzoic acid (CH3)2NC6H4N:NC6H4COOH 493-52-7 80 NA 2 25 g None Inflammation No specific Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health : irritate to English skin, eyes and may cause inflamation. If 3,7-Bis(dimethylamino)phenothiazine-5-ium chloride trihydrate 294 MSDS 294 EN Methylene blue MSDS-294-EN Methylene blue.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Methylene blue C16H18ClN3S*3H2O 7220-79-3 98.5 NA 2 25 g None Inflammation No specific Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health : irritate to English skin, eyes and may cause inflamation. If 295 MSDS 295 EN MSDS-295-EN metito-fze.pdf Poison, danger, vapor harmfull, may be English metito-FZE fatal or cause blindless if swallowed. 296 MSDS 296 EN Mizucrin T-301 MSDS-296-EN mizucrin t-301.pdf Corrosion Inhibitor PT. Kurita Indonesia Powder Inorganic Phosphates NA NA NA NA NA Strong Acid Irritation Irritation Irritation Irritation Utilities James Lempoy Do not eat, drink or smoke at the English working place. Avoid any direct contact 297 MSDS 297 EN mobil 6100 synergie 15W50 MSDS-297-EN mobil 6100 synergie 15W50.pdf Do not eat, drink or smoke at the English working place. Avoid any direct 298 MSDS 298 EN mobil ATF 220 MSDS-298-EN mobil ATF 220.pdf The product contains no substances English known to be hazardous to health in 299 MSDS 299 EN mobil DTE 11M MSDS-299-EN mobil DTE 11M.pdf Non hazardous substance. Non English dangerous good. Health Hazard; low 300 MSDS 300 EN mobil DTE 26 MSDS-300-EN mobil DTE 26.pdf Under normal conditions of use, this English product is not considered hazardous 301 MSDS 301 EN MSDS-301-EN mobil DTE 800 series.pdf NA English mobil DTE 800 series 302 MSDS 302 EN mobil DTE-846 MSDS-302-EN mobil DTE-846.pdf This material is not considered to be English Toksiditashazardous rendah. according Paparan to regulatory berlebih bisa MSDS 302 IN mobil DTE-846 MSDS-302-IN Mobil DTE 846_indo.pdf Minyak turbin ExxonMobil menyebabkan iritasi pada mata, kulit atau Bahasa Lowpernafasan. order of Injeksi toxicity. tekanan Excessive tinggi exposuredi bawah 303 MSDS 303 IN Mobil polyrex EM MSDS-303-IN mobil polyrex EM.pdf may result in eye, skin, or respiratory English Toksiditasirritation. High-pressurerendah. Paparan injection berlebih under bisa MSDS 303 IN Mobil Polyrex EM_indo MSDS-303-IN Mobil Polyrex EM_indo.pdf Gemuk ExxonMobil menyebabkan iritasi pada mata, kulit atau Bahasa pernafasan. Injeksi tekanan tinggi di bawah 304 MSDS 304 EN mobil rarus 427 MSDS-304-EN mobil rarus 427.pdf Under normal conditions of use, this English product is not considered hazardous 305 MSDS 305 EN mobil SHC 634 MSDS-305-EN mobil SHC 634.pdf Product assessed in accordance with English OSHA 29 CFR 1910.1200 and 306 MSDS 306 EN mobil vactra oil#1 MSDS-306-EN mobil vactra oil#1.pdf Inhale: irritating to the eyes, nose, English throat & lungs. Avoid breathing vapor 307 MSDS 307 EN MSDS-307-EN mobilarma 798.pdf This material may be considered to be English mobilarma 798 Toksiditashazardous rendah. according Paparan to regulatory berlebih bisa MSDS 307 IN MSDS-307-IN Mobil Arma 798_indo.pdf Zat yang Menghambat korosi ExxonMobil menyebabkan iritasi pada mata, kulit atau Bahasa mobilarma 798 pernafasan. Injeksi tekanan tinggi di bawah 308 MSDS 308 EN mobilgear 600xp 220 MSDS-308-EN mobilgear 600xp 220.pdf Gear Oil This material is not considered to be English Toksiditashazardous rendah. according Paparan to regulatory berlebih bisa MSDS 308 IN Mobil Gear 600XP 220_indo MSDS-308-IN Mobil Gear 600XP 220_indo.pdf Oli Persneling ExxonMobil menyebabkan iritasi pada mata, kulit atau Bahasa pernafasan. Injeksi tekanan tinggi di bawah 309 MSDS 309 EN mobilgear 630 MSDS-309-EN mobilgear 630.pdf This material is not considered to be English hazardous according to regulatory 310 MSDS 310 EN mobilgear 634 MSDS-310-EN mobilgear 634.pdf This material is not considered to be English hazardous according to regulatory 311 MSDS 311 EN mobilgrease XHP-222 MSDS-311-EN mobilgrease XHP-222.pdf Non hazardous substance. Non English Toksiditasdangerous rendah. good. HealthPaparan Hazard: berlebih Lowbisa MSDS 311 IN Mobil Grease XHP 222_indo MSDS-311-IN Mobil Grease XHP 222_indo.pdf Gemuk ExxonMobil menyebabkan iritasi pada mata, kulit atau Bahasa pernafasan. Injeksi tekanan tinggi di bawah 312 MSDS 312 EN mobilith SHC 100 MSDS-312-EN mobilith SHC 100.pdf Non hazardous substance. Non English dangerous good. Health Hazard: Low 313 MSDS 313 IN Mobilith SHC 221 MSDS-313-IN mobilith SHC 221.pdf

314 MSDS 314 EN mobilith SHC-007 MSDS-314-EN mobilith SHC-007.pdf Under normal condition of use, this English product is not considered hazardous 315 MSDS 315 EN mobilith XHP 222 MSDS-315-EN mobilith XHP 222.pdf Not classified as hazardous according English to criteria of National Occupational 316 MSDS 316 EN MOLYBDATE 3 REAGENT MSDS-316-EN molybdate 3 reagen for silica.pdf Causes eye burns harmful if inhaled. English

317 MSDS 317 EN Molybdate reagent MSDS-317-EN molybdate reagent.pdf Causes eye burns harmful if inhaled. English Causes skin irritation.

Soluble compounds: 0.5 mg/m3, metal and insoluble compounds: 10 mg/m3, 3 mg/m3 318 MSDS 318 EN Molybdenum standard solution (Mo-1000) MSDS-318-EN Molybdenum standard solution (Mo-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Ammonium molybdate 4-Hydrate [(NH4)6MO7O24.4H2O) 12054-85-2 100 ml N/A N/A N/A Irritation, nausea, vomiting Irritation Hazard for drinking water, toxic to Operation Lab. Sr. Chemist No Hazardous as specified English

319 MSDS 319 EN morlina Oil-22 MSDS-319-EN morlina Oil-22.pdf Health Hazard: Nort classified as English dangerous for supply or conveyance, 320 MSDS 320 EN motul 6100 synergie 15W50 MSDS-320-EN motul 6100 synergie 15W50.pdf The product no cantains no sustance English known to be hazardous to health in 321 MSDS 321 EN motul HD 80W-90 MSDS-321-EN motul HD 80W-90.pdf Specific hazard: none under normal English use, Physico-chemical properties: No 322 MSDS 322 EN N-1-Naphthylethylenediamine dihydrochloride MSDS-322-EN N-1-Naphthylethylenediamine dihydrochloride.pdf Operation Lab. Analysis Merck KGaA Solid N-1-Naphthylethylenediamine dihydrochloride Naphthylethylenediamine dihydrochloride C12H16Cl2N2 1465-25-4 259.18 g/mol Operation Lab. Sr. Chemist Irritating to eyes and skins. English

323 MSDS 323 EN NaOH MSDS-323-EN NaOH.pdf Alkaline source & cleaning booster PT. Luas Birus Utama Liquid Sodium hydroxide Caustic Soda NaOH 1310-73-2 NA 2 (Ceiling) Strong oxidizing agents, direct heat or sunlight Irritation Irritation Irritation Irritation Increase the pH dramatically Utilities Asrory Irritant, harmfull English

324 MSDS 324 EN natural gas MSDS-324-EN natural gas.pdf Effect of over exposure: This mixture English is flammable and classified as an

325 MSDS 325 EN n-Hexadecane MSDS-325-EN n-Hexadecane.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid n-Hexadecane Cetane CH 3(CH2)14CH3 544-76-3 98 NA 2 500 mL None Irritation Irritation Irritation Irritation Combustible Operation Lab. Sr. Chemist 1) The most important danger and English hazard :combustible. 2) Adverse human 326 MSDS 326 EN n-Hexyl alcohol MSDS-326-EN n-Hexanol alcohol.pdf Operation Lab. Analysis Merck KGaA Liquid 1-Hexanol 1-hexanol C6H14OH 111-27-3 102.18 g/mol 1000 ml Operation Lab. Sr. Chemist Harmful is swallowed. English

327 MSDS 327 EN Nickel standard solution (Ni-1000) MSDS-327-EN Nickel standard solution (Ni-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Nickel (II) Nitrate Ni(NO3)2 13138-45-9 (Nickel(II) Nitrate) Elemental: 1.5 mg/m3, Soluble inorgannic compounds: 0,1 mg/m3, Insoluble inorganic compounds: 0.2 mg/m3 500 mL Unsuitable working materials: metals Irritation Irritation Irritation Irritation toxic to aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin Harmful to English aquatic organism, may cause long - term 328 MSDS 328 EN nitra-X test N tube reagent MSDS-328-EN nitra-X test N tube reagent.pdf Causes severe burns harmfull if English inhalled for research and development 329 MSDS 329 EN Nitric acid 1.40 MSDS-329-EN Nitric acid 60% 1.40.pdf Operation Lab. Analysis Merck KGaA Liquid Nitric Acid 65 % Nitric Acid 65 % HNO3 7697-37-2 65% 2.6 2.5 L Metals burns, risk of blindness Burns of Mucus membrane Tissue damage Burns hazard for drinking water, toxic to Operation Lab. Sr. Chemist Causes severe burns. English

330 MSDS 330 EN nitrogen MSDS-330-EN nitrogen.pdf Air Liquide Simple asphyxiant - this product does English not contain oxygen and may cause 331 MSDS 331 EN nitrogen - BOC Gases MSDS-331-EN Nitrogen-BOC gases.pdf BOC Gases Nitrogen is collorles and odorless gas. English The main health hazard associated 332 MSDS 332 EN nitrogen (refrigerated) MSDS-332-EN Nitrogen (Refrigerated).pdf Air Liquide Refrigerated liquified gas. Contact with English product may cause cold burn or MSDS 332 IN nitrogen (refrigerated) MSDS-332-IN MSDS Nitrogen B.Indo.pdf AIR LIQUIDE SA Gas Nitrogen 7727-37-9 100% Gas cair didinginkan. Kontak dengan Bahasa produk dapat menyebabkan luka bakar 333 MSDS 333 EN nitrogen oksida MSDS-333-EN nitrogen oksida.pdf Nitrogen Dioksida adalah gas English bertekaanan cair yang tak beracun, tak 334 MSDS 334 EN nitrogen-ansul MSDS-334-EN nitrogen-ansul.pdf This product has not been listed as English crcinogenic by National Toxicology 335 MSDS 335 EN nitrous oxide MSDS-335-EN nitrous oxide.pdf This is clorless, odorles gas mixture. English Releases of this gas mixture may 336 MSDS 336 EN Nonflammable gas mixture MSDS-336-EN nonflammable gas mixture.pdf This is a colorless, odorless gas English mixture. Release of this gas mixture 337 MSDS 337 EN NORIT RBHG 4 MSDS-337-EN Norit RBHG 4.pdf Occupational Exposure Standard : 10 English mg/Nm3 8 h Time weight average (there 338 MSDS 338 EN norit-activated carbon MSDS-338-EN norit-activated carbon.pdf Odorless black granules or powder. English Activated carbon (especially when wet) 339 MSDS 339 EN Oil Spill Dispersant.pdf MSDS-339-EN Oil Spill Dispersant.pdf Lower toxic level is not to danger to English animal and human. No irritation to skin, 340 MSDS 340 EN Omala Oil HD-320 MSDS-340-EN Omala Oil HD-320.pdf 1) Health hazards : not classified as English dangerous for supply or conveyonce. 2) 341 MSDS 341 EN Omala Oil RL 150 MSDS-341-EN Omala Oil RL 150.pdf 1) Health hazards : not classified as English dangerous for supply or conveyonce. 2) 342 MSDS 342 EN Omeflock - 35 MSDS-342-EN Omeflock-35.pdf Water treatment chemical Omega Chemical Powder Not specified in the original MSDS NA NA NA NA NA Stable None None None None NA Logistic Tugu - Willy Material & product are not completely English harmless 343 MSDS 343 EN Omeflock Activator MSDS-343-EN OMEFLOCK ACTIVATOR.pdf Water treatment chemical Omega Chemical Powder Not specified in the original MSDS NA NA NA NA NA Stable Mild irritating None None Mild irritating NA Logistic Tugu - Willy Effect of over exposure : May cause eye English or skin irritation 344 MSDS 344 EN Omefoam - 10 High Grade MSDS-344-EN OMEFOAM-10 HIGH GRADE.pdf Water treatment chemical Omega Chemical Liquid Not specified in the original MSDS NA NA NA NA NA Stable Mild irritating None None None NA Logistic Tugu - Willy Eyes : Mildly eye irritant. Skin : No English irritating to skin 345 MSDS 345 EN Omegtant MSDS-345-EN Omegtant.pdf Water treatment chemical Omega Chemical Powder Chlorine Chlorine tablet 7782-50-5 NA 0.5 ppm (TWA), 1 ppm (STEL) NA Slightly irritating Slightly irritating No significant Slightly irritating NA Logistic Tugu - Willy Harmfull if swallowed. It has easy to English vaporize when it has dissolved and put 346 MSDS 346 EN Oxalic acid anhydrous MSDS-346-EN Oxalic acid anhydrous.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal COOH:COOH 144-62-7 95% 1 500 g Oxidizers Irritation Nausea, vomiting Irritation toxic to aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : harmful to humans. 2) Adverse 347 MSDS 347 EN oxygen MSDS-347-EN Oxygen.pdf Compressed gas. Oxidant. Strongly English supports combustion. May react violently 348 MSDS 348 EN Oxygen-air liquide MSDS-348-EN Oxygen-air liquide.pdf Danger! Strong oxidizer. High pressure English gas. Contact with other material may 349 MSDS 349 IN Oxygen-BOC Gases MSDS-349-IN Oxygen-BOC gases.pdf

350 MSDS 350 EN Oxynon M-201 MSDS-350-EN Oxynon M-201.pdf Corrosion Inhibitor & pH control PT. Kurita Indonesia Liquid Filming Amine NA NA NA NA 8 (TWA) Acid & Oxidizer Irritation Irritation Irritation Irritation Utilities James Lempoy Do not eat, drink or smoke at the English working place. Avoid any direct contact 351 MSDS 351 EN Paint Color RAL 7032 MSDS-351-EN Paint color RAL 7032.pdf 1) Eyes : liquid or vapor can cause English irritation. 2) Skin : repeated or prolong 352 MSDS 352 EN paper machine oil MSDS-352-EN paper machine oil.pdf May be harmfull if swallowed. May English irritate to eyes, skin, 353 MSDS 353 EN p-Dimethylaminobenzylidene rhodanine MSDS-353-EN p-Dimethylaminobenzylidene rhodanine.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder p-Dimethylaminobenzylidene rhodanine 5-(4-Dimethylaminobenzylidene )-2-thioxo-4-thiazolidinone 536-17-4 80% N/A 25 g Light,heat, strong oxidizers Irritation nausea, vomiting, abdominal pain Operation Lab. Sr. Chemist 1) Adverse human health : Irritate to English skin, eyes and cause inflamation. If 354 MSDS 354 EN pegasus miticide MSDS-354-EN pegasus miticide.pdf Acute: This product is moderatelly English hazardous (WHO Hazard Class II). 355 MSDS 355 EN penguard primer-comp A MSDS-355-EN penguard primer-comp A.pdf The preparation is classified English asdangerous according to dirrective 356 MSDS 356 EN penguard primer-comp B MSDS-356-EN penguard primer-comp B.pdf The preparation is classified English asdangerous according to dirrective 357 MSDS 357 EN Peptone MSDS-357-EN Peptone.pdf Operation Lab. Analysis Sigma - Aldrich Solid peptone 73049-73-7 N/A N/A 500 g Strong oxidizing agents Irritation Irritation harmful Irritation N/A Operation Lab. Sr. Chemist No hazardous as specified English

358 MSDS 358 EN Perchloric acid, 70% MSDS-358-EN Perchloric acid, 70%.pdf Operation Lab. Analysis Merck KGaA Liquid Perchloric acid, 70% Perchloric acid, 70% HCLO4 7601-90-3 70-72% N/A 1000 mL reducing agents, metals, light metals, rubber Burns, risk of blindness Burns of mucus membrane, pulmonary edema Burns Harmful to aquatic organisms Operation Lab. Sr. Chemist Heating may cause an explosion. English Contact with combustible material may 359 MSDS 359 EN permaTreat PC-191 MSDS-359-EN permaTreat PC-191.pdf May cause irritation with prolonged English contact. Do not get in eye, on skin, on 360 MSDS 360 EN Avtur MSDS-360-EN avtur-msds_Pertamina.pdf Produk ini tidak megandung bahan- English bahan berbahaya bagi kesehatan. Efek 361 MSDS 361 EN Phenol MSDS-361-EN Phenol.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal phenol phenol C6H5OH 108-95-2 99 19 500 g oxidizing substance Irritation vomiting, abdominal pain inflammation Corrosive, harmful to aquatic orga Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to the human body. 2) 362 MSDS 362 EN Phenolphthalin MSDS-362-EN Phenolphthalin.pdf Operation Lab. Analysis Merck KGaA Solid phenolphthaelein C20H14O4 77-09-8 318.33 g/mol N/A 25 g N/A N/A N/A N/A N/A Operation Lab. Sr. Chemist No hazardous as specified English

363 MSDS 363 EN Phosphoric acid MSDS-363-EN Phosphoric acid.pdf Operation Lab. Analysis Merck KGaA Liquid ortho-Phosporic acid ortho-Phosporic acid 7764-38-2 85% Short term: 2 mg/m3, STEL:3 mg/m3 2,5 L iron/iron containing compounds, steel, aluminium burns, conjunctivities irritation burns, strong pain burns harmful to aquatic organisms Operation Lab. Sr. Chemist Causes burns. English

364 MSDS 364 EN Pix MV Switchgear MSDS-364-EN PiX MV Switchgear.pdf 1) Eyes : the flame and explosive can English cause irritation and scald. 2) Skin : the 365 MSDS 365 EN PIX-M Vacuum Contactor Panel MSDS-365-EN PiX-M Vacuum contactor panel.pdf 1) Eyes : the flame and explosive can English cause irritation and scald. 2) Skin : the 366 MSDS 366 EN pkw MSDS-366-EN pkw.pdf This preparation is not classified as English dangerous according to dirrective 367 MSDS 367 EN plasmet ZF MSDS-367-EN plasmet ZF.pdf When using this product safety English precautions should be observed. Avoid 368 MSDS 368 EN plasmet ZF activator MSDS-368-EN plasmet ZF activator.pdf Specific hazard: Harmfull Xn, Physical English hazard: Flammable, harmfullby 369 MSDS 369 EN plasmet ZF Base MSDS-369-EN plasmet ZF Base.pdf Specific hazard: Harmfull Xn, Physical English hazard: Flammable, harmfullby 370 MSDS 370 EN Polifilm KS3 MSDS-370-EN Polifilm KS3.pdf not classified as dangerous substances English under EU directive 88/379/EEC. 371 MSDS 371 EN MSDS-371-EN polycrin R-213.pdf Do not eat, drink or smoke at the English polycrin R-213 working place. Avoid any direct 372 MSDS 372 EN MSDS-372-EN polyol ester.pdf This material has no known hazard English polyol ester under applicable laws. The product 373 MSDS 373 EN PORPHYRIN 1 REAGENT MSDS-373-EN porphyrin 1 reagen.pdf May cause eye and respiratory tract English iritation 374 MSDS 374 EN PORPHYRIN 2 REAGENT MSDS-374-EN porphyrin 2 reagen.pdf May cause eye and respiratory tract English iritation may cause allergic respiratory 375 MSDS 375 EN Potassium chloride MSDS-375-EN Potassium chloride.pdf Operation Lab. Analysis Merck KGaA Solid KCl 7447-40-47 74.55 g/mol 10 mg/m3 500 g N/A Irritation N/A Nausea, vomiitng N/A N/A Operation Lab. Sr. Chemist No hazardous as specified English

376 MSDS 376 EN Potassium chromate MSDS-376-EN Potassium chromate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Potassium chromate K2CrO4 7789-00-6 98.5 0.05 500g Light, heat, organic subsytances, reducing substances N/A inflammation Nausea, vomiting Dermatitis/ulcer N/A Operation Lab. Sr. Chemist 1) The most important danger and English hazard : toxic to humans, combustible. 377 MSDS 377 EN Potassium cyanide GR MSDS-377-EN Potassium cyanide GR.pdf Operation Lab. Analysis Merck KGaA Solid potassium cyanide potassium cyanide KCN 151-50-8 65.12 g/mol STEL: 5 mg/m3 250 g strong oxidizing agents, sensitive with moisture,fluorine, magnesiumirritation Irritation respiratory paralysis, letha Danger of skin absorption toxic to aquatic organisms Operation Lab. Sr. Chemist Very toxic by inhalation, in contact with English skin and if swallowed. Contact with acids 378 MSDS 378 EN Potassium dihydrogenphosphate MSDS-378-EN Potassium dihydrogenphosphate.pdf Operation Lab. Analysis Merck KGaA Solid Potassium biphospate KH2PO4 7778-77-0 136.09 g/mol N/A 500 g N/A Irritation N/A Nausea, vomiitng N/A May contribute to the eutrophicatioOperation Lab. Sr. Chemist No hazardous as specified English

379 MSDS 379 EN Potassium hexacyanoferrate(III) MSDS-379-EN Potassium hexacyanoferrate(III).pdf Potassium hexacyanoferrate(III) Merck KGaA Solid Potassium hexacyanoferrate(III) Potassium hexacyanoferrate( K3(Fe(CN)6) 13746-66-2 329.26 g/mol N/A 250 g oxiziding agents, fluorine, ammonia, nitrates, hydrogen halide, acidslight irritation slight irritation slight irritation Operation Lab. Sr. Chemist No hazardous as specified English

380 MSDS 380 EN Potassium hydrogen phthalate MSDS-380-EN potassium hydrogen phatalate.pdf Operation Lab. Analysis Merck KGaA Solid Potassium hydrogen phtalate C8H5KO4 877-24-7 204.22 g/mol N/A 250g Strong heating Irrittation N/A N/A Irritation Combustible Operation Lab. Sr. Chemist No hazardous as specified English

381 MSDS 381 EN MSDS-381-EN potassium hydroxide.pdf Clinic Lab. Sciencelab.com, Inc. Liquid Potassium Hydroxide NA KOH 1310-58-3 10 2 (STEL) 1 bottle/100ml Yearly Acids Irritation Irritation Irritation Irritation HSE MP Clinic 1) Potential Acute Health Effects: Very English potassium hydroxide Water H2O 7732-18-5 90 - hazardous in case of skin contact 382 MSDS 382 EN MSDS-382-EN potassium hydroxide solutions 10-55%.pdf Danger! Corrosive, water reactive. English potassium hydroxide solutions 10-55% Harmfullif swallowed. Causes severe 383 MSDS 383 EN Potassium hydroxide, Pellets MSDS-383-EN Potassium hydroxide, Pellets.pdf Operation Lab. Analysis Merck KGaA Solid Potash Caustic KOH 1310-58-3 56.11 g/mol STEL: C 2 mg/m3 500 g Metals, plastics, glass, animal/vegetable tissues Burns Burns of Mucous membran burns in mouth, throat Burns Harmful to aquatic organisms Operation Lab. Sr. Chemist Harmful if swallowed. Causes severe English burns. 384 MSDS 384 EN Potassium iodide MSDS-384-EN Potassium iodide.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder KI 7681-11-0 99 0.1 ppm 500 g light, heat Irritation N/A N/A N/A N/A Operation Lab. Sr. Chemist 1) Adverse human health : Weak toxicity English to humans. 2) Physical and chemical 385 MSDS 385 EN Potassium nitrate MSDS-385-EN Potassium nitrate.pdf Operation Lab. Analysis Merck KGaA Solid Nitric acid potassium salt KNO3 7757-79-1 101.11 g/mol N/A 500 g Metals, phosphides,phosphorud slight irritation N/A Nausea, vomiting N/A N/A Operation Lab. Sr. Chemist Contact with combustible material may English cause fire. 386 MSDS 386 EN Potassium nitrit MSDS-386-EN Potassium nitrit.pdf Operation Lab. Analysis Merck KGaA Powder Potassium nitrite KNO2 7758-9-9 85 N/A 500 g fine powder of organic substances/metals, irritation disorder of red blood cels airritaation toxic to aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : this substance has oxidizibility 387 MSDS 387 EN Potassium permanganate MSDS-387-EN Potassium permanganate.pdf Operation Lab. Analysis Merck KGaA Solid Permanganic acid potassium salt KMnO4 7722-64-7 158.04g/mol N/A 250 g Acids, strong reducing agents, oxidizable substances Corneal Clouding irritation burns in mouth, GI tract, Burns combustible, adverse effect to aqu Operation Lab. Sr. Chemist Contact with combustible material may English cause fire. Harmful if swallowed. Very 388 MSDS 388 EN Potassium sodium (+)-tartrate tetrahydrate MSDS-388-EN Potassium sodium (+)-tartrate tetrahydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Potassium sodium (+)-tartrate tetrahydrate KNaC4H4O6 6381-59-5 99 N/A 500 g Metallic salt, mineral acids, strong oxidizing agents Irritation irritation Nausea, vomiting irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health : may irritate to English skin, eyes. If inhaled dust, nose, throat, 389 MSDS 389 EN Potassium standard solution (K-1000) MSDS-389-EN Potassium standard solution (K-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Potassium Nitrate KNO3 7757-79-1 N/A 500 mL Unsuitable working materials: metal, metal alloys (generation of hydirritation irritation irritation irritation Hazard for drinking water Operation Lab. Sr. Chemist Irritating to eyes and skin English

390 MSDS 390 EN Potassium sulfate MSDS-390-EN Potassium sulfate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal K2S04 7778-80-5 98.5% 0.5 mg/m3 500 g Light, heats, react with oxidizing substances Irritation N/A Hyperkalemia Irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health : a large dose English swallow may cause nausea 391 MSDS 391 EN Powder buffer solution, pH 10.01 for 500mL, 5pcs./pak MSDS-391-EN Powder buffer solution, pH 10.01 for 500mL.pdf Operation Lab. Analysis DKK-TOA-Corporation Powder Sodium hydrogencarbonate+ Sodium carbonate NaHCO3, Na2CO3 144-5-8 44 N/A 5 pcs/pack N/A N/A N/A N/A N/A Operation Lab. Sr. Chemist No hazardous as specified English 392 MSDS 392 EN Powder buffer solution, pH 4,01 for 500mL, 5pcs./pak MSDS-392-EN Powder buffer solution, pH 4,01 for 500ml.pdf Operation Lab. Analysis DKK-TOA-Corporation Powder Potassium hydrogen phtalate KH8C8H4O4 877-24-7 99.5 N/A 5 pcs/pack N/A Irritation irritation Irritation irritation Flame resistant Operation Lab. Sr. Chemist May cause eye and skin irritation. English

393 MSDS 393 EN Powder buffer solution, pH 6.86 for 500mL, 5pcs./pak MSDS-393-EN Powder buffer solution, pH 6.86 for 500mL.pdf Operation Lab. Analysis DKK-TOA-Corporation Powder Potassium dihydrogenphtalat KH2PO4, Na2HPO4 7778-77-0 49 N/A 5 pcs/pack N/A Irritation N/A N/A N/A N/A Operation Lab. Sr. Chemist No hazardous as specified English

394 MSDS 394 EN Prot 88 R MSDS-394-EN Prot 88IR.pdf 1) For man : frequent and/or prolonged English contact may give rise to skin irritation 395 MSDS 395 EN MSDS-395-EN protector series ATF TQ-D III.pdf This preparation is not classified as English protector series ATF TQ-D III dangerous. 396 MSDS 396 EN MSDS-396-EN protoKlenz GT.pdf Labelling per Ecdirective: IRRITANT English protoKlenz GT information concerning particular 397 MSDS 397 EN MSDS-397-EN Propane.pdf Propane 398 MSDS 398 EN p-Xylene MSDS-398-EN p-Xylene.pdf Operation Lab. Analysis P-xylene for sysnthesis Liquid p-Xylene C8H10 106-42-3 106.17 STEL: 651, TWA:434 1000 ml light metals, rubber, plastics irritation oedemas in respiratory tract irritation flammable, toxic to aquatic organis Operation Lab. Sr. Chemist Flammable. Harmful by inhalation and in English contact with skin. Irritating to skin. 399 MSDS 399 EN Pyridine MSDS-399-EN Pyridine.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Liquid Pyridine Pyridine C5H5N 110-86-1 99 (TLV-TWA): 5 ppm, 16 mg/m3 500 ml Oxiziding substances irritation headache, dizzines,vomiting Irritation flammable, toxic to aquatic organis Operation Lab. Sr. Chemist 1) The most important danger and English hazard : flammable. 2) Adverse human 400 MSDS 400 EN Pyrogallol MSDS-400-EN Pyrogallol.pdf Operation Lab. Analysis Merck KGaA Solid pyrogallol Pyrogallic acid 1,2,3- Trihydroxybenzene C6H6O3 87-66-1 126.11 g/mpl N/A 50 g bases, ammonium hydroxide, antipyrine, camphor, phenol, iodine, Irritation irritation, coughing vomiting, diarrhoea Irritation Combustible,long term adverse eff Operation Lab. Sr. Chemist Harmful by inhalation, in contact with English skin and if swallowed. Harmful to aquatic 401 MSDS 401 EN R404A MSDS-401-EN R404A-Co2 chiller.pdf In high concentrations may cause English asphyxiation. Liquid gas. Not classified 402 MSDS 402 EN MSDS-402-EN renolin t 32.pdf During use, these oil are not English renolin t 32 considered to be hazardous under 403 MSDS 403 EN Resist 78/86 - Comp. B MSDS-403-EN Resist 78_86 - Comp. B.pdf TBD Jotun Solid Zinc NA Zn 7440-66-6 50 - 100 5 None TBD TBD TBD TBD Highly flammable GPF & ORF TBD The product is classified as dangerous English according to Directive 1999/45/EC and 404 MSDS 404 EN MSDS-404-EN rored HD A 90.pdf Efek pemaparan: Tidak ada pengaruh English rored HD A 90 yang berarti kontak lama dan berulang 405 MSDS 405 EN MSDS-405-EN rored hd a sae 140.pdf Efek pemaparan: Tidak ada pengaruh English rored hd a sae 140 yang berarti kontak lama dan berulang 406 MSDS 406 EN MSDS-406-EN rored mtf 80w-90 gl 4.pdf Efek pemaparan: Tidak ada pengaruh English rored mtf 80w-90 gl 4 yang berarti kontak lama dan berulang 407 MSDS 407 EN MSDS-407-EN roto glide.pdf This prodcut consist of highly refined English roto glide base oil with additives. Including 408 MSDS 408 EN MSDS-408-EN roto injectfluid.pdf EC Classification: Not classified as English roto injectfluid Dangerous under EC criteria. Human 409 MSDS 409 EN MSDS-409-EN roto z.pdf EC Classification: Not classified as English roto z Dangerous under EC criteria. Human 410 MSDS 410 EN rustbond part a MSDS-410-EN rustbond part a.pdf Warning! May cause allergic skin English reactions. May cause eyes irritation. 411 MSDS 411 EN rustbond part b MSDS-411-EN rustbond part b.pdf May cause diarrhea if swallowed. May English cause severe skin and eye irritation or 412 MSDS 412 EN S 322 MSDS-412-EN S322.pdf Scale Inhibitor, Desalting Chemical PT. Luas Birus Utama Liquid Polymaleic acid NA NA NA NA NA Not specified in the original MSDS Not specified Not specified Not specified irritation NA Utilities Asrory Human health effects : Irritating to eyes. English Environmental effects : On the basis of MSDS 412 IN S 322 MSDS-412-IN S 322 B.Indo.pdf Scale Inhibitor, Desalting Chemical PT. Luas Birus Utama Liquid Polymaleic acid NA NA NA NA NA Not specified in the original MSDS Not specified Not specified Not specified irritation NA Utilities Asrory Human health effects : Irritating to eyes. Bahasa Environmental effects : On the basis of 413 MSDS 413 EN S-19P MSDS-413-EN S19P.pdf Phosphate Injection Package PT. Luas Birus Utama Powder Disodium phosphate NA NA NA NA NA Aluminum, mild steel, extreme temperature Irritation None None None NA Utilities Asrory Human health effects : Irritating to eyes. English Trisodium phosphate Environmental effects : On the basis of MSDS 413 IN S-19P MSDS-413-IN S 19P B.Indo.pdf Phosphate Injection Package PT. Luas Birus Utama Powder Disodium phosphate NA NA NA NA NA Aluminum, mild steel, extreme temperature Irritation None None None NA Utilities Asrory Human health effects : Irritating to eyes. Bahasa Trisodium phosphate Environmental effects : On the basis of 414 MSDS 414 EN S-316 Solvent for oil meter, or equivalent MSDS-414-EN S-316 Solvent for oil meter, or equivalent.pdf Operation Lab. Analysis Daikin Liquid chlorotrifluroethylen dimer Cl(CF2CFCl)2Cl 9002-83-9 HF (TLV as F: 3 ppm), COF2 ( TLV: 2ppm, STEL: 5ppm) 1 kG Aluminium, magnesium, sodium, potassium, amines, and fluorine Irritation irritation irritation irritation N/A Operation Lab. Sr. Chemist Harmful if thermal decomposition English products are inhaled. 415 MSDS 415 EN S-48 MSDS-415-EN S48.pdf Condensate Chemical PT. Luas Birus Utama Liquid Morpholine NA TBD 110-91-8 5 - 15 NA liquid bleach, oxidizing agents, reducing agents, amines, mercapta Irritation Harmful Not likely route of entry irritation NA Utilities Asrory HUMAN HEALTH HAZARDS : Corrosive English Cyclo hexylamine NA 108-91-8 15 - 35 to skin , Corrosive to eyes. Vapors, MSDS 415 IN S-48 Ind MSDS-415-IN S48 msds1 _B.Indo.pdf Condensate Chemical PT. Luas Birus Utama Liquid Morpholine NA TBD 110-91-8 5 - 15 NA liquid bleach, oxidizing agents, reducing agents, amines, mercapta Irritation Harmful Not likely route of entry irritation NA Utilities Asrory HUMAN HEALTH HAZARDS : Corrosive Bahasa Cyclo hexylamine NA 108-91-8 15 - 35 to skin , Corrosive to eyes. Vapors, 416 MSDS 416 EN S-580 MSDS-416-EN S- 580.pdf Anti Foam PT. Luas Birus Utama Liquid Propylene oxide block copolymer NA NA NA NA NA Strong acid, strong oxidizing agent Irritation Light irritation Light irritation Light irritation NA Utilities Asrory Swallowed : Material is harmful if English swallowed. Eye : Material can cause the MSDS 416 IN S-580 MSDS-416-IN S 580 B.Indo.pdf Anti Foam PT. Luas Birus Utama Liquid Propylene oxide block copolymer NA NA NA NA NA Strong acid, strong oxidizing agent Irritation Light irritation Light irritation Light irritation NA Utilities Asrory Swallowed : Material is harmful if Bahasa swallowed. Eye : Material can cause the 417 MSDS 417 EN sag 7133 MSDS-417-EN sag 7133.pdf N/A English

418 MSDS 418 EN Salicylaldehyde MSDS-418-EN Salicylaldehyde.pdf Operation Lab. Analysis Merck KGaA Liquid 2-Hydroxybenzaldehyde HOC6H4CHO 90-02-8 98 5 ppm 250 9r To be avoided: fluorine, air, strong acids, strong bases Irritation irritation N/A Irritation toxic to aquatic organisms Operation Lab. Sr. Chemist Harmful if swallowed English

419 MSDS 419 EN Sealed Lead Battery Cyclon,Genesis,SBS MSDS-419-EN Sealed lead Battery.pdf Special fire fighting procedures : Cool English battery exterior to prevent rupture. Acid 420 MSDS 420 EN Sealed Lead Battery Powersafe VM MSDS-420-EN Sealed lead Battery Powersafe VM.pdf Special fire fighting procedures : Cool English battery exterior to prevent rupture. Acid 421 MSDS 421 IN MSDS-421-IN sebana p-22 iso vg22.pdf Tidak ada pengaruh yang berarti. Bahasa sebana p-22 iso vg22 422 MSDS 422 EN Selenium standard solution (Se-1000) MSDS-422-EN Selenium standard solution (Se-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Selenious acid SeO2 7783-00-8 (selenious acid) 0.2 mg/m3 (NOASH) 100 mL Unsuitable working materials: metal, metal alloys (generation of hydIrritation Irritation Irritation Irritation Hazard for drinking water, toxic to Operation Lab. Sr. Chemist Irritating to eyes and skin English

423 MSDS 423 EN Selenium, Powder MSDS-423-EN Selenium, Powder.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Selenium Se 7782-49-2 99 0.2 mg/m3 25g None Irritation irritation abdominal pain, vomiting, d eczema, yellow colour skin None Operation Lab. Sr. Chemist 1) The most important danger and English hazard : toxic to the human body. 2) 424 MSDS 424 EN shell abida grease HDX-2 MSDS-424-EN shell abida grease HDX-2.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 425 MSDS 425 EN Shell alvania grease EP (LF)1 MSDS-425-EN Shell alvania grease EP (LF)1.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 426 MSDS 426 EN Shell alvania grease EP (LF)2 MSDS-426-EN Shell alvania grease EP (LF)2.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 427 MSDS 427 EN Shell alvania grease RL 2 MSDS-427-EN Shell alvania grease RL 2.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 428 MSDS 428 EN Shell alvania grease RL 3 MSDS-428-EN Shell alvania grease RL 3.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 429 MSDS 429 EN shell alvania rl MSDS-429-EN shell alvania rl.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 430 MSDS 430 EN Shell Asphalt Component - Antistrip 023 MSDS-430-EN Shell Asphalt Component - Antistrip 023.pdf Hot Mix Equilon Enterprises LLC Liquid Aliphatic Polyamine Amine NA NA 100 NA 3000 Drum Uncertain Strong acid and Oxidizing Agents Corrosive Corrosive Corrosive Corrosive and Toxic Corrosive Nana S 1) Eye contact: based on English manufacturer's product testing, product 431 MSDS 431 EN shell diala b MSDS-431-EN shell diala b.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 432 MSDS 432 EN shell HD premium n Antifreezer MSDS-432-EN shell HD premium n Antifreezer.pdf Human health hazards : harmful if English swallowed. Ingestion may cause central 433 MSDS 433 EN shell morlina oil T MSDS-433-EN shell morlina oil T.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 434 MSDS 434 EN shell rimula c oil MSDS-434-EN shell rimula c oil.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 435 MSDS 435 EN shell rimula dd MSDS-435-EN shell rimula dd.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 436 MSDS 436 EN shell spirax oil g MSDS-436-EN shell spirax oil g.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 437 MSDS 437 EN shell tellus oil t32 MSDS-437-EN shell tellus oil t32.pdf Health hazards : high-pressure injection English under the skin may cause serious 438 MSDS 438 EN Shell turbo oil T46 MSDS-438-EN Shell turbo oil T46.pdf 1) Human health hazards : no specific English hazards under normal use conditions. 439 MSDS 439 EN MSDS-439-EN shell vitrea oils.pdf N/A English shell vitrea oils 440 MSDS 440 EN MSDS-440-EN sigma thinner 21-06.pdf Flammable. Harmful by inhalation and in English sigma thinner 21-06 contact with skin. Irritating to skin. 441 MSDS 441 EN sigmadur 520 MSDS-441-EN sigmadur 520.pdf Flammable. harmful by inhalation and in English contact with skin. Irritating to skin. 442 MSDS 442 EN MSDS-442-EN sikafloor 156.pdf Irritant, harmful. English sikafloor 156 443 MSDS 443 IN Sikafloor 161 HC MSDS-443-IN Sikafloor 161 HC.pdf

444 MSDS 444 IN Sikafloor 261 HD MSDS-444-IN Sikafloor 261 HD.pdf

445 MSDS 445 EN sikafloor 261 part A MSDS-445-EN sikafloor 261 part A.pdf The product may lead to skin irritation English (Dermatosis). 446 MSDS 446 IN Sikafloor 81 Epochem ID MSDS-446-IN Sikafloor 81 EpoCem ID.pdf

447 MSDS 447 EN sikafloor-156 Comp B MSDS-447-EN sikafloor-156 Comp B.pdf Harmful by inhalation, in contact with English skin and if swallowed. Causes burns. 448 MSDS 448 EN Silica gel, Blue, big granule MSDS-448-EN Silica gel, Blue, big granule.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Silicon dioxide SiO2.nH2O 7631-86-9 0.02 mg/m3 (as cobalt), 10 mg/m3 as Silicone dioxide 500 g Oxidizing substances irritation irritation N/A irritation toxic to aquatic organisms Operation Lab. Sr. Chemist 1) Adverse human health hazards may English irritate to skin, eyes. If inhaled dust, 449 MSDS 449 EN Silica gel, Blue, middle granule MSDS-449-EN Silica gel, Blue, middle granule.pdf Operation Lab. Analysis Merck KGaA Solid Silicon dioxide amorphous Blue gel SiO2.nH2O 7631-86-9 0.02 mg/m3 (as cobalt), 10 mg/m3 as Silicone dioxide 500 g Oxidizing substances irritation irritation, coughing, dyspnedamage of lungs Sensitization Operation Lab. Sr. Chemist May cause cancer by inhalation. English

450 MSDS 450 EN MSDS-450-EN siliporite.pdf N/A English siliporite 451 MSDS 451 EN Silver nitrate MSDS-451-EN Silver nitrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Silver nitrate AgNO3 7761-88-8 99.7 0.01 (mg/m3) as silver 500 g sunlight, heat, and combistible materials Inflammation Irritation Irritation, vomiting, and Sto Black colour Harmful to Aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : this substance has oxidizibility 452 MSDS 452 EN Silver standard solution (Ag-1000) MSDS-452-EN Silver standard solution (Ag-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Silver nitrate AgNO3 in HNO3 7761-88-8 Metal, dust and Fume: 0.1 mg/m3, soluble compounds a Ag: 0.01 mg/m3 100 mL Unsuitable working materials: metal, metal alloys (generation of hydIrritation Coughing and dyspnea Irritation of mucous membr irritation toxic to aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin English

453 MSDS 453 EN Silver(I) perchlorate MSDS-453-EN Silver(I) perchlorate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Silver(I) perchlorate AgClO4 7783-93-9 99 0.01 (mg/m3) as silver 25 g sunlight, heat, and combistible materials Irritation to conjunctiva and inflammation Irritation, vomiting, and Sto Irritation Harmful to Aquatic organisms Operation Lab. Sr. Chemist 1) The most important danger and English hazard : this substance has oxidizibility 454 MSDS 454 EN Sinto K 4S MSDS-454-EN Sinto K 4S.pdf It can cause skin and eye irritation English

455 MSDS 455 EN skf grease lgep-2 MSDS-455-EN skf grease lgep-2.pdf 1) Inhalation : if product is heated or English mists are formed, inhalation may cause 456 MSDS 456 EN Sodium acetate MSDS-456-EN Sodium acetate.pdf Operation Lab. Analysis Merck KGaA Powder Sodium acetat anhydrous Sodium acetat anhydrous CH3COONa 127-09-03 82.03 g/mol N/A 250 g None irritation irritation GI Complains irritation N/A Operation Lab. Sr. Chemist No hazardous as specified English

457 MSDS 457 EN Sodium acetate trihydrate MSDS-457-EN Sodium acetate trihydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder sodium acetat trihydrate anhydrous sodium acetat trihydrate anhy CH3COONa.3H2O 6131-90-4 98.5 N/A 500 g Light,heat irritation irritation N/A N/A N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards: as English sodium acetate is permitted to be used 458 MSDS 458 EN Sodium arsenite MSDS-458-EN Sodium arsenite.pdf Operation Lab. Analysis Wako Pure Chemical Industries Solid Sodium Arsenite Sodium arsenic acid NaSO2 7784-46-5 MW:129.9 OSHA: 0.5 mg/m3, ACGHI: 0.01 mg/m3 500 g Oxiziders acid irritation irritation Toxic cause cancer Irritation N/A Operation Lab. Sr. Chemist Toxic by inhalation, in contact with skin English and if swallowed. May cause cancer. 459 MSDS 459 EN Sodium bisulfate MSDS-459-EN Sodium bisulfate.pdf Operation Lab. Analysis Sigma Aldrich Powder sodium hydrogen sulfate anhydrous Nitrate cake, sodium bisulfate NaHSO4 7681-38-1 Mw:120.06 N/A 250 g Strong bases, strong oxidizing agents irritation irritation N/A Irritation N/A Operation Lab. Sr. Chemist Irritant. Risk of serious damage to eyes. English

460 MSDS 460 EN sodium bisulfite MSDS-460-EN sodium bisulfite.pdf Hazardous in case of eye contact English (irritant), slightly hazardous in case of 461 MSDS 461 EN Sodium borohydride MSDS-461-EN Sodium borohydride.pdf Operation Lab. Analysis Merck KGaA Granule Sodium borohydrate Sodium boranate NaBH4 16940-66-2 37.839 g/mol N/A 25 g n/A Burns irritation burns Burns Harmful to aquatic organisms Operation Lab. Sr. Chemist Contact with water liberates extremely English flammable gases. Toxic in contact with 462 MSDS 462 EN Sodium carbonate - Kanto MSDS-462-EN Sodium carbonate-Kanto.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Sodium carbonate Sodium carbonate Na2CO3 479-19-8 99 N/A 500 g Light,heat Inflamation N/A Irritation Irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards: water English solution is strong alkaline, causes 463 MSDS 463 EN Sodium carbonate anhydrous GR MSDS-463-EN sodium carbonat anhydrous GR.pdf Operation Lab. Analysis Merck KGaA Solid Sodium carbonate anhydrous Na2CO3 497-19-8 105.99 g/mol N/A 250g N/A Irritation Irritation Irritation Irritation Hygroscopis, toxic to aquatic orga Operation Lab. Sr. Chemist 1) Adverse human health hazards : English Water solution is strong alkaline, causes 464 MSDS 464 EN Sodium chloride MSDS-464-EN Sodium chloride.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal Sodium chloride Sodium chloride NaCl 7647-14-5 99 N/A 500 g Light,heat irritation N/A N/A N/A N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards: this English substance has low harmfulness, but a 465 MSDS 465 EN Sodium dihydrogen phosphate monohydrate MSDS-465-EN Sodium dihydrogen phosphate monohydrate.pdf Operation Lab. Analysis Merck KGaA Crystal Sodium dhydrogen phospate monohydrate Sodium phospate monobasic NaH2PO4.H2O 10049-21-5 137.99 g/mol N/A 500g strong heating irritation N/A N/A N/A Eutrophication of water supplies Operation Lab. Sr. Chemist No hazardous as specified English

466 MSDS 466 EN Sodium dodecylbenzenesulfonate MSDS-466-EN Sodium dodecylbenzenesulfonate.pdf Operation Lab. Analysis Sigma Aldrich Solid Sodium dodecylbenzene sulfonate Abeson nam C18H29NaO3S 25155-30-0 Mw:348.48 N/A 500 g strong oxidizing agents irritation irritation irritation irritation may contribute to the eutrophicatioOperation Lab. Sr. Chemist Toxic (USA) harmful (EU). Harmful if English swallowed.Irritating to respiratory system 467 MSDS 467 EN Sodium fluoride MSDS-467-EN Sodium fluoride.pdf Operation Lab. Analysis Merck KGaA Crystal Sodium Floride NaF 7681-49-4 41.99 g/mol 2.5 (mg/m3) 250 g strong oxidizing agents irritation irritation Burns, vomiting, spasme irritation N/A Operation Lab. Sr. Chemist Toxic if swallowed. Contact with acids English liberates very toxic gas. Irritating to eyes 468 MSDS 468 EN Sodium hydrogen carbonate MSDS-468-EN Sodium hydrogen carbonate.pdf Operation Lab. Analysis Merck KGaA Powder Sodium Hydrogen Carbonat NaHCO3 144-55-8 84.01 N/A 500 g N/A irritation irritation Nausea, vomiitng irritation N/A Operation Lab. Sr. Chemist No hazardous as specified English

469 MSDS 469 EN Sodium hydrogen sulfite MSDS-469-EN Sodium hydrogen sulfite.pdf Operation Lab. Analysis Merck KGaA Liquid Sodium bisulfite Sodium bisulfite solution Na2SO3 7631-90-5 39% 5 mg/m3 1000 g Oxidizing agents, acids irritation irritation irritation irritation N/A Operation Lab. Sr. Chemist Harmful if swallowed.Contact with acids English liberates toxic gas. 470 MSDS 470 EN sodium hydroxide solution 40% MSDS-470-EN sodium hydroxide solution 40%.pdf Causes severe irritation and burns. May English be harmful if swallowed. Avoid breathing 471 MSDS 471 EN Sodium hydroxide, Pellets-Kanto MSDS-471-EN Sodium hydroxide, Pellets-Kanto.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Sodium hydroxide NaOH 1310-73-2 2 mg/m3 Sunligh6,heat,acids,alumunium. , tin, zinc, chrom loss of vision Inflammation N/A irritation Form corrosive mixtures with wate Operation Lab. Sr. Chemist 1) The most important danger and English hazard : corrosive to the human body. 2) 472 MSDS 472 EN Sodium hydroxide, Pellets-Merck MSDS-472-EN Sodium hydroxide, Pellets-Merck.pdf Operation Lab. Analysis Merck KGaA Solid Sodium hydroxide NaOH 1310-73-2 40.9 C 2 mg/m3 500 g metals, alumunium,zinc burns burns burns burns Form corrosive mixtures with wate Operation Lab. Sr. Chemist Causes severe burns. English

473 MSDS 473 EN Sodium Hydroxide-Science Lab MSDS-473-EN Sodium Hydroxide-Science Lab.pdf TBD PT. Mitra Agung S. Liquid Sodium Hydroxide Caustic Soda 1310-73-2 40 2 (TWA) Acid, organic halogen Irritation Irritation Irritation Irritation Corrosive Utilities James Lempoy Very hazardous in case of skin contact English (corrosive,irritant, permeator), of eye 474 MSDS 474 EN sodium metabisulfite MSDS-474-EN Sodium Metabisulfite.pdf Kurita Harmful if swallowed or inhaled, cause English irritation to skin, eyes and respiratory 475 MSDS 475 EN Sodium metasilicate anhydrous MSDS-475-EN Sodium metasilicate anhydrous.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Sodium meta silicate anhydrous Na2SiO3 6834-92-0 47-53 N/A 500 g Light,heat Inflammation N/A irritation irrritation N/A Operation Lab. Sr. Chemist 1) The most important danger and English hazard : water solution is strong alkaline, 476 MSDS 476 EN Sodium standard solution (Na-1000) MSDS-476-EN Sodium standard solution (Na-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Sodium Nitrate NaNO3 in H2O 7631-99-4 N/A 500 ml N/A N/A N/A N/A N/A Hazard for drinking water Operation Lab. Sr. Chemist No Hazardous as specified English

477 MSDS 477 EN Sodium sulfate MSDS-477-EN Sodium sulfate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Crystal sodium sulfate Na2SO4 7757-82-6 98.5 N/A 500 g Light, heat irritation N/A irritation irrritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : as English sodium sulfate is permitted to be used 478 MSDS 478 EN Sodium Sulfide Nonahydrate MSDS-478-EN Sodium Sulfide Nonahydrate.pdf Operation Lab. Analysis Sigma Aldrich Crystal Disodium sulfide nonahydrate Na2S.9H2O 1313-84-4 240.18 N/A 500 g Lights,moisture, Acids, oxidizing agents, Alumunium, Copper, zinc Buns Destructive to mucus mem Burns Burns Very toxic to aquatic organism Operation Lab. Sr. Chemist Risk advice to man and the environment English : contact with acids liberates toxic gas. 479 MSDS 479 EN Sodium sulfite MSDS-479-EN Sodium sulfite.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder sodium sulfite Na2SO3 7757-83-7 95 N/A 500 g Light, heat, air N/A N/A Vomiting irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : the English chemical has slight irritation of skin, 480 MSDS 480 EN Sodium tetraborate, anhydrous MSDS-480-EN Sodium tetraborate, anhydrous.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Sodium tetraborate anhydrous Na2B4O7 1330-43-4 97 5 mg/m3 250 g Light, heat, oxidizing agents irritation irritation vomiting, nausea Irritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : may English cause irritation of skin and eyes. If 481 MSDS 481 EN Sodium thiosulfate MSDS-481-EN Sodium thiosulfate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Sodium Thiosulfate Na2S2O3 7772-98--7 95 N/A 500 g oxidizing substance irritation N/A nausea, abdominal pain, voIrritation N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : This English substance has low harmfulness, but a 482 MSDS 482 EN solest 68 MSDS-482-EN solest 68.pdf N/A English

483 MSDS 483 EN solest LT-32 MSDS-483-EN solest LT-32.pdf This material has no known hazards English under applicable laws. The product 484 MSDS 484 EN solest Series MSDS-484-EN solest Series.pdf This product is non hazardous. The English product contains no known carcinogens. 485 MSDS 485 EN Spotcheck® SKC-S MSDS-485-EN Spotcheck SKCS.pdf Solvent Remover / Cleaner Magnaflux Liquid Aliphatic solvent naphtha NA TBD 64742-89-8 60 - 100 300 ppm None Irritation Dizziness and nausea No significant Irritation Flammable Maintenance Wisnugroho Flammable liquid and aerosol. Vapor English Carbon dioxide 124-38-9 3 - 7 NA may cause flash fire. Harmful or fatal if 486 MSDS 486 EN Spotcheck® SKD-S2 MSDS-486-EN Spotcheck SKDS2.pdf Penetrant Inspection Developer Magnaflux Liquid 2-propanol NA TBD 67-63-0 40 – 70 400 ppm None Irritation Dizziness and nausea No significant Irritation Flammable Maintenance Wisnugroho Extremely flammable white liquid and English 2-propanone NA 67-64-1 10 – 30 750 ppm aerosol. Fast evaporating vapors can 487 MSDS 487 EN Spotcheck® SKL-SP1 MSDS-487-EN Spotcheck SKL SP1.pdf Visible Inspection Penetrant Magnaflux Liquid Petroleum White mineral oil TBD 64742-47-8 60 - 80 5 None Irritation Dizziness and nausea No significant Irritation Flammable Maintenance Wisnugroho Bland, oily liquid which may irritate the English Phthalic Esters NA 71888-89-6 5 - 25 5 skin and eyes. Bulk material is difficult to 488 MSDS 488 EN Starborn S 121 MSDS-488-EN starborn s-121.pdf Biocide & Slimecide PT. Luas Birus Utama Liquid Not specified in the original MSDS NA NA NA NA NA Liquid bleach, oxidizing agents, reducing agents, amines, mercapt Corrosive Harmful harmful Burns Very toxic to aquatic organism Utilities Asrory EYE CONTACT: Corrosive. Will cause English eye burns and permanent tissue MSDS 488 IN Starborn S 121 MSDS-488-IN S 121 B.Indo.pdf Biocide & Slimecide PT. Luas Birus Utama Liquid Not specified in the original MSDS NA NA NA NA NA Liquid bleach, oxidizing agents, reducing agents, amines, mercapt Corrosive Harmful harmful Burns Very toxic to aquatic organism Utilities Asrory EYE CONTACT: Corrosive. Will cause Bahasa eye burns and permanent tissue 489 MSDS 489 EN Starborn S 161 MSDS-489-EN Starborn S161.pdf Corrosion Inhibitor for closed coolin PT. Luas Birus Utama Liquid Sodium nitrite NA NaNO2 7632-00-0 36 - 45 NA Strong oxidizers Irritation Not specified Not specified Not specified NA Utilities Asrory EYE CONTACT : May cause irritation English with prolonged contact. SKIN CONTACT MSDS 489 IN Starborn S 161 MSDS-489-IN S 161 B.Indo.pdf Corrosion Inhibitor for closed coolin PT. Luas Birus Utama Liquid Sodium nitrite NA NaNO2 7632-00-0 36 - 45 NA Strong oxidizers Irritation Not specified Not specified Not specified NA Utilities Asrory EYE CONTACT : May cause irritation Bahasa with prolonged contact. SKIN CONTACT 490 MSDS 490 EN Starborn S-431 MSDS-490-EN starborn s-431.pdf Oxygen Scavenger PT. Luas Birus Utama Liquid Carbohydrazide NA NA Na <20 NA Liquid bleach, oxidizing agents, reducing agents, amines, mercapt Corrosive Harmful Harmful irritation Very toxic to aquatic organism Utilities Asrory HUMAN HEALTH HAZARDS : Corrosive English to skin , Corrosive to eyes. Vapors, MSDS 490 IN Starborn S-431 MSDS-490-IN S 431 B.Indo.pdf Oxygen Scavenger PT. Luas Birus Utama Liquid Carbohydrazide NA NA Na <20 NA Liquid bleach, oxidizing agents, reducing agents, amines, mercapt Corrosive Harmful Harmful irritation Very toxic to aquatic organism Utilities Asrory HUMAN HEALTH HAZARDS : Corrosive English to skin , Corrosive to eyes. Vapors, 491 MSDS 491 EN Starch, soluble, potato MSDS-491-EN Starch, soluble, potato.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Starch Amilodextrine C6H10O5n 9005-84-9 80 10 mg/m3 500 g Light,heat irritation N/A N/A N/A N/A Operation Lab. Sr. Chemist 1) Adverse human health hazards : English Strach is polyner of D-glucose and one 492 MSDS 492 EN Sulfuric Acid MSDS-492-EN Sulfuric Acid.pdf TBD NA Liquid Sulfuric Acid TBD H2SO4 TBD 98 TBD Sulfur Dioxide Irritation Irritation Irritation Irritation Corrosive Utilities James Lempoy Causes severe burns to eyes, skin and English all body tissue. Inhalation of mist may 493 MSDS 493 EN Sulfuric acid 95-97% GR MSDS-493-EN Sulfuric acid 95-97% GR.pdf Operation Lab. Analysis Merck KGaA Liquid Sulfuric acid H2SO4 7664-95-9 98.089 g/mol 0.2 mg/m3 2.5 L Metal, animal/vegetable tissues burns Damage to affected mucus nausea, vomit, severe pain Severe burns Toxic effect on fish and algae Operation Lab. Sr. Chemist Causes severe burns. English

494 MSDS 494 EN sulfuric acid reagent a-c-s MSDS-494-EN sulfuric acid reagent a-c-s.pdf Causes severe irritation and burns. May English be harmful if swallowed. Avoid breathing 495 MSDS 495 EN MSDS-495-EN sulfuric acid 98% min.pdf Kurita Poison, Danger, Corrosive, liquid and English surfuric acid 98% min mist cause severe burns to all body 496 MSDS 496 EN MSDS-496-EN synergen 501.pdf N/A English synergen 501 497 MSDS 497 EN Thianaphthene MSDS-497-EN Thianaphthene.pdf Operation Lab. Analysis Sigma Aldrich Solid 1-Benzothopene C8H65 95-15-8 95 N/A 50 g strong Oxidizing agents Irritation Irritation harmful irritation N/A Operation Lab. Sr. Chemist Toxic (USA) harmful (EU). Harmful if English swallowed. Stench. 498 MSDS 498 EN thinner trans 120-cleaner MSDS-498-EN thinner trans 120-cleaner.pdf N/A English

499 MSDS 499 EN thinner trans 220-solvent cleaner MSDS-499-EN thinner trans 220-solvent cleaner.pdf N/A English

500 MSDS 500 EN thuban gl5 ep sae 140 MSDS-500-EN thuban gl5 ep sae 140.pdf 1) Eyes : Expected to cause no more English than minor eye irritation characterized 501 MSDS 501 EN thuban gl5 ep sae 90 MSDS-501-EN thuban gl5 ep sae 90.pdf 1) Eyes : Expected to cause no more English than minor eye irritation characterized 502 MSDS 502 EN Tin standard solution (Sn-1000) MSDS-502-EN Tin standard solution (Sn-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Tin (II) Chloride SnCl4 7772-99-8 2 mg/m3 500 mL Unsuitable working materials: metal, metal alloys (generation of hydIrritation Irritation N/A Irritation hazard for drinking water, harmful Operation Lab. Sr. Chemist No Hazardous as specified English

503 MSDS 503 EN Tin(II) chloride dihydrate MSDS-503-EN Tin(II) chloride dihydrate.pdf Operation Lab. Analysis Merck KGaA Solid Tin dichloride dihydrate, stannous chloride SnCl2.2H2O 10025-69-1 225.63 2 mg/m3 100 g None irritation irritation irritation irritation N/A Operation Lab. Sr. Chemist Harmful if swallowed. Irritating to eyes, English respiratory system and skin. May cause 504 MSDS 504 EN Tin, Drops MSDS-504-EN Tin, Drops.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Solid Tin Sn 7440-31-5 BM; 259 Metal: 2 mg/m3, Oxide & inorganic compounds: 2 mg/m3, organic compounds: 0.1 mg/m3 25 g Oxygen Irritation Irritation N/A irritation Harmful effect Operation Lab. Sr. Chemist 1) Adverse human health hazards : If English inhaled the dust, cause irritation of nose, 505 MSDS 505 EN TOC persulfate MSDS-505-EN TOC persulfate.pdf Causes eye and respiratory tract English irritation may cause allergic skin and 506 MSDS 506 EN Toluene GR MSDS-506-EN Toluene GR.pdf Operation Lab. Analysis Merck KGaA Liquid Toluene MethylBenzene C6H5CH3 108-88-3 92.14 20 ppm 2.5L Various plastics, rubber irritation irritation Nausea and vomiting irritation Flammable Operation Lab. Sr. Chemist Highly flammable. Irritating to skin. English Harmful : danger of serious damage to 507 MSDS 507 EN MSDS-507-EN Total nitrogen (TN) hydroxide reagent.pdf Causes eye irritation. English Total nitrogen (TN) hydroxide reagent 508 MSDS 508 EN Total nitrogen (TN) persulfate reagent MSDS-508-EN Total nitrogen (TN) persulfate reagent.pdf Causes eye and respiratory tract English irritation may cause allergic skin and 509 MSDS 509 EN Total nitrogen (TN) reagent A MSDS-509-EN Total nitrogen (TN) reagent A.pdf May causes eye and respiratory tract English irritation. may cause allergic respiratory 510 MSDS 510 EN Total nitrogen (TN) reagent B MSDS-510-EN Total nitrogen (TN) reagent B.pdf May causes eye and respiratory tract English irritation. may cause allergic respiratory 511 MSDS 511 EN Total Protein MSDS-511-EN total protein.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Total Protein Aqueous Solution NA NA NA NA 1 kit/ 300 ml Quarterly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 512 MSDS 512 EN Touch up light grey RAL 7032 MSDS-512-EN Touch up light grey RAL 7032.pdf no data available English

513 MSDS 513 EN Trans-1,2-Cyclohexanediamine-N,N,N',N'-tetraacetic acid monohydrate MSDS-513-EN Trans-1,2-Cyclohexanediamine-N,N,N',N'-tetraacetic acid monohydrate.pdf Operation Lab. Analysis Kanto Chemical Co., Inc Powder Trans-1,2-Cyclohexanediamine-N,N,N',N'-tetraacetic CyDTA C 6H10N2(CH2COOH)4*H2O 87095-89-4 98 NA 4 25 g Irritation Irritation Irritation Irritation Operation Lab. Sr. Chemist 1) Adverse human health hazard : Irritate English to skin, eyes and cause inflammation. If 514 MSDS 514 EN transfloor p100 MSDS-514-EN transfloor p100.pdf N/A English

515 MSDS 515 EN MSDS-515-EN transfloor t120.pdf N/A English transfloor t120 516 MSDS 516 EN Transformer Oil MSDS-516-EN Transformer Oil.pdf 1) Human health : inhalation of vapours English and/or mists might irritate respiratory 517 MSDS 517 EN trichloroisocyanuric acid MSDS-517-EN trichloroisocyanuric acid.pdf Strong oxidizer. Contact with other English material may cause a fire. Harmful if 518 MSDS 518 EN tricloroisocyanuric acid 90% MSDS-518-EN tricloroisocyanuric acid 90%.pdf Inhalation, burn and burn eye damage, English blindness. 519 MSDS 519 EN Triethanolamine MSDS-519-EN Triethanolamine.pdf Operation Lab. Analysis Merck KGaA Liquid Triethanolamine Tris(2-hydroxethylamine), TEA N (CH2CH2OH)3 102-71-6 141.19 g/mol 5 mg/m3 1000 mL Acids, anhydrides, halogenating agents, oxidizing agents N/A Coughing Abdominal pain N/A Combustible Operation Lab. Sr. Chemist No hazardous as specified English

520 MSDS 520 EN Triglyseride MSDS-520-EN triglycerides.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Triglycerides Aqueous Solution NA NA NA NA 1 kit/ 300 ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 521 MSDS 521 EN triklorit 90% MSDS-521-EN triklorit 90%.pdf Harmfull if swallowed. Irritating to eyes English and respiratory system. Contact with 522 MSDS 522 EN triton DF-20 surfactan MSDS-522-EN triton DF-20 surfactan.pdf Causes burns. Harmful in contact with English skin and if swallowed. 523 MSDS 523 EN TS-66 Extreme temperature grease MSDS-523-EN TS-66 Extreme temperature grease.pdf Overexposure to this product may cause English mild skin irritation, moderate eye 524 MSDS 524 IN MSDS-524-IN turalik 48 iso vg46.pdf Tidak ada pengaruh yang berarti. Bahasa turalik 48 iso vg46 525 MSDS 525 IN MSDS-525-IN turalik 52 iso vg 68.pdf Tidak ada pengaruh yang berarti. Bahasa turalik 52 iso vg 68 526 MSDS 526 IN MSDS-526-IN turalik c 10 iso vg10.pdf Tidak ada pengaruh yang berarti dalam Bahasa turalik c 10 iso vg10 jangka panjang. Dapat menimbulkan 527 MSDS 527 IN MSDS-527-IN turalik c10.pdf Tidak ada pengaruh yang berarti dalam Bahasa turalik c10 jangka panjang. Dapat menimbulkan 528 MSDS 528 EN Unirex N3 MSDS-528-EN Unirex N3.pdf Under normal condition of use, this English product is not considered hazardous 529 MSDS 529 EN Urea UV MSDS-529-EN urea uv.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid NA Aqueous Solution NA NA NA NA 1 kit/ 300 ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 530 MSDS 530 EN Uric Acid MSDS-530-EN uric acid.pdf Clinic Lab. Dialine Diagnostic System Pte. Ltd. Liquid Uric Acid Solution Aqueous Solution NA NA NA NA 1 kit/ 300 ml Bi-monthly None No specific No specific No specific No specific HSE MP Clinic Dangerous properties cannot be English excluded. However, risks are not to be 531 MSDS 531 IN Used Oil MSDS-531-IN used oil.pdf

532 MSDS 532 EN vanellus v3 extra 15w-40 MSDS-532-EN vanellus v3 extra 15w-40.pdf Environmental hazards : unlikely to be English harmful to aquatic organism. Used 533 MSDS 533 EN vitrea oil32 MSDS-533-EN vitrea oil32.pdf 1) Health hazards : not classified as English dangerous for supply or conveyance. 2) 534 MSDS 534 EN v-top hb pl-s hardener MSDS-534-EN v-top hb pl-s hardener.pdf Flammable liquid, acutely toxic English substance. May cause organic solvent 535 MSDS 535 EN water acrylic resin MSDS-535-EN water acrylic resin.pdf no data available English

536 MSDS 536 EN waxtreat 3671 MSDS-536-EN waxtreat 3671.pdf Flammable. Irritating to skin. Limited English evidence of a carcinogenic effect. 537 MSDS 537 EN Xylene MSDS-537-EN Xylene.pdf Operation Lab. Analysis Merck KGaA Liquid xylene Xylene C6H4(CH3)2 1330-20-7 106.17 g/mol TWA: 100 ppm, STEL: 150 ppm 1000 mL light metals, rubber, plastics Irritation oedemas in respiratory tra GI symptoms Irritation Flammable Operation Lab. Sr. Chemist Flammable. Harmful by inhalation and in English contact with skin. Irritating to skin. 538 MSDS 538 EN YaraMilaTM MSDS-538-EN Yaramila.pdf Water treatment chemical Yara North America, Inc. Solid Ammonium Chloride 12125-02-9 < 15 10 (fume) Stable under recommended storage & handling conditions Slightly irritating Slightly irritating No significant Slightly irritating NA Logistic Tugu - Willy may cause respiratory tract, eye and English skin irritation 539 MSDS 539 EN Zinc acetate dihydrate GR MSDS-539-EN Zinc acetate dihydrate GR.pdf Operation Lab. Analysis Merck KGaA Solid zinc acetat dihydrate (CH3COO2)Zn.2H20 5970-45-6 219.49 g/mol N/A 1000 g N/A Irritation Irritation Diarrhea N/A N/A Operation Lab. Sr. Chemist Harmful if swallowed. Very toxic to English aquatic organism, may cause long-term 540 MSDS 540 EN Zinc standard solution (Zn-1000) MSDS-540-EN Zinc standard solution (Zn-1000).pdf Operation Lab. Analysis Merck KGaA Liquid Zinc Nitrate Zn(NO3)2 7779-88-6 N/A 500 ml Unsuitable working materials: metal, metal alloys (generation of hydirritation irritation irritation irritation harmful to aquatic organisms Operation Lab. Sr. Chemist Irritating to eyes and skin Harmful to English aquatic organism, may cause long - term 541 MSDS 541 EN Zinc, Powder GR MSDS-541-EN Zinc Powder GR.pdf Operation Lab. Analysis Merck KGaA Solid Zinc Zinc Zn 7440-66-6 65.37 g/mol N/A 500 g Alkali hydroxides, moitsure, Cl, F, acids, arsenic oxides, carbondis N/A Irritation Fever, pain Irritation Flammable, combustible, highly to Operation Lab. Sr. Chemist Very toxic to aquatic organism, may English cause long-term adverse effects in the Simple asphyxiant - Maintain oxygen 542 542 Bimethyl; Dimethyl Ethyl MSDS EN Ethane MSDS-542-EN Ethane.pdf Operation BOC Gases Ethane C2H6 74-84-0 levels above 19.5%. Extremely English Hydride; Methylmethane Berbahaya.flammable. Iritasi pernafasan, pusing, 543 543 MSDS IN Minyak-Solar+[1] MSDS-543-IN Minyak-Solar+[1].pdf Diesel fuel Petroleum Hydrocarbon mual, pingsan. Pada pemaparan dalam Bahasa Poisonwaktu lama : Danger! dan berulang-ulang May be fatal if akan 544 544 MSDS EN Strychnine MSDS-544-EN Strychnine.pdf Pest Control (dog&cat bite) J.T. Barker Powder Strychnine Strychnos CH21H22N2O2 57-24-9 swallowed or inhaled. Causes irritation English to skin, eyes and respiratory tract. Affect 545 MSDS 545 EN GMA Garnet MSDS-545-EN GMA Garnet.pdf Blasting Operation at Shore Base GMA Garnet Pty Ltd Pink to red Almandine Garnet Fe3Al2(SiO4)3 1302-62-1 Exposure to nuisance Not irritating to the skin. Acute: None known. Use as a blast English coloured dust created by use as a cleaning media may create conditions of 546 MSDS 546 EN Agratawn Crabrass Control MSDS-546-EN Agratawn Crabrass Control.PDF Irritating to the skin and eyes on contact. English Inhalation will cause irritation to the lungs 547 MSDS 547 EN C - 16 BRS MSDS-547-EN C - 16 BRS.pdf Eye : mechanical irritation from English aggregate or fine particles during 548 MSDS 548 EN Dry Magnetic Particles MSDS-548-EN Dry Magnetic Particles.pdf Dusty and gritty powder which can English mechanically irritate the eye. Skin 549 MSDS 549 EN Belzona 2921 MSDS-549-EN Belzona 2921.pdf Belzona America Inc. 101-68-8 0.051 mg/cum Skin/respiratory/eye/tract irritation English

550 MSDS 550 EN DuPont Freon 22 MSDS-550-EN DuPont Freon 22. pdf DuPont de Nemours 75-45-6 3590 mg/m3 Dangerous for the ozone layer. Rapid English evaporation of the liquid may cause 551 MSDS 551 EN DuPont Isceon MO59 Refrigerant MSDS-551-EN DuPont Isceon MO59 Refrigerant.pdf DuPont New Zaeland Ltd. 811-97-2 Not classified as hazardous. Rapid English evaporation of the liquid may cause 552 MSDS 552 EN Terostat MS 930 MSDS-552-EN Terostat MS 930.pdf Henkel Limited 5 mg/m3 The product not hazardous within the English meaning of the valid EU preparation 553 MSDS 553 EN Axtrap 273 MSDS-553-EN MSDS_AxTrap273.pdf Axens This product is not classified as English flammable. Avoid spread to atmosphere 554 MSDS 554 EN Mercsorb Mercury Amalgamation Powder MSDS-554-EN Mercsorb Mercury Amalgamation Powder.pdf NPS Corporation Eye: May cause irritation. English Skin: May cause irritation. Repeated 555 MSDS 555 EN Mercury Indicator Powder MSDS-555-EN Mercury Indicator Powder.pdf NPS Corporation Eye: May cause irritation. English Skin: May cause irritation. 556 MSDS 556 EN Mercury Vapor Suppressor MSDS-556-EN Mercury Vapor Suppressor NPS Corporation Eye: May cause irritation. English Skin: May cause irritation. Repeated 557 MSDS 557 EN SULFUSORB-8_4x10 MSDS-557-EN SULFUSORB-8_4x10.pdf Calgon Carbon Corporation Contact may cause eye irritation. English Dust may be slightly irritating to eyes 558 MSDS 558 EN Spilfyter MSDS-558-EN Spilfyter.pdf NPS Corporation Eye: May cause irritation. English Skin: May cause irritation. Repeated 559 MSDS 559 EN Nitrogen MSDS-559-EN Nitrogen.pdf Irish Oxygen Co Ltd, Compressed gas English In high concentrations, may cause 560 MSDS 560 EN N2 Airgas MSDS-560-EN N2 Airgas.pdf AIRGAS INC., Eye : Contact with rapidly expanding gas English may cause burns or frostbite. Contact 561 MSDS 561 EN No Heat MeDex 80 MSDS-561-EN No Heat MeDex 80.pdf No Heat Resources Pte Ltd Inhalation Concentration exceeds the English ACGIH TLV causes irritating to the nose, 562 MSDS 562 EN CERAMIC BALLS MSDS-562-EN CERAMIC BALLS.pdf Axens Flammable English

563 MSDS 563 EN MeDeX 80 MSDS-563-EN MeDeX 80.pdf No Heat Resources Pte Ltd INHALATION : Very high concentrations English may cause irritation to the skin, nose, 564 MSDS 564 EN HGR_4x10 MSDS-564-EN HGR_4x10.pdf Calgon Carbon Corporation Black particulate solid, pellet or powder. English Contact may cause eye irritation. 565 MSDS 565 EN Intergard 475 HS Part A MSDS-565-EN Intergard 475 HS Part A.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment, irritant 566 MSDS 566 EN Intergard 475 HS Part B MSDS-566-EN Intergard 475 HS Part B.pdf Internasional Paint Indonesia Flamable and carcinogenic English

567 MSDS 567 EN Intergard 740 surf grey Part A MSDS-567-EN Intergard 740 surf grey Part A.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment 568 MSDS 568 EN Intergard 740 surf grey Part B MSDS-568-EN Intergard 740 surf grey Part B.pdf Internasional Paint Indonesia Flamable and carcinogenic English

569 MSDS 569 EN Interline 399 white Part A MSDS-569-EN Interline 399 white Part A.pdf Internasional Paint Indonesia Flamable and carcinogenic English

570 MSDS 570 EN Interline 399 white Part B MSDS-570-EN Interline 399 white Part B.pdf Internasional Paint Indonesia Flamable and carcinogenic English

571 MSDS 571 EN Intershield 300 Bronze Part A MSDS-571-EN Intershield 300 Bronze Part A.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment 572 MSDS 572 EN Intershield 300 Bronze Part B MSDS-572-EN Intershield 300 Bronze Part B.pdf Internasional Paint Indonesia Flamable, corrosive and carcinogenic English

573 MSDS 573 EN Interthane 990 light grey Part A MSDS-573-EN Interthane 990 light grey Part A.pdf Internasional Paint Indonesia Flamable and carcinogenic English

574 MSDS 574 EN Interthane 990 light grey Part B MSDS-574-EN Interthane 990 light grey Part B.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment, irritant 575 MSDS 575 EN Intertherm 875 Aluminium MSDS-575-EN Intertherm 875 Aluminium.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment 576 MSDS 576 EN Interzinc 42 Part A MSDS-576-EN Interzinc 42 Part A.pdf Internasional Paint Indonesia Flamable, Carcinogenic, Dangerous to English environment 577 MSDS 577 EN Interzinc 42 Part B MSDS-577-EN Interzinc 42 Part B.pdf Internasional Paint Indonesia Flamable, corrosive and carcinogenic English

578 MSDS 578 EN Interzinc 52 Grey Part A MSDS-578-EN Interzinc 52 Grey Part A.pdf Internasional Paint Indonesia Flamable, corrosive and carcinogenic English

579 MSDS 579 EN Interzinc 52 Grey Part B MSDS-579-EN Interzinc 52 Grey Part B.pdf Internasional Paint Indonesia Flamable, corrosive and carcinogenic English

580 MSDS 580 EN Thinner GTA 007 MSDS-580-EN Thinner GTA 007.pdf Internasional Paint Indonesia Flamable and carcinogenic English

581 MSDS 581 EN Thinner GTA 220 MSDS-581-EN Thinner GTA 220.pdf Internasional Paint Indonesia Flamable, corrosive and carcinogenic English

582 MSDS 582 EN Thinner GTA 733 MSDS-582-EN Thinner GTA 733 Internasional Paint Indonesia Flamable and carcinogenic English

583 MSDS 583 EN Kobelco B-10 B-14 B-17 MSDS-583-EN Kobelco B-10 B-14 B-17.pdf Kobelco Arc Rays can severly damage eyes and English skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary 584 MSDS 584 EN Kobelco LB52-18 MSDS-584-EN Kobelco LB52-18.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 585 MSDS 585 EN Kobelco LB-52 LB-52U LB-50A MSDS-585-EN Kobelco LB-52 LB-52U LB-50A.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 586 MSDS 586 EN Kobelco LB-52, LB-52U MSDS-586-EN Kobelco LB-52, LB-52U.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 587 MSDS 587 EN Kobelco MF-33H MSDS-587-EN Kobelco MF-33H.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 588 MSDS 588 EN Kobelco NIC-1S MSDS-588-EN Kobelco NIC-1S.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 589 MSDS 589 EN Kobelco PFN-4 MSDS-589-EN Kobelco PFN-4.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 590 MSDS 590 EN Kobelco TGS-50 TGS-51T NO65G MSDS-590-EN Kobelco TGS-50 TGS-51T NO65G.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 591 MSDS 591 EN Kobelco US-36 MSDS-591-EN Kobelco US-36.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 592 MSDS 592 EN Kobelco US-709S TGS-709S MSDS-592-EN Kobelco US-709S TGS-709S.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 593 MSDS 593 EN Kobelco US-709S MSDS-593-EN Kobelco US-709S.pdf Kobelco Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 594 MSDS 594 EN NIPPON Bare Stanless 2 MSDS-594-EN NIPPON Bare Stanless 2.pdf Nippon Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 595 MSDS 595 EN NIPPON Stainless SMAW 1 MSDS-595-EN NIPPON Stainless SMAW 1.pdf Nippon Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 596 MSDS 596 EN NIPPON Stainless SMAW 2 MSDS-596-EN NIPPON Stainless SMAW 2.pdf Nippon Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 597 MSDS 597 EN NIPPON WEL Bare Stainless 1 MSDS-597-EN NIPPON WEL Bare Stainless 1.pdf Nippon Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 598 MSDS 598 EN Yawata Weld B(M) MSDS-598-EN Yawata Weld B(M).pdf Nippon Electric shock can kill. Gases may English cause gas poisoning. Arc Rays can severly damage eyes and skin. Overexposure to welding fumes may result in symptoms like dizziness, nausea, dryness or irritation of the nose, throat or eyes. Chronic overexposure to welding fumes may affect pulmonary function. 599 MSDS 599 EN Taseto New Bright #300 (Pickling Acid) MSDS-599-EN Taseto New Bright #300 (Pickling Acid).pdf Taseto Toxic by inhilation, in contact with skin English and if swallowed 600 MSDS 600 EN Intergard 475 HS MSDS-600-EN Intergard 475 HS.pdf Skin : causes skin irritation, may cause allergic reaction . Eye : Cause serious eye irritation. May cause respiratory irritation. May cause damage to kidney, liver and central nervous system. Toxic to aquatic life. 601 MSDS 601 EN Interline 399 MSDS-601-EN Interline 399.pdf Highly flammable liquid and vapour. Causes skin irritation. Cause seriuos eye irritation. Skin : may cause allergic reaction . May cause damage to kidney, liver and central nervous system.

602 MSDS 602 EN Intershield 300 MSDS-602-EN Intershield 300.pdf Flammable liquid and vapour. May cause damage to skin through prolonged or repeated exposure. May cause damage to kidney, liver and central nervous system. Toxic to aquatic life.

603 MSDS 603 EN Interthane 990 MSDS-603-EN Interthane 990.pdf Highly flammable liquid and vapour. May be harmful in contact with skin. Causes skin irritation. May cause damage to skin through prolonged or repeated exposure. May cause damage to kidney, liver and central nervous system. Known to cause human aspiration toxicity hazards. Toxic to aquatic life.

604 MSDS 604 EN Interzinc 42 MSDS-604-EN Interzinc 42.pdf Flammable liquid and vapour. May cause damage to skin through prolonged or repeated exposure. May cause damage to kidney, liver and central nervous system. Toxic to aquatic life. Known to cause human aspiration toxicity hazards. Very toxic to aquatic life.

605 MSDS 605 EN Jotun Thinner No. 07 - Marine_Protective - English (uk) - United KingdomMSDS-605-EN Jotun Thinner No. 07 - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Highly flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic MSDS 605 IN Jotun Thinner No. 07 - Marine_Protective - Indonesian (id) - Indonesia MSDS-605-IN Jotun Thinner No. 07 - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka- 606 MSDS 606 EN Jotun Thinner No. 10 - Marine_Protective - English (uk) - United KingdomMSDS-606-EN Jotun Thinner No. 10 - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Highly flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic MSDS 606 IN Jotun Thinner No. 10 - Marine_Protective - Indonesian (id) - Indonesia MSDS-606-IN Jotun Thinner No. 10 - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka- 607 MSDS 607 EN Urea MSDS-607-EN Urea MSDS.pdf Mitra Agung Sejati Health rating : 2 - Moderate (life), slightly English flamable, Moderate reactivity. Cause irritation to skin, eyes and respiartory tract 608 MSDS 608 EN Dishodium phospate MSDS-608-EN Dishodium phospate MSDS.pdf Aditya Biria Chemicals No Known Hazard English 609 MSDS 609 EN Nalco 3279 MSDS-609-EN Nalco_3279.pdf Nalco Human health hazards - Acute, eye English irritation, skin irritation 610 MSDS 610 EN Re-Solv Ultimer EC6028A MSDS-610-EN Re_Solv_Ultimer_R_EC6028A.pdf Human health hazards - Acute, eye English irritation, skin irritation, keep out of waterways 611 MSDS 611 EN Carbon Dioxide, Nitrogen, and Methane Balance MSDS-611-EN Carbon Dioxide, Nitrogen, and Methane Balance.pdf National Oxygen Rapid Respiration, muscular English incoordination, fatique, dizziness, nausea, vomiting, unconsciousness, and death 612 MSDS 612 EN Carbon Dioxide and Nitrogen Balance MSDS-612-EN Carbon Dioxide and Nitrogen Balance.pdf National Oxygen Rapid Respiration, muscular English incoordination, fatique, dizziness, nausea, vomiting, unconsciousness, and death 613 MSDS 613 EN Nitrogen Compressed Gas MSDS-613-EN Nitrogen Compressed Gas.pdf National Oxygen Difficult breathing, nausea, vomitting, English suffocation, coma, headache, drowsiness, dizziness, fatique, irruguler heart beat 614 MSDS 614 IN Mobil DTE 10 Excel 15 MSDS-614-IN Mobil DTE 10 excel 15_indo.pdf Oli Hydrolic ExxonMobil Jika tertelan, mungkin diaspirasi dan Indonesia menyebabkan kerusakan paru-paru. Kontak yang berulang atau cukup lama bisa menimbulkan peluruhan lemak kulit serta membuat kulit kering, yang mengakibatkan ketidaknyamanan dan radang kulit . Mungkin mengiritasi mata, hidung, tenggorokan, dan paru-paru. Injeksi tekanan tinggi di bawah kulit bisa menimbulkan bahaya yang serius MSDS 614 EN Mobil DTE 10 Excel 15 MSDS-614-EN Mobil DTE 10 excel 15_english.pdf Hydrolic Oil ExxonMobil If swallowed, may be aspirated and cause English lung damage. Frequent or prolonged contact may defat and dry the skin, leading to discomfort and dermatitis. May be irritating to the eyes, nose, throat, and lungs. High-pressure injection under skin may cause serious damage. 615 MSDS 615 EN Jotatemp 650 - Marine_Protective - English (uk) - United Kingdom MSDS-615-EN Jotatemp 650 - Marine_Protective - English (uk) - United Kingdom.pdf Paints Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Highly flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 615 IN Jotatemp 650 - Marine_Protective - Indonesian (id) - Indonesia MSDS-615-IN Jotatemp 650 - Marine_Protective - Indonesian (id) - Indonesia.pdf Paints Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 616 MSDS 616 EN Jotun Thinner No. 17 - Marine_Protective - English (uk) - United KingdomMSDS-616-EN Jotun Thinner No. 17 - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Highly flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 616 IN Jotun Thinner No. 17 - Marine_Protective - Indonesian (id) - Indonesia MSDS-616-IN Jotun Thinner No. 17 - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Bahasa Produk ini terdaftar sebagai produk berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 617 MSDS 617 EN Penguard - Comp. B - Marine_Protective - English (uk) - United Kingdom MSDS-617-EN Penguard - Comp. B - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 617 IN Penguard - Comp. B - Marine_Protective - Indonesian (id) - Indonesia MSDS-617-IN Penguard - Comp. B - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 618 MSDS 618 EN Penguard FC - Comp. A - Marine_Protective - English (uk) - United King MSDS-618-EN Penguard FC - Comp. A - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 618 IN Penguard FC - Comp. A - Marine_Protective - Indonesian (id) - Indonesi MSDS-618-IN Penguard FC - Comp. A - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 619 MSDS 619 EN Penguard FC - Comp. B - Marine_Protective - English (uk) - United King MSDS-619-EN Penguard FC - Comp. B - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Flammable. Harmful by inhalation and in contact with skin. Irritating to skin. MSDS 619 IN Penguard FC - Comp. B - Marine_Protective - Indonesian (id) - Indonesi MSDS-619-IN Penguard FC - Comp. B - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Indonesia berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Mengiritasi kulit. 620 MSDS 620 EN Penguard Midcoat - Comp. B - Marine_Protective - English (uk) - United MSDS-620-EN Penguard Midcoat - Comp. B - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. Flammable. Harmful by inhalation. Risk of serious damage to eyes. Irritating to skin. May cause sensitisation by skin contact MSDS 620 IN Penguard Midcoat - Comp. B - Marine_Protective - Indonesian (id) - Indo MSDS-620-IN Penguard Midcoat - Comp. B - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan. Risiko kerusakan serius pada mata. Mengiritasi kulit. Dapat menyebabkan sensitisasi akibat terkena kulit 621 MSDS 621 EN Penguard Midcoat MIO - Comp. A - Marine_Protective - English (uk) - Un MSDS-621-EN Penguard Midcoat MIO - Comp. A - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 621 IN Penguard Midcoat MIO - Comp. A - Marine_Protective - Indonesian (id) - MSDS-621-IN Penguard Midcoat MIO - Comp. A - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 622 MSDS 622 EN Penguard Special - Comp. A - Marine_Protective - English (uk) - United MSDS-622-EN Penguard Special - Comp. A - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 622 IN Penguard Special - Comp. A - Marine_Protective - Indonesian (id) - Indo MSDS-622-IN Penguard Special - Comp. A - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 623 MSDS 623 EN Solvalitt - Marine_Protective - English (uk) - United Kingdom MSDS-623-EN Solvalitt - Marine_Protective - English (uk) - United Kingdom.pdf Coating Jotun The product is classified as dangerous English according to Directive 1999/45/EC and its amendments. flammable. Harmful: may cause lung damage if swallowed. Vapours may cause drowsiness and dizziness. Harmful to aquatic organisms, may cause long-term adverse effects in the aquatic environment MSDS 623 IN Solvalitt - Marine_Protective - Indonesian (id) - Indonesia MSDS-623-IN Solvalitt - Marine_Protective - Indonesian (id) - Indonesia.pdf Coating Jotun Produk ini terdaftar sebagai produk Bahasa berbahaya menurut Instruksi/Peraturan 1999/45/EC dan amandemennya. Mudah menyala. Berbahaya melalui penghirupan dan bila terkena kulit. Berbahaya bagi organisme air, dapat menyebabkan efek buruk jangka-panjang pada lingkungan air. 624 MSDS 624 IN Castrol Aircol PD 100-INA MSDS-624-IN Castrol Aircol PD 100-INA.pdf Pelumas Compressor Castrol Liquid Tidak diketahui efek signifikan atau bahaya Bahasa – bahaya kritis 625 MSDS 625 IN Castrol Alpha SP 68-INA MSDS-625-IN Castrol Alpha SP 68-INA.pdf Pelumas Roda Gigi Castrol Liquid Tidak diketahui efek signifikan atau bahaya Bahasa – bahaya kritis 626 MSDS 626 IN Castrol Hyspin AWH-M 46 Ina MSDS-626-IN Castrol Hyspin AWH-M 46 Ina.pdf Pelumas Hydrolik Castrol Liquid Tidak diketahui efek signifikan atau bahaya Bahasa – bahaya kritis 627 MSDS 627 IN Castrol MHP 154 Ina MSDS-627-IN Castrol MHP 154 Ina.pdf Pelumas Mesin Castrol Liquid Tidak diketahui efek signifikan atau bahaya Bahasa – bahaya kritis 628 MSDS 628 IN Castrol Tection Global 15W-40 Ina MSDS-628-IN Castrol Tection Global 15W-40 Ina.pdf Pelumas Mesin Castrol Liquid Menyebabkan iritasi kulit ringan. Bahasa Menyebabkan iritasi serius pada mata. 629 MSDS 629 EN ACTIVATED METHYLDIETHANOLAMINE 03-EN MSDS-629-EN ACTIVATED METHYLDIETHANOLAMINE 03-EN.pdf BASF Liquid Causes serious eye damage. May cause English allergy or asthma symptoms or breathing difficulties if inhaled. May cause an allergic skin reaction. Suspected of damaging fertility. Suspected of damaging the unborn child. MSDS 629 IN ACTIVATED METHYLDIETHANOLAMINE 03-IN MSDS-629-IN ACTIVATED METHYLDIETHANOLAMINE 03-IN.pdf BASF Liquid Menyebabkan kerusakan mata yang serius. Indonesia Dapat menyebabkan alergi atau gejala asma atau kesulitan bernapas jika terhirup. Dapat menyebabkan reaksi alergi pada kulit. Dicurigai merusak kesuburan. Dicurigai merusak janin. 630 MSDS 630 EN AmdeaEnriched_EN MSDS-630-EN AmdeaEnriched_EN.pdf BASF Liquid Causes serious eye damage. May cause English allergy or asthma symptoms or breathing difficulties if inhaled. May cause an allergic skin reaction. Suspected of damaging fertility. Suspected of damaging the unborn child. MSDS 630 IN AmdeaEnriched_IN MSDS-630-IN AmdeaEnriched_IN.pdf BASF Liquid Menyebabkan luka bakar pada kulit dan Bahasa kerusakan mata. Dapat menyebabkan alergi atau gejala asma atau kesulitan bernapas jika terhirup. Dapat menyebabkan reaksi alergi pada kulit. Dicurigai merusak kesuburan. Dicurigai merusak janin. 631 MSDS 631 EN M-74 MSDS-631-EN M-74.pdf Membrane Cleaning Compound Metito Liquid Non-Hazardous English

MSDS 631 IN M-74 IND MSDS-631-IN M-74 IND.pdf Pembersih membran Metito Liquid Tidak diketahui efek signifikan atau bahaya English – bahaya kritis 632 MSDS 632 EN M-75 MSDS-632-EN M-75.pdf Membrane cleaning compound to Metito Liquid Harmful in contact with skin and eyes and if English combat organic swallowed MSDS 632 IN M-75 in Bahasa MSDS-632-IN M-75 in Bahasa .pdf Pembersih Membran Metito Liquid Berbahaya apabila tertelan, terjadi kontak Bahasa dengan kulit atau mata 633 MSDS 633 EN M-77 MSDS-633-EN M-77.pdf Membrane cleaning compound Metito Liquid Non-Hazardous English

MSDS 633 IN M-77 in Bahasa MSDS-633-IN M-77 in Bahasa.pdf Pembersih membran Metito Liquid Tidak diketahui efek signifikan atau bahaya English – bahaya kritis 634 MSDS 634 EN Sodium Hypochlorite MSDS-634-EN Sodium Hypochlorite.pdf Disinfectant Metito Liquid Sodium Hypochlorite NaOCl Keep out of reach of children. Do not English breathe vapour/spray Avoid contact with skin and eyes In case of contact with sin or eyes rinse immediately with plenty of clean water and seek medical advice. 635 MSDS 635 EN SODIUM HYDROXIDE Flake MSDS-635-EN SODIUM HYDROXIDE Flake.pdf Alkalinity Builder Metito Liquid CAUSTIC SODA CAUSTIC SODA NaOH Avoid contact with skin and eyes English Wear suitable protective clothing, gloves and eye/face protection After contact with skin, wash immediately with plenty of water In case of contact with eyes, rinse MSDS 635 IN SODIUM HYDROXIDE Flake in Bahasa MSDS-635-IN SODIUM HYDROXIDE Flake in Bahasa.pdf Peningkat Alkalinitas Metito Liquid CAUSTIC SODA CAUSTIC SODA NaOH Berpotensi menyebabkan luka bakar Indonesia Hindari terjadi kontak mata atau kulit Wear Gunakan selalu Alat Pelindung Diri Jika terjadi kontak kulit, siram dengan air yang banyak Jika terjadi kontak mata basuh segera 636 MSDS 636 EN SODIUM METABISULPHITE MSDS-636-EN SODIUM METABISULPHITE.pdf Dechlorination Metito Liquid SODIUM BISULPHITE Non-Hazardous English

MSDS 636 IN sodium metabisulfite MSDS-636-IN Sodium Metabisulphite in Bahasa.pdf Deklorinasi Metito Liquid Sodium Metabisulphite Berbahaya jika tertelan. Bahasa Iritasi pada mata. Iritasi pada kulit– dapat menyebabkan alergi. Iritasi pada saluran nafas jika terhirup.

637 MSDS 637 EN HCl 32% MSDS-637-EN HCl 32%.pdf pH Adjuster Metito Liquid Hydrochloric Acid, HCl HCL Keep out of reach of children. English MSDS 637 IN HCl 32% in Bahasa MSDS-637-IN HCl 32% in Bahasa.pdf Peningkat pH Metito Liquid Hydrochloric Acid, HCl HCL Jauhkan dari jangkauan anak-anak Bahasa

638 MSDS 638 IN S-1224 MSDS-638-IN S-1224 B.Indo.pdf Biocide & Corrosion Inhibitor for Starborn Liquid Tetrakis Hydroxymethyl Phosphonium Sulphate 55566-30-8 10 - 30% Bahan dapat Menghirup uap atau kabut Bahan berbahaya jika Efek iritasi kulit dapat Operation Corrosive dan Irritant Bahasa Condensate Tank menyebabkan sebagai bisa menyebabkan tertelan ditunda selama beberapa berikut: kerusakan sebagai berikut: iritasi jam. Bahan ini berbahaya permanen pada mata kuat untuk hidung, jika terserap melalui kulit. tenggorokan dan paru- Bahan dapat paru. menyebabkan sebagai 639 MSDS 639 IN Starborn - NaOH MSDS-639-IN NaOH B.Indo.pdf Alkaline source and cleaning Starborn Liquid NaOH Operation Marcelinus Haryanto 62-811-103739 Mengiritasi, berbahaya Bahasa booster

640 MSDS 640 IN Starborn - Methanol MSDS-640-IN Methanol B.Indo.pdf Starborn Liquid Methanol 98% Operation Marcelinus Haryanto 62-811103739 dapat menyebabkan kerusakan dalam Bahasa jangka lama jika tertelan. Mudah terbakar, jika melebihi titik nyala

641 MSDS 641 IN Starborn - Sodium Metabisulfite MSDS-641-IN Sodium metabisulfite B.Indo.pdf Oxygen Scavenger Starborn Powder Sodium Metabisulfite 90-100% Korosif, akan Berbahaya jika terhirup. Bukan jalur paparan. Menyebabkan iritasi pada Operation Marcelinus Haryanto 62-811103739 Korosif terhadap kulit, korosif terhadap Bahasa menyebabkan iritasi Aerosol atau kabut yang Berbahaya jika ditelan. kulit mata,uap, gas, kabut dan aerosol dapat beracun karena oksigen Pastikan menyebabkan iritasi terhadap saluran kimia bersaing penderita/korban pernapasan bagian atas. Jangan mendapatkan oksigen bernapas selama kabut, dapat menyebabkan kekurangan oksigen 642 MSDS 642 EN Temik 15G MSDS-642-EN Temik 15G.pdf Rentokil Granule Aldicarb 212 C7H14N2O2S 116-06-3 0.07 mg/m3 strong bases may causes redness, may fatal if swallowed fatal if swallowed harmful or fatal if HSE English irritation, tearing. absorbed through the skin.

642 MSDS 643 EN Albumin Cobas c111 MSDS-643-EN Albumin Cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. Note: slightly hazardous to water and 643 MSDS 644 EN ALTL cobas c111 MSDS-644-EN ALTL cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. Note: slightly hazardous to water and 644 MSDS 645 EN ASTL cobas c111 MSDS-645-EN ASTL cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. Note: slightly hazardous to water and ground

645 MSDS 646 EN Bilirubin Direct cobas c111 MSDS-646-EN Bilirubin Direct cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. Note: slightly hazardous to water and ground

646 MSDS 647 EN Cfas (Calibrator For Auto System) MSDS-647-EN Cfas (Calibrator For Auto System).pdf Risk advice to man and the environment English According to the documentation available is not a hazardous substance/preparation within the meaning of the EEC directive 67/548 and 99/45. 647 MSDS 648 EN Cfas Lipid MSDS-648-EN Cfas Lipid.pdf Risk advice to man and the environment English : Is to be classified according to EEC directive 67/548 and 99/45 as hazardous.The usual hygienic measures taken when handling biological materials 648 MSDS 649 EN Cholesterin cobas c111 MSDS-649-EN Cholesterin cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 649 MSDS 650 EN CK-MB cobas c111 MSDS-650-EN CK-MB cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 650 MSDS 651 EN cobas Integra Cleaner MSDS-651-EN cobas Integra Cleaner.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 651 MSDS 652 EN Creatinin cobas c111 MSDS-652-EN Creatinin cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 652 MSDS 653 EN Diluent (NaCl 9%) MSDS-653-EN Diluent (NaCl 9%).pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 653 MSDS 654 EN GGT cobas c111 MSDS-654-EN GGT cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 654 MSDS 655 EN Glucose 400T cobas c111 MSDS-655-EN Glucose 400T cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 655 MSDS 656 EN HDL-C PLUS cobas c111 MSDS-656-EN HDL-C PLUS cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 656 MSDS 657 EN ISE Deproteineizer MSDS-657-EN ISE Deproteineizer.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 657 MSDS 658 EN LDL-C cobas c111 MSDS-658-EN LDL-C cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 658 MSDS 659 EN Precinorm U MSDS-659-EN Precinorm U.pdf Risk advice to man and the environment: English According to the documentation available is not a hazardous substance/preparation within the meaning of the EEC directive 67/548 and 99/45 . 659 MSDS 660 EN Precipath U MSDS-660-EN Precipath U.pdf Risk advice to man and the environment English According to the documentation available is not a hazardous substance/preparation within the meaning of the EEC directive 67/548 and 99/45 . 660 MSDS 661 EN TG cobas c111 MSDS-661-EN TG cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 661 MSDS 662 EN Total Bilirubin cobas c111 MSDS-662-EN Total Bilirubin cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 662 MSDS 663 EN UA Plus cobas c111 MSDS-663-EN UA Plus cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed. 663 MSDS 664 EN Urea cobas c111 MSDS-664-EN Urea cobas c111.pdf Risk advice to man and the environment English : There is at present no information or indication of hazardous properties. The usual precautions taken when handling chemicals should be observed.

Critical Habitat Assessment and Biodiversity Action Plan

Tangguh Expansion Project

October 2016

Contents

Tables

Figures

1 Introduction

1.1 Project Background

Figure 1 í Project location

1.2 Rationale for this Report

1.3 General Approach

Table 1 í Key Definitions and Abbreviations

Term Definition

≥

1.4 Project Description

1.4.1 History of the Tangguh Train 1 and 2 and TEP

Figure 2 í Project timeline

1.4.2 Tangguh Expansion Project • • • • • • • • • • • • • •

Figure 3 í Existing and planned project layout

Figure 4 í Offshore Development Plan Showing Existing and Planned Platforms for TEP Initial Phase

Figure 5 í Tentative plot plan of onshore and nearshore facilities

1.4.3 Alternatives • • • •

• •

1.5 Structure of this Document

Figure 6 í Structure of this document

2 Scope and Objectives

2.1 Project Scope

2.2 Scope of this Report • • • • no project activity will be implemented in areas of critical habitat unless the following requirements are met: (i) There are no measurable adverse impacts, or likelihood of such, on the critical habitat which could impair its high biodiversity value or the ability to function. (ii) The project is not anticipated to lead to a reduction in the population of any recognized endangered or critically endangered species or a loss in area of the habitat concerned such that the persistence of a viable and representative host ecosystem be compromised. (iii) Any lesser impacts are mitigated.

2.3 Aim and Objectives

Figure 7 í Applying the Mitigation Hierarchy to achieve No Net Loss

2.3.1 Application of the Mitigation Hierarchy • Avoidance • Minimization • Restoration • Offsets

Figure 8 í The Four Key Actions in the Mitigation Hierarchy

2.3.2 Development of the Biodiversity Action Plan • • • •

3 Policy and Regulatory Framework

3.1 International Conventions • • • •

3.2 National Legislative and Policy Framework • • • • • •

3.2.1 Environmental Law • • • •

3.2.2 Environmental Impact Assessment Legislation

• • • • • • • • • • • •

3.2.3 Conservation and Forestry Laws • • • • adat • •

Hutan Produksi •

3.2.4 Marine and Fisheries Laws

3.2.5 Species Protection and Trade • • • • • • • • Pritis • • • • • •

3.2.6 Biodiversity and Species Action Plans • • • •

3.3 ADB Safeguard Policy Statement • • •

• • •

3.4 IFC Performance Standards • • • •

4 Biodiversity Baseline

4.1 Methodology

4.1.1 Study Area • • et al.

Figure 9 í Study area

4.1.2 Desktop Information • • • • • • • • •

4.1.3 Field Surveys

Table 2 í List of biodiversity surveys commissioned by Tangguh

Abbreviated name1 Full title Period of survey

4.1.4 Sensitivity Mapping

4.1.5 Stakeholder Engagement on Biodiversity Values

4.2 Environmental Setting

4.2.1 Physiography

Figure 10 í Geographical Features within the Study Area

4.2.2 Main Habitats NypaMetroxylon Lowland forest Agathis Calophyllum inophyllumEugenia malaccensis AgathisCalophyllum Calamus Intsia bijuga Calophyllum inophyllum Macaranga Pometia pinnata Dendrocalamus

Figure 11 í Photos of main habitat types

Savannah BaeckiaKeraudreniaMelaleucaXyris EucalyptusChenopodium Meulaleuca leucodedendronChenopodium Melastoma malabatricum LycopodiumDigitaria Eragrostis Fimbristylis Kyllinga Cyperus Melastoma Lindernia Nephrolepis sp. Imperata cylindrica Nepenthes MelaleucaCasuarinaEucalyptus Beach Forest Ipomoea pescaprae Hibiscus tiliaceus Pometia pinnata, Inocarpus Mangifera Alstonia scholaris Cerberra odollam Ficus Pometia pinnataCalophyllum inophyllumAlstonia scholaris Eugenia malaccensis Pandanus tectorius Calamus Calophyllum soulatri Fresh Water Nypa-Metroxylon Palm Swamp Forest Nypa Nypa Nypa fruticans Nypa Avicennia-Rhizophora- Bruguiera-Sonneratia NypaMetroxylon Nypa Metroxylon sagu NypaBuchanania Gluta Terminalia catappa Sapium Myristica argentea Mangrove Avicennia Bruguiera, Rhizophora, Sonneratia, Xylocarpus Rhizophora mucronata R. apiculata Bruguiera gymnoriza Bruguiera parviflora Xylocarpus Ceriops tagal Avicennia officinalis Acanthus ebracteatus Acanthus ilicifolius Aegiceras corniculatum Avicennia intermedia. Nypa fructicans

Berau / Bintuni Bay

4.2.3 Species of Conservation Concern • • •

Flora

Table 3 - Species of flora of conservation concern

Name Conservation status Latin Common name Endemic IUCN1 Legal protection2 Calophyllum insularum Nepenthes ampullaria Nepenthes mirabilis Grammatophyllum speciosum Grammatophyllum pantherinum Bryobium Bulbophyllum Bulbophyllum Bulbophyllum Bulbophyllum Bulbophyllum Robiquieta Dendrobium Flindersia pimenteliana Myristica inaequalis Livistona Glochidion daviesii burnettii Freycinetia bomberaiensis

Birds

Table 4 í Bird species of conservation concern

Name Conservation status Latin Common name Congregatory / Endemic IUCN1 Legal migratory protection2 species Accipiter poliocephalus Alcedo azurea Alcedo pusilla Aquila gurneyi Ardea alba Aviceda subcristata Cacatua galerita Calidris tenuirostris Casuarius casuarius Casuarius unappendiculatus Chalcopsitta atra Charmosyna placentis Chlamydera cerviniventris Chlidonias hybridus Chlidonias leucopterus Clytoceyx rex Dacelo gaudichaud Dacelo leachii Dicaeum pectorale Eclectus roratus Egretta alba

Name Conservation status Latin Common name Congregatory / Endemic IUCN1 Legal migratory protection2 species Egretta garzetta Egretta novaehollandiae Egretta picata Goura cristata Halcyon chloris Haliaeetus leucogaster Haliastur indus Haliastur sphenurus Henicopernis longicauda Megapodius freycinet Megapodius rainwardt Meliphaga montana Mesophoyx (Ardea) intermedia Myzomela eques Myzomela nigrita Myzomela obscura Nectarinia aspasia Nectarinia jugularis Nycticorax caledonicus Pandion haliaetus Paradisaea minor Paradisaea raggiana Philemon buceroides Philemon corniculatus Pitta erythrogaster Pitta sordida Probosciger aterrimus Ptilinopus ornatus Pycnopygius cinereus Rhyticeros plicatus Sterna bergii

Name Conservation status Latin Common name Congregatory / Endemic IUCN1 Legal migratory protection2 species Sterna fuscata Sterna hirundo Syma torotoro Talegalla cuvieri Talegalla fuscirostris Tanysiptera galatea Tanysiptera nympha Todiramphus chloris Todiramphus macleayii Todiramphus sanctus Mammals

Table 5 í Mammal species of conservation concern

Name Conservation status Latin Common name Endemic IUCN1 Legal protection2 Balaenoptera edeni4 Cervus timorensis3 Dendrolagus inustus Dendrolagus ursinus Dorcopsis muelleri Megaptera novaeangliae4 Nyctimene draconilla Sousa chinensis chinensis Spilocuscus (Phalanger) maculatus Stenella attenuata4 Stenella longirostris4 Strigocuscus (Phalanger) gymnotis Tursiops aduncus4

Cervus timorensisRusa timorensis Reptiles and Amphibians

Table 6 í Herpetofauna species of conservation concern

Name Conservation status Latin Common name Endemic IUCN1 Legal protection2 Caretta caretta Carlia bomberai Chelonia mydas Cophixalius sp. nov. Crocodylus novaeguineae Crocodylus porosus Dermochelys coriacea Elseya novaeguineae Emoia sp. nov. Eretmochelys imbricata Hylophorbus sp. nov. Hypsilurus dilophus Lepidochelys olivacea Morelia viridis Platymantis punctatus Tiliqua gigas Varanus indicus

Fish

Table 7 í Fish species of conservation concern

Name Conservation status Latin Common name Endemic IUCN1 Legal protection2 Melanotaenia irianjaya Melanotaenia arfakensis Pseudomugil reticulatus

Invertebrates and Algae Cantharellus noumeaeIsopora togianensis Cantharellus Isopora togianensis

4.2.4 Ecosystem Services • • • •

Metroxylon

4.2.5 National and International Protected Areas Bintuni Bay Nature Reserve Nypa fruticans

Gunung Wagura Kote Nature Reserve International Protected Areas

Figure 12 í Location of proposed protected areas

4.2.6 Other Nature Conservation Areas • • • • Key Biodiversity Areas et al., Important Bird and Biodiversity Areas Alliance for Zero Extinction Sites et al., Biodiversity hotspots, WWF Global Ecoregions and Endemic Bird Areas (EBA) et al. et al., 2011 large unit of land or water containing a geographically distinct assemblage of species, natural communities, and environmental conditions • •

5 Critical Habitat Assessment

5.1 Methodology

5.1.1 Criteria for assessment • • • • • • •

5.1.2 Critical Habitat Assessment approach et al,

Table 8 - Quantitative Thresholds Tiers 1 and 2 of Critical Habitat Criteria 1 to 3

Criteria Tier 1 Tier 2 ≥ ≥ ≥ ≥ ≥ ≥

Table 9 í DMU areal coverage estimates

Habitat type Area of coverage

Figure 13 í Discrete Management Units for terrestrial and estuarine habitats

5.2 Assessment of Critical Habitats

5.2.1 Criterion 1: Critically endangered or endangered species Calophyllum insularum í IUCN Endangered and endemic Calophyllum insularum Calophyllum Calophyllum inophyllum Calophyllum soulattri Calophyllum insularum

Calophyllum insularumqualifies as Tier 2 Critical Habitat Pitcher plants Nepenthes ampullaria and Nepenthes mirabilis í IUCN Least Concern and Nationally Protected Nepenthes Nepenthes ampullaria Nepenthes mirabilis Nepenthes mirabilis N. ampullaria Nepenthes ampullaria Nepenthes mirabilis N. mirabilis do not qualify Orchids Grammatophyllum speciosum and Grammatophyllum pantherinum í IUCN Not Evaluated and Nationally Protected Grammatophyllum speciosum Grammatophyllum pantherinumG. papuanum do not qualify Flindersia pimenteliana ímaple silkwood í IUCN Endangered Flindersia pimenteliana Flindersia laevicarpa Flindersia Flindersia pimenteliana does not qualify Livistona sp í Fan Palm í IUCN Not Evaluated, Endemic and Nationally Protected Livistona Livistona does qualify under Tier 2

Humpback dolphin Sousa chinensis chinensis í IUCN Near Threatened & Nationally Protected S.c.chinensis does qualify under Tier 2 Grizzled Tree Kangaroo Dendrolagus inustus í IUCN Vulnerable & Nationally Protected does not qualify Zaglossus bruijnii Great Knot Calidris tenuirostris - IUCN Endangered et al.,

does qualify under Tier 2 Southern Cassowary Casuarius casuarius - IUCN Vulnerable) & Northern cassowary Casuarius unappendiculatus - IUCN Vulnerable & Nationally Protected does qualify under Tier 2 does not qualify Sea Turtles (Green turtle Chelonia mydas í IUCN Endangered; Loggerhead turtle Caretta caretta í IUCN Vulnerable; Hawksbill turtle Eretmochelys imbricate í IUCN Critically Endangered; Olive Ridley turtle Lepidochelys olivacea í IUCN Vulnerable; Leatherback turtle Dermochelys coriacea í IUCN Vulnerable) Loggerhead TurtleHawksbill Turtle Olive Ridley Turtle qualify under Tier 2

Green turtle and Leatherback Turtledo not qualify,

5.2.2 Criterion 2: Endemic or restricted range species . Orchids of genera Bryobium, Bulbophyllum, Robiquieta, Dendrobium - Endemic et al., Dendrobium Dendrobium Dendrobium do qualify Myristica inaequalis í IUCN Vulnerable and Endemic Myristica inaequalis Myristica Myristica fatua Myristica lancifolia Myristica inaequalisdoes qualify as Tier 2 Glochidion daviesii, Scaevola burnettii and Freycinetia bomberaiensis í IUCN Not Evaluated and Endemic Glochidion daviesii Glochidion daviesii G. daviessi Scaevola burnettii Freycinetia bomberaiensis qualify for Tier 2 Black lory Chalcopsitta atra - Restricted Range does not qualify under Tier 2

Olive-crowned Flowerpecker Dicaeum pectoral í Restricted Range does not qualify under Tier 2 Western Crowned-pigeon Goura cristata í Restricted Range, IUCN Vulnerable & Nationally Protected does qualify under Tier 2 Dusky Scrubfowl Megapodius freycinet í Restricted Range & Nationally Protected does qualify under Tier 2 Western Ornate Fruit-dove Ptilinopus ornatus í Restricted Range species does not qualify

Red-billed Brush-Turkey Talegalla cuvieri í Restricted Range & Nationally Protected does qualify under Tier 2 Forest Honeyeater Meliphaga montana í Restricted Range & Nationally Protected does not qualify Marbled honeyeater Pycnopygius cinereus í Restricted Range & Nationally Protected does not qualify Cekakak Pita Tanysiptera nympha í Restricted Range & Nationally Protected does not qualify Lesser Tube-nosed Bat Nyctimene draconilla í Restricted Range & IUCN Data Deficient

N. draconilla is Nyctimene albiventerN.albiventer does qualify under Tier 2 Vogelkop Tree-Kangeroo Dendrolagus ursinus í Restricted Range & IUCN Vulnerable et al. ( does not qualify Brown Dorcopsis Dorcopsis muelleri í Restricted Range & Nationally Protected does not qualify Four-fingered skink Carlia bombarai í Restricted Range does qualify under Tier 2 Nursery frog Cophixalus sp. nov., Mawatta frog Hylophorbus sp. nov & Skink Emoia sp. nov í Restricted Range & New Species Cophixalus Hylophorbus Emoia Emoia qualify under Tier 1 Papua wrinkled frog Platymantis (Cornufer) punctatus í Restricted Range does not qualify Melanotaenia irianjaya Irian Jaya Rainbow Fish í Endemic; Melanotaenia arfakensis Arfak Rainbow Fish í IUCN Vulnerable í Endemic & Pseudomugil reticulatus Vogelkop Blue-Eye - Endemic M. irianjayaP. reticulatus M. arfakensis M. irianjaya. Melanotaenia irianjaya Pseudomugil reticulatus, Melanotaenia irianjaya Pseudomugil reticulatus not to qualify

5.2.3 Criterion 3: Migratory or congregatory species Great White Egret Ardea alba & Little Egret Egretta garzetta

et al. et al. do not qualify Species of Sternidae Chlidonias hybridus, Chlidonias leucopterus, Sterna bergii, Sterna fuscata, and Sterna hirundo. Sterna bergiiSterna fuscata Sterna hirundo, et al do not qualify

5.2.4 Criterion 4: Unique species assemblages associated with key evolutionary processes or providing key ecosystem services • •

Nypa Metroxylon

5.2.5 Criterion 5: Biodiversity of significant social, economic, or cultural importance to local communities • • • • • • • •

priority ecosystem service

5.2.6 Criterion 6: Protected areas or proposed for protection. • • doesqualify does not qualify

5.2.7 Criterion 7: Highly threatened and/or unique ecosystems

not qualify

Table 10 - Forest ecosystem cover in West Papua in 2011 (GCF, 2013)

Forest type Condition and area Total Primary Secondary et alet al

5.3 Priority Biodiversity Features

5.3.1 Priority Species and Associated Habitats

Table 11 í Stages for the Identification of Tier 1 & Tier 2 Critical Habitat Assessment Species

Stage in the Number and species assessed assessment

Cophixalus sp. nov. (Restricted Range) Hylophorbus sp. nov Emoia sp. nov

Calophyllum insularum Livistona sp Bryobium, Bulbophyllum, Robiquieta Dendrobium Myristica inaequalis Glochidion daviesii Scaevola burnettii Freycinetia bomberaiensis Calidris tenuirostris Nyctimene draconilla Sousa chinensis chinensis Eretmochelys imbricate Lepidochelys olivacea ( Caretta caretta Carlia bombarai Megapodius freycinet Goura cristata Talegalla cuvieri Casuarius unappendiculatus

• Megapodius freycinetGoura cristataLivistonia • Nyctimene draconilla, Casuarius unappendicultus Talegalla cuvieri Calophyllum insularum Myristica inaequalis • Eretmochelys imbricate Lepidochelys olivacea, Caretta carettaSousa chinensis chinensis

5.3.2 Priority Ecosystem Services

5.3.3 Priority Protected Areas

6 Impact Assessment and Mitigation

6.1 Impact Evaluation • • • • • • • • • •

Table 12 í Overview of significant impacts (AMDAL, 2014)

Receptor Development Phase1 Description of Impact Source of Impact Construction phase Operations Phase

Figure 14 í Map of project infrastructure

6.2 Evaluation of Impacts on Priority Species and Associated Habitats

6.2.1 Discharge of drilling mud / cuttings Sousa chinensis Eretmochelys imbricateLepidochelys olivacea Caretta caretta • • • •

6.2.2 Foreshore development, dredging and dredge disposal Sousa chinensis Eretmochelys imbricateLepidochelys olivacea Caretta caretta

6.2.3 Operational discharge of effluents Sousa chinensis Eretmochelys imbricate Lepidochelys olivacea Caretta caretta Sousa chinensis et al., • • • • 6.2.4 Presence of offshore platforms Sousa chinensis Eretmochelys imbricate Lepidochelys olivacea Caretta caretta

6.2.5 Sea transportation (including LNG tanker traffic) Sousa chinensis Eretmochelys imbricate Lepidochelys olivacea Caretta caretta Sousa chinensis et al. • • •

• •

6.2.6 Underwater sound Sousa chinensis Eretmochelys imbricate Lepidochelys olivacea Caretta caretta et al. Sousa chinensis • • o o o • o o o • •

6.2.7 Land clearance • Calophyllum insularum Livistona Myristica inaequalisGlochidion daviessiScaevola burnettiFreycinetia bomberaensis

• Cophixalussp. novHylophorbus sp. novEmoia sp. novCarlia bombarai • • • • • • • • Calophyllum insularum Livistona Myristica inaequalis Freycinetia bomberaensis, Cophixalus sp. nov., Hylophorbus sp. nov., Emoia sp. nov., Carlia bombarai, • Scaevola burnetti • • •

6.2.8 Noise and visual disturbance • Cophixalus sp. nov., Hylophorbus sp. nov., Emoia sp. nov Carlia bombarai Eretmochelys imbricate Lepidochelys olivacea Caretta caretta • •

Calidris tenuirostris

• • • • • • •

6.2.9 Invasive species • Calophyllum insularum, Livistona sp., Myristica inaequalis, , Glochidion daviessi, Scaevola burnetti, Freycinetia bomberaensis • Cophixalus sp. nov., Hylophorbus sp. nov., Emoia sp. nov.Carlia bombarai • Phrynoidis (Bufo) aspera • • • • • • • •

6.2.10 Spills of hazardous material, including hydrocarbon and chemicals • • • • • •

• • • • • • • • •

6.3 Evaluation of Impacts on Ecosystem Services • • • •

6.3.1 Evaluation of impact • • • • • • • • •

6.4 Evaluation of Impacts on Protected Areas • • • •

6.4.1 Evaluation of impact

• • • •

6.5 Strategy for Additional Mitigations • •

6.5.1 Generic measures • • •

• •

6.5.2 Avoidance • • Scaevola •

6.5.3 Minimization • • • • • • o o • • • • •

6.5.4 Restoration • • Calophyllum insularum Livistona Myristica inaequalis Glochidion daviesii Freycinetia bomberaiensis •

6.5.5 Offsets (Replacement of Forest Area) •

6.5.6 Additional Conservation Actions • • •

6.5.7 Monitoring • • • •

•

6.6 Impacts on Priority Habitats

Table 13 í Habitat loss1 in Project Area

Habitat areas Area to be Area to be Total area of Total area Total area being cleared revegetated habitat cleared as lost as impacted (Ha) (Ha) being lost percentage of percentage of the habitat in the habitat in the DMU the DMU

Total habitat 164 91 73 0.30% 0.31% areas (56% of total (44%) area)

Built areas being impacted

Total project 219 91 71 - - footprint

6.7 Impacts on Priority Species

6.7.1 Plants Calophyllum insularum (Endangered and Endemic)

no reduction in the population Fan PalmLivistona sp (Endemic and Nationally Protected) no adverse impact Orchid species of genus Bryobium, Bulbophyllum, Robiquieta and Dendrobium (Endemic) et al., no adverse impact Myristica inaequalis (Endemic) no adverse impact Glochidion daviesii (Endemic), Scaevola burnettii (Endemic) and Freycinetia bomberaiensis (Endemic) Scaevola burnetti no adverse impact

6.7.2 Mammals Lesser Tube-nosed Bat Nyctimene draconilla (Restricted Range) et al no adverse impact Humpback dolphin Sousa chinensis chinensis2 (Nationally Protected and Near Threatened) S.chinensis no adverse impact

6.7.3 Birds Great Knot Calidris tenuirostris (Endangered and Migratory) no adverse impact Dusky Scrubfowl Megapodius freycinet (Restricted Range and Nationally Protected) no adverse impact

Sousa sahulensis

Western Crowned-pigeon Goura cristata (Restricted Range, Vulnerable and Nationally Protected) no adverse impact Red-billed Brush-Turkey Talegalla cuvieri (Restricted Range and Nationally Protected) no adverse impact Northern Cassowary Casuarius unappendiculatus (Nationally Protected and Vulnerable) , no adverse impact

6.7.4 Amphibians and reptiles Nursery frog Cophixalus sp. nov. and Mawatta frogs Hylophorbus sp. nov. (Restricted Range) Cophixalus et al., no long-term adverse impact Skink Emoia sp. nov. (Restricted Range)

no long-term adverse impact Four-fingered skink Carlia bombarai (Restricted Range) no adverse impact Hawksbill turtle Eretmochelys imbricate (Nationally Protected and Critically Endangered) Olive Ridley turtle Lepidochelys olivacea (Nationally Protected and Vulnerable) and Loggerhead turtle Caretta caretta (Nationally Protected and Vulnerable) no adverse impacts

6.8 Summary

Table 14 í Critical Habitats and associated species

Critical Habitat Critical habitat triggering species Lowland forest • Calophyllum insularum • Myristica inaequalis, • Glochidion daviessi • Freycinetia bomberaiensis • • Talegalla cuvieri • Casuarius unappendicultus • Nyctimene draconilla, • Carlia bombarai • Emoia sp. nov • Cophixalus sp. nov • Hylophorbus Swamp forest • Livistonia • Megapodius freycinet • Goura cristata • Nyctimene draconilla Estuary • Calidris tenuirostris • Eretmochelys imbricate • Lepidochelys olivacea • Caretta caretta • Sousa chinensis chinensis

• • • • • • • • •

7 Tangguh Biodiversity Action Plan

7.1 Overview

7.1.1 BAP Objectives • • • •

7.1.2 Priority species and associated habitats Plants 1. Calophyllum insularum Livistona sp. Bryobium, Bulbophyllum, Robiquieta, Dendrobium 4. Myristica inaequalis 5. Glochidion daviesii 6. Scaevola burnettii 7. Freycinetia bomberaiensis

Mammals Nyctimene draconilla Sousa chinensis chinensis Birds Megapodius freycinet Goura cristata Talegalla cuvieri Casuarius unappendiculatus Amphibians and Reptiles Cophixalus sp. nov. Hylophorbus sp. nov Emoia sp. nov. Carlia bombarai Eretmochelys imbricate Lepidochelys olivacea Caretta caretta

7.1.3 Further surveys and assessments • Cophixalus Hylophorbus Emoia. • Nyctimene draconilla

7.2 External Engagement and consultation

• •

7.3 Activity Plans

Table 15 - Summary of existing and new documents

No. Reference Document Status

7.3.1 Land Clearance Activities • •

Table 16 - Management of land clearance

Components Main Activities Selected Milestones (Targets)

Related plans and specifications:

Performance Indicators:

7.3.2 Re-vegetation Activities • •

Table 17 - Management of re-vegetation

Components Main Activities Selected Milestones (Targets)

Related plans and requirements:

Performance Indicators:

7.3.3 Noise and Visual Disturbance Activities • • Sousa chinensis chinensis • Eretmochelys imbricate • Lepidochelys olivacea • Caretta caretta

Table 18 - Management of noise and visual disturbance

Components Main Activities Selected Milestones (Targets)

Related plans and specifications:

Performance Indicators:

7.3.4 Management of Invasive Species • •

Table 19 - Management of Invasive Species

Component Main Activities Selected Milestones (Targets)

Related plans and requirements: Performance Indicators:

7.3.5 Offset agreement (Replacement of Forest Area)

Figure 15 í One of the Proposed Offset Areas (1,320Ha)

7.3.6 Environmental awareness activities • •

Table 20 í Environmental awareness building

Components Main Activities Selected Milestones (Targets)

Related plans and requirements:

Performance Indicators

7.4 Role and responsibilities

7.4.1 Construction phase VP Project • • • • Project Managers • • • • Project HSSE Manager • • • • • •

Environmental Team Leader • • • • • • Environmental Advisor • • • • • • Forestry Specialist • • • • •

Project Ecologist • • • • •

7.4.2 Operation phase

7.5 Monitoring, evaluation and reporting • •

7.5.1 Monitoring During Construction

Land Clearing Activities • • • • • Noise and Vibration • • • Dredging Activity • • • • Marine Mammal Monitoring • • Flora and Fauna Monitoring •

• Social Monitoring • • •

7.5.2 Monitoring during Operation • •

7.5.3 Reporting • • •

8 References

Melanotaenia arfakensis Ardea alba & Egretta garzetta Chalcopsitta atra Tanysiptera nympha Meliphaga montana Casuarius casuarius Casuarius unappendiculatus Goura cristata

Nepenthes ampullaria Nepenthes mirabilis Bruguiera hainesii Calophyllum insularum. Flindersia pimenteliana

Sousa chinensis Platymantis Freycineti . .

Platymantis (Cornufer) punctatus Dorcopsis muelleri Dendrolagus inustus Sousa chinensis chinensis Nyctimene draconilla Dendrolagus ursinus Dicaeum pectoral Megapodius freycinet Ptilinopus ornatus Carlia bombarai Talegalla cuvieri Pseudomugil reticulatus ,

Megapodius freycinet Varanus komodoensis Melanotaenia arfakensis Calophyllum insularum Sousa chinensis

Casuarius unappendiculatus ş

Myristica inaequalis Grammatophyllum speciosum Carlia fusca

A.1 Description of Biodiversity Surveys Commissioned by Tangguh

Name Description Year Survey method Team of Experts Marine surveys Name Description Year Survey method Team of Experts Terrestrial Surveys Name Description Year Survey method Team of Experts Name Description Year Survey method Team of Experts Name Description Year Survey method Team of Experts

A.2 List of Species of Conservation Concern

Table 21 í Species of flora of conservation concern

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type Latin Common Endemic5 IUCN6 Natio- nally pro- tected7 1 Calophyllum insularum . LF Reportedly endemic to islands in Teluk EN B1+2c - Cendrawasih ver 2.3 2 Nepenthes ampullaria . - LC ver 2.3 Protected 3 Nepenthes mirabilis 4 Grammatophyllum speciosum 5 Grammatophyllum papuanum Grammatophyllum pantherinum

6 Bryobium sp Assumed endemic

7 Bulbophyllum sp. Assumed endemic - 8 Bulbophyllum sp Assumed endemic

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type Latin Common Endemic5 IUCN6 Natio- nally pro- tected7 9 Bulbophyllum sp-1 Assumed endemic

10 Bulbophyllum sp-2 Assumed endemic

11 Bulbophyllum sp-3 Assumed endemic

12 Robiquieta sp Assumed endemic

13 Dendrobium sp Assumed endemic Dendrobium 14 Flindersia pimenteliana 15 Myristica inaequalis Endemic

16 Livistona sp. Assumed endemic Livistona Livistona

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type Latin Common Endemic5 IUCN6 Natio- nally pro- tected7 17 Glochidion daviesii New species, Endemic

18 Scaevola burnettii New species, Endemic

19 Freycinetia bomberaiensis

Shorea AnisopteraHopeaVatica Bruguiera hainesii

Table 22 í Bird species of conservation concern

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type Latin Common Congregatory Endemic / IUCN6 Nationally pro- species Restricted-range tected7 1 Accipiter poliocephalus 2 Alcedo azurea 3 Alcedo pusilla 4 Aquila gurneyi 5 Ardea alba 6 Aviceda subcristata 7 Cacatua galerita 8 Calidris tenuirostris Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 9 Casuarius casuarius 10 Casuarius unappendiculatus 11 Chalcopsitta atra 12 Charmosyna placentis 13 Chlamydera cerviniventris 14 Chlidonias hybridus 15 Chlidonias leucopterus Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 16 Clytoceyx rex 17 Dacelo gaudichaud 18 Dacelo leachii 19 Dicaeum pectorale 20 Eclectus roratus 21 Egretta alba 22 Egretta garzetta 23 Egretta novaehollandiae Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 24 Egretta picata 25 Goura cristata 26 Halcyon chloris 27 Haliaeetus leucogaster

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 28 Haliastur indus 29 Haliastur sphenurus 30 Henicopernis longicauda 31 Megapodius freycinet 32 Megapodius Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type rainwardt 33 Meliphaga montana 34 Mesophoyx (Ardea) intermedia 35 Myzomela eques 36 Myzomela nigrita 37 Myzomela obscura 38 Nectarinia aspasia 39 Nectarinia jugularis 40 Nycticorax Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type caledonicus 41 Pandion haliaetus 42 Paradisaea minor 43 Paradisaea raggiana 44 Philemon buceroides 45 Philemon corniculatus 46 Pitta erythrogaster 47 Pitta sordida

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 48 Probosciger aterrimus

49 Ptilinopus ornatus 50 Pycnopygius cinereus 51 Rhyticeros plicatus 52 Sterna bergii 53 Sterna fuscata Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type Sterna hirundo 54 55 Syma torotoro 56 Talegalla cuvieri 57 Talegalla fuscirostris 58 Tanysiptera galatea 59 Tanysiptera nympha 60 Todiramphus chloris

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type 61 Todiramphus macleayii 62 Todiramphus sanctus

Species name Survey Modified / Habitat Conservation status4 2 3 Record1 Natural Type - Ducula concinna - Accipiter novaehollandiae Accipiter hiogaster ( - Threskiornis aethiopicus - Myzomela albigulaM.obscura - Myzomela sclateri only M.sclater. - Melidectes fuscus - Paradisaea rubra - Philemon brassi P.mayeri.

Table 23 í Mammal species of conservation concern

Species name Survey Modified / Habitat Type Conservation status record Natural Latin Common Endemic / IUCN Nationally Restricted-range protected 1 Balaenoptera edeni 2 Cervus timorensis 3 Dendrolagus 4 Dendrolagus ursinus 5 Dorcopsis muelleri 6 Megaptera novaeangliae

Species name Survey Modified / Habitat Type Conservation status record Natural Latin Common Endemic / IUCN Nationally Restricted-range protected 7 Nyctimene draconilla 8 Sousa chinensis chinensis 9 Spilocuscus (Phalanger) maculatus 10 Stenella attenuata 11 Stenella longirostris 12 Strigocuscus (Phalanger) gymnotis

Species name Survey Modified / Habitat Type Conservation status record Natural Latin Common Endemic / IUCN Nationally Restricted-range protected 13 Tursiops aduncus

Table 24 í Herpetofauna species of conservation concern

Species name Survey Modified Habitat Type Conservation status record / Natural Latin Common Endemic / Restricted- IUCN Nationally range protected 1 Caretta caretta

Species name Survey Modified Habitat Type Conservation status record / Natural Latin Common Endemic / Restricted- IUCN Nationally range protected 2 Carlia bombarai 3 Chelonia mydas 4 Cophixalius sp. nov. 5 Crocodylus novaeguineae 6 Crocodylus porosus 7 Dermochelys coriacea 8 Elseya

Species name Survey Modified Habitat Type Conservation status record / Natural Latin Common Endemic / Restricted- IUCN Nationally range protected novaeguineae 9 Emoia sp. nov. 10 Eretmochelys imbricata 11 Hylophorbus sp. nov. 12 Hypsilurus dilophus 13 Lepidochelys olivacea 14 Morelia viridis

Species name Survey Modified Habitat Type Conservation status record / Natural Latin Common Endemic / Restricted- IUCN Nationally range protected 15 Platymantis punctatus 16 Tiliqua gigas 17 Varanus indicus - Platymantis (Cornufer) batantae - Hydrosaurus amboinensis (pustulatus)

Table 25 í Fish species of conservation concern

Species name Survey Modified / Habitat Type Endemic / Conservation status record Natural Restricted-range Latin Common IUCN Nationally protected Melanotaenia irianjaya Melanotaenia arfakensis Pseudomugil reticulatus

A.3 Consultation with Biodiversity Experts on Critical Habitat Assessment

Questions to Experts: He is one of the experts of flora and fauna survey since 2007 + 250 ¨21.6 • • • - ≥ - ≥

Expert Response:

Translated Expert Response:

1.

Expert Response:

Livistona sp., Bruguiera haenesii B.haenesii

Expert Response: Calidris tenuirostris. Chalcopsitta atra, Dicaeum pectorale

Goura cristata Megapodius freycinet (burung gosong). Paradisaea minor) Probosciger aterrimus Megapodius reinwardt (Talegalla cavieri, Talegalla fuscirostris

Nyctophilus cf. bifax Nyctophilus cf. bifax

Translated Expert Response:

Livistona sp ., Bruguiera haenesii B.haenesii

Calidris tenuirostris.

Translated Expert Response:

Goura cristata

Megapodius freycinet (burung gosong).

Paradisaea minor Probosciger aterrimus Megapodius reinwardt Talegallacavieri, Talegalla fuscirostris

Nyctophilus cf. bifax Nyctophilus cf. bifax

Expert Response:

Translated Expert Response:

Cophixalus sp. novHylophorbus sp. nov Emoia sp. nov

Expert Response:

CophixalusHylophorbus

Emoia astrocostata, Emoia caeruleocauda, Emoia cyanogaster, Emoia pallidiceps, Emoia physicae. Sedangkan jenis Katak dari genus Emoia Emoia

Translated Expert Response:

CophixalusHylophorbus CophixalusHylophorbus

Emoia astrocostata, Emoia caeruleocauda, Emoia cyanogaster, Emoia pallidiceps, Emoia physicae. Emoia Emoia

Calidris tenuirostris

Expert Response:

Calidris tenuirostris. Expert Response:

Calidris tenuirostris.

Questions to Experts: He is one of the experts of flora and fauna survey since 2007

Expert Response:

Flora Species No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi Calophyllum insularum • • • • Nepenthes ampullaria • • • • • • • • • • • Nepenthes ampullaria

No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi • Nepenthes mirabilis • Nepenthes mirabilis Grammatophyllum Grammatophyllum papuanum speciosum • • • • • • • • • • • • • • • • No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi • • • • • • • • • • • • • • • • Bryobium sp Bulbophyllum Bulbophyllumsp Bulbophyllum sp- 1 No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi Bulbophyllum sp- 2 Bulbophyllum sp- 3 Robiquieta sp Grammatophyllum Grammatophyllum speciosum papuanum • • • • • • • • • • • • • • No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi • • • • • • • • • • • • • • • • • • Dendrobium sp Flindersia pimenteliana • Flindersia pimenteliana • Flindersia pimenteliana

No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi • • • Myristica inaequalis • • Livistona sp. Livistona benthamii (all Livistona family is protected under Indonesian Regulation, however the 2003 did not specify the Livistona species • found during the survey) • Glochidion daviesii • Error! Hyperlink reference not valid. • Scaevola burnettii No Nama Ilmiah Nama Lokal Keterangan/Konfirmasi & Referensi Freycinetia bomberaiensis • Bruguiera hainesii • • •

Translated Expert Response:

Flora Species (for cited references see table above)

No Scientific Name Local Name Description / Confirmation & Reference Calophyllum insularum Nepenthes ampullaria Nepenthes mirabilis Grammatophyllum speciosum Bryobium sp Bulbophyllum Bulbophyllumsp Bulbophyllum sp-1

No Scientific Name Local Name Description / Confirmation & Reference Bulbophyllum sp-2 Bulbophyllum sp-3 Robiquieta sp Grammatophyllum papuanum Dendrobium sp Flindersia pimenteliana Myristica inaequalis Livistona sp. (all Livistona family

No Scientific Name Local Name Description / Confirmation & Reference is protected under Indonesian Regulation, however the 2003 did not specify the Livistona species found during the survey) Glochidion daviesii Scaevola burnettii Freycinetia bomberaiensis Bruguiera hainesii

Expert Response:

Mammal Species

Flannery, T. F.Mammals of New Guinea, revised and updated ed Bonnacorso, F.J. Bats of Papua New Guinea. Flannery, T. F.Mammals of New Guinea, revised and updated ed

Translated Expert Response:

Mammal Species

Yth. Pak Aldi

Flannery, T. F. Bonnacorso, F.J. Flannery, T. F. Rudolph P., Smeenk C., and Leatherwood S.

Tim Mamalia, Martua Sinaga

Mammals Distribution Data According to Bogor Zoology Museum MZB_Number Collector Collector Date_From Locality_Detail Family Genus Species TMP Number MZB_Number Collector Collector Date_From Locality_Detail Family Genus Species TMP Number MZB_Number Collector Collector Date_From Locality_Detail Family Genus Species TMP Number

Expert Response:

Herpetofauna Species

Probably new species Cophixalus biroi No. Kelompok Ordo Famili Spesies

Amfibi Cophixalus Hylophorbus Hylophorbus Reptil Emoia astrocostata Emoia caeruleocauda Emoia cyanogaster Emoia pallidiceps Emoia physicae Emoia Emoia Emoia Emoia

Expert Response:

Herpetofauna Species

Cophixalus Cophixalus biroi No. Group Ordo Family Sepcies

Amphibi Cophixalus Hylophorbus Hylophorbus Reptile Emoia astrocostata Emoia caeruleocauda Emoia cyanogaster Emoia pallidiceps Emoia physicae Emoia Emoia Emoia Emoia

Questions to Experts: • Ducula concinna • Accipiter novaehollandiae • Myzomela albigula • Myzomela sclateri • Paradisaea rubra • Philemon brassi

Expert Response: Ducula concina Accipiter novaehollandiae Accipiter hiogaster A. novaehollandiae Myzomela albigula Myzomela obscura Myzomela sclater Myzomela equesM. sclater Paradisaea rubra Philemon brassi Philemon meyeri

Questions to Experts: He is one of the experts of flora and fauna survey since 2007 Melanotaenia arfakensis Melanotaenia irianjaya?

Expert Response: Ficus fistulosa Freycinetia Scaveola