Limited Phase 1 Environmental Site Assessment and Phase 2 Environmental Site Assessment Eastern Portion of New Brighton Park, Vancouver, BC

Prepared for: Port Metro Vancouver, Habitat Enhancement Program 100 The Pointe – 999 Canada Place Vancouver, BC V6C3T4

Prepared by: Hemmera Envirochem Inc. 18th Floor, 4730 Kingsway Burnaby, BC V5H 0C6

File: 302-035.04 August 20, 2015

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - i - August 2015

EXECUTIVE SUMMARY

Hemmera Envirochem Inc. (Hemmera) was retained by Port Metro Vancouver (PMV) Habitat Enhancement Program (HEP) to conduct a limited Phase 1 Environmental Site Assessment (ESA) and a Phase 2 ESA for the eastern portion of New Brighton Park, in Vancouver, BC (the ‘Site’). Based on information provided by PMV, an opportunity exists to create fish and wildlife habitat by creating a wetland habitat feature on the east side of the New Brighton Park (the ‘Project’). The majority of the current Project area falls within a single parcel. The portion of the park for which the Project is planned for is leased to the City of Vancouver by PMV, under lease reference 1-01-00444.

A Stage 1 Preliminary Site Investigation (PSI) was completed at the Site by Keystone Environmental Ltd (Keystone) in May 1997. Based on those findings, a subsequent Stage 2 PSI was completed by Keystone in July 1997. Both phases of work were completed for the City of Vancouver. The objectives of this limited Phase 1 ESA was to update the environmental conditions at the Site since the previous PSIs were completed in May/July 1997, and identify areas of potential environmental concern (APECs) and potential contaminants of concern (PCOCs) associated with present and/or historical on and off-Site activities that may have impacted environmental media at the Site. Also, the work is being completed to document soil and groundwater quality in advance of potential construction works planned for the Project.

Information reviewed indicates that the original shoreline was located approximately 150 metres (m) south of its present location. Fill material used to reclaim this intertidal zone is of unknown quality/origin. As such, one on-Site APEC has been identified through the Phase 1 ESA and is discussed in Table ES-1 below.

Table ES-1 Summary of APEC and PCOCs

APEC Source Comments PCOCs Media There has been extensive intertidal zone infilling of the north end of the Petroleum Fill Material of park, beginning in the early-1960s. Hydrocarbons (VOCs Soil and 1 unknown incl. BTEX/VPH, EPH, Information reviewed indicates that the groundwater quality/origin original shoreline was located PAHs, LEPH, HEPH), approximately 150 metres south of its metals present location. Notes: APEC = Area of Potential Environmental Concern PCOCs = Potential Contaminants of Concern VOCs = Volatile Organic Compounds BTEX = Benzene, Toluene, Ethylbenzene, and Xylenes VPH = Volatile Petroleum Hydrocarbons EPH = Extractable Petroleum Hydrocarbons LEPH/HEPH = Light/Heavy Extractable Petroleum Hydrocarbons PAH = Polycyclic Aromatic Hydrocarbons

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - ii - August 2015

Based on the Phase 1 ESA, Hemmera conducted a Phase 2 ESA to assess soil and groundwater in the vicinity of the APEC and proposed habitat enhancement project. A total of eleven boreholes were advanced at the Site, with four completed as monitoring wells. Soil and groundwater samples were submitted for analysis of PCOCs listed in Table ES-1. The soil analytical data was evaluated using the CCME Canadian Soil Quality Guidelines for the Protection of Environmental and Human Health, Park Land Use (PL). Groundwater data was evaluated using the CCME Canadian Water Quality Guidelines (CWQG) for the Protection of Aquatic Life (marine), including a ten-fold dilution. Soil and groundwater data collected at the Site was also evaluated using the Contaminated Sites Regulation (CSR) Park Land (PL) use standards to CSR Aquatic Life (AW marine) standards, respectively, for comparison purposes only. The following is a summary of the Phase 2 ESA investigation results.

Table ES-2 Summary Phase 1 and 2 ESA Results

APEC Description Results COCs

Fill Material of Soil > CSR PL, CCME RL/PL Soil: copper, lead, zinc 1 unknown Groundwater > BC CSR AW, Groundwater: LEPHw, naphthalene, quality/origin CCME MAL(x10) phenanthrene, and pyrene Notes: APEC = Area of Potential Environmental Concern COCs = Contaminants of Concern DW = Drinking Water standards/AW = Aquatic Life standards

Based on the above results, the Phase 2 ESA identified elevated concentrations of metals in soil exceeding both the Federal guidelines and Provincial standards. In groundwater, elevated concentrations of petroleum hydrocarbons exceeding the applicable Federal guidelines, as well as Provincial standards (used for comparison purposes) within the footprint of the proposed Project, were identified.

Additional work is required to fully delineate the contaminated soil and groundwater within the Project area. Furthermore, if excavated soil requires off-site disposal as part of the future/potential construction activities, soils with concentrations exceeding Soil Relocation standards would require disposal at an appropriately licensed landfill facility, or they would require a Contaminated Soil Relocation Agreement (CSRA) if relocated to property under Provincial jurisdiction.

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PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - iii - August 2015

TABLE OF CONTENTS

EXECUTIVE SUMMARY ...... I 1.0 INTRODUCTION ...... 1

1.1 HABITAT ENHANCEMENT PROJECT ...... 1

1.2 SITE DESCRIPTION AND BACKGROUND ...... 1 2.0 LIMITED PHASE 1 ENVIRONMENTAL SITE ASSESSMENT ...... 2

2.1 SCOPE OF WORK ...... 2

2.2 LAND TITLE INFORMATION ...... 2

2.3 TOPOGRAPHY AND SURFICIAL GEOLOGY ...... 3

2.4 SITE HISTORY ...... 3

2.5 REGULATORY INFORMATION ...... 5 2.5.1 BC MOE Site Registry ...... 5 2.5.2 Federal Contaminated Site Search ...... 5 2.5.3 Water Well Search ...... 6

2.6 SITE VISIT ...... 6 2.6.1 Ground Observations ...... 6 2.6.2 Building Observations ...... 7 2.6.3 Current Surrounding Land Use ...... 7

2.7 PHASE 1 ESA CONCLUSIONS ...... 7 3.0 PHASE 2 ENVIRONMENTAL SITE ASSESSMENT ...... 8

3.1 SCOPE OF WORK ...... 8

3.2 REGULATORY FRAMEWORK ...... 9 3.2.1 Soil ...... 10 3.2.1.1 Federal Guidelines ...... 10 3.2.1.2 Provincial Standards ...... 10 3.2.2 Groundwater ...... 10 3.2.2.1 Federal Standards ...... 10 3.2.2.2 Provincial Standards ...... 11

3.3 RESULTS ...... 11 3.3.1 Soil Stratigraphy and Drilling Observations ...... 11 3.3.2 Groundwater Monitoring ...... 12

3.4 ANALYTICAL RESULTS ...... 12 PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - iv - August 2015

3.4.1 Soil Results ...... 13 3.4.1.1 Federal Guidelines ...... 13 3.4.1.2 Provincial Standards ...... 14 3.4.2 Groundwater Results ...... 14 3.4.2.1 Federal Guidelines ...... 15 3.4.2.2 Provincial Standards ...... 15 3.4.3 QA/QC ...... 15

3.5 SUMMARY AND DISCUSSION ...... 16 4.0 PHASE 1 AND 2 ESA CONCLUSIONS ...... 17 5.0 REFERENCES ...... 19 6.0 STATEMENT OF LIMITATIONS ...... 20

List of Tables (within text)

Table ES-1 Summary of APEC and PCOCs ...... i Table ES-2 Summary Phase 1 and 2 ESA Results ...... ii Table A Site Description ...... 2 Table B Legal Description and Current Title Information ...... 3 Table C Topography ...... 3 Table D Ground Observations ...... 6 Table E Current Surrounding Land Use ...... 7 Table F Summary of APEC and PCOCs ...... 7 Table G Summary of Investigation Locations and Rationale ...... 8 Table H Summary of Soil Stratigraphy ...... 12 Table I Summary Phase 1 and 2 ESA Results ...... 17

List of Figures (following text)

Figure 1 Site Location Map

Figure 2 Site Plan and Surrounding Land Use

Figure 3 Historical Land Use Plan

Figure 4 Site Plan with APECs

Figure 5 Investigation Locations

Figure 6 Soil Analytical Results

Figure 7 Groundwater Analytical Results PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - v - August 2015

List of Tables (following text)

Table 1a Soil Metals Analytical Results

Table 1b Soil Saturated Paste and Leachable Metals Analytical Results

Table 1c Soil Hydrocarbons Analytical Results

Table 1d Soil Volatile Organic Compounds Analytical Results

Table 1e Soil Relocation – Metals Analytical Results

Table 1f Soil Relocation – Hydrocarbons Analytical Results

Table 1g Soil Metals TCLP Results

Table 2a Groundwater Dissolved Metals Analytical Results

Table 2b Groundwater Hydrocarbons Analytical Results

List of Appendices

Appendix A Site Photographs

Appendix B Project Concept and PMV Documents

Appendix C Aerial Photographs

Appendix D Previous Reports (Report of Findings. Preliminary Site Investigation, Stage 1 (May 1997) and Report of Findings. Preliminary Site Investigation, Stage 2 (July 1997)

Appendix E BC MOE Site Registry Search

Appendix F Federal Contaminated Sites Inventory

Appendix G Water Well Search

Appendix H Borehole Logs

Appendix I Field Methodology

Appendix J Certified Analytical Lab Reports PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 1 - August 2015

1.0 INTRODUCTION

Hemmera Envirochem Inc. (Hemmera) was retained by Port Metro Vancouver (PMV) Habitat Enhancement Program (HEP) to conduct a limited Phase 1 Environmental Site Assessment (ESA) and a Phase 2 ESA for the eastern portion of New Brighton Park, in Vancouver, BC (the ‘Site’).

The location and defined boundaries of the Site (for the purposes of this assessment) is illustrated on Figure 1 and the current Site layout and features, and individual parcel ownership descriptions, are shown on Figure 2. Site photographs are included in Appendix A.

The overall objective of this project is to a complete a step wise approach to 1) understand the history of the Site and how it was developed (complete a limited Phase 1 ESA), and 2) to further assess soil and groundwater conditions (complete a Phase 2 ESA) in preparation for a proposed habitat enhancement project which is described further below.

1.1 HABITAT ENHANCEMENT PROJECT

Based on information provided by PMV, an opportunity exists to create fish and wildlife habitat by creating a wetland habitat feature on the east side of New Brighton Park (the ‘Project’). The eastern side of New Brighton Park offers a restoration opportunity to create marine/freshwater habitat in a historic fill area of the Burrard Inlet. The project concept is provided in a figure in Appendix B. The Project areas falls within a single parcel (B, as identified in Vanmap). The portion of the park for which the Project is planned for is leased by PMV to the City of Vancouver, under lease reference 1-01-00444.

1.2 SITE DESCRIPTION AND BACKGROUND

New Brighton Park fronts onto Burrard Inlet, in the vicinity of the Second Narrows Bridge. New Brighton was previously known as Hastings Town Site in circa 1865, and is considered to be the original area in which the City of Vancouver began. The Site (for which the Project is slated for) is situated in the area of a former industrial harbour. New Brighton Park was created in circa 1930s, and is a well-used park within eastern Vancouver that offers recreation for local residents including opportunities for dog walking, picnicking and jogging. There is a pool, playgrounds, playing fields/tennis courts, and grassed areas for public use. The Site is bordered by Burrard Inlet to the north, Canadian Pacific Railway to the south, the remainder of the park to the west (which is either on property owned by the City of Vancouver, or owned by PMV and leased to the City of Vancouver, and Viterra/Cascadia Terminals to the east. There has been extensive intertidal zone infilling of the north end of the park, beginning in the early-1960s. Pictorial evidence of this infilling is provided in the documents provided in Appendix B and Appendix C.

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 2 - August 2015

2.0 LIMITED PHASE 1 ENVIRONMENTAL SITE ASSESSMENT

A Stage 1 Preliminary Site Investigation (PSI) was completed at the Site by Keystone Environmental Ltd. (Keystone) in May 1997. A subsequent Stage 2 PSI was completed by Keystone in July 1997. Both phases of work were completed for the City of Vancouver. The objective of this Phase 1 ESA is to update the environmental conditions at the Site since the previous PSIs were completed in May/July 1997, and identify areas of potential environmental concern (APECs) and potential contaminants of concern (PCOCs) associated with present and/or historical on and off-site activities that may have impacted environmental media at the Site. The findings of this Phase 1 ESA also provide a basis for the Phase 2 ESA scope of work (discussed further in Section 3.0, below).

2.1 SCOPE OF WORK

The limited Phase 1 ESA involved a review of select historical documents that aided in gaining an understanding of the current conditions and historical operations on the Site, and concerns associated with the current and historical use of adjacent and up-gradient properties. Sources of information reviewed included:

 Topographic and geology maps;  Aerial photographs;  Water well search via BC Water Resource Atlas;  BC Ministry of Environment (BC MOE) Site Registry;  Fire Insurance Plans (obtained from Vanmap);  Federal Contaminated Site Inventory Search;  Previous environmental reports and records provided by PMV; and,  Site visit: the site visit included a review of the Site for APECs (e.g., observed or suspected spills, storage tanks, etc.), as well as other potential environmental concerns (e.g., proximity of the Site to sensitive areas, activities on adjacent properties).

2.2 LAND TITLE INFORMATION

The following tables summarize the land title information for the Site.

Table A Site Description

The Project Site is not identified with a civic address. The park Site Address itself is identified as 3201 New Brighton Road, Vancouver, BC. Latitude and Longitude (investigation area/ 49° 17’ 24” N, 123° 02’ 07” W proposed habitat enhancement project) Size Approximately 10 ha. Current Use Park/recreational use Zoning CD-1 – Comprehensive Development District (258) PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 3 - August 2015

Table B Legal Description and Current Title Information

Legal Description Parcel B is not defined by a legal description. Parcel Identifier Number (PID) Parcel B is not defined by a PID. Parcel B – PMV owns the Site. The Site leased to the City of Registered Land Owner Vancouver, reference 1-01-00444.

2.3 TOPOGRAPHY AND SURFICIAL GEOLOGY

The anticipated surficial geology on-Site, based on a review of published government maps, is comprised of Vashon Drift and Capilano Sediments. Bedrock is expected at more than 10 m below surface.

Table C Topography

Site Topography In general, the Site slopes gently north towards Burrard Inlet. Regional topography slopes generally downwards toward the north Regional Topography towards Burrard Inlet. Closest Surface Water Body Burrard Inlet Inferred Groundwater Flow Direction North towards the Burrard Inlet. Areas Considered Up-Gradient South Area Considered Cross-Gradient East and West Areas Considered Down-Gradient North

2.4 SITE HISTORY

Records reviewed to gain knowledge Site history for this assessment include previous environmental Site investigation reports, aerial photographs, and Site information provided by PMV (e.g., previous environmental reports, photos and Site plans, and lease information). The purpose of reviewing these records is to document historical activities on-Site and identify potential sources of contamination and operations of concern. A historical land use plan is provided in Figure 3, attached.

Keystone reviewed ten previous environmental reports as part of the May 1997 Stage 1 PSI, and provided a summary of relevant findings for each. As indicated in Section 3.7 and Figure 4 of the Keystone May 1997 report, the reports reviewed were primarily related to the western portion of the park and were outside of the Project footprint. A summary of these reports are provided by Keystone, and not repeated here. However, the results of those investigations which are relevant to the Site have been considered for the findings of this Phase 1 ESA.

As summarized in the Keystone Stage 1 PSI report, and findings of the records review by Hemmera, as early as 1913, the park had not been developed, but the eastern portion was occupied by two shingle mills. The central and western portions of the park had yet to be developed. The central portion of the Site has been occupied by a park/pool since the 1930s. Off-site properties to the south and southwest of the PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 4 - August 2015 park (on Wall and McGill Streets, respectively) were occupied by commercial and industrial operations from the 1930s to 1980s. These operations include timber processing and shingle manufacturing, gypsum product manufacturing, and boat yards/building. It is also noted that although several of these businesses were listed in street directories with Wall Street addresses, the aerial photograph interpretation showed these operations actually occupying areas north of the Canadian Pacific Railway lines, and operated on the western portion of the Site/park.

By the mid-1950s, the park was expanded in an eastward direction. The lumber operations on the western portion of the park were reduced in size. The pool is observed in the 1963 aerial photograph. The boat houses and shacks present in the mid-1940s are no longer visible, and the lumber operations on the western portions of the park are gone. Aerial photographs reviewed for the early-1970s show the park in its present day configuration, with the shoreline extending further into Burrard Inlet. The western portion of the park remains entirely industrial. City of Vancouver land use maps show that the eastern portion of the park was zoned for public use, while the western portion was zoned for warehousing and manufacturing. The park has remained relatively unchanged from the late 1970s to present day.

Information provided in the Keystone report and Site information provided by PMV and VanMap indicates that the original shoreline was located approximately 150 m south of its present location (pictorial evidence of this infilling is provided in the documents provided in Appendix B and in Figure 3, attached). Soil material used to reclaim this intertidal zone is of unknown quality/origin. Keystone reported in the May 1997 Stage 1 PSI report that environmental investigations conducted in the western portion of the park have identified contamination, with elevated concentrations of metals (primarily arsenic) and petroleum hydrocarbons in fill. Groundwater quality in these areas in the western portion of the park has also been found to contain elevated concentrations of arsenic and other dissolved metals. The Keystone Stage 1 PSI found that contamination may be present on the eastern portion of the Site, similar to what was identified in the western portions (e.g., as portions of the New Brighton Park underwent land reclamation concurrently with the properties to the west of the park).

Based on the findings of the Stage 1 PSI, Keystone undertook a Stage 2 PSI in July 1997 over the eastern portion of the park/vicinity of the Project. The investigation included advancing 15 boreholes, with one completed as a groundwater monitoring well (see Figure 5 for the Keystone PSI 2 drill locations near the Project area). The following summarizes the results:

 Drilling depths reached an average depth of 4.5 m. The monitoring well (MW97-1) was installed to a depth of 3 m. Of these fifteen locations, a total of seven (7) locations (MW97-1, BH97-10 to BH97-15) are located near or within the proposed habitat enhancement Project area.

 Fil material containing wood waste, bricks, glass shards, and metal fragments in minor quantities were found in the majority of the boreholes. Some asphalt waste was found in the vicinity of the tennis courts. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 5 - August 2015

 Soil samples were analyzed for total metals and petroleum hydrocarbons at depths ranging from 0.6 to 4.3 m below ground surface (bgs). Concentrations of these parameters met the Contaminated Sites Regulation (CSR) Urban Park (PL) standards (in place at the time of the assessment).

 Groundwater samples were collected from MW97-1, which is located approximately 50 m southeast of the tennis courts and up-gradient of the proposed habitat enhancement Project area. It was analyzed for polycyclic aromatic hydrocarbons (PAHs) and volatile organic compounds (VOCs). Concentrations of these parameters met the CSR Aquatic Life (AW) standards (in place at the time of the assessment), with the majority less than the laboratory detection limits. The Keystone report contained an error, whereby the naphthalene concentration at MW97-1 was reported as meeting the standard (in effect at the time of the assessment, but was actually slightly above the CSR standard (0.5 µg/L vs a standard of 0.3 µg/L1).

Site information provided by PMV is included in Appendix B. Aerial photographs are provided in Appendix C. Previous environmental reports are included in Appendix D.

2.5 REGULATORY INFORMATION

2.5.1 BC MOE Site Registry

A search of the BC MOE Online Site Registry was conducted and contained Sites listed as of March 15, 2015. The BC Online Site Registry is a database of Sites that have submitted information to the BC MOE with respect to the BC Environmental Management Act. A search of the Site Registry was conducted using a one square kilometre search centred on the approximate longitude and latitude of the Site. A total of 4 records were found in the registry; none of the records are associated with the Site. Two records were related to a property on Wall Street (~450 m east of the Site), a property on Bridgeway Street (350 m east), and one record related to the ‘north foot’ of the Cassiar Tunnel. The results are provided in Appendix E.

2.5.2 Federal Contaminated Site Search

The Federal Contaminated Sites Inventory includes information on all known federal contaminated Sites under the custodianship of departments, agencies and consolidated Crown corporations as well as those that are being or have been investigated to determine whether they have contamination arising from past use that could pose a risk to human health or the environment. The inventory also includes non-federal contaminated Sites for which the Government of Canada has accepted some or all financial responsibility. A search of the Online Federal Contaminated Sites inventory was conducted on March 15, 2015. The closest federal contaminated Site is located approximately 950 m west of the Site. The results of the federal contaminated Sites search are located in Appendix F.

1 The CSR AW standard for naphthalene using current Schedule 6 is 10 µg/L and the FIGWQG is 1.4 µg/L. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 6 - August 2015

2.5.3 Water Well Search

A search of the British Columbia Water Resource Atlas was conducted on March 17, 2015, to determine the presence of water wells registered within 500 m of the Site. No water wells were identified within 1.5 km of the Site. Results of the BC Water Resource Atlas search are included in Appendix G.

2.6 SITE VISIT

Hemmera conducted a Site visit, unaccompanied, on March 17, 2015. Photographs from the Site visit are included in Appendix A. Ground and building observations are provided below.

2.6.1 Ground Observations

The Site grounds consist primarily of a grassy field with walking paths. Tennis courts are located in the southeast corner of the Site, and a parking area is located along the southwest edge of the Site. The corner of a nearby New Brighton Park caretaker house and adjoining concession is located on-Site, in the southwest corner. This building was not accessed during the Site visit. Observations of the grounds of the Site are provided below.

Table D Ground Observations

Ground Cover Upland area: Approximately 70% unpaved, 5% structures, 20% vegetated, 5% paved. The Site is graded consistent with surrounding properties. As the former shoreline Evidence of Fill was historically 150 m south from its current location, a significant amount of fill of unknown quality is present on the Site. Site drainage is primarily via infiltration and overland flow to the water lot portion of the Site. Catch basins were observed in northwest corner of the tennis court area, as Site Drainage well as along the parking area on the south edge of the Site. The drains are anticipated to discharge to Burrard Inlet. The north portion of the Site is located adjacent to Vancouver Harbour. Sheen was Surface Water not observed in surface water during the Site visit. Monitoring Wells No monitoring wells were observed on-Site. Waste Water or Other None observed. Discharges from Site The Site is connected to the municipal water system, and a water fountain is located Water Connection just northwest of the tennis courts on-Site. Water Wells No water wells were observed or reported on-Site. Gas Connection None. Evidence of USTs No evidence USTs was observed at the Site. ASTs No ASTs were observed at the Site. Storage of Hazardous Materials and/or No storage of hazardous materials or wastes was observed on-Site. Wastes Evidence of Surface No stressed vegetation was observed on-Site. Contamination PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 7 - August 2015

Signs of Spills, No signs of spills or staining within the Site area. Minor surficial soil staining in the Staining on Ground parking area/roadway on- Site, which is due to normal vehicle traffic. Transformers or None observed. Capacitors Right of Ways None. Drains / Sumps / Oil None observed/reported. Water Separators

2.6.2 Building Observations

The northeast corner of the caretaker house/concession building for the pool adjacent to the Site is located on the Site and was constructed in the mid to late 1970s. The building was not accessed during the Site visit.

2.6.3 Current Surrounding Land Use

The current surrounding land use, as observed during the Site visit, consists of the following.

Table E Current Surrounding Land Use

Orientation Land Use Potential Concern / Comments to the Site North Burrard Inlet No concerns identified. Cascadia Terminal, beyond is East No concerns identified Second Narrows Bridge No concerns identified. Previous analytical data South Canadian Pacific Railway corridor collected by Keystone in 1997 suggests the Site has not been impacted by rail activities. West Remainder of New Brighton Park No concerns identified.

2.7 PHASE 1 ESA CONCLUSIONS

One on-Site APEC has been identified through the Phase 1 ESA, and is shown in Figure 4 and discussed in Table F, below.

Table F Summary of APEC and PCOCs

APEC Source Comments PCOCs Media

There has been extensive intertidal zone Petroleum infilling of the north end of the park, Hydrocarbons Fill Material of beginning in the early-1960s. (VOCs incl. Soil and 1 unknown BTEX/VPH, EPH, groundwater quality/origin Information reviewed indicates that the original shoreline was located approximately PAHs, LEPH, 150 m south of its present location. HEPH), metals Notes: APEC = Area of Potential Environmental Concern PCOCs = Potential Contaminants of Concern VOCs = Volatile Organic Compounds BTEX = Benzene, Toluene, Ethylbenzene, and Xylenes VPH = Volatile Petroleum Hydrocarbons EPH = Extractable Petroleum Hydrocarbons LEPH/HEPH = Light/Heavy Extractable Petroleum Hydrocarbons PAH = Polycyclic Aromatic Hydrocarbons PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 8 - August 2015

3.0 PHASE 2 ENVIRONMENTAL SITE ASSESSMENT

Hemmera conducted a Phase 2 ESA to assess soil and groundwater in the vicinity of the identified APEC and proposed habitat enhancement Project. As discussed above, the investigative work is being completed to document soil and groundwater quality in advance of potential construction works planned for the project (e.g., if soils need to be transported off-site for disposal or managed on-Site).

Sampling locations are based on the APEC identified in the Phase 1 ESA. The drill locations have been oriented in an approximate 20 m by 20 m grid over the Project area (11 in total). The habitat Project estimates the handling of nearly 20,000 m3 of material. As such, the level of sampling is considered adequate for the Project area and anticipated APECs present (e.g., fill of an unknown origin), and if any of the material requires off-site disposal.

The Phase 2 ESA sampling locations are shown on Figure 4.

Table G Summary of Investigation Locations and Rationale

Location/ APEC Investigation ID/Sample ID Potential Source

Fill Material of unknown Soil and Groundwater 1 quality/origin MW15-1, MW15-2, MW15-3, MW15-4, BH15-5 to BH15-11

3.1 SCOPE OF WORK

In order to achieve the objective, the following tasks were completed as part of the Phase 2 ESA at the Site (detailed in the sections following):

Pre-Field Preparations

1. Prepared a Site-specific health and safety plan. 2. Investigated the presence of underground utilities through BC “One” Call. 3. Coordinated Site access, field equipment, subcontractors (driller and utility locators, and analytical laboratory) and field mobilization. 4. Prepared the necessary PMV permit applications for the work.

Field Program – Drilling and Groundwater Sampling

5. Completed a daily health and safety tailgate meeting on-Site before the start of fieldwork. 6. Confirmed on-Site utility locations using a private utility locator. 7. Conducted a two-day drilling program that included the drilling of eleven (11) boreholes. Boreholes were advanced using the Sonic drill method. Each borehole was extended to depths ranging from 4.6 m to 8.5 m bgs (depending on depth of excavation activities planned for the proposed habitat enhancement Project). Four of the boreholes were completed as monitoring wells. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 9 - August 2015

8. Submitted up to two soil samples (based on a number of factors including field observations, depth, stratigraphy, APECs/PCOCs) from each borehole (plus a duplicate sample) to Maxxam Analytics for analysis of PCOCs identified in the Phase 1 ESA. 9. Based on the analytical results, one sample (from MW15-8) was submitted to Maxxam Analytics for Toxicity Characteristic Leachate Procedure (TCLP) analysis for leachable lead. 10. Developed the groundwater in the newly-installed monitoring wells after installation using Waterra tubing and foot valve to extract six well volumes (where possible). 11. Monitored and sampled the groundwater in the newly-installed monitoring wells after installation, using a low-flow sampling technique, on an out-going tide. 12. Submitted groundwater samples for analysis of PCOCs based on the limited Phase 1 ESA findings. 13. Returned to the Site and re-developed/re-sampled groundwater monitoring well MW15-1 to confirm or refute original groundwater analytical results for select parameters.

Prior to the execution of the drill program, the proposed drill locations were plotted on an AutoCAD drawing, and Global Positioning System (GPS) coordinates and geodetic surface elevations were provided. A professional surveyor (from Van Bower Construction Services Ltd.) visited the Site and marked the physical locations and measured the ground elevations at each drill location.

Representatives from Stantec Consulting were also on-Site for the duration of the drill program providing archaeological monitoring. The Stantec Consulting report and their findings are provided under separate cover.

Reporting and Data Interpretation

The analytical results for soil and groundwater were evaluated using Federal guidelines, as well as Provincial standards (for comparison purposes only). These guidelines and standards are summarized in detail, below.

3.2 REGULATORY FRAMEWORK

The Site is under Federal jurisdiction, and therefore, is subject to Federal environmental regulations and guidelines. As such, it was determined that the Canadian Council of Ministers of the Environment (CCME) guidelines should be used to evaluate the analytical data collected at the Site.

However, as the Site is currently leased to the City of Vancouver, it is also under Provincial jurisdiction. We understand that as part of the proposed habitat enhancement Project, some soils excavated during the course of construction may require additional management off-site (i.e., to a provincially licensed facility). Therefore, the standards contained in the BC Environmental Management Act (EMA) and the associated Contaminated Sites Regulation (CSR) and Hazardous Waste Regulation (HWR) have also been used to evaluate the Site data. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 10 - August 2015

3.2.1 Soil

3.2.1.1 Federal Guidelines

The CCME Canadian Soil Quality Guidelines for the Protection of Environmental and Human Health, Park Land Use (PL) were used to evaluate the soil data collected at the Site.

3.2.1.2 Provincial Standards

The CSR Urban Park (PL) standards were used to evaluate the soil data collected at the Site, for comparison purposes. The CSR Generic Numerical Soil Standards and Matrix Numerical Soil Standards for CL as presented in Schedules 4, 5 and 10 of the CSR, are provided in this report, and are the basis for comparison of the soil analytical results.

In accordance with the CSR, and based on the groundwater use in the vicinity of the Site, the following Site-specific factors were considered to determine the applicable matrix soil standards:

 Intake of contaminated soil (mandatory at all Sites).

 Toxicity to soil invertebrates and plants (mandatory at all Sites).

 Groundwater flow to surface water used by aquatic life (generic and marine).

 Groundwater used for drinking water.

Where applicable, the most stringent of the above-noted matrix standards was used for assessing the soil analytical results at the Site.

Additionally, CSR Schedule 7 Standards Triggering Contaminated Soil Relocation Agreements were reviewed for potential soil relocation purposes to both agricultural and/or non-agricultural land.

The Leachate Quality Standards (LQS) listed in Table 1 of Schedule 4 of the HWR are applicable to concentrations obtained using TCLP laboratory analysis.

3.2.2 Groundwater

3.2.2.1 Federal Standards

The CCME Canadian Water Quality Guidelines (CWQG) for the Protection of Aquatic Life (marine) have been used to evaluate the groundwater analytical results. However, these guidelines were established for ambient concentrations in surface waters and as such, do not provide a scientifically defendable basis to evaluate groundwater analytical data as aquatic life is potentially exposed to diluted groundwater entering and mixing with surface waters. It is assumed that there will be a ten-fold dilution of groundwater within the receiving environment, and as such, the CCME CWQG have been multiplied by ten (i.e. CCME MAL x10) for comparison to the groundwater analytical data. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 11 - August 2015

The Canadian Drinking Water Quality Guidelines (CDWWQ), published by Health Canada on behalf of the Federal-Provincial-Territorial Committee on Drinking Water (December, 2010), were reviewed. Health Canada has recommended that custodians consider comparing Site groundwater data with the CDWQG for the protection of future aquifer use as a drinking water source, unless specific aquifer conditions are present at the Site that would make Site groundwater not appropriate for drinking water use. A Health Canada draft memo titled “Memorandum: Contaminated Sites Assessment – Aquifer Protection for Future Use, Health Canada (document not dated)” was referenced as a source which list these conditions. Based on the current Site use and location (former industrial use, immediately adjacent to the coastal shoreline) and the information provided in the Health Canada draft memorandum, drinking water guidelines are not applicable to evaluate Site groundwater.

3.2.2.2 Provincial Standards

For comparison purposes, the CSR Generic Numerical Water Standards for the protection of Marine Aquatic Life (AW), as presented in Schedule 6 of the CSR, were used (for comparison purposes) to evaluate the groundwater data collected at the Site.

3.3 RESULTS

The investigation methodology utilized during the soil and groundwater investigation, including the quality assurance/quality control (QA/QC) methodology, is provided in Appendix I. The investigation locations and results are shown on Figure 5.

3.3.1 Soil Stratigraphy and Drilling Observations

The surficial geology encountered during the drilling program was generally consistent. The surface elevations of the boreholes were relatively similar (within 30 cm), with the exception of BH15-11 (located at the southern-most portion of the Site). The maximum investigated drilling depth was 8.5 m bgs at MW15-1, MW15-2, MW15-3 and BH15-8. General surficial geology encountered at the Site is detailed below in Table H. Detailed descriptions of soil stratigraphy from each borehole, and monitoring well completion details, are included in the borehole logs attached as Appendix H.

The Sonic drill method was chosen in order to obtain representative soil samples and to limit cross contamination across the depth of a location. Visual and olfactory evidence of hydrocarbon impacts were observed in MW15-1 from approximately 2.4 m to 4.0 m. At the same location and depth, recovery was limited with significant amounts of wood debris. It was interpreted that there may be a treated timber within the fill at this location. Combustible headspace readings (CHRs) were measured from soil samples and ranged from less than 5 parts per million (ppm) to 17% lower explosive limit (LEL, or 1870 ppm). These readings are recorded on the borehole logs in Appendix H. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 12 - August 2015

Table H Summary of Soil Stratigraphy

Approximate Depth Primary General Soil Description Below Grade (m) Soil Type 0 – 0.3 Topsoil Roots and black, loamy topsoil observed. Sand and Sandy layers with variable amounts of silt, containing suspicious fill-like 0.3 – ~4.0 Silt material including glass, brick, treated lumber and/or asphalt. 4.0 – ~5.5 Sand Coarse-grained sand, with shell fragments. ~5.5 – 8.5 Silty Sand Fine to medium-grained sand with silt.

3.3.2 Groundwater Monitoring

The results of the groundwater monitoring conducted on June 1 and 5, 2015 (MW15-1 only) are as follows:

 As indicated in Section 3.1, groundwater samples were collected on an out-going tide. Tidal efficiency, which is a measure of the aquifer’s responsiveness to the amplitude change of tidal fluctuations in Burrard Inlet, was not evaluated. The hydraulic gradient towards the Burrard Inlet would theoretically be increasing over time during a ‘falling tide’ and be at its greatest at low tide. The wells located at the southern portion of the Site are anticipated to be the least influenced by tidal changes.

 Combustible wellspace readings (CWRs) measured in the groundwater wells were less than 100 ppm in multiple wells and are considered to be low and not indicative of significant petroleum hydrocarbon impacts. The maximum measured CWR from the groundwater was at MW15-2 and was 34% Lower Explosive Limit (LEL). A duplicate sample was obtained from MW15-2 (duplicate MW15-100).

 Depth to groundwater ranged from 2.44 m below top of casing (BTOC) in MW15-4 to 2.65 m BTOC in MW15-2. The inferred general groundwater flow direction was determined to be towards the northwest based on proximity to Burrard Inlet.

 Light Non-Aqueous Phase Liquid (LNAPL) was not detected in the newly installed monitoring wells. One well, MW15-1, was observed to contain a creosote-like odour.

 Conductivity reading for samples collected ranged from 0.37 mS/cm (at MW15-4) to 1.7 mS/cm (at MW15-2).

 Groundwater at the Site is expected, at least in part, to be hydraulically influenced by the changes in tidal stages of Burrard Inlet (based on the proximity to the Site) and/or likely responds to surface water infiltration. Sources of recharge to groundwater in the aquifer are most likely a combination of infiltration of precipitation and influent groundwater flow within the aquifer up- gradient of the Site.

3.4 ANALYTICAL RESULTS

Presented below is a summary of the analytical results of the targeted investigation. Detailed analytical results are tabled in the attached Table 1a-g and Table 2a-b. Analytical reports are attached as Appendix J. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 13 - August 2015

3.4.1 Soil Results

Eighteen samples (including two duplicates) were submitted for analysis of one or more of the following parameters; petroleum hydrocarbons including BTEX, VPH, LEPH, HEPH, EPH, PAHs, VOCs, metals (including pH), and saturated paste chloride and sodium. One soil sample was submitted for the TCLP analysis of leachable lead. The soil analytical results are presented in Tables 1a to 1g and on Figure 6.

The overall objective was to characterize soil quality throughout the planned Project area. As discussed in Section 3.3.1, surficial geology encountered during the drilling program was generally consistent. As it relates to potential metals impacts in soil, sample intervals (ranging from 0.3 m to 4.6 m bgs) were selected in order to provide sufficient coverage for each of the soil units observed at the Site. Considering the assessment for potential hydrocarbon impacts, visual and olfactory evidence of hydrocarbon impacts were only observed at one location (MW15-1); however, presence of wood material in-situ prevented the collection of a sample. Higher than expected CHRs (where no visual and olfactory evidence of hydrocarbon impacts were observed) were measured at MW15-2 and greater than 5.5 m bgs (17% LEL, and 370 ppm, respective). Difficult drilling conditions were encountered at many locations (drilling through dense till), and as such, the sonic drill cores brought to the surface were very hot and contributed to the elevated vapour measurements. This location (MW15-2) with the highest headspace readings did not contain visual or olfactory evidence of hydrocarbon impacts, particularly at depth. Therefore, these specific samples were not selected for analysis based on the field observations made. Sample intervals were selected in order to provide sufficient coverage for each of the soil units observed at the Site, with depths ranging from 1.83 m to 3.05 m bgs, which was consistent with the depth to groundwater observed at the Site.

3.4.1.1 Federal Guidelines

The soil analytical results were compared to the CCME PL guidelines. Concentrations of the analyzed parameters were less than the CCME PL guidelines in each soil sample analyzed with the following exceptions:

 Numerous soil samples submitted for analysis had pH values that were outside the CCME PL guideline range for which the CCME IL guidelines were established (pH of 6 to 8), namely MW15- 1-3, MW15-2-1, BH15-5-1, BH15-5-2, BH15-8-2; and,

 Concentrations of select metals were greater than the applicable CCME guideline and/or CSR PL standards at MW15-3-1 (lead and zinc) at 0.3 m below ground surface (mbgs) and BH15-8-2 (copper, lead and zinc) at 0.6 mbgs. Both locations had a sample at a greater depth (2.6 mbgs) that had concentrations of all metals below the applicable standards. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 14 - August 2015

3.4.1.2 Provincial Standards

BC CSR

The soil analytical results were compared to the BC CSR PL standards.

Concentrations of the analyzed parameters were less than the BC CSR PL standards in each soil sample analyzed with the exception of zinc at MW15-3-1 at 0.3 mbgs. The sample collected below this interval at 2.6 mbgs had a zinc concentration less than the CSR standard.

BC HWR

Upon receipt of the soil analytical results, three samples (MW15-2-1, MW15-3-1 and BH15-8-2) had lead concentrations greater than twenty times the HWR LQS concentration for lead, which is regarded as a trigger to analyze for TCLP leachable concentrations. One sample was submitted for analysis, BH15-8-2, which had the highest concentration of lead.

Analytical results showed that the concentration of leachable lead in BH15-8-2 was below the applicable HWR LQS standard (see Table 1g).

Schedule 7 Soil Relocation

The soil analytical results were also evaluated using the BC CSR Schedule 7 standards for soil relocation to agricultural and non-agricultural land.

Concentrations of select metals (lead, mercury, tin and/or zinc) were greater than the Schedule 7 standard at MW15-2, MW15-3 and MW15-8. Concentrations of select PAHs (benzo(a)anthracene, benzo(a)pyrene, benzo(b,j)fluoranthene, phenanthrene and/or pyrene) were greater than the Schedule 7 standards at MW15-1, MW15-3, BH15-9 and BH15-10 (see Table 1e).

All other concentrations of analyzed parameters were less than the BC CSR Schedule 7 standards.

3.4.2 Groundwater Results

Four samples (including one duplicate (MW15-100) were submitted for analysis of petroleum hydrocarbons, BTEX, VHw, VPHw, EPH, LEPHw, HEPHw, PAHs, MTBE, dissolved metals and/or hardness. Upon receipt of the groundwater analytical results, elevated concentrations in one location (MW15-1) prompted the re-development and re-sampling for select parameters. The groundwater analytical results are presented in Tables 2a and 2b and on Figure 7. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 15 - August 2015

3.4.2.1 Federal Guidelines

Analytical results for the groundwater samples collected from the newly installed groundwater monitoring wells were evaluated using CCME MAL (x10). The groundwater results were less than the applicable CCME MAL (x10) in the four wells sampled, with the exception of an elevated concentration of naphthalene (sampled twice; 25 µg/L and 29 µg/L, respectively) in the samples collected from MW15-1.

3.4.2.2 Provincial Standards

Analytical results for the groundwater samples were also compared to BC CSR AW standards.

The groundwater results were less than the CSR AW standards in wells MW15-2, MW15-3, and MW15-4. Concentrations of LEPHw, naphthalene, phenanthrene and pyrene exceeded the CSR AW standard in MW15-1.

The analytical results obtained from the resampling event on June 5, 2015 at MW15-1 confirmed the presence of groundwater petroleum hydrocarbons at that location.

3.4.3 QA/QC

Hemmera’s field quality assurance/quality control program (QA/QC) included practicing standard soil and groundwater sampling protocols to minimise the potential for cross contamination between samples. The field QA/QC procedure also included the collection and analysis of field duplicates. Where field duplicates were collected, relative percent difference (RPD) calculations were completed between characterization samples and their duplicates. RPDs are calculated as the difference between a sample and its field duplicate, over the average of the two values. RPDs were not calculated where concentrations were less than five times the detection limit, which is considered to be too low to accurately calculate RPD values. RPD calculations were completed for soil and groundwater samples, and are presented with analytical results in Tables 1a-d and 2a-b. The RPD data quality objectives (DQO) selected for soil and groundwater were 40% and 20% respectively and are considered acceptable for this investigation.

The soil duplicate set RPD results were within the quality objective with the exception of antimony (54%) and tin (60%). The groundwater sample duplicate set results are within the stated DQOs for RPDs.

The discrepancy in RPD calculations are likely attributable to the general heterogeneous nature of fill material. This variability between the original and duplicate sample analytical results is not expected to significantly affect the interpretation of the overall findings and is considered to be adequate to warrant the conclusions made in this report. PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 16 - August 2015

Soil and groundwater sample analyses were completed by Maxxam Analytics in Burnaby, BC. The samples submitted to Maxxam were subjected to QA/QC procedures specific to the laboratory. Laboratory QA/QC included internal/surrogate standards, replicates and duplicates, method blanks and method spikes. As a general QA/QC measure, the analytical detection limits were also reviewed to check that they were below the applicable standards for each parameter tested. The Maxxam QA/QC results are included with each certified laboratory report (Appendix J).

3.5 SUMMARY AND DISCUSSION

The following is a summary of the Phase 2 ESA investigation results:

 Suspect fill material was found across the Site upwards of 4 to 5 mbgs;

 Soil sample analytical results were less than the CCME PL and CSR PL guidelines/standards with the exception of copper, lead and zinc in surface soil within the centre of the Site. These exceedances were delineated vertically, but the horizontal extent has not been analyzed or delineated by this Phase 2 ESA;

 Numerous soil samples submitted for analysis had pH values that were outside the CCME PL guideline range. This does not appear to be impacting groundwater quality at the Site, based on groundwater monitoring (pH in groundwater ranged from 6.6 to 7.6 – relatively neutral) ;

 Soil samples across the Site exceeded the BC CSR Schedule 7 standards for soil relocation to agricultural and non-agricultural lands;

 The soil samples submitted for TCLP analysis of leachable lead did not exceed the HWR LQS for lead; and,

 Elevated concentrations of LEPHw, naphthalene, phenanthrene and pyrene were identified in Site groundwater (at one location (MW15-1) above the applicable CCME guidelines and/or the BC CSR standards.

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 17 - August 2015

4.0 PHASE 1 AND 2 ESA CONCLUSIONS

Table I below summarizes the results of the Phase 1 and 2 ESA.

Table I Summary Phase 1 and 2 ESA Results

APEC Description Results COCs

Fill Material of Soil > CSR PL, CCME PL Soil: copper, lead, zinc 1 unknown Groundwater > BC CSR AW, Groundwater: LEPHw, naphthalene, quality/origin CCME MAL(x10) phenanthrene, and pyrene Notes: APEC = Area of Potential Environmental Concern COCs = Contaminants of Concern

Based on the above results, the Phase 2 ESA identified elevated concentrations of metals in soil exceeding both the Federal guidelines and Provincial standards. In groundwater, elevated concentrations of petroleum hydrocarbons exceeding the applicable Federal guidelines, as well as the Provincial standards (used for comparison purposes) within the footprint of the proposed Project, were identified.

Additional work is required to fully delineate the contaminated soil and groundwater within the Project area. Furthermore, if excavated soil requires off-site disposal as part of the future/potential construction activities, soils with concentrations above Soil Relocation standards would require disposal at an appropriately licensed landfill facility, or they would require a Contaminated Soil Relocation Agreement (CSRA) if relocated to property under Provincial jurisdiction.

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 18 - August 2015

We trust this meets your requirements at this time. If you have any questions please feel free to contact either of the undersigned.

Report prepared by: Hemmera Envirochem Inc.

Tracey L’Espérance, B.Sc., R.P.Bio. Environmental Scientist 604.669.0424 (428) [email protected]

Report reviewed by: Hemmera Envirochem Inc.

James Mair, Geo.L., PMP Chuck Jochems, P.Eng., CSAP Project Manager Project Director 604.669.0424 (119) 604.669.0424 (433) [email protected] [email protected]

This document represents an electronic version of the original hard copy document, sealed, signed and dated by Tracey L’Espérance, B.Sc., R.P.Bio., James Mair, Geo.L., PMP and Chuck Jochems, P.Eng., CSAP and retained on file. The content of the electronically transmitted document can be confirmed by referring to the original hard copy and file. This document is provided in electronic format for convenience only. Hemmera Envirochem Inc. shall not be liable in any way for errors or omissions in any electronic version of its report document.

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 19 - August 2015

5.0 REFERENCES

Aerial photographs obtained from the University of British Columbia Geographic Information Centre and the City of Vancouver VanMap website: 1949, 1954, 1963, 1969, 1978, 1979, 1986, 1993, 1999, 2004, 2009, 2011, and 2013.

British Columbia Contaminated Sites Regulation (BC CSR). 2009 BC Reg. 375/96 (Effective April 1997 and amended July 1999, November 1999, February 2002, November 2003, July 2004, July 2007, January 2013 and January 2014), including amendments up to B.C. Reg. 4/2014, effective January 31, 2014.

British Columbia Ministry of Environment. 2005. Environmental Management Act, Contaminated Sites Regulation, B. C. Reg. 375/96, July 2004 (including amendments as of January 24, 2013).

British Columbia Ministry of Environment. 2005. Technical Guidance Document 10, Checklist for Reviewing a Preliminary Site Investigation, October 2005.

British Columbia Ministry of Environment, BC Water Resource Atlas website available at: http://www.env.gov.bc.ca/wsd/data_searches/wrbc/

BC Ministry of Environment Site Registry [Online] accessed via < https://www.bconline.gov.bc.ca/>

Canadian Council of Ministers of the Environment. Environmental Guidelines, 1999.

Canadian Council of Ministers of the Environment. Canada Wide Standards for Petroleum Hydrocarbons (PHC) in Soil, April – May 2004.

Canadian Council of Ministers of the Environment, Canada-Wide Standard for Petroleum Hydrocarbons (PHC) in Soil. January 2008.

Canada-Wide Standard for Petroleum Hydrocarbons in Soil: Scientific Rationale Supporting Technical Document. January, 2008. PN1399.

Geological Survey of Canada. 1976. Surficial Geology Vancouver. Map 1486.

Goad’s Fire Insurance, Map 1912. Obtained from VanMap

Keystone Environmental Limited. Report of Findings. Preliminary Site Investigation, Stage 1. New Brighton Park, Vancouver, BC. May 1997.

Keystone Environmental Limited. Report of Findings. Preliminary Site Investigation, Stage 2. New Brighton Park, Vancouver, BC. July 1997.

Treasury Board of Canada Secretariat, Federal Contaminated Sites Inventory, [Online], accessed via http://www.federalcontaminatedSites.gc.ca/default.asp?lang=En

PMV – Habitat Enhancement Program Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 20 - August 2015

6.0 STATEMENT OF LIMITATIONS

This report was prepared by Hemmera Envirochem Inc. (“Hemmera”), based on fieldwork conducted by Hemmera, for the sole benefit and exclusive use of Port Metro Vancouver. The material in it reflects Hemmera’s best judgment in light of the information available to it at the time of preparing this Report. Any use that a third party makes of this Report, or any reliance on or decision made based on it, is the responsibility of such third parties. Hemmera accepts no responsibility for damages, if any, suffered by any third party as a result of decisions made or actions taken based on this Report.

Hemmera has performed the work as described above and made the findings and conclusions set out in this Report in a manner consistent with the level of care and skill normally exercised by members of the environmental science profession practicing under similar conditions at the time the work was performed.

This Report represents a reasonable review of the information available to Hemmera within the established Scope, work schedule and budgetary constraints. It is possible that the levels of contamination or hazardous materials may vary across the Site, and hence currently unrecognised contamination or potentially hazardous materials may exist at the Site. No warranty, expressed or implied, is given concerning the presence or level of contamination on the Site, except as specifically noted in this Report. The conclusions and recommendations contained in this Report are based upon applicable legislation existing at the time the Report was drafted. Any changes in the legislation may alter the conclusions and/or recommendations contained in the Report. Regulatory implications discussed in this Report were based on the applicable legislation existing at the time this Report was written.

In preparing this Report, Hemmera has relied in good faith on information provided by others as noted in this Report, and has assumed that the information provided by those individuals is both factual and accurate. Hemmera accepts no responsibility for any deficiency, mis-statement or inaccuracy in this Report resulting from the information provided by those individuals.

The liability of Hemmera to Port Metro Vancouver shall be limited to injury or loss caused by the negligent acts of Hemmera. The total aggregate liability of Hemmera related to this agreement shall not exceed the lesser of the actual damages incurred, or the total fee of Hemmera for services rendered on this project.

FIGURES

Site Location

VANCOUVER HARBOUR

0 5 10

Kilometres Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig01_302_035_04_SiteLocation_150618.mxdBrighton Path:

Wall St

Canadian PacificRailway

McGill St N Win der mer e St

p

m a E Hastings St Onramp r p n m O ra t ff S l O l t i S E Hastings St Offramp l G il c G c M M

Site Boundary / Proposed area FIG No. 1 Habitat Enhancement Program for habitat enhancement project ± 0 50 100 TITLE: New Brighton Park Metres Site Location Map Note: Map Scale - 1:2500; Imagery - City of Vancouver (2011) NAD 1983 UTM Zone 10N Date: 19/08/2015 Lease NEW reference BRIGHTON PARK 1-01-0046 VANCOUVER HARBOUR

Lease Lease reference reference 1-01-00445 Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig02_302_035_04_SitePlan_SLU_150618.mxdBrighton Path: 1-01-0043

Lease reference CASCADIA TERMINALS 1-01-00444

Wall St N Windermere St Canadian PacificRailway

CREEKWAY E Hastings HASTINGS St Offramp RACECOURSE PARK E Hastings St Onramp McGill St McGill St Offramp McGill St Onramp

City of Vancouver owned property Parcel Boundary FIG No. 2 Habitat Enhancement Program PMV Lease to City Of Vancouver Site Boundary / Proposed area for ± habitat enhancement project 0 50 100 TITLE: New Brighton Park Metres Site Plan and Surrounding Land Use Note: Map Scale - 1:2500; Imagery - City of Vancouver (2011); Parcel Boundaries - City of Vancouver (2014) NAD 1983 UTM Zone 10N Date: 19/08/2015 Former industrial activity. Industry themes include VANCOUVER gypsum, coal shingles, HARBOUR timber & boatyards.

Yale St

New Brighton Park Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig03_302_035_04_HistoricLandUse_150618.mxdBrighton Path: Park and Pool

Wall St (mid 30s to present)

Cascadia Terminals (FormerlyWheat Alberta Pool)

N Windermere St

Canadian PacificRailway

Creekway Park McGill St Offramp McGill St HASTINGS

RACECOURSE McGill St Onramp N Renfrew St

Parcel Boundary FIG No. 3 Habitat Enhancement Program Site Boundary / Proposed area ± for habitat enhancement project 0 50 100 TITLE: New Brighton Park Metres Historic Land Use Plan Note: Map Scale - 1:2500; Imagery - City of Vancouver (1969); Parcel Boundaries - City of Vancouver (2014) NAD 1983 UTM Zone 10N Date: 19/08/2015 VANCOUVER HARBOUR

APEC 1

Fill of unknown quality/ origin placed during site infilling.

Former Industrial Activites at the South Shore of Burrard Inlet. Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig04_302_035_04_APECS_150618.mxdBrighton Path:

New Brighton Park

APEC Site Boundary / Proposed area FIG No. 4 Habitat Enhancement Program Parcel Boundary for habitat enhancement project ± 0 15 30 TITLE: New Brighton Park Metres Site Plan with APEC Note: Map Scale - 1:750; Imagery - City of Vancouver (2011); Parcel Boundaries - City of Vancouver (2014) NAD 1983 UTM Zone 10N Date: 19/08/2015 VANCOUVER HARBOUR

BH97-14 BH97-10

BH97-12

BH15-5 BH15-6 MW15-1

BH15-7 MW15-2 BH97-15

BH15-8 MW15-3

BH97-11 New BH15-10 Brighton BH97-13 BH15-9 Park MW15-4 Path: O:\!300-325\302-035_HEP\04\G - Special Projects\New Park\mxd\Fig05_302_035_04_InvestLocations_150618.mxdBrighton Special Projects\New - O:\!300-325\302-035_HEP\04\G Path:

BH15-11 MW97-1

Canadian PacificRailway Monitoring Well Storm sewer drain Parcel Boundary FIG No. Borehole 5 Habitat Enhancement Program Keystone, 1997 (Approximate Site Boundary Location) 0 15 30 TITLE: New Brighton Park Metres Catch Basin Investigation Locations NAD 1983 UTM Zone 10N Date: 18/06/2015 Note: Map Scale - 1:750; Imagery - City of Vancouver (2011); Parcel Boundaries - City of Vancouver (2014) Location ID: MW15-1 MW15-2 MW15-3 MW15-4 BH15-5 BH15-6 Sample ID: MW15-1-1 MW15-1-2 MW15-1-3 MW15-1-4 MW15-2-1 MW15-2-2 MW15-2-6 MW15-3-1 MW15-3-2 MW15-3-4 MW15-4-3 BH15-5-1 BH15-5-2 BH15-6-1 VANCOUVER Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 HARBOUR Sample Depth (m): 0.30-0.61 1.83-2.13 3.05-4.57 6.10-6.40 0.30-0.61 1.83-2.13 4.72-5.03 0.30-1.22 2.59-3.05 5.18-5.49 1.07-1.30 0.91-2.44 2.74-3.05 0.46-0.76 Parameter BC CSR PL CCME RL/PL Copper 90-150 63 31.2 - 6.55 - 33.7 28.7 - 48.2 34.4 - 25.1 27.4 27.6 26.5

Lead 100-400 140 40.4 - 8.84 - 101 35.6 - 163 55.5 - 81.7 28.4 37.4 26.9 Zinc 150-450 200 76.4 - 25.1 - 81.3 61.1 - 234 88.5 - 119 69.6 61.8 54.8 Remaining Total Metals VPH * * ------ND - - - - - PHCs * * ------ND - - - - - BH15-5 BH15-6 ! !&>! MW15-2 (Duplicate) (Duplicate) !! &< BH97-15 !! &> 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 26/05/2015 26/05/2015

Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig06_302_035_04_Soil_150618.mxdBrighton Path: 0.15-0.46 1.83-2.13 0.61-0.91 2.59-2.90 2.59-2.90 4.27-4.57 1.68-1.98 2.59-2.90 2.59-2.90 0.46-0.76 1.98-2.29 0.15-0.76 2.59-3.05 BH15-8 Parameter &>! MW15-3 Copper 22.3 20 65.3 20.3 19.7 - 14.1 26 24.5 18.3 - 22.4 - ! Lead 20.1 12.8 47.6 33.9 - 35.3 54.7 56.9 8.44 - 48.8 - &! Total Inorganics - - - - - &>! ! MW15-4 Brighton ! BTEXS ------ND ND - - - ND &

Notes: All results in ug/g, unless otherw ise stated BTEX = Benzene, Toluene, Ethylbenzene, Xylenes, Styrene * = Refer to report tables for applicable standard(s) EPH = Extractable Petroleum Hydrocarbons < = one or more results detectable, but less than applicable standards VPH = Volatile Petroleum Hydrocarbons ND = All results non-detectable and less than applicable standards PHCs = Petroleum Hydrocarbons - = not analyzed PAH = Polycyclic Aromatic Hydrocarbons CSR = British Columbia Contaminated Sites Regulation VOC = Volatile Organic Compounds CCME = Canadian Environmental Quality Guidelines

PL = Urban Park Land Use Standards 123 greater than BC CSR standards BH15-11 RL = Residential Land Use Standards 123 greater than CCME standards !&>! MW97-1 &> Canadian PacificRailway

&< Monitoring Well ! Soil result is less than BC CSR Storm sewer drain FIG No. ! standards and/or CCME guidelines 6 Habitat Enhancement Program &> Borehole Parcel Boundary ± Soil result exceeds BC CSR standards 0 15 30 TITLE: g Catch Basin !! Site Boundary New Brighton Park and/or CCME guidelines Metres Soil Analytical Results Note: Map Scale - 1:750; Imagery - City of Vancouver (2011); Parcel Boundaries - City of Vancouver (2014) NAD 1983 UTM Zone 10N Date: 19/08/2015 Provincial Standards Have Been Used For Comparison Purposes Only VANCOUVER HARBOUR

Location ID: MW15-1 MW15-2 MW15-3 MW15-4 New BH97-14 MW15-100 Sample ID: MW15-1 MW15-2 MW15-3 MW15-4 Brighton &> (dup) BH97-10 &> Park Date Sampled: 6/1/2015 6/5/2015 6/1/2015 6/1/2015 6/1/2015 6/1/2015 Parameter BC CSR AW CCME MALx10 Screen interval (m) - - 2.3 - 3.9 2.3 - 3.9 2.3 - 3.0 2.3 - 3.9 1.8 - 3.4 1.9 - 3.5 BH97-12 Well Depth, To Water (m) - - 2.588 3.333 2.653 2.653 2.641 2.442 &> &> MW15-2 Remaining EPH * * VHw /VPHw * * ND - ND ND ND ND

Path: O:\!300-325\302-035_HEP\New Park\mxd\Fig07_302_035_04_GW_150813.mxdBrighton Path: PHCs F1 - - ND - ND ND ND ND

BH15-8 Naphthalene 10 14 25 29 1.4 1.6 0.18 ND &> MW15-3 & g (x10) BH15-10 BH97-13 BH15-9 &> MTBE 4400 50000 ND ND ND ND ND ND &> &> &

Notes: All results in ug/L, unless otherw ise stated BTEX = Benzene, Toluene, Ethylbenzene, Xylenes * = Refer to report tables for applicable guideline(s)/standard(s) LEPH = Light Extractable Petroleum Hydrocarbons < = one or more results detectable, but less than applicable standards EPH = Extractable Petroleum Hydrocarbons ND = All results non-detectable and less than applicable standards VPH = Volatile Petroleum Hydrocarbons - = not analyzed PHCs = Petroleum Hydrocarbons CSR = British Columbia Contaminated Sites Regulation PAH = Polycyclic Aromatic Hydrocarbons CCME = Canadian Environmental Quality Guidelines MTBE = Methyl tert-butyl ether AW = Aquatic Life Use standard BH15-11 MAL = Marine Aquatic Life 2200 greater than BC CSR AW standards &> PL = Urban Park Land Use Standards 0.12 greater than CCME MAL (x10) guidelines MW97-1 RL = Residential Land Use Standards &>

Canadian PacificRailway

&< Monitoring Well Groundwater result is less than BC CSR Storm sewer drain ! FIG No. ! standards and/or CCME MAL (x10) guidelines 7 Habitat Enhancement Program &> Borehole Parcel Boundary ± ! Groundwater result exceeds BC CSR standard 0 15 30 TITLE: g Catch Basin ! and/or CCME MAL (x10) guidelines Site Boundary New Brighton Park Metres Note: Map Scale - 1:750; Imagery - City of Vancouver (2011); Parcel Boundaries - City of Vancouver (2014) Groundwater Analytical Results Date: 19/08/2015 Provincial Standards Have Been Used For Comparison Purposes Only NAD 1983 UTM Zone 10N

TABLES Table 1a: Soil Metals Analytical Results

Location ID: MW15-1 MW15-2 MW15-3MW15-4 BH15-5 Sample ID: MW15-1-1 MW15-1-3 MW15-2-1 MW15-2-2 MW15-3-1 MW15-3-2 MW15-4-3 BH15-5-1 BH15-5-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 Sample Depth (m): 0.30-0.61 3.05-4.57 0.30-0.61 1.83-2.13 0.30-1.22 2.59-3.05 1.07-1.30 0.91-2.44 2.74-3.05

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

Plant Available Nutrients Potassium (K) - - 818 484 843 900 570 779 612 1050 861

Field Tests

pH - 6-8 18,19 7.75 8.7 8.27 7.46 6.36 6.64 6.68 9.97 8.3

Total Metals Aluminum - - 13000 5010 14500 23100 20500 14300 17500 16100 18100 Antimony 20 7 20 18 0.89 0.24 1.48 0.41 0.97 0.81 0.9 0.52 0.63 Arsenic 25 8 12 20 3.45 1.91 3.55 5.69 4.89 3.09 4.98 2.84 4.11 Barium 1000 9 500 20 73.5 21.9 85.6 118 110 96.4 103 82 88.5 Beryllium 4 7 4 18 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 Bismuth - - <0.10 <0.10 <0.10 <0.10 0.13 <0.10 0.11 <0.10 <0.10 Cadmium 2-70 10 10 20 0.252 0.116 0.34 0.151 0.709 0.224 0.278 0.225 0.199 Calcium - - 6880 26800 6060 3920 3250 3980 3710 15000 7780 Chromium 60 8 64 20 21 7 18.9 27.8 22.3 15.8 16.6 17.3 24.3 Cobalt 50 7 50 18 7.43 3.02 6.83 10.8 9.58 7.47 5.87 8.24 7.9 Copper 90-150 11 63 20 31.2 6.55 33.7 28.7 48.2 34.4 25.1 27.4 27.6 Iron - - 19200 9750 19700 24700 22700 18300 18300 20300 21300

Lead 150-400 12 140 20 40.4 8.84 101 35.6 163 55.5 81.7 28.4 37.4 Lithium 1600 13 - 7.7 <5.0 6.7 10.7 8.1 6.9 5.8 8.5 8.5 Magnesium - - 5600 2770 4620 6530 4530 5550 3820 6130 5190 Manganese 1800 13 - 352 148 289 369 314 239 268 323 342 Mercury 15 14 6.6 20 0.062 <0.050 0.685 0.057 0.296 <0.050 0.07 <0.050 0.06 Molybdenum 10 7 10 18 0.77 0.54 0.74 0.98 0.97 0.62 1.18 0.66 1.62 Nickel 100 7 50 20 18.5 5.08 13.2 19.3 17 11.7 10.3 11.7 13.8 Phosphorus - - 527 276 452 408 710 343 545 384 421 Sodium (Na) - - 246 496 344 408 148 194 212 396 323 Selenium 3 7 1 20 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 Silver 20 7 20 18 0.068 <0.050 0.098 0.056 0.418 0.056 0.094 0.052 0.065 Strontium 47000 13 - 38.6 156 44.6 36.8 34.8 34.7 34.9 59.5 42.1 Thallium - 1 20 0.059 0.078 0.054 0.065 <0.050 0.058 0.055 0.063 0.067 Tin 50 7 50 18 1.92 0.36 15.4 12.5 6.83 2.01 2.96 1.94 1.6 Titanium - - 621 283 559 955 685 522 687 626 788 Uranium 16 13 23 20 0.41 0.369 0.375 0.564 0.483 0.507 0.414 0.492 0.48 Vanadium 200 7 130 20 44.7 22.7 46.3 61.4 50 43.5 50.1 48 53.7 Zinc 150-450 15 200 20 76.4 25.1 81.3 61.1 234 88.5 119 69.6 61.8 Zirconium - - 1.06 0.99 1.44 2.49 0.69 1.73 0.76 2.48 1.26

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 1 of 7 August 2015 Table 1a: Soil Metals Analytical Results

Location ID: BH15-6 BH15-7 BH15-8 BH15-9 BH15-10 BH15-11 Sample ID: BH15-6-1 BH15-7-1 BH15-7-2 BH15-8-2 BH15-8-4 BH15-8-5 BH15-9-1 BH15-9-3 BH15-9-4 BH15-10-1 BH15-11-1 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015RPD% 25/05/2015 25/05/2015 25/05/2015RPD% 25/05/2015 26/05/2015 Sample Depth (m): 0.46-0.76 0.15-0.46 1.83-2.13 0.61-0.91 2.59-2.90 2.59-2.90 1.68-1.98 2.59-2.90 2.59-2.90 0.46-0.76 0.15-0.76

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

Plant Available Nutrients Potassium (K) - - 727 864 842 761 553 587 6 442 722 641 12 606 536

Field Tests

pH - 6-8 18,19 7.26 7.93 7.48 8.1 7.02 6.95 1 7.23 7.52 7.23 4 6.52 6.5

Total Metals Aluminum - - 14700 12300 19700 14300 16400 15900 3 13700 16300 16300 0 18100 17300 Antimony 20 7 20 18 0.4 0.3 0.16 7.44 1.49 0.86 54 1 1.61 0.78 69 0.22 1.3 Arsenic 25 8 12 20 2.91 1.84 3.19 5.82 3.23 2.97 8 2.74 3.51 3.56 1 3.1 3.86 Barium 1000 9 500 20 78.6 66.2 96.3 222 85.5 85.8 0 60.7 113 110 3 91 85.7 Beryllium 4 7 4 18 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 nc <0.40 <0.40 <0.40 nc <0.40 <0.40 Bismuth - - <0.10 <0.10 <0.10 0.14 <0.10 <0.10 nc <0.10 <0.10 <0.10 nc <0.10 <0.10 Cadmium 2-70 10 10 20 0.14 0.114 0.111 0.856 0.192 0.195 2 0.106 0.28 0.258 8 0.12 0.211 Calcium - - 3550 3450 2750 9810 3170 2640 18 2990 4410 3540 22 3980 3330 Chromium 60 8 64 20 17.3 14 19.1 20.6 15.8 15.4 3 10.6 20.4 20 2 22.8 16 Cobalt 50 7 50 18 6.93 7.08 9.23 7 6.32 6.38 1 5.57 6.82 6.66 2 8.79 5.9 Copper 90-150 11 63 20 26.5 22.3 20 65.3 20.3 19.7 3 14.1 26 24.5 6 18.3 22.4 Iron - - 17900 17500 20400 25400 16800 17000 1 13800 18200 17200 6 20100 16900

Lead 150-400 12 140 20 26.9 20.1 12.8 180 47.6 33.9 34 35.3 54.7 56.9 4 8.44 48.8 Lithium 1600 13 - 8.2 6.1 10 8.1 8.1 7.7 5 6.9 7.9 7.9 0 9.7 7.4 Magnesium - - 4930 5090 6620 4400 4920 4650 6 4020 4360 4090 6 4740 4240 Manganese 1800 13 - 294 287 287 391 280 260 7 272 291 278 5 423 294 Mercury 15 14 6.6 20 <0.050 0.059 <0.050 0.107 <0.050 <0.050 nc <0.050 <0.050 0.056 nc <0.050 0.083 Molybdenum 10 7 10 18 0.52 0.35 0.65 1.21 0.7 0.64 9 0.62 1.12 1.23 9 0.62 0.65 Nickel 100 7 50 20 12.5 10.7 14.3 18 10.9 10.2 7 7.38 11.9 12 1 15.7 11.5 Phosphorus - - 400 365 322 651 403 349 14 319 415 364 13 290 439 Sodium (Na) - - 218 256 205 414 161 160 1 135 166 164 1 190 125 Selenium 3 7 1 20 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 nc <0.50 <0.50 <0.50 nc <0.50 <0.50 Silver 20 7 20 18 0.055 <0.050 <0.050 0.131 0.077 0.064 18 0.061 0.06 0.068 13 <0.050 0.074 Strontium 47000 13 - 31.1 28.3 32.9 130 36.2 32.7 10 30.5 43.7 40.7 7 40 28 Thallium - 1 20 0.06 <0.050 0.071 <0.050 <0.050 <0.050 nc <0.050 0.069 0.068 1 <0.050 <0.050 Tin 50 7 50 18 1.17 1.15 0.35 32.1 3.99 2.15 60 0.8 4.15 4.18 1 0.35 3.71 Titanium - - 559 588 770 585 589 609 3 512 511 534 4 771 583 Uranium 16 13 23 20 0.458 0.307 0.375 0.497 0.402 0.406 1 0.354 0.46 0.451 2 0.449 0.513 Vanadium 200 7 130 20 44.8 42.1 50.7 48.1 44.9 45.6 2 36.2 41.7 41.4 1 51.8 41.3 Zinc 150-450 15 200 20 54.8 45.4 65.7 379 70.4 69.6 1 52.7 81.3 99.2 20 37.5 78.4 Zirconium - - 0.77 2.05 2.92 1.42 0.98 1.2 20 <0.50 1.47 1.24 17 0.94 0.57

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 2 of 7 August 2015 Table 1b: Soil Saturated Paste and Leachable Metals Analytical Results

Location ID: MW15-1 MW15-2 MW15-3 BH15-8 Sample ID: MW15-1-4 MW15-2-6 MW15-3-4 BH15-8-6 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 Sample Depth (m): 6.10-6.40 4.72-5.03 5.18-5.49 4.27-4.57

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

Leachate Inorganics Chloride (mg/L) - - 29.1 85.1 105 78.5 Sodium (ug/L) - - 18100 36500 27600 16900

Total Inorganics Chloride 90 - 14.8 52.4 82.3 41 Sodium 200 - 9.2 22.5 21.6 8.8

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 3 of 7 August 2015 Table 1c: Soil Hydrocarbons Analytical Results

Location ID: MW15-1 MW15-3BH15-9 BH15-10 BH15-11 Sample ID: MW15-1-2 MW15-1-3 MW15-3-2 BH15-9-3 BH15-9-4 BH15-10-2 BH15-11-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015RPD% 25/05/2015 26/05/2015 Sample Depth (m): 1.83-2.13 3.05-4.57 2.59-3.05 2.59-2.90 2.59-2.90 1.98-2.29 2.59-3.05

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

Field Tests Field Vapours (ppm) - - 0 5 150 160 160 - 10 200

Physical Tests Moisture (%) - - 8 18 15 17 18 - 24 19

BTEX Benzene 2.5 8 0.0068-0.030 21 - - <0.0050 <0.0050 <0.0050 nc - <0.0050 Ethylbenzene 1 9 0.018-0.082 22 - - <0.010 <0.010 <0.010 nc - <0.010 Styrene 5 7 5 18 - - <0.030 <0.030 <0.030 nc - <0.030 Toluene 1.5 9 0.08-0.37 23 - - <0.020 <0.020 <0.020 nc - <0.020 Xylenes 5 9 2.4-11 24 - - <0.040 <0.040 <0.040 nc - <0.040

EPH EPH10-19 - - <100 <100 - <100 <100 nc 659 <100 EPH19-32 - - 126 <100 - <100 <100 nc 342 <100 LEPH 1000 7 - <100 <100 - <100 <100 nc 659 <100 HEPH 1000 7 - 126 <100 - <100 <100 nc 342 <100

VPH VH6-10 - - - - <10 <10 <10 nc - <10 VPH 200 7 - - - <10 <10 <10 nc - <10

PHCs F1 (C6-C10) - BTEX 200 16 - - - <10 <10 <10 nc - <10 F1 nC6-10 uncorrected - - - - <10 - - - - <10

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 4 of 7 August 2015 Table 1c: Soil Hydrocarbons Analytical Results

Location ID: MW15-1 MW15-3BH15-9 BH15-10 BH15-11 Sample ID: MW15-1-2 MW15-1-3 MW15-3-2 BH15-9-3 BH15-9-4 BH15-10-2 BH15-11-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015RPD% 25/05/2015 26/05/2015 Sample Depth (m): 1.83-2.13 3.05-4.57 2.59-3.05 2.59-2.90 2.59-2.90 1.98-2.29 2.59-3.05

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

PAH 2-Methylnaphthalene - - <0.020 <0.020 - 0.043 0.025 nc 0.46 <0.020 Acenaphthene - - <0.0050 0.029 - 0.011 0.0092 18 0.05 <0.0050 Acenaphthylene - - 0.011 <0.0050 - 0.055 0.055 0 <0.019 <0.0050 Anthracene - 2.5 25 0.018 0.021 - 0.081 0.076 6 <0.040 <0.0040 Benzo(a)anthracene 1 7 1 26 0.058 0.02 - 0.16 0.14 13 0.074 <0.020 Benzo(a)pyrene 1 9 0.7 27 0.062 <0.020 - 0.16 0.15 6 0.083 <0.020 Benzo(b,j)fluoranthene 1 7 1 26 0.092 0.023 - 0.24 0.24 0 0.12 <0.020 Benzo(g,h,i)perylene - - 0.05 <0.050 - 0.12 0.11 9 0.072 <0.050 Benzo(k)fluoranthene 1 7 1 26 0.027 <0.020 - 0.08 0.074 8 0.03 <0.020 Chrysene - - 0.073 0.026 - 0.21 0.2 5 0.14 <0.020 Dibenz(a,h)anthracene 1 7 1 26 <0.050 <0.050 - <0.050 <0.050 nc <0.050 <0.050 Fluoranthene - 50 25 0.12 0.11 - 0.44 0.42 5 0.19 <0.020 Fluorene - - <0.020 0.033 - 0.042 0.044 5 0.18 <0.020 Indeno(1,2,3-c,d)pyrene 1 7 1 26 <0.050 <0.050 - 0.097 0.097 0 <0.050 <0.050 Naphthalene 5 7 0.6 27 <0.010 0.02 - 0.096 0.036 nc 0.082 <0.010 Phenanthrene 5 7 5 26 0.053 0.11 - 0.34 0.31 9 0.41 <0.020 Pyrene 10 7 10 26 0.13 0.083 - 0.42 0.41 2 0.2 <0.020 Total HMW PAH's - - 0.61 0.26 - 1.9 1.8 5 0.91 <0.050 Total LMW PAH's - - 0.083 0.21 - 0.67 0.55 20 1.2 <0.050 Total PAH's - - 0.7 0.47 - 2.6 2.4 8 2.1 <0.050

Benzo(a)pyrene Total Potency Equivalents (text) - - 0.11 <0.10 - 0.25 0.24 - 0.14 <0.10

Index of Additive Cancer Risk (text) - - 1.2 0.43 - 3.2 3.1 - 1.6 0.31

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 5 of 7 August 2015 Table 1d: Soil Volatile Organic Compounds Analytical Results

Location ID: MW15-3BH15-9 BH15-11 Sample ID: MW15-3-2 BH15-9-3 BH15-9-4 BH15-11-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015RPD% 26/05/2015 Sample Depth (m): 2.59-3.05 2.59-2.90 2.59-2.90 2.59-3.05

Parameter BCCSR PL 3,4 CCME RL/PL 5,6

VOC 1,1,1,2-Tetrachloroethane 32 13 - - <0.025 <0.025 nc <0.025 1,1,1-Trichloroethane 5 7 5 18 - <0.025 <0.025 nc <0.025 1,1,2,2-Tetrachloroethane 4.1 13 5 18 - <0.025 <0.025 nc <0.025 1,1,2-Trichloroethane 5 7 5 18 - <0.025 <0.025 nc <0.025 1,1-Dichloroethane 5 7 5 18 - <0.025 <0.025 nc <0.025 1,1-Dichloroethene 5 7 5 18 - <0.025 <0.025 nc <0.025 1,2,3-Trichlorobenzene - 2 18 - <0.025 <0.025 nc <0.025 1,2,4-Trichlorobenzene - 2 18 - <0.025 <0.025 nc <0.025 1,2-Dibromoethane (ethylene dibromide) (EDB) 0.32 13 - - <0.025 <0.025 nc <0.025 1,2-Dichlorobenzene 1 7 1 18 - <0.025 <0.025 nc <0.025 1,2-Dichloroethane 5 7 5 18 - <0.025 <0.025 nc <0.025 1,2-Dichloroethene (cis) 5 13 5 18 - <0.025 <0.025 nc <0.025 1,2-Dichloroethene (trans) 5 13 5 18 - <0.025 <0.025 nc <0.025 1,2-Dichloropropane 5 7 5 18 - <0.025 <0.025 nc <0.025 1,3-Dichlorobenzene 1 7 1 18 - <0.025 <0.025 nc <0.025 1,3-Dichloropropene (cis) 5 7 - - <0.050 <0.050 nc <0.050 1,3-Dichloropropene (trans) 5 7 - - <0.050 <0.050 nc <0.050 1,4-Dichlorobenzene 1 7 1 18 - <0.025 <0.025 nc <0.025 Bromodichloromethane (BDCM) 8.2 13 - - <0.050 <0.050 nc <0.050 Bromomethane (methyl bromide) 3.9 13 - - <0.30 <0.30 nc <0.30 Chlorobenzene 1 7 1 18 - <0.025 <0.025 nc <0.025 Chloroethane (ethyl chloride) 30 13 - - <0.10 <0.10 nc <0.10 Chloroethene (vinyl chloride) 0.79 13 - - <0.060 <0.060 nc <0.060 Dibromochloromethane (DBCM) 11 13 - - <0.050 <0.050 nc <0.050 Dichloromethane (methylene chloride) 5 7 5 18 - <0.10 <0.10 nc <0.10 Hexachlorobutadiene (HCBD) 62 13 - - <0.20 <0.20 nc <0.20 Methyl tert-butyl ether (MTBE) 320 13 - <0.10 <0.10 <0.10 nc <0.10 Monochloromethane (methyl chloride) 47 13 - - <0.10 <0.10 nc <0.10 Tetrachloroethylene (PERC) 5 9 0.2 20 - 0.035 <0.025 nc <0.025 Tetrachloromethane (carbon tetrachloride) 5 7 5 18 - <0.025 <0.025 nc <0.025 Tribromomethane (bromoform) 620 13 - - <0.050 <0.050 nc <0.050 Trichloroethylene (TCE) 0.65 17 0.01 20 - <0.0090 <0.0090 nc <0.0090 Trichlorofluoromethane (Freon 11) 390 13 - - <0.20 <0.20 nc <0.20 Trichloromethane (chloroform) 5 7 5 18 - <0.050 <0.050 nc <0.050

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 6 of 7 August 2015 Notes for Tables 1a to 1d

(1) All values are reported as µg/g unless otherwise noted (13) Schedule 10, Generic Numerical Soil and Water Standards, Column III, (2) - = No standard or not analyzed Agricultural, Urban Park, Residential Soil Standard (3) BCCSR = BC Environmental Management Act, Contaminated Sites Regulation, (14) Schedule 5, Human Health Protection, Intake of contaminated soil B.C. Reg. 375/96 - includes amendments up to B.C. Reg. 4/2014, January 31, (15) Zinc varies with pH as follows for BCCSR PL, Schedule 5, Environmental 2014 Protection, Groundwater flow to surface water used by aquatic life, Marine: (4) BCCSR PL = Schedules 4 (Generic) and/or 5 (Matrix), Column III Urban Park, 150 if pH<6.5 and/or Schedule 10, Column III, Agricultural, Urban Park, Residential Soil 300 if pH>=6.5 and pH<7 Standard Otherwise, Schedule 5, Environmental Protection, Toxicity to soil (5) CCME = Canadian Council of Ministers of the Environment, Canadian invertebrates and plants applies (450 ug/g). Environmental Quality Guidelines, 1999, updated to November 30, 2011 (16) Schedule 4, Generic Numerical Soil Standards for VPH (equivalent to C6-C10 (6) CCME RL/PL = Chapter 7, Canadian Soil Quality Guidelines for the Protection minus BTEX) of Environmental and Human Health, Residential/Parkland land use, updated (17) Schedule 5, Environmental Protection, Groundwater flow to surface water to October 22, 2008 used by aquatic life (7) Schedule 4, Generic Numerical Soil Standards (18) Summary Table 2, Interim remediation criteria for soil that have not yet (8) Schedule 5, Environmental Protection, Groundwater flow to surface water been replaced by Canadian Soil Quality Guidelines used by aquatic life, Marine (19) CCME RL/PL stipulates pH not < 6 and not > 8 (9) Schedule 5, Environmental Protection, Toxicity to soil invertebrates and (20) Summary Table 1, Canadian Soil Quality Guidelines plants (21) Benzene varies with Median grain size in µm as follows for CCME RL/PL, (10) Cadmium varies with pH as follows for BCCSR PL, Schedule 5, Environmental Summary Table 1, Canadian Soil Quality Guidelines: Protection, Groundwater flow to surface water used by aquatic life, Marine: 0.0068 if Median grain size<=75 2 if pH<7 0.030 if Median grain size>75 3.5 if pH>=7 and pH<7.5 (22) Ethylbenzene varies with Median grain size in µm as follows for CCME RL/PL, 35 if pH>=7.5 and pH<8 Summary Table 1, Canadian Soil Quality Guidelines: Otherwise, Schedule 5, Environmental Protection, Toxicity to soil 0.018 if Median grain size<=75 invertebrates and plants applies (70 ug/g). 0.082 if Median grain size>75 (11) Copper varies with pH as follows for BCCSR PL, Schedule 5, Environmental (23) Toluene varies with Median grain size in µm as follows for CCME RL/PL, Protection, Groundwater flow to surface water used by aquatic life: Summary Table 1, Canadian Soil Quality Guidelines: 90 if pH<5 0.08 if Median grain size<=75 100 if pH>=5 and pH<5.5 0.37 if Median grain size>75 Otherwise, Schedule 5, Environmental Protection, Toxicity to soil (24) Xylenes varies with Median grain size in µm as follows for CCME RL/PL, invertebrates and plants applies (150 ug/g). Summary Table 1, Canadian Soil Quality Guidelines: (12) Lead varies with pH as follows for BCCSR PL, Schedule 5, Environmental 2.4 if Median grain size<=75 Protection, Groundwater flow to surface water used by aquatic life: 11 if Median grain size>75 150 if pH<5.5 (25) Fact Sheet, Table 2, Environmental health guidelines/check values, Soil 250 if pH>=5.5 and pH<6 contact Otherwise, Schedule 5, Human Health Protection, Intake of contaminated soil (26) Fact Sheet, Table 2, Environmental health guidelines/check values, see applies (400 ug/g). notes j, o and/or q in guidelines

(27) Fact Sheet, Table 2, Environmental health guidelines/check values, see note n in guidelines RPD = Relative percent Difference. RPD is calculated as the difference between a samples and its field duplicate, over the average of the two values. nc = not calculated. RPD is not calculated if either the sample or the field duplicate concentration is less than five times the detection limit.

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 7 of 7 August 2015 Table 1e: Soil Relocation - Metals Analytical Results

Location ID: MW15-1 MW15-2 MW15-3 Sample ID: MW15-1-1 MW15-1-3 MW15-2-1 MW15-2-2 MW15-3-1 MW15-3-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 Sample Depth (m): 0.30-0.61 3.05-4.57 0.30-0.61 1.83-2.13 0.30-1.22 2.59-3.05

Parameter BCCSR SRNL 3,4 BCCSR SRAL 3,5 Sample Info Sample Depth, From (m) - - 0.3048 3.048 0.3048 1.828 0.3048 2.59 Sample Depth, To (m) - - 0.6096 4.572 0.6096 2.133 1.219 3.048

Field Tests pH - - 7.75 8.7 8.27 7.46 6.36 6.64

Physical Tests Moisture (%) - - - 18 - - - 15

Total Metals Aluminum - - 13000 5010 14500 23100 20500 14300 Antimony 20 20 0.89 0.24 1.48 0.41 0.97 0.81 Arsenic 15 15 3.45 1.91 3.55 5.69 4.89 3.09 Barium 400 400 73.5 21.9 85.6 118 110 96.4 Beryllium 4 4 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 Bismuth - - <0.10 <0.10 <0.10 <0.10 0.13 <0.10 Cadmium 1.5 1.5 0.252 0.116 0.34 0.151 0.709 0.224 Calcium - - 6880 26800 6060 3920 3250 3980 Chromium 60 50 21 7 18.9 27.8 22.3 15.8 Cobalt 50 40 7.43 3.02 6.83 10.8 9.58 7.47 Copper 90 90 31.2 6.55 33.7 28.7 48.2 34.4 Iron - - 19200 9750 19700 24700 22700 18300 Lead 100 100 40.4 8.84 101 35.6 163 55.5 Lithium - - 7.7 <5.0 6.7 10.7 8.1 6.9 Magnesium - - 5600 2770 4620 6530 4530 5550 Manganese - - 352 148 289 369 314 239 Mercury 15 0.6 0.062 <0.050 0.685 0.057 0.296 <0.050 Molybdenum 10 5 0.77 0.54 0.74 0.98 0.97 0.62 Phosphorus - - 527 276 452 408 710 343 Potassium (K) - - 818 484 843 900 570 779 Nickel 100 150 18.5 5.08 13.2 19.3 17 11.7 Selenium 3 2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 Silver 20 20 0.068 <0.050 0.098 0.056 0.418 0.056 Sodium (Na) - - 246 496 344 408 148 194 Strontium - - 38.6 156 44.6 36.8 34.8 34.7 Thallium - 2 0.059 0.078 0.054 0.065 <0.050 0.058 Tin 50 5 1.92 0.36 15.4 12.5 6.83 2.01 Titanium - - 621 283 559 955 685 522 Uranium - - 0.41 0.369 0.375 0.564 0.483 0.507 Vanadium 200 200 44.7 22.7 46.3 61.4 50 43.5 Zinc 150 150 76.4 25.1 81.3 61.1 234 88.5 Zirconium - - 1.06 0.99 1.44 2.49 0.69 1.73

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 1 of 6 August 2015 Table 1e: Soil Relocation - Metals Analytical Results

Location ID: MW15-4 BH15-5 BH15-6 BH15-7 BH15-8 Sample ID: MW15-4-3 BH15-5-1 BH15-5-2 BH15-6-1 BH15-7-1 BH15-7-2 BH15-8-2 BH15-8-4 BH15-8-5 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 RPD% Sample Depth (m): 1.07-1.30 0.91-2.44 2.74-3.05 0.46-0.76 0.15-0.46 1.83-2.13 0.61-0.91 2.59-2.90 2.59-2.90

Parameter BCCSR SRNL 3,4 BCCSR SRAL 3,5 Sample Info Sample Depth, From (m) - - 1.066 0.9144 2.743 0.4572 0.1524 1.828 0.6096 2.59 2.59 - Sample Depth, To (m) - - 1.295 2.438 3.048 0.762 0.4572 2.133 0.9144 2.895 2.895 -

Field Tests pH - - 6.68 9.97 8.3 7.26 7.93 7.48 8.1 7.02 6.95 -

Physical Tests Moisture (%) ------

Total Metals Aluminum - - 17500 16100 18100 14700 12300 19700 14300 16400 15900 3 Antimony 20 20 0.9 0.52 0.63 0.4 0.3 0.16 7.44 1.49 0.86 54 Arsenic 15 15 4.98 2.84 4.11 2.91 1.84 3.19 5.82 3.23 2.97 8 Barium 400 400 103 82 88.5 78.6 66.2 96.3 222 85.5 85.8 0 Beryllium 4 4 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 <0.40 nc Bismuth - - 0.11 <0.10 <0.10 <0.10 <0.10 <0.10 0.14 <0.10 <0.10 nc Cadmium 1.5 1.5 0.278 0.225 0.199 0.14 0.114 0.111 0.856 0.192 0.195 2 Calcium - - 3710 15000 7780 3550 3450 2750 9810 3170 2640 18 Chromium 60 50 16.6 17.3 24.3 17.3 14 19.1 20.6 15.8 15.4 3 Cobalt 50 40 5.87 8.24 7.9 6.93 7.08 9.23 7 6.32 6.38 1 Copper 90 90 25.1 27.4 27.6 26.5 22.3 20 65.3 20.3 19.7 3 Iron - - 18300 20300 21300 17900 17500 20400 25400 16800 17000 1 Lead 100 100 81.7 28.4 37.4 26.9 20.1 12.8 180 47.6 33.9 34 Lithium - - 5.8 8.5 8.5 8.2 6.1 10 8.1 8.1 7.7 5 Magnesium - - 3820 6130 5190 4930 5090 6620 4400 4920 4650 6 Manganese - - 268 323 342 294 287 287 391 280 260 7 Mercury 15 0.6 0.07 <0.050 0.06 <0.050 0.059 <0.050 0.107 <0.050 <0.050 nc Molybdenum 10 5 1.18 0.66 1.62 0.52 0.35 0.65 1.21 0.7 0.64 9 Phosphorus - - 545 384 421 400 365 322 651 403 349 14 Potassium (K) - - 612 1050 861 727 864 842 761 553 587 6 Nickel 100 150 10.3 11.7 13.8 12.5 10.7 14.3 18 10.9 10.2 7 Selenium 3 2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 nc Silver 20 20 0.094 0.052 0.065 0.055 <0.050 <0.050 0.131 0.077 0.064 18 Sodium (Na) - - 212 396 323 218 256 205 414 161 160 1 Strontium - - 34.9 59.5 42.1 31.1 28.3 32.9 130 36.2 32.7 10 Thallium - 2 0.055 0.063 0.067 0.06 <0.050 0.071 <0.050 <0.050 <0.050 nc Tin 50 5 2.96 1.94 1.6 1.17 1.15 0.35 32.1 3.99 2.15 60 Titanium - - 687 626 788 559 588 770 585 589 609 3 Uranium - - 0.414 0.492 0.48 0.458 0.307 0.375 0.497 0.402 0.406 1 Vanadium 200 200 50.1 48 53.7 44.8 42.1 50.7 48.1 44.9 45.6 2 Zinc 150 150 119 69.6 61.8 54.8 45.4 65.7 379 70.4 69.6 1 Zirconium - - 0.76 2.48 1.26 0.77 2.05 2.92 1.42 0.98 1.2 20

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 2 of 6 August 2015 Table 1e: Soil Relocation - Metals Analytical Results

Location ID: BH15-9 BH15-10 BH15-11 Sample ID: BH15-9-1 BH15-9-3 BH15-9-4 BH15-10-1 BH15-11-1 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 26/05/2015 RPD% Sample Depth (m): 1.68-1.98 2.59-2.90 2.59-2.90 0.46-0.76 0.15-0.76

Parameter BCCSR SRNL 3,4 BCCSR SRAL 3,5 Sample Info Sample Depth, From (m) - - 1.676 2.59 2.59 - 0.4572 0.1524 Sample Depth, To (m) - - 1.981 2.895 2.895 - 0.762 0.762

Field Tests pH - - 7.23 7.52 7.23 - 6.52 6.5

Physical Tests Moisture (%) - - -1718---

Total Metals Aluminum - - 13700 16300 16300 nc 18100 17300 Antimony 20 20 1 1.61 0.78 69 0.22 1.3 Arsenic 15 15 2.74 3.51 3.56 1 3.1 3.86 Barium 400 400 60.7 113 110 3 91 85.7 Beryllium 4 4 <0.40 <0.40 <0.40 nc <0.40 <0.40 Bismuth - - <0.10 <0.10 <0.10 nc <0.10 <0.10 Cadmium 1.5 1.5 0.106 0.28 0.258 8 0.12 0.211 Calcium - - 2990 4410 3540 22 3980 3330 Chromium 60 50 10.6 20.4 20 2 22.8 16 Cobalt 50 40 5.57 6.82 6.66 2 8.79 5.9 Copper 90 90 14.1 26 24.5 6 18.3 22.4 Iron - - 13800 18200 17200 6 20100 16900 Lead 100 100 35.3 54.7 56.9 4 8.44 48.8 Lithium - - 6.9 7.9 7.9 nc 9.7 7.4 Magnesium - - 4020 4360 4090 6 4740 4240 Manganese - - 272 291 278 5 423 294 Mercury 15 0.6 <0.050 <0.050 0.056 nc <0.050 0.083 Molybdenum 10 5 0.62 1.12 1.23 9 0.62 0.65 Phosphorus - - 319 415 364 13 290 439 Potassium (K) - - 442 722 641 12 606 536 Nickel 100 150 7.38 11.9 12 1 15.7 11.5 Selenium 3 2 <0.50 <0.50 <0.50 nc <0.50 <0.50 Silver 20 20 0.061 0.06 0.068 13 <0.050 0.074 Sodium (Na) - - 135 166 164 1 190 125 Strontium - - 30.5 43.7 40.7 7 40 28 Thallium - 2 <0.050 0.069 0.068 nc <0.050 <0.050 Tin 50 5 0.8 4.15 4.18 1 0.35 3.71 Titanium - - 512 511 534 4 771 583 Uranium - - 0.354 0.46 0.451 2 0.449 0.513 Vanadium 200 200 36.2 41.7 41.4 1 51.8 41.3 Zinc 150 150 52.7 81.3 99.2 20 37.5 78.4 Zirconium - - <0.50 1.47 1.24 17 0.94 0.57

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 3 of 6 August 2015 Table 1f: Soil Relocation - Hydrocarbon Analytical Results

Location ID: MW15-1 MW15-3 BH15-9 BH15-10 BH15-11 Sample ID: MW15-1-2 MW15-1-3 MW15-3-2 BH15-9-3 BH15-9-4 BH15-10-2 BH15-11-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 26/05/2015 RPD% Sample Depth (m): 1.83-2.13 3.05-4.57 2.59-3.05 2.59-2.90 2.59-2.90 1.98-2.29 2.59-3.05

Parameter BCCSR SRNL 3,4 BCCSR SRAL 3,5 Field Tests Field Vapours (ppm) - - 0 5 150 160 160 - 10 200

Physical Tests Moisture (%) - - 8 18 15 17 18 - 24 19

BTEX Benzene 0.04 0.04 - - <0.0050 <0.0050 <0.0050 nc - <0.0050 Ethylbenzene 1 1 - - <0.010 <0.010 <0.010 nc - <0.010 Styrene 5 0.1 - - <0.030 <0.030 <0.030 nc - <0.030 Toluene 1.5 1.5 - - <0.020 <0.020 <0.020 nc - <0.020 Xylenes 5 0.1 - - <0.040 <0.040 <0.040 nc - <0.040

EPH EPH10-19 - - <100 <100 - <100 <100 nc 659 <100 EPH19-32 - - 126 <100 - <100 <100 nc 342 <100 LEPH 1000 1000 <100 <100 - <100 <100 nc 659 <100 HEPH 1000 1000 126 <100 - <100 <100 nc 342 <100

VPH VH6-10 - - - - <10 <10 <10 nc - <10 VPH 200 200 - - <10 <10 <10 nc - <10

PHCs F1 (C6-C10) - BTEX - - - - <10 <10 <10 nc - <10 F1 nC6-10 uncorrected - - - - <10 - - - - <10

PAH 2-Methylnaphthalene - - <0.020 <0.020 - 0.043 0.025 53 0.46 <0.020 Acenaphthene - - <0.0050 0.029 - 0.011 0.0092 18 0.05 <0.0050 Acenaphthylene - - 0.011 <0.0050 - 0.055 0.055 nc <0.019 <0.0050 Anthracene - - 0.018 0.021 - 0.081 0.076 6 <0.040 <0.0040 Benzo(a)anthracene 1 0.1 0.058 0.02 - 0.16 0.14 13 0.074 <0.020 Benzo(a)pyrene 1 0.1 0.062 <0.020 - 0.16 0.15 6 0.083 <0.020 Benzo(b,j)fluoranthene 1 0.1 0.092 0.023 - 0.24 0.24 nc 0.12 <0.020 Benzo(g,h,i)perylene - - 0.05 <0.050 - 0.12 0.11 9 0.072 <0.050 Benzo(k)fluoranthene 1 0.1 0.027 <0.020 - 0.08 0.074 8 0.03 <0.020 Chrysene - - 0.073 0.026 - 0.21 0.2 5 0.14 <0.020 Dibenz(a,h)anthracene 1 0.1 <0.050 <0.050 - <0.050 <0.050 nc <0.050 <0.050 Fluoranthene - - 0.12 0.11 - 0.44 0.42 5 0.19 <0.020 Fluorene - - <0.020 0.033 - 0.042 0.044 5 0.18 <0.020 Indeno(1,2,3-c,d)pyrene 1 0.1 <0.050 <0.050 - 0.097 0.097 nc <0.050 <0.050 Naphthalene 5 0.1 <0.010 0.02 - 0.096 0.036 91 0.082 <0.010 Phenanthrene 5 0.1 0.053 0.11 - 0.34 0.31 9 0.41 <0.020 Pyrene 10 0.1 0.13 0.083 - 0.42 0.41 2 0.2 <0.020 Total HMW PAH's - - 0.61 0.26 - 1.9 1.8 5 0.91 <0.050 Total LMW PAH's - - 0.083 0.21 - 0.67 0.55 20 1.2 <0.050 Total PAH's - - 0.7 0.47 - 2.6 2.4 8 2.1 <0.050

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 4 of 6 August 2015 Table 1f: Soil Relocation - Hydrocarbon Analytical Results

Location ID: MW15-1 MW15-3 BH15-9 BH15-10 BH15-11 Sample ID: MW15-1-2 MW15-1-3 MW15-3-2 BH15-9-3 BH15-9-4 BH15-10-2 BH15-11-2 Date Sampled: 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 25/05/2015 26/05/2015 RPD% Sample Depth (m): 1.83-2.13 3.05-4.57 2.59-3.05 2.59-2.90 2.59-2.90 1.98-2.29 2.59-3.05

Parameter BCCSR SRNL 3,4 BCCSR SRAL 3,5

VOC 1,1,1,2-Tetrachloroethane - - - - - <0.025 <0.025 nc - <0.025 1,1,1-Trichloroethane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,1,2,2-Tetrachloroethane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,1,2-Trichloroethane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,1-Dichloroethane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,1-Dichloroethene 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,2,3-Trichlorobenzene - - - - - <0.025 <0.025 nc - <0.025 1,2,4-Trichlorobenzene - - - - - <0.025 <0.025 nc - <0.025

1,2-Dibromoethane (ethylene dibromide) (EDB) - - - - - <0.025 <0.025 nc - <0.025

1,2-Dichlorobenzene 1 0.1 - - - <0.025 <0.025 nc - <0.025 1,2-Dichloroethane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,2-Dichloroethene (cis) - - - - - <0.025 <0.025 nc - <0.025 1,2-Dichloroethene (trans) - - - - - <0.025 <0.025 nc - <0.025 1,2-Dichloropropane 5 0.1 - - - <0.025 <0.025 nc - <0.025 1,3-Dichlorobenzene 1 0.1 - - - <0.025 <0.025 nc - <0.025 1,3-Dichloropropene (cis) 5 0.1 - - - <0.050 <0.050 nc - <0.050 1,3-Dichloropropene (trans) 5 0.1 - - - <0.050 <0.050 nc - <0.050 1,4-Dichlorobenzene 1 0.1 - - - <0.025 <0.025 nc - <0.025 Bromodichloromethane (BDCM) - - - - - <0.050 <0.050 nc - <0.050 Bromomethane (methyl bromide) - - - - - <0.30 <0.30 nc - <0.30 Chlorobenzene 1 0.1 - - - <0.025 <0.025 nc - <0.025 Chloroethane (ethyl chloride) - - - - - <0.10 <0.10 nc - <0.10 Chloroethene (vinyl chloride) - - - - - <0.060 <0.060 nc - <0.060 Dibromochloromethane (DBCM) - - - - - <0.050 <0.050 nc - <0.050 Dichloromethane (methylene chloride) 5 0.1 - - - <0.10 <0.10 nc - <0.10 Hexachlorobutadiene (HCBD) - - - - - <0.20 <0.20 nc - <0.20 Methyl tert-butyl ether (MTBE) - - - - <0.10 <0.10 <0.10 nc - <0.10 Monochloromethane (methyl chloride) - - - - - <0.10 <0.10 nc - <0.10 Tetrachloroethylene (PERC) 5 0.1 - - - 0.035 <0.025 nc - <0.025 Tetrachloromethane (carbon tetrachloride) 5 0.1 - - - <0.025 <0.025 nc - <0.025 Tribromomethane (bromoform) - - - - - <0.050 <0.050 nc - <0.050 Trichloroethylene (TCE) 0.015 0.015 - - - <0.0090 <0.0090 nc - <0.0090 Trichlorofluoromethane (Freon 11) - - - - - <0.20 <0.20 nc - <0.20 Trichloromethane (chloroform) 5 0.1 - - - <0.050 <0.050 nc - <0.050

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 5 of 6 August 2015 Notes for Table 1e and f

(1) All values are reported as µg/g unless otherwise noted (2) - = No standard or not analyzed (3) BCCSR = BC Environmental Management Act, Contaminated Sites Regulation, B.C Reg. 375/96 - includes amendments up to B.C. Reg. 4/2014, January 31, 2014 (4) BCCSR SRNL = Schedule 7, Standards Triggering Contaminated Soil Relocation Agreements, Column II, Soil Relocation to Nonagricultural Land (5) BCCSR SRAL = Schedule 7, Standards Triggering Contaminated Soil Relocation Agreements, Column III, Soil Relocation to Agricultural Land

RPD = Relative percent Difference. RPD is calculated as the difference between a samples and its field duplicate, over the average of the two values. nc = not calculated. RPD is not calculated if either the sample or the field duplicate concentration is less than five times the detection limit.

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 6 of 6 August 2015 Table 1g: Soil Metals TCLP Results

Location ID: BH15-8 Sample ID: BH15-8-2 Date Sampled: 25/05/2015 Sample Depth (m): 0.61-0.91

Parameter BCHWR LQS 3,4

Physical Tests pH after HCl - 1.44 pH, final - 5.06 pH, initial - 8.67 pH, leaching fluid - 4.93 Leachate Metals Lead (ug/L) 5000 330

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 1 of 2 August 2015 Notes for Table 1g

(1) All values are reported as µg/g unless otherwise noted (2) - = No standard or not analyzed (3) BCHWR = BC Environmental Management Act, Hazardous Waste Regulation, B.C. Reg. 63/88 includes amendments up to B.C. Reg. 63/2009, April 1, 2009 (4) BCHWR LQS = Schedule 4, Table 1, Leachate Quality Standards

PMV – Habitat Enhancement Program Limited Phase 1 and 2 ESA – New Brighton Park Hemmera File: 302-035.04 Page 2 of 2 August 2015 Table 2a: Groundwater Dissolved Metals Analytical Results

Location ID: MW15-1MW15-2 MW15-3 MW15-4 Sample ID: MW15-1 MW15-100 MW15-2 MW15-3 MW15-4 RPD% Date Sampled: 01/06/2015 01/06/2015 01/06/2015 01/06/2015 01/06/2015

Parameter BCCSR AW 3,4 CCME MALx10 5,6 Well Depth, To Bottom (m) - - 3.932 3.91 3.91 - 3.442 3.524 Well Depth, To Water (m) - - 2.588 2.653 2.653 - 2.641 2.442

Physical Tests Hardness, Total (CaCO3) (mg/L) - - 272 498 491 1 254 169

Dissolved Inorganics Sulfur (mg/L) - - 16.2 7.8 8.6 10 <3.0 4.1

Dissolved Metals Aluminum - - 257 67.6 59.4 13 16.4 47.9 Antimony 200 7 - 2.02 <0.50 <0.50 nc <0.50 <0.50 Arsenic 125 8 125 7 3.18 3.21 1 1.2 1.91 Barium 5000 8 - 115 217 236 8 97.9 47 Beryllium 1000 8 - <0.10 <0.10 <0.10 nc <0.10 <0.10 Bismuth - - <1.0 <1.0 <1.0 nc <1.0 <1.0 Boron 50000 7 - 172 360 360 0 72 <50 Cadmium 1 8 1.2 0.012 0.04 0.04 0 0.02 <0.010 Calcium - - 91400 137000 135000 1 85900 61200 Chromium 150 8 15 8.1 1.9 1.9 0 <1.0 <1.0 Cobalt 40 7 - 0.59 7.92 8.14 3 1.5 0.77 Copper 20 8 - 1.62 0.74 0.7 6 0.77 0.28 Iron - - 3050 37600 38400 2 2620 271 Lead 20 8 - 2.86 <0.20 <0.20 nc <0.20 <0.20 Lithium - - <5.0 <5.0 <5.0 nc <5.0 <5.0 Magnesium - - 10700 38100 37400 2 9600 3870 Manganese - - 607 2710 2600 4 1630 228 Molybdenum 10000 7 - 58 7.4 7.7 4 5.4 2.8 Nickel 83 8 - 6.4 10.7 11.1 4 3 1.8 Potassium - - 9720 13300 13100 2 2910 2810 Selenium 540 8 - 2.19 0.88 0.84 5 0.14 0.2 Silicon - - 8680 10800 11400 5 8460 6600 Silver 15 8 - <0.020 <0.020 <0.020 nc <0.020 <0.020 Sodium - - 185000 186000 181000 3 10000 4310 Strontium - - 679 1250 1260 1 509 223 Thallium 3 7 - <0.050 <0.050 <0.050 nc <0.050 <0.050 Tin - - <5.0 <5.0 <5.0 nc <5.0 <5.0 Titanium 1000 7 - 22.3 <5.0 <5.0 nc <5.0 <5.0 Uranium 1000 8 - 0.86 1.19 1.25 5 0.78 0.63 Vanadium - - 30.2 5.3 5.1 4 <5.0 <5.0 Zinc 100 8 - <5.0 24.2 23.6 3 12.6 <5.0 Zirconium - - 2.88 1.89 1.98 5 <0.50 <0.50

Metals Mercury 1 7 0.16 <0.010 <0.010 <0.010 nc <0.010 <0.010

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 1 of 4 August 2015 Table 2b: Groundwater Hydrocarbon Analytical Results

Location ID: MW15-1 MW15-2 MW15-3 MW15-4 Sample ID: MW15-1 MW15-1 MW15-100 MW15-2 MW15-3 MW15-4 RPD% Date Sampled: 01/06/2015 05/06/2015 01/06/2015 01/06/2015 01/06/2015 01/06/2015

Parameter BCCSR AW 3,4 CCME MALx10 5,6 BTEX Benzene 1000 8 1100 0.89 - <0.40 <0.40 nc 1.3 <0.40 Ethylbenzene 2500 8 250 2.5 - <0.40 <0.40 nc <0.40 <0.40 meta- & para-Xylene - - <0.40 - <0.40 <0.40 nc <0.40 <0.40 ortho-Xylene - - 1.1 - <0.40 <0.40 nc <0.40 <0.40 Styrene 720 7 - <0.40 - <0.40 <0.40 nc <0.40 <0.40 Toluene 3300 8 2150 0.47 - <0.40 <0.40 nc <0.40 <0.40 Xylenes - - 1.1 - <0.40 <0.40 nc <0.40 <0.40

EPH EPH10-19 5000 7 - 2300 2000 <200 <200 nc <200 <200 EPH19-32 - - 270 <200 <200 <200 nc <200 <200 LEPH 500 7 - 2200 2000 <200 <200 nc <200 <200 HEPH - - 270 <200 <200 <200 nc <200 <200

VPH VH6-10 15000 7 - <300 - <300 <300 nc <300 <300 VPH 1500 7 - <300 - <300 <300 nc <300 <300

PHCs F1 (C6-C10) - BTEX - - <300 - <300 <300 nc <300 <300 F1 nC6-10 uncorrected - - <300 - <300 <300 nc <300 <300

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 2 of 4 August 2015 Table 2b: Groundwater Hydrocarbon Analytical Results

Location ID: MW15-1 MW15-2 MW15-3 MW15-4 Sample ID: MW15-1 MW15-1 MW15-100 MW15-2 MW15-3 MW15-4 RPD% Date Sampled: 01/06/2015 05/06/2015 01/06/2015 01/06/2015 01/06/2015 01/06/2015

Parameter BCCSR AW 3,4 CCME MALx10 5,6

PAH 2-Methylnaphthalene - - 53 71 0.31 0.29 7 0.22 <0.10 Acenaphthene 60 7 - 6.3 7.3 1.3 1.3 0 0.8 <0.050 Acenaphthylene - - <1.3 <0.26 <0.050 <0.050 nc <0.050 <0.050 Acridine 0.5 7 - 0.06 0.083 <0.050 <0.050 nc <0.050 <0.050 Anthracene 1 7 - 0.76 0.72 0.024 0.025 4 0.088 <0.010 Benzo(a)anthracene 1 7 - 0.058 0.024 <0.010 <0.010 nc 0.038 <0.010 Benzo(a)pyrene 0.1 7 - 0.039 0.015 <0.0090 <0.0090 nc 0.034 <0.0090 Benzo(b,j)fluoranthene - - 0.051 <0.050 <0.050 <0.050 nc <0.050 <0.050 Benzo(g,h,i)perylene - - <0.050 <0.050 <0.050 <0.050 nc <0.050 <0.050 Benzo(k)fluoranthene - - <0.050 <0.050 <0.050 <0.050 nc <0.050 <0.050 Chrysene 1 7 - 0.12 <0.050 0.052 0.053 2 <0.050 <0.050 Dibenz(a,h)anthracene - - <0.050 <0.050 <0.050 <0.050 nc <0.050 <0.050 Fluoranthene 2 7 - 0.33 0.18 0.045 0.042 7 0.11 <0.020 Fluorene 120 7 - 4.2 5.0 0.31 0.31 0 0.8 <0.050 Indeno(1,2,3-c,d)pyrene - - <0.050 <0.050 <0.050 <0.050 nc <0.050 <0.050

Naphthalene 10 7 14 25 29 1.6 1.4 13 0.18 <0.10 Phenanthrene 3 7 - 8.3 8.9 0.18 0.18 0 0.46 <0.050 Pyrene 0.2 7 - 0.37 0.22 0.035 0.034 3 0.11 <0.020 Quinoline 34 7 - <3.2 <0.67 <0.24 <0.24 nc <0.24 <0.24 Total HMW PAH's - - 0.97 0.44 0.13 0.13 0 0.29 <0.050 Total LMW PAH's - - 97 120 3.7 3.6 3 2.5 <0.24 Total PAH's - - 98 120 3.8 3.7 3 2.8 <0.24

VOC Methyl tert-butyl ether (MTBE) 4400 8 50000 <4.0 - <4.0 <4.0 nc <4.0 <4.0

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 3 of 4 August 2015 Notes for Tables 2a and 2b

(1) All values are reported as µg/L unless otherwise noted (2) - = No standard or not analyzed (3) BCCSR = BC Environmental Management Act, Contaminated Sites Regulation, B.C Reg. 375/96 - includes amendments up to B.C. Reg. 4/2014, January 31, 2014 (4) BCCSR AW = Schedule 6, Column II Aquatic Life (5) CCME = Canadian Council of Ministers of the Environment, Canadian Environmental Quality Guidelines, 1999, updated to November 30, 2011 (6) CCME MALx10 = Chapter 4, Canadian Water Quality Guidelines for the Protection of Aquatic Life, Marine, updated to November 30, 2011; all values multiplied by an assumed 10x dilution factor for groundwater entering surface water body (7) Schedule 6, Generic Numerical Water Standards (8) Schedule 6, Generic Numerical Water Standards, Standard to protect marine and/or estuarine aquatic life (Schedule 6, Note 8) RPD = Relative percent Difference. RPD is calculated as the difference between a samples and its field duplicate, over the average of the two values. nc = not calculated. RPD is not calculated if either the sample or the field duplicate concentration is less than five times the detection limit.

Hemmera PMV – Habitat Enhancement Program File: 302-035.04 Limited Phase 1 and 2 ESA – New Brighton Park Page 4 of 4 August 2015

APPENDIX A Site Photographs PMV – Habitat Enhancement Program APPENDIX A Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 1 - August 2015

Photo 1: View of park and investigation area, looking southeast.

Photo 2: View of park area and pool, looking southwest.

PMV – Habitat Enhancement Program APPENDIX A Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 2 - August 2015

Photo 3: View of park area, looking north. Cascadia Terminals (Viterra) is present in the photo.

Photo 4: View of park area near north end, at shore looking east.

PMV – Habitat Enhancement Program APPENDIX A Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 3 - August 2015

Photo 5: View of gravel pathway, looking south.

Photo 6: View of park area, looking west.

PMV – Habitat Enhancement Program APPENDIX A Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 4 - August 2015

Photo 7: View Cascadia Terminals (Viterra) to the east of the site.

Photo 8: View of parking area at south end of the park, beside the New Brighton Park caretaker house and adjoining concession.

APPENDIX B Project Concept and PMV Documents New Brighton Park March 2009

Approximate Extent of Intertidal Fill

New Brighton Park June 1961

Extensive intertidal zone

Approximate Park Boundary

NEW BRIGHTON PARK: HISTORICAL HABITAT CHANGE r General Notis

‘BOE CONJRUC7I”SRvICI

VAN BOWER CONSTRUCTIONSERViCES LTD. 999 CANADAPLACE SUITE 404 VANCOUVER,BC

ALL ELEVATIONS GEODETIC

)RIGINAL GROUND SURVEY 09/09/2014 RIPARIAN FOREST = 7,800M2 RIPARIAN PLANTING — WEST SHORELINE = 5000M2 — SMALL SHORELINE AREA = 215M2 — EAST FILL AREA = 1,826M2 — WEST FILL AREA = 5,000M2 DUNEGRASS MEADOW= i,700M2

SALT MARSH = 3,900M2 CHANNEL = 1,060M2 KELP BED = 1,250M2

DUT VOLUME= 18,000M3 FILL AREA VOLUME = 18,000M3

Ron/Issue :i. I N. I PORT OF METRO I VANCOUVER I 100 THE POINTE I VANCOUVER,BC V6C L% 1 N NEW BRIGHTONPARK OPTION 2 CONCEPT DESIGN PLAN VIEW ] r*.’ 2014—044 IoaI EPT 19, 201 Isc 1 i% 1:1.000

FIP - New Brighton Park

50M Map Scale 1:2118 Data Quality not Guaranteed Jun 10, 2015 13:06

APPENDIX C Aerial Photographs

4 7777r

I

I

I

I

‘

____

l’i

iU

NI

j

r ‘

APPENDIX D Previous Reports

APPENDIX E BC MOE Site Registry Search As Of: MAR 15, 2015 BC Online: Site Registry 15/03/17 For: PF66793 HEMMERA ENVIROCHEM INC. 11:15:59 Folio: 302-035.04 Page 1 4 records selected for 0.5 km from latitude 49 deg, 17 min, 24 sec and Longitude 123 deg, 02 min, 07 sec Site Id Lastupd Address / City 0000016 02MAR22 0 CASSIAR NORTH FOOT VANCOUVER 0001476 05FEB18 2995 WALL STREET VANCOUVER 0009566 05NOV07 2995 WALL STREET VANCOUVER 0010904 10FEB19 3399 BRIDGEWAY STREET VANCOUVER

file:///P|/...Sites/Phase%201%20and%202%20ESA%20Report/Appendices/App%20E%20Site%20Registry/SiteRegSearchLat49Long123.txt[20/08/2015 8:25:35 AM]

APPENDIX F Federal Contaminated Sites Inventory

3/17/2015 Site 00020158 ­ Terminal Dock

Treasury Board of Canada Secretariat Home > FCSI > Site 00020158 Site 00020158 ­ Terminal Dock

Status Historical review completed. No further action required.

Site Status Closed

Classification

Site Details

Reporting Organization Fisheries and Oceans Canada

Reason for Involvement Federal Real Property

Property Type Federal (DFRP Property Number84702)

Site Location Locate this site on map

Latitude, Longitude 49.29414, ­123.04947

Municipality Vancouver, BC

Federal Electoral District Vancouver East

Additional Information

Unassessed

Population

This table contains the population estimates at distances around the site.

Radius Population

1 km 6,086

http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020158­eng.aspx 1/3 3/17/2015 Site 00020158 ­ Terminal Dock 5 km 238,113

10 km 852,045

25 km 1,964,755

50 km 2,577,800

Summary of Annually Reported Data

Total Expenditures

Assessment $1,381.38

FCSAP Expenditures

Assessment $1,381.38

Financial/Annual Information 2012­2013 2011­2012 2010­2011 2009­2010 2008­2009 2007­2008 2006­2007

2012­2013

Reporting Organization Fisheries and Oceans Canada

Internal Identifier P K 00880

Highest Step Completed 02 Historical Review

Planned Completion Date (Step 7) no data

Planned Completion Date (Step 8) no data

Planned Completion Date (Step 9) no data

Total Assessment Expenditure $0.00

Total Remediation Expenditure $0.00

Total Care Maintenance Expenditure $0.00

Total Monitoring Expenditure http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020158­eng.aspx 2/3 3/17/2015 Site 00020158 ­ Terminal Dock $0.00

FCSAP Assessment Expenditure $0.00

FCSAP Remediation Expenditure $0.00

FCSAP Care Maintenance Expenditure $0.00

FCSAP Monitoring Expenditure $0.00

Actual Cubic Meters Remediated 0 m3

Actual Hectares Remediated 0 ha

Actual Tons Remediated 0 t

Closed Yes

Version: 9.84

http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020158­eng.aspx 3/3 3/17/2015 Site 00020819 ­ CN Railway Bridge SE NW NE SW

Treasury Board of Canada Secretariat Home > FCSI > Site 00020819 Site 00020819 ­ CN Railway Bridge SE NW NE SW

Status Historical review completed. No further action required.

Site Status Closed

Classification

Site Details

Reporting Organization Fisheries and Oceans Canada

Reason for Involvement Federal Real Property

Property Type Federal (DFRP Property Number84911)

Site Location Locate this site on map

Latitude, Longitude 49.29472, ­123.02444

Municipality North Vancouver, BC

Federal Electoral District North Vancouver

Site Management Strategy

Other

Population

This table contains the population estimates at distances around the site.

Radius Population

1 km 2,752

http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020819­eng.aspx 1/3 3/17/2015 Site 00020819 ­ CN Railway Bridge SE NW NE SW 5 km 196,135

10 km 797,023

25 km 2,002,631

50 km 2,575,945

Summary of Annually Reported Data

Total Expenditures

Assessment $1,344.00

FCSAP Expenditures

Assessment $1,061.82

Financial/Annual Information 2012­2013 2011­2012 2010­2011 2009­2010 2008­2009 2007­2008 2006­2007

2012­2013

Reporting Organization Fisheries and Oceans Canada

Internal Identifier P K 01599

Highest Step Completed 02 Historical Review

Planned Completion Date (Step 7) no data

Planned Completion Date (Step 8) no data

Planned Completion Date (Step 9) no data

Total Assessment Expenditure $0.00

Total Remediation Expenditure $0.00

Total Care Maintenance Expenditure $0.00

Total Monitoring Expenditure http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020819­eng.aspx 2/3 3/17/2015 Site 00020819 ­ CN Railway Bridge SE NW NE SW $0.00

FCSAP Assessment Expenditure $0.00

FCSAP Remediation Expenditure $0.00

FCSAP Care Maintenance Expenditure $0.00

FCSAP Monitoring Expenditure $0.00

Actual Cubic Meters Remediated 0 m3

Actual Hectares Remediated 0 ha

Actual Tons Remediated 0 t

Closed Yes

Version: 9.84

http://www.tbs­sct.gc.ca/fcsi­rscf/fsi­isf/00020819­eng.aspx 3/3

APPENDIX G Water Well Search Water Resources Atlas - WaterLegend Wells 1.5 km

Artesian Wells Water Wells Water Wells - Lithology Abandoned Well Use Commercial and Industrial Well Use Domestic Well Use Irrigation Well Use Observation Well Use Other Well Use Test Well Use Unknown Well Use Drinking Water Supply System Well Use Drilled Water Wells Driven Water Wells Dug Water Wells 0 0.67 1.34 km Jetted Water Wells 1: 33,017Other Water Wells BC Government Active Observation Wells BCCopyright/Disclaimer Government Inactive Observation Wells The materialTileCache contained in this web site is owned by the Government of British Columbia and protected by copyright law. It may not be reproduced or redistributed without the prior written permission of the Province of British Columbia. To request permission to reproduce all or part of the material on this web site please complete the Copyright Permission Request Form which can be accessed through the Copyright Information Page. CAUTION: Maps obtained using this site are not designed to assist in navigation. These maps may be generalized and may not reflect current conditions. Uncharted hazards may exist. DO NOT USE THESE MAPS FOR NAVIGATIONAL PURPOSES.

Datum: NAD83 Projection: NAD_1983_BC_Environment_Albers

Key Map of British Columbia

APPENDIX H Borehole Logs

Log of Monitoring Well: MW15-1

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 1 of 2

Well location: MW15-1 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.93m (12.90ft)

Depth to water level (TOC): 2.59m (8.49ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.26m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.30m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 2.41m (7.90ft) - 3.93m (12.90ft) Log of Monitoring Well: MW15-1

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

16 5

17

18

19

6 20 5ppm MW15-1-4 Y

21

22

-3.71 23 7 GRAVEL AND COBBLES 7.01 COBBLES AND GRAVEL (coarse grained) -3.86 7.16 SILTY SAND 24 SILTY SAND (fine-medium grained), light brown, dense, blocky, wet, no odour 0ppm MW15-1-5 N

25

26 8

27

-5.24 28 End of Log 8.53

29

9

30

Well location: MW15-1 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.93m (12.90ft)

Depth to water level (TOC): 2.59m (8.49ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.26m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.30m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 2.41m (7.90ft) - 3.93m (12.90ft) Log of Monitoring Well: MW15-2

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 1 of 2

Well location: MW15-2 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.91m (12.83ft)

Depth to water level (TOC): 2.65m (8.70ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.17m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.22m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 2.39m (7.83ft) - 3.91m (12.83ft) Log of Monitoring Well: MW15-2

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

SAND SAND (coarse grained), dark grey, loose, wet, no odour, significant white broken shell fragments, 0ppm stringy wood waste 16 MW15-2-6 Y 5

17

-2.27 18 SILTY SAND 5.49 SILTY SAND (fine-medium grained), light brown, dense, blocky, wet, no odour 19

6 17% LEL 20 MW15-2-7 N

21

22

23 7

24 370ppm MW15-2-8 N

25

26 8

27

-5.32 28 End of Log 8.53

29

9

30

Well location: MW15-2 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.91m (12.83ft)

Depth to water level (TOC): 2.65m (8.70ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.17m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.22m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 2.39m (7.83ft) - 3.91m (12.83ft) Log of Monitoring Well: MW15-3

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 1 of 2

Well location: MW15-2 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.44m (11.29ft)

Depth to water level (TOC): 2.64m (8.66ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.30m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.39m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 1.92m (6.29ft) - 3.44m (11.29ft) Log of Monitoring Well: MW15-3

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

16 5

17 0ppm MW15-3-4 Y

18

19

6 20 -2.86 SILTY SAND 6.25 SILTY SAND (fine-medium grained), light brown, 21 30ppm dense, blocky, wet, no odour MW15-3-5 N

22

23 7 15ppm MW15-3-6 N

24

25

26 8

27

-5.15 28 End of Log 8.53

29

9

30

Well location: MW15-2 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.44m (11.29ft)

Depth to water level (TOC): 2.64m (8.66ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.30m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.39m

Borehole diameter: 10.6cm (4") Well screen interval (bgs): 1.92m (6.29ft) - 3.44m (11.29ft) Log of Monitoring Well: MW15-4

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 1 of 2

Well location: MW15-4 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.58m (11.75ft)

Depth to water level (TOC): 2.30m (7.53ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.15m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.20m

Borehole diameter: 10.16cm (4") Well screen interval (bgs): 2.00m (6.56ft) - 3.52m (11.56ft) Log of Monitoring Well: MW15-4

Project Name/No: 302-035.04 Drilling Company: OMEGA

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled: May 25th 2015 Logged by: A Brown, J Chua

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

16 5

17

-2.29 18 End of Log 5.49

19

6 20

21

22

23 7

24

25

26 8

27

28

29

9

30

Well location: MW15-4 Well casing diameter: 5.08cm (2") Depth of well (TOC): 3.58m (11.75ft)

Depth to water level (TOC): 2.30m (7.53ft) Well casing material: PVC Schedule 40 Well Elevation (TOC): 3.15m

Date of water level: June 1st 2015 Well screen slot size: 10 Ground Elevation: 3.20m

Borehole diameter: 10.16cm (4") Well screen interval (bgs): 2.00m (6.56ft) - 3.52m (11.56ft) Log of Borehole: BH15-5

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.27 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

2.97 1 SAND 0.30 SAND, (fine-medium grained),some silt, some gravel 5ppm (subangular-subrounded, fine grained), light brown, BH15-5-1 Y 2 loose, dry, no odour 2.51 UNKNOWN 0.76 3 UNKNOWN, poor recovery, boulder blocked core barrel 1

4

5

6

2 7

0.83 8 SILTY SAND 2.44 SAND (fine-medium grained), clayey scattered wood waste (stringy wood and bark), dark brown, very loose, 9 wet 20ppm BH15-5-2 Y 3 10

11

12

13 4

-1.00 14 SAND 4.27 SAND (coarse grained), grey / brown, loose, homogenous, wet, no odour 5ppm 15 BH15-5-3 N

Borehole location:BH15-5 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.27m Borehole depth: 5.49m (18ft) Log of Borehole: BH15-5

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100 5ppm BH15-5-3

16 5

17

-2.22 18 End of Log 5.49

19

6 20

21

22

23 7

24

25

26 8

27

28

29

9

30

Borehole location:BH15-5 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.27m Borehole depth: 5.49m (18ft) Log of Borehole: BH15-6

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.62 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

3.31 1 0.30 SILTY SAND 5ppm SILTY SAND, (fine-medium grained), gravelly BH15-6-1 Y (subrounded, fine-coarse grained), light brown, loose, dry, no odour 3.01 2 0.61 SAND AND SILT SAND, (fine grained) and SILT, gravelly (subrounded, fine-coarse grained), dark brown/grey, loose, dry, no 3 odour 1

4

5 30ppm BH15-6-2 N

6

2 7

8

9

3 10

11

12

-0.34 13 4 SANDY SILT 3.96 180ppm SILT, SANDY (fine-coarse grained), dark brown, very BH15-6-3 N loose, wet, significant wood waste 14

15

Borehole location:BH15-6 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.62m Borehole depth: 5.49m (18ft) Log of Borehole: BH15-6

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

-1.26 16 CLAY 4.88 5 CLAY, grey, medium dense, homogenous, no odour -1.44 5.06 SAND 17 SAND (coarse grained), dark grey / black, significant BH15-6-4 N 10ppm broken white shell fragments, loose, wet, no odour BH15-6-5 N -1.87 18 End of Log 5.49

19

6 20

21

22

23 7

24

25

26 8

27

28

29

9

30

Borehole location:BH15-6 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.62m Borehole depth: 5.49m (18ft) Log of Borehole: BH15-7

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 1

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.32 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

3.01 1 0.30 SILTY SAND 0ppm SILTY SAND, (fine-medium grained), trace clay, dark BH15-7-1 Y brown/grey, loose, dry, no odour 2

3 1

2.10 4 SILTY SAND 1.22 SILTY SAND, (fine-medium grained), gravelly (subrounded, fine-coarse grained), dark brown/grey, 5 medium dense to dense, blocky, dry, no odour

6 10ppm 2 BH15-7-2 Y 7

8

9 0.42 SAND AND SILT 2.90 3 10 SAND (fine-medium grained) and SILT, clayey, trace gravel (subangular - subrounded, fine grained), dark 5ppm grey, loose to medium dense, blocky, wet, no odour BH15-7-3 N

11

12

13 4

14

-1.25 15 4.57

Borehole location:BH15-7 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.32m Borehole depth: 4.57m (15ft) Log of Borehole: BH15-8

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.29 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

2.98 1 0.30 SILTY SAND 0ppm SILTY SAND, (fine-medium grained), gravelly BH15-8-1 N (subrounded-subangular, fine-coarse grained), light 2 brown, loose, dry, no odour. Becoming brown-black, with some trace brick fragments at 1.2 m. 10ppm BH15-8-2 Y

3 1

4 45ppm BH15-8-3 N

1.77 5 UNKNOWN 1.52 UNKNOWN, poor recovery, core barrel blocked

6

2 7

0.85 8 SAND AND SILT 2.44 SAND (fine-medium grained) and SILT, clayey, trace gravel (fine grained, subangular-subrounded), dark BH15-8-4 Y 15ppm 9 grey, loose to medium dense, blocky, wet, no odour BH15-8-5 (dup) Y

3 10

11

12

13 4

-0.98 14 4.27 SAND 0ppm SAND (coarse grained), dark grey, loose, wet, no BH15-8-6 Y odour, significant broken shell fragments 15

Borehole location:BH15-8 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.29m Borehole depth: 8.53m (28ft) Log of Borehole: BH15-8

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

16 5

17 0ppm BH15-8-7 N

18

19 -2.65 5.94 6 SAND 20 SILTY SAND (fine - medium grained), light brown - brown, medium dense - dense, blocky, wet, no odour 0ppm BH15-8-8 N

21

22

23 7

24

0ppm 25 BH15-8-9 N

26 8

27

-5.25 28 End of Log 8.53

29

9

30

Borehole location:BH15-8 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.29m Borehole depth: 8.53m (28ft) Log of Borehole: BH15-9

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.42 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

3.12 1 0.30 SILTY SAND 0ppm SILTY SAND, (fine-medium grained), gravelly BH15-9-2 N (subrounded-subangular, fine-coarse grained), light 2 brown, loose, dry, no odour, trace debris (brick fragments)

3 1 2.35 SILTY SAND 1.07 4 SILTY SAND, (fine-medium grained), gravelly (subrounded-subangular, fine-coarse grained), dark brown, loose - medium dense, moist, no odour

5

0ppm 6 BH15-9-1 Y

2 7 1.13 SILTY SAND AND CLAY 2.29 8 SILTY SAND (fine grained) and CLAY, some gravel (fine-coarse grained, subangular-subrounded), dark grey, loose to medium dense, blocky, wet, no odour BH15-9-3 Y 160ppm 9 BH15-9-4 (dup) Y

3 10

11

12 -0.39 3.81 SAND 0ppm SAND (coarse grained), dark grey, loose, no odour, 13 BH15-9-5 N 4 significant white broken shell fragments

14

-1.15 15 4.57

Borehole location:BH15-9 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.420m Borehole depth: 5.486m (18ft) Log of Borehole: BH15-9

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

CLAY CLAY, grey, soft, wet, homogenous, no odour

-1.46 16 PEAT 4.88 10ppm 5 PEAT, loamy organic materials, some debris (wood BH15-9-6 N fragments, marsh materials) 17

-2.07 18 End of Log 5.49

19

6 20

21

22

23 7

24

25

26 8

27

28

29

9

30

Borehole location:BH15-9 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.420m Borehole depth: 5.486m (18ft) Log of Borehole: BH15-10

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 25th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 1

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 3.56 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

3.26 1 SAND 0.30 SAND, (fine-medium grained), some silt, some gravel (subrounded, fine-coarse grained), light brown mottled 20ppm brown silt, loose, dense, no odour 2 BH15-10-1 Y

3 1

4

2.04 5 SANDY SILT 1.52 SANDY (fine) SILT, some clay, dark brown, loose, moist, debris ( traces of asphalt remnants / wood 6 waste)

2 10ppm 7 BH15-10-2 Y

1.12 8 CLAY 2.44 SANDY (fine) CLAY, some silt trace of gravel (subrounded, fine), dark brown/grey, wet, medium 40ppm dense, no odour 9 BH15-10-3 N

3 0.51 10 UNKNOWN 3.05 UNKNOWN, poor recovery, core barrel blocked with wood debris and boulder 11

12

-0.40 13 4 End of Log 3.96

14

15

Borehole location:BH15-10 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 3.56m Borehole depth: 4.00m (13ft) Log of Borehole: BH15-11

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 26th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 1 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

ft m Ground Surface 4.36 0 0 ROOTS and TOPSOIL 0.00 ROOTS and TOPSOIL, black organic loamy, rootlets

4.05 1 SAND AND SILT 0.30 SAND, (fine grained) and SILT, gravelly (subrounded, 5ppm fine-coarse grained), dark brown, loose, blocky, dry, no BH15-11-1 Y 2 odour, trace debris (brick fragment) 3.59 SILTY SAND 0.76 3 SILTY SAND, (fine-medium grained), trace clay, dark brown - black, loose, dry, no odour, trace debris 1 (asphalt), poor revcovery

4

5

6

2 7

1.92 8 SAND AND SILT 2.44 SAND (fine grained) AND SILT, brown - grey w/ red mottling, dense, blocky, wet 9 200ppm BH15-11-2 Y

3 10

11

12

13 4 92ppm BH15-11-3 N 14

15

Borehole location:BH15-11 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 4.36m Borehole depth: 5.49m (18ft) Log of Borehole: BH15-11

Project Name/No: 302-035.04 Logged by: A Brown, J Chua

Client: Port Metro Vancouver Drilling Method: Sonic

Date Drilled:May 26th 2015 Drilling Company: OMEGA

Site Location: New Brighton Park Sheet: 2 of 2

SUBSURFACE PROFILE SAMPLE

Vapour LEL Backfill details Description ppm %

0 250 500 0 50 100

16 5

17

-1.13 18 End of Log 5.49

19

6 20

21

22

23 7

24

25

26 8

27

28

29

9

30

Borehole location:BH15-11 Borehole diameter: 10.16cm (4")

Borehole ground elevation: 4.36m Borehole depth: 5.49m (18ft)

APPENDIX I Field Methodology

PMV – Habitat Enhancement Program APPENDIX I Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 1 - August 2015

1.0 STAGE 2 PSI INVESTIGATION METHODOLOGY

Hemmera was on Site from May 14 to June 5, 2015 to complete a Phase 2 Environmental Site Assessment (ESA) investigation. The investigation included development of a site-specific health and safety plan, a private utility locate, a drilling program and soil and groundwater sampling and analysis.

1.1 HEALTH AND SAFETY

Prior to the Stage 2 PSI field work, a site-specific Health and Safety Plan (HASP) was prepared to address contaminants which may be encountered on-site and to outline the health and safety concerns associated with site activities. Prior to commencing work, Hemmera held a health and safety meeting with the sub-consultants (utility locators, drillers and boat operator) to review the potential hazards present on the Site, and discuss emergency plans and procedures.

1.2 UTILITY LOCATING PROGRAM

Prior to arriving on-Site a BC “One” Call was completed and the site contact was consulted to make available any utility records specific to the site. The information retrieved was shared with the private utility locator whom used the information in conjunction with remote sensing equipment to approximate the location of buried utilities. The utility locate field program was completed on May 15, 2015. The BC One Call was completed on May 11, 2015.

1.3 SOIL INVESTIGATION PROGRAM (DRILLING INVESTIGATION)

On May 25, 2015, eleven boreholes (MW15-1 to MW15-4 and BH15-5 to BH15-11) approximately 0.25 m in diameter were advanced to a maximum depth of approximately 8.5 mbgs. The boreholes were advanced using a track-mounted sonic drill supplied by Omega Environmental Drilling Ltd. of Pitt Meadows, BC. The track rig was ‘walked’ to each drill location using plywood sections to minimize damage to the park. Boreholes were logged with respect to geologic properties; specifically colour, moisture, density, grain size, and soil type.

Soil samples were collected according to established procedures outlined in the BC MOE’s British Columbia Field Sampling Manual, and Hemmera’s Standard Operating Procedures (SOPs). Soil material was brought to surface and discrete grab soil samples were collected directly from the sonic core based on changes in stratigraphic units, visual or olfactory evidence of potential contamination, and moisture content. To prevent cross-contamination, dedicated nitrile gloves were used to collect soil samples. All samples were collected for both potential laboratory submission and for measurement of combustible vapour concentrations. Samples collected and used to analyze vapour concentrations were placed in Ziploc bags to prevent the loss of volatile compounds to the atmosphere. After the sample was placed in the Ziploc bag it was set aside to allow the samples to reach appropriate temperatures to ensure representative combustible soil vapour (CSV) results. Hemmera used an RKI eagle combustible gas PMV – Habitat Enhancement Program APPENDIX I Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 2 - August 2015 detector, which recorded hexane (the industry accepted representative gas) concentrations in parts per million (ppm), and lower explosive limit percent (%LEL). Samples for potential laboratory submission were placed into 125-mL glass jars supplied by Maxxam Analytics (Maxxam) of Burnaby, BC and sealed.

The jarred samples were packed tightly and filled completely to prevent oxidation and loss of volatile organic compounds. Sample jars were identified using labels supplied by Maxxam, noting the date and sample number. The sample jars were then temporarily stored in chilled coolers to minimize chemical alteration prior to laboratory analysis. The coolers were delivered to Maxxam as soon as possible after drilling was complete (and within acceptable holding times). A site-specific chain-of-custody form accompanied the samples to be shipped for analysis. This form contained pertinent sampling information and analytical requirements, and followed the samples through the analytical process to final sample disposal. Details of pertinent sampling information for the Site were also recorded in a field notebook.

1.4 GROUNDWATER INVESTIGATION PROGRAM

1.4.1 Monitoring Well Installation

Of the eleven boreholes that were advanced during the drilling program, four were completed as 5.1 cm (2-inch) diameter PVC groundwater monitoring wells. Monitoring wells were installed to a maximum depth of approximately 8.5 m (28 feet) with screen lengths of approximately 1.5 m (5 feet). The monitoring wells were capped with a J-plug and finished at ground surface with a flush-mount casing.

After installation, groundwater monitoring wells were developed using a 10 mm diameter Waterra tubing and foot valve system. A minimum of six times the volume of the monitoring well filter sand pack was removed from MW15-2 and MW15-4. Due to slow recharge rates, monitoring wells MW15-1 and MW15-3 had less than six well volumes removed. Well purging occurred on May 26, 2015. Well development was conducted to remove foreign materials that may have entered the well and to ensure adequate permeability through the sand filter pack surrounding the PVC monitoring well screen length. Upon receipt of the analytical results, one location, MW15-1 was re-developed until the well was dry using a disposable bailer on June 4, 2015. Details of well lengths and installation are shown in the borehole logs in Appendix H.

1.4.2 Groundwater Monitoring and Sampling

The groundwater monitoring and sampling program was conducted on June 1, 2015 and one well, MW15-1 was re-sampled on June 5, 2015. Groundwater samples were collected according to established procedures outlined in the BC MOE’s British Columbia Field Sampling Manual. Specifically Hemmera performed the following site monitoring and sampling activities according to the following methodology:

a) Measurement of combustible headspace vapours (CHV) in the monitoring well using an RKI eagle combustible gas detector. PMV – Habitat Enhancement Program APPENDIX I Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 3 - August 2015

b) Measurement of light non-aqueous phased liquid (LNAPL) thickness (if any) and static water levels in all monitoring wells using a Heron H.01L interface probe; c) With the aid of a low flow peristaltic pump, monitoring well water was purged through a closed cell YSI sensor apparatus and into a pail. d) Purged water was monitored for physical parameters at 3 minute intervals, with the exception of MW15-1, which had low recharge and only one set of physical parameters were obtained prior to the collection of groundwater samples. Monitored physical parameters were temperature, conductivity, pH and groundwater elevation relative to surface. e) Groundwater was sampled using a peristaltic pump once field physical parameters had stabilized. f) Groundwater samples were collected in pre-cleaned bottles supplied by Maxxam and specific to the requested analysis. Groundwater samples were temporarily stored in ice-chilled, insulated shipping coolers. The coolers were delivered by Hemmera staff to Maxxam shortly after collection of the samples (and within acceptable hold times).

A site-specific chain-of-custody form accompanied the samples shipped for analysis. This form contained pertinent sampling information and analytical requirements, and followed the samples through the analytical process to final sample disposal. This documentation provided a traceable history of the sample from the time of collection to disposal, and ensured that analytical determinations were performed within recommended holding times. Details of pertinent sampling information for the Site were also recorded in a field notebook.

2.0 QUALITY ASSURANCE / QUALITY CONTROL (QA / QC)

2.1 FIELD QA / QC

The field quality assurance / quality control program (QA / QC) included practicing standard soil and groundwater sampling protocols to minimise the potential for cross contamination between samples.

The field QA / QC procedure included the collection and analysis of field duplicates for soil and groundwater samples from select sampling locations. Soil and sediment field duplicate samples were collected by dividing grab samples between characterization sample jars and duplicate sample jars. Groundwater samples and their matching field duplicates samples were collected concurrently by alternately filling sample bottles during collection using the sample methodologies described above.

The QA / QC methods were evaluated by determining the relative percent differences (RPD) between characterisation samples and their field duplicates. The RPD data quality objectives (DQO) selected for soil and groundwater were 40% and 20%, respectively and are considered acceptable for this investigation. PMV – Habitat Enhancement Program APPENDIX I Hemmera Limited Phase 1 and 2 ESA – New Brighton Park - 4 - August 2015

2.2 PROJECT LAB QA / QC

Maxxam was retained to conduct the chemical analyses for the soil and groundwater investigation. Select soil and groundwater samples were submitted to Maxxam and were subjected to QA / QC procedures specific to the laboratory. The analytical detection limits were reviewed to verify that they were below the applicable standard for each parameter tested. Certified lab reports are provided in Appendix J.

APPENDIX J Certified Analytical Lab Reports

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zŽƵƌ͘K͘͘η͗ϰϲϲϯϮϱͲϬϯͲϬϭ͕ϰϲϲϯϮϱͲϬϰͲϬϭ͕ϰϲϲϯϮϱͲϬϱͲϬϭ͕ϰϲϲϯϮϱͲϬϲͲ Ϭϭ͕ϰϲϲϯϮϱͲϬϳͲϬϭ͕ϰϲϲϯϮϱͲϬϴͲϬϭ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ZĞƉŽƌƚη͗Zϭϵϳϯϳϯϴ sĞƌƐŝŽŶ͗ϮͲZĞǀŝƐŝŽŶ

Zd/&/dK&E>z^/^ʹZs/^ZWKZd DyyD:Kη͗ϱϰϯϰϴϵ ZĞĐĞŝǀĞĚ͗ϮϬϭϱͬϬϱͬϮϲ͕ϭϰ͗ϬϬ

Jennifer Villocero ŶĐƌLJƉƚŝŽŶ<ĞLJ 10 Jun 2015 15:35:05 -07:00

WůĞĂƐĞĚŝƌĞĐƚĂůůƋƵĞƐƚŝŽŶƐƌĞŐĂƌĚŝŶŐƚŚŝƐĞƌƚŝĨŝĐĂƚĞŽĨŶĂůLJƐŝƐƚŽLJŽƵƌWƌŽũĞĐƚDĂŶĂŐĞƌ͘ ŵĂŶĚĞĞƉEĂŐƌĂ͕ĐĐŽƵŶƚ^ƉĞĐŝĂůŝƐƚ ŵĂŝů͗EĂŐƌĂΛŵĂdždžĂŵ͘ĐĂ WŚŽŶĞη;ϲϬϰͿϲϯϵͲϮϲϬϮ сссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссс DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

dŽƚĂůŽǀĞƌWĂŐĞƐ͗Ϯ WĂŐĞϮŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ W,z^/>d^d/E';^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϮϲ D,ϴϬϮϳ D,ϴϬϯϮ D,ϴϬϯϱ D,ϴϬϴϵ D,ϴϬϵϬ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ ,ϭϱͲϵͲϯ ,ϭϱͲϵͲϰ ,ϭϱͲϭϬͲϮ DtϭϱͲϯͲϮ DtϭϱͲϭͲϮ DtϭϱͲϭͲϯ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ DŽŝƐƚƵƌĞ й ϭϳ ϭϴ Ϯϰ ϭϱ ϴ͘Ϭ ϭϴ Ϭ͘ϯϬ ϳϵϭϰϰϴϱ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

DĂdždžĂŵ/ D,ϴϬϵϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϲ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ ,ϭϱͲϭϭͲϮ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ DŽŝƐƚƵƌĞ й ϭϵ Ϭ͘ϯϬ ϳϵϭϰϰϴϱ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϯŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ >DEd^zdKD/^WdZK^KWz;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϱϲ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϱͲϬϭ hŶŝƚƐ ,ϭϱͲϴͲϮ YĂƚĐŚ d>WdžƚƌĂĐƚŝŽŶWƌŽĐĞĚƵƌĞ /ŶŝƚŝĂůƉ,ŽĨ^ĂŵƉůĞ Ɖ, ϴ͘ϲϳ ϳϵϮϲϴϲϵ Ɖ,ĂĨƚĞƌ,ů Ɖ, ϭ͘ϰϰ ϳϵϮϲϴϲϵ &ŝŶĂůƉ,ŽĨ>ĞĂĐŚĂƚĞ Ɖ, ϱ͘Ϭϲ ϳϵϮϲϴϲϵ Ɖ,ŽĨ>ĞĂĐŚŝŶŐ&ůƵŝĚ Ɖ, ϰ͘ϵϯ ϳϵϮϲϴϲϵ

WĂŐĞϰŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ DΘ^Zdyͬ&ϭͬsW,/E^K/>Ͳ&/>WZ^;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϯϱ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϰͲϬϭ hŶŝƚƐ DtϭϱͲϯͲϮ Z> YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ &ϭ;ϲͲϭϬͿͲdy ŵŐͬŬŐ фϭϬ ϭϬ ϳϵϭϯϰϰϭ sŽůĂƚŝůĞƐ sW,;s,ϲƚŽϭϬͲdyͿ ŵŐͬŬŐ фϭϬ ϭϬ ϳϵϭϯϬϳϲ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ŵŐͬŬŐ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϭϬϭ ĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϲϭϬϭ dŽůƵĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϲϭϬϭ ƚŚLJůďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϭϲϭϬϭ ŵΘƉͲyLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϬϭ ŽͲyLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϬϭ ^ƚLJƌĞŶĞ ŵŐͬŬŐ фϬ͘ϬϯϬ Ϭ͘ϬϯϬ ϳϵϭϲϭϬϭ yLJůĞŶĞƐ;dŽƚĂůͿ ŵŐͬŬŐ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϬϭ s,ϲͲϭϬ ŵŐͬŬŐ фϭϬ ϭϬ ϳϵϭϲϭϬϭ ;ϲͲϭϬͿ ŵŐͬŬŐ фϭϬ ϭϬ ϳϵϭϲϭϬϭ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϭϬϰ ϳϵϭϲϭϬϭ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϵϵ ϳϵϭϲϭϬϭ ϭϬͲd,z>EE;ƐƵƌ͘Ϳ й ϴϯ ϳϵϭϲϭϬϭ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ й ϵϴ ϳϵϭϲϭϬϭ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϱŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ >W,Θ,W,&KZ^Z/E^K/>t/d,>>W,;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϮϲ D,ϴϬϮϳ D,ϴϬϯϮ D,ϴϬϴϵ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ ,ϭϱͲϵͲϯ ,ϭϱͲϵͲϰ Z> ,ϭϱͲϭϬͲϮ Z> YĂƚĐŚ DtϭϱͲϭͲϮ Z> YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ /ŶĚĞdžŽĨĚĚŝƚŝǀĞĂŶĐĞƌZŝƐŬ;/ZͿ Eͬ ϯ͘Ϯ ϯ͘ϭ Ϭ͘ϭϬ ϭ͘ϲ Ϭ͘ϭϬ ϳϵϭϮϴϰϴ ϭ͘Ϯ Ϭ͘ϭϬ ϳϵϭϰϬϭϮ ĞŶnjŽ΀Ă΁ƉLJƌĞŶĞĞƋƵŝǀĂůĞŶĐLJ Eͬ Ϭ͘Ϯϱ Ϭ͘Ϯϰ Ϭ͘ϭϬ Ϭ͘ϭϰ Ϭ͘ϭϬ ϳϵϭϮϴϰϴ Ϭ͘ϭϭ Ϭ͘ϭϬ ϳϵϭϰϬϭϮ WŽůLJĐLJĐůŝĐƌŽŵĂƚŝĐƐ EĂƉŚƚŚĂůĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϵϲ Ϭ͘Ϭϯϲ Ϭ͘ϬϭϬ Ϭ͘ϬϴϮ Ϭ͘ϬϭϬ ϳϵϭϵϯϱϭ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϭϵϯϱϭ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϰϯ Ϭ͘ϬϮϱ Ϭ͘ϬϮϬ Ϭ͘ϰϲ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚLJůĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϱϱ Ϭ͘Ϭϱϱ Ϭ͘ϬϬϱϬ фϬ͘Ϭϭϵ;ϭͿ Ϭ͘Ϭϭϵ ϳϵϭϵϯϱϭ Ϭ͘Ϭϭϭ Ϭ͘ϬϬϱϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϭϭ Ϭ͘ϬϬϵϮ Ϭ͘ϬϬϱϬ Ϭ͘ϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϵϯϱϭ фϬ͘ϬϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϵϯϱϭ &ůƵŽƌĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϰϮ Ϭ͘Ϭϰϰ Ϭ͘ϬϮϬ Ϭ͘ϭϴ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ WŚĞŶĂŶƚŚƌĞŶĞ ŵŐͬŬŐ Ϭ͘ϯϰ Ϭ͘ϯϭ Ϭ͘ϬϮϬ Ϭ͘ϰϭ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘Ϭϱϯ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϴϭ Ϭ͘Ϭϳϲ Ϭ͘ϬϬϰϬ фϬ͘ϬϰϬ;ϭͿ Ϭ͘ϬϰϬ ϳϵϭϵϯϱϭ Ϭ͘Ϭϭϴ Ϭ͘ϬϬϰϬ ϳϵϭϵϯϱϭ &ůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘ϰϰ Ϭ͘ϰϮ Ϭ͘ϬϮϬ Ϭ͘ϭϵ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘ϭϮ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ WLJƌĞŶĞ ŵŐͬŬŐ Ϭ͘ϰϮ Ϭ͘ϰϭ Ϭ͘ϬϮϬ Ϭ͘ϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘ϭϯ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ Ϭ͘ϭϲ Ϭ͘ϭϰ Ϭ͘ϬϮϬ Ϭ͘Ϭϳϰ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘Ϭϱϴ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ŚƌLJƐĞŶĞ ŵŐͬŬŐ Ϭ͘Ϯϭ Ϭ͘ϮϬ Ϭ͘ϬϮϬ Ϭ͘ϭϰ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘Ϭϳϯ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘Ϯϰ Ϭ͘Ϯϰ Ϭ͘ϬϮϬ Ϭ͘ϭϮ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘ϬϵϮ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϴϬ Ϭ͘Ϭϳϰ Ϭ͘ϬϮϬ Ϭ͘ϬϯϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘ϬϮϳ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ŵŐͬŬŐ Ϭ͘ϭϲ Ϭ͘ϭϱ Ϭ͘ϬϮϬ Ϭ͘Ϭϴϯ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ Ϭ͘ϬϲϮ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϵϳ Ϭ͘Ϭϵϳ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ŵŐͬŬŐ Ϭ͘ϭϮ Ϭ͘ϭϭ Ϭ͘ϬϱϬ Ϭ͘ϬϳϮ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ Ϭ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ >ŽǁDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ŵŐͬŬŐ Ϭ͘ϲϳ Ϭ͘ϱϱ Ϭ͘ϬϱϬ ϭ͘Ϯ Ϭ͘ϬϱϬ ϳϵϭϮϴϰϵ Ϭ͘Ϭϴϯ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ ,ŝŐŚDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ŵŐͬŬŐ ϭ͘ϵ ϭ͘ϴ Ϭ͘ϬϱϬ Ϭ͘ϵϭ Ϭ͘ϬϱϬ ϳϵϭϮϴϰϵ Ϭ͘ϲϭ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ dŽƚĂůW, ŵŐͬŬŐ Ϯ͘ϲ Ϯ͘ϰ Ϭ͘ϬϱϬ Ϯ͘ϭ Ϭ͘ϬϱϬ ϳϵϭϮϴϰϵ Ϭ͘ϳϬ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ >W,;ϭϬͲϭϵůĞƐƐW,Ϳ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϲϱϵ ϭϬϬ ϳϵϭϯϱϴϰ фϭϬϬ ϭϬϬ ϳϵϭϰϮϴϰ ,W,;ϭϵͲϯϮůĞƐƐW,Ϳ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϯϰϮ ϭϬϬ ϳϵϭϯϱϴϰ ϭϮϲ ϭϬϬ ϳϵϭϰϮϴϰ ,LJĚƌŽĐĂƌďŽŶƐ W,;ϭϬͲϭϵͿ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϲϱϵ ϭϬϬ ϳϵϭϵϯϯϲ фϭϬϬ ϭϬϬ ϳϵϭϵϯϯϲ W,;ϭϵͲϯϮͿ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϯϰϮ ϭϬϬ ϳϵϭϵϯϯϲ ϭϮϲ ϭϬϬ ϳϵϭϵϯϯϲ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ й ϭϬϰ ϵϲ ϵϴ ϳϵϭϵϯϱϭ ϭϭϬ ϳϵϭϵϯϱϭ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ й ϵϮ ϴϴ ϴϮ ϳϵϭϵϯϱϭ ϵϲ ϳϵϭϵϯϱϭ ϴͲEW,d,>E;ƐƵƌ͘Ϳ й ϵϳ ϵϭ ϴϭ ϳϵϭϵϯϱϭ ϵϴ ϳϵϭϵϯϱϭ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ й ϭϬϲ ϵϵ ϵϴ ϳϵϭϵϯϱϭ ϭϬϴ ϳϵϭϵϯϱϭ KͲdZW,Ez>;ƐƵƌ͘Ϳ й ϵϮ ϵϬ ϵϱ ϳϵϭϵϯϯϲ ϵϴ ϳϵϭϵϯϯϲ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ ;ϭͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘

WĂŐĞϲŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ >W,Θ,W,&KZ^Z/E^K/>t/d,>>W,;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϵϬ D,ϴϬϵϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϲ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϴͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ DtϭϱͲϭͲϯ ,ϭϱͲϭϭͲϮ Z> YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ /ŶĚĞdžŽĨĚĚŝƚŝǀĞĂŶĐĞƌZŝƐŬ;/ZͿ Eͬ Ϭ͘ϰϯ Ϭ͘ϯϭ Ϭ͘ϭϬ ϳϵϭϰϬϭϮ ĞŶnjŽ΀Ă΁ƉLJƌĞŶĞĞƋƵŝǀĂůĞŶĐLJ Eͬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϰϬϭϮ WŽůLJĐLJĐůŝĐƌŽŵĂƚŝĐƐ EĂƉŚƚŚĂůĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϬ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϭϵϯϱϭ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϬϱϬ фϬ͘ϬϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϵ фϬ͘ϬϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϵϯϱϭ &ůƵŽƌĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϯϯ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ WŚĞŶĂŶƚŚƌĞŶĞ ŵŐͬŬŐ Ϭ͘ϭϭ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϭ фϬ͘ϬϬϰϬ Ϭ͘ϬϬϰϬ ϳϵϭϵϯϱϭ &ůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘ϭϭ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ WLJƌĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϴϯ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ŚƌLJƐĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϲ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘ϬϮϯ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϯϱϭ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϯϱϭ >ŽǁDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ŵŐͬŬŐ Ϭ͘Ϯϭ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ ,ŝŐŚDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ŵŐͬŬŐ Ϭ͘Ϯϲ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ dŽƚĂůW, ŵŐͬŬŐ Ϭ͘ϰϳ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϰϬϭϯ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ >W,;ϭϬͲϭϵůĞƐƐW,Ϳ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϳϵϭϰϮϴϰ ,W,;ϭϵͲϯϮůĞƐƐW,Ϳ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϳϵϭϰϮϴϰ ,LJĚƌŽĐĂƌďŽŶƐ W,;ϭϬͲϭϵͿ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϳϵϭϵϯϯϲ W,;ϭϵͲϯϮͿ ŵŐͬŬŐ фϭϬϬ фϭϬϬ ϭϬϬ ϳϵϭϵϯϯϲ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ й ϭϬϳ ϭϭϭ ϳϵϭϵϯϱϭ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ й ϵϰ ϵϲ ϳϵϭϵϯϱϭ ϴͲEW,d,>E;ƐƵƌ͘Ϳ й ϵϲ ϭϬϬ ϳϵϭϵϯϱϭ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ й ϭϬϯ ϭϬϲ ϳϵϭϵϯϱϭ KͲdZW,Ez>;ƐƵƌ͘Ϳ й ϵϯ ϵϭ ϳϵϭϵϯϯϲ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϳŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ ^ZͬDDd>^/E^K/>;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϮϬ D,ϴϬϮϰ D,ϴϬϮϲ D,ϴϬϮϳ D,ϴϬϯϭ D,ϴϬϯϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϰͲϬϭ hŶŝƚƐ DtϭϱͲϰͲϯ ,ϭϱͲϵͲϭ ,ϭϱͲϵͲϯ ,ϭϱͲϵͲϰ ,ϭϱͲϭϬͲϭ DtϭϱͲϯͲϭ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ ^ŽůƵďůĞ;Ϯ͗ϭͿƉ, Ɖ, ϲ͘ϲϴ ϳ͘Ϯϯ ϳ͘ϱϮ ϳ͘Ϯϯ ϲ͘ϱϮ ϲ͘ϯϲ Eͬ ϳϵϭϱϰϵϬ dŽƚĂůDĞƚĂůƐďLJ/WD^ dŽƚĂůůƵŵŝŶƵŵ;ůͿ ŵŐͬŬŐ ϭϳϱϬϬ ϭϯϳϬϬ ϭϲϯϬϬ ϭϲϯϬϬ ϭϴϭϬϬ ϮϬϱϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŶƚŝŵŽŶLJ;^ďͿ ŵŐͬŬŐ Ϭ͘ϵϬ ϭ͘ϬϬ ϭ͘ϲϭ;ϭͿ Ϭ͘ϳϴ Ϭ͘ϮϮ Ϭ͘ϵϳ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůƌƐĞŶŝĐ;ƐͿ ŵŐͬŬŐ ϰ͘ϵϴ Ϯ͘ϳϰ ϯ͘ϱϭ ϯ͘ϱϲ ϯ͘ϭϬ ϰ͘ϴϵ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂƌŝƵŵ;ĂͿ ŵŐͬŬŐ ϭϬϯ ϲϬ͘ϳ ϭϭϯ ϭϭϬ ϵϭ͘Ϭ ϭϭϬ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĞƌLJůůŝƵŵ;ĞͿ ŵŐͬŬŐ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƐŵƵƚŚ;ŝͿ ŵŐͬŬŐ Ϭ͘ϭϭ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϯ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĂĚŵŝƵŵ;ĚͿ ŵŐͬŬŐ Ϭ͘Ϯϳϴ Ϭ͘ϭϬϲ Ϭ͘ϮϴϬ Ϭ͘Ϯϱϴ Ϭ͘ϭϮϬ Ϭ͘ϳϬϵ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂůĐŝƵŵ;ĂͿ ŵŐͬŬŐ ϯϳϭϬ ϮϵϵϬ ϰϰϭϬ ϯϱϰϬ ϯϵϴϬ ϯϮϱϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŚƌŽŵŝƵŵ;ƌͿ ŵŐͬŬŐ ϭϲ͘ϲ ϭϬ͘ϲ ϮϬ͘ϰ ϮϬ͘Ϭ ϮϮ͘ϴ ϮϮ͘ϯ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŽďĂůƚ;ŽͿ ŵŐͬŬŐ ϱ͘ϴϳ ϱ͘ϱϳ ϲ͘ϴϮ ϲ͘ϲϲ ϴ͘ϳϵ ϵ͘ϱϴ Ϭ͘ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽƉƉĞƌ;ƵͿ ŵŐͬŬŐ Ϯϱ͘ϭ ϭϰ͘ϭ Ϯϲ͘Ϭ Ϯϰ͘ϱ ϭϴ͘ϯ ϰϴ͘Ϯ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů/ƌŽŶ;&ĞͿ ŵŐͬŬŐ ϭϴϯϬϬ ϭϯϴϬϬ ϭϴϮϬϬ ϭϳϮϬϬ ϮϬϭϬϬ ϮϮϳϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů>ĞĂĚ;WďͿ ŵŐͬŬŐ ϴϭ͘ϳ ϯϱ͘ϯ ϱϰ͘ϳ ϱϲ͘ϵ ϴ͘ϰϰ ϭϲϯ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂů>ŝƚŚŝƵŵ;>ŝͿ ŵŐͬŬŐ ϱ͘ϴ ϲ͘ϵ ϳ͘ϵ ϳ͘ϵ ϵ͘ϳ ϴ͘ϭ ϱ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůDĂŐŶĞƐŝƵŵ;DŐͿ ŵŐͬŬŐ ϯϴϮϬ ϰϬϮϬ ϰϯϲϬ ϰϬϵϬ ϰϳϰϬ ϰϱϯϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŶŐĂŶĞƐĞ;DŶͿ ŵŐͬŬŐ Ϯϲϴ ϮϳϮ Ϯϵϭ Ϯϳϴ ϰϮϯ ϯϭϰ Ϭ͘ϮϬ ϳϵϭϲϰϱϯ dŽƚĂůDĞƌĐƵƌLJ;,ŐͿ ŵŐͬŬŐ Ϭ͘ϬϳϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘Ϭϱϲ фϬ͘ϬϱϬ Ϭ͘Ϯϵϲ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůDŽůLJďĚĞŶƵŵ;DŽͿ ŵŐͬŬŐ ϭ͘ϭϴ Ϭ͘ϲϮ ϭ͘ϭϮ ϭ͘Ϯϯ Ϭ͘ϲϮ Ϭ͘ϵϳ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůEŝĐŬĞů;EŝͿ ŵŐͬŬŐ ϭϬ͘ϯ ϳ͘ϯϴ ϭϭ͘ϵ ϭϮ͘Ϭ ϭϱ͘ϳ ϭϳ͘Ϭ Ϭ͘ϴϬ ϳϵϭϲϰϱϯ dŽƚĂůWŚŽƐƉŚŽƌƵƐ;WͿ ŵŐͬŬŐ ϱϰϱ ϯϭϵ ϰϭϱ ϯϲϰ ϮϵϬ ϳϭϬ ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůWŽƚĂƐƐŝƵŵ;<Ϳ ŵŐͬŬŐ ϲϭϮ ϰϰϮ ϳϮϮ ϲϰϭ ϲϬϲ ϱϳϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ĞůĞŶŝƵŵ;^ĞͿ ŵŐͬŬŐ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŝůǀĞƌ;ŐͿ ŵŐͬŬŐ Ϭ͘Ϭϵϰ Ϭ͘Ϭϲϭ Ϭ͘ϬϲϬ Ϭ͘Ϭϲϴ фϬ͘ϬϱϬ Ϭ͘ϰϭϴ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŽĚŝƵŵ;EĂͿ ŵŐͬŬŐ ϮϭϮ ϭϯϱ ϭϲϲ ϭϲϰ ϭϵϬ ϭϰϴ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ƚƌŽŶƚŝƵŵ;^ƌͿ ŵŐͬŬŐ ϯϰ͘ϵ ϯϬ͘ϱ ϰϯ͘ϳ ϰϬ͘ϳ ϰϬ͘Ϭ ϯϰ͘ϴ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŚĂůůŝƵŵ;důͿ ŵŐͬŬŐ Ϭ͘Ϭϱϱ фϬ͘ϬϱϬ Ϭ͘Ϭϲϵ Ϭ͘Ϭϲϴ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝŶ;^ŶͿ ŵŐͬŬŐ Ϯ͘ϵϲ Ϭ͘ϴϬ ϰ͘ϭϱ ϰ͘ϭϴ Ϭ͘ϯϱ ϲ͘ϴϯ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝƚĂŶŝƵŵ;dŝͿ ŵŐͬŬŐ ϲϴϳ ϱϭϮ ϱϭϭ ϱϯϰ ϳϳϭ ϲϴϱ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůhƌĂŶŝƵŵ;hͿ ŵŐͬŬŐ Ϭ͘ϰϭϰ Ϭ͘ϯϱϰ Ϭ͘ϰϲϬ Ϭ͘ϰϱϭ Ϭ͘ϰϰϵ Ϭ͘ϰϴϯ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůsĂŶĂĚŝƵŵ;sͿ ŵŐͬŬŐ ϱϬ͘ϭ ϯϲ͘Ϯ ϰϭ͘ϳ ϰϭ͘ϰ ϱϭ͘ϴ ϱϬ͘Ϭ Ϯ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝŶĐ;ŶͿ ŵŐͬŬŐ ϭϭϵ ϱϮ͘ϳ ϴϭ͘ϯ ϵϵ͘Ϯ ϯϳ͘ϱ Ϯϯϰ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝƌĐŽŶŝƵŵ;ƌͿ ŵŐͬŬŐ Ϭ͘ϳϲ фϬ͘ϱϬ ϭ͘ϰϳ ϭ͘Ϯϰ Ϭ͘ϵϰ Ϭ͘ϲϵ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ EͬсEŽƚƉƉůŝĐĂďůĞ ;ϭͿƵƉůŝĐĂƚĞĞdžĐĞĞĚƐĂĐĐĞƉƚĂŶĐĞĐƌŝƚĞƌŝĂĨŽƌ^ď͘ϭϬйŽĨĂŶĂůLJƚĞƐĨĂŝůƵƌĞŝŶŵƵůƚŝĞůĞŵĞŶƚƐĐĂŶƐĂƌĞĂůůŽǁĞĚ͘

WĂŐĞϴŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ ^ZͬDDd>^/E^K/>;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϯϱ D,ϴϬϱϬ D,ϴϬϱϲ D,ϴϬϱϴ D,ϴϬϱϵ D,ϴϬϲϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϱͲϬϭ ϰϲϲϯϮϱͲϬϱͲϬϭ ϰϲϲϯϮϱͲϬϱͲϬϭ ϰϲϲϯϮϱͲϬϲͲϬϭ ϰϲϲϯϮϱͲϬϲͲϬϭ hŶŝƚƐ DtϭϱͲϯͲϮ ,ϭϱͲϲͲϭ ,ϭϱͲϴͲϮ ,ϭϱͲϴͲϰ ,ϭϱͲϴͲϱ DtϭϱͲϮͲϭ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ ^ŽůƵďůĞ;Ϯ͗ϭͿƉ, Ɖ, ϲ͘ϲϰ ϳ͘Ϯϲ ϴ͘ϭϬ ϳ͘ϬϮ ϲ͘ϵϱ ϴ͘Ϯϳ Eͬ ϳϵϭϱϰϵϬ dŽƚĂůDĞƚĂůƐďLJ/WD^ dŽƚĂůůƵŵŝŶƵŵ;ůͿ ŵŐͬŬŐ ϭϰϯϬϬ ϭϰϳϬϬ ϭϰϯϬϬ ϭϲϰϬϬ ϭϱϵϬϬ ϭϰϱϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŶƚŝŵŽŶLJ;^ďͿ ŵŐͬŬŐ Ϭ͘ϴϭ Ϭ͘ϰϬ ϳ͘ϰϰ ϭ͘ϰϵ Ϭ͘ϴϲ ϭ͘ϰϴ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůƌƐĞŶŝĐ;ƐͿ ŵŐͬŬŐ ϯ͘Ϭϵ Ϯ͘ϵϭ ϱ͘ϴϮ ϯ͘Ϯϯ Ϯ͘ϵϳ ϯ͘ϱϱ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂƌŝƵŵ;ĂͿ ŵŐͬŬŐ ϵϲ͘ϰ ϳϴ͘ϲ ϮϮϮ ϴϱ͘ϱ ϴϱ͘ϴ ϴϱ͘ϲ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĞƌLJůůŝƵŵ;ĞͿ ŵŐͬŬŐ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƐŵƵƚŚ;ŝͿ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϰ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĂĚŵŝƵŵ;ĚͿ ŵŐͬŬŐ Ϭ͘ϮϮϰ Ϭ͘ϭϰϬ Ϭ͘ϴϱϲ Ϭ͘ϭϵϮ Ϭ͘ϭϵϱ Ϭ͘ϯϰϬ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂůĐŝƵŵ;ĂͿ ŵŐͬŬŐ ϯϵϴϬ ϯϱϱϬ ϵϴϭϬ ϯϭϳϬ ϮϲϰϬ ϲϬϲϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŚƌŽŵŝƵŵ;ƌͿ ŵŐͬŬŐ ϭϱ͘ϴ ϭϳ͘ϯ ϮϬ͘ϲ ϭϱ͘ϴ ϭϱ͘ϰ ϭϴ͘ϵ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŽďĂůƚ;ŽͿ ŵŐͬŬŐ ϳ͘ϰϳ ϲ͘ϵϯ ϳ͘ϬϬ ϲ͘ϯϮ ϲ͘ϯϴ ϲ͘ϴϯ Ϭ͘ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽƉƉĞƌ;ƵͿ ŵŐͬŬŐ ϯϰ͘ϰ Ϯϲ͘ϱ ϲϱ͘ϯ ϮϬ͘ϯ ϭϵ͘ϳ ϯϯ͘ϳ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů/ƌŽŶ;&ĞͿ ŵŐͬŬŐ ϭϴϯϬϬ ϭϳϵϬϬ ϮϱϰϬϬ ϭϲϴϬϬ ϭϳϬϬϬ ϭϵϳϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů>ĞĂĚ;WďͿ ŵŐͬŬŐ ϱϱ͘ϱ Ϯϲ͘ϵ ϭϴϬ ϰϳ͘ϲ ϯϯ͘ϵ ϭϬϭ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂů>ŝƚŚŝƵŵ;>ŝͿ ŵŐͬŬŐ ϲ͘ϵ ϴ͘Ϯ ϴ͘ϭ ϴ͘ϭ ϳ͘ϳ ϲ͘ϳ ϱ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůDĂŐŶĞƐŝƵŵ;DŐͿ ŵŐͬŬŐ ϱϱϱϬ ϰϵϯϬ ϰϰϬϬ ϰϵϮϬ ϰϲϱϬ ϰϲϮϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŶŐĂŶĞƐĞ;DŶͿ ŵŐͬŬŐ Ϯϯϵ Ϯϵϰ ϯϵϭ ϮϴϬ ϮϲϬ Ϯϴϵ Ϭ͘ϮϬ ϳϵϭϲϰϱϯ dŽƚĂůDĞƌĐƵƌLJ;,ŐͿ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϭϬϳ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϲϴϱ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůDŽůLJďĚĞŶƵŵ;DŽͿ ŵŐͬŬŐ Ϭ͘ϲϮ Ϭ͘ϱϮ ϭ͘Ϯϭ Ϭ͘ϳϬ Ϭ͘ϲϰ Ϭ͘ϳϰ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůEŝĐŬĞů;EŝͿ ŵŐͬŬŐ ϭϭ͘ϳ ϭϮ͘ϱ ϭϴ͘Ϭ ϭϬ͘ϵ ϭϬ͘Ϯ ϭϯ͘Ϯ Ϭ͘ϴϬ ϳϵϭϲϰϱϯ dŽƚĂůWŚŽƐƉŚŽƌƵƐ;WͿ ŵŐͬŬŐ ϯϰϯ ϰϬϬ ϲϱϭ ϰϬϯ ϯϰϵ ϰϱϮ ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůWŽƚĂƐƐŝƵŵ;<Ϳ ŵŐͬŬŐ ϳϳϵ ϳϮϳ ϳϲϭ ϱϱϯ ϱϴϳ ϴϰϯ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ĞůĞŶŝƵŵ;^ĞͿ ŵŐͬŬŐ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŝůǀĞƌ;ŐͿ ŵŐͬŬŐ Ϭ͘Ϭϱϲ Ϭ͘Ϭϱϱ Ϭ͘ϭϯϭ Ϭ͘Ϭϳϳ Ϭ͘Ϭϲϰ Ϭ͘Ϭϵϴ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŽĚŝƵŵ;EĂͿ ŵŐͬŬŐ ϭϵϰ Ϯϭϴ ϰϭϰ ϭϲϭ ϭϲϬ ϯϰϰ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ƚƌŽŶƚŝƵŵ;^ƌͿ ŵŐͬŬŐ ϯϰ͘ϳ ϯϭ͘ϭ ϭϯϬ ϯϲ͘Ϯ ϯϮ͘ϳ ϰϰ͘ϲ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŚĂůůŝƵŵ;důͿ ŵŐͬŬŐ Ϭ͘Ϭϱϴ Ϭ͘ϬϲϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘Ϭϱϰ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝŶ;^ŶͿ ŵŐͬŬŐ Ϯ͘Ϭϭ ϭ͘ϭϳ ϯϮ͘ϭ ϯ͘ϵϵ Ϯ͘ϭϱ ϭϱ͘ϰ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝƚĂŶŝƵŵ;dŝͿ ŵŐͬŬŐ ϱϮϮ ϱϱϵ ϱϴϱ ϱϴϵ ϲϬϵ ϱϱϵ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůhƌĂŶŝƵŵ;hͿ ŵŐͬŬŐ Ϭ͘ϱϬϳ Ϭ͘ϰϱϴ Ϭ͘ϰϵϳ Ϭ͘ϰϬϮ Ϭ͘ϰϬϲ Ϭ͘ϯϳϱ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůsĂŶĂĚŝƵŵ;sͿ ŵŐͬŬŐ ϰϯ͘ϱ ϰϰ͘ϴ ϰϴ͘ϭ ϰϰ͘ϵ ϰϱ͘ϲ ϰϲ͘ϯ Ϯ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝŶĐ;ŶͿ ŵŐͬŬŐ ϴϴ͘ϱ ϱϰ͘ϴ ϯϳϵ ϳϬ͘ϰ ϲϵ͘ϲ ϴϭ͘ϯ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝƌĐŽŶŝƵŵ;ƌͿ ŵŐͬŬŐ ϭ͘ϳϯ Ϭ͘ϳϳ ϭ͘ϰϮ Ϭ͘ϵϴ ϭ͘ϮϬ ϭ͘ϰϰ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ EͬсEŽƚƉƉůŝĐĂďůĞ

WĂŐĞϵŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ ^ZͬDDd>^/E^K/>;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϲϱ D,ϴϬϳϮ D,ϴϬϳϯ D,ϴϬϳϱ D,ϴϬϳϲ D,ϴϬϳϴ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϲͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ hŶŝƚƐ DtϭϱͲϮͲϮ ,ϭϱͲϳͲϭ ,ϭϱͲϳͲϮ ,ϭϱͲϱͲϭ ,ϭϱͲϱͲϮ DtϭϱͲϭͲϭ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ ^ŽůƵďůĞ;Ϯ͗ϭͿƉ, Ɖ, ϳ͘ϰϲ ϳ͘ϵϯ ϳ͘ϰϴ ϵ͘ϵϳ ϴ͘ϯϬ ϳ͘ϳϱ Eͬ ϳϵϭϱϰϵϬ dŽƚĂůDĞƚĂůƐďLJ/WD^ dŽƚĂůůƵŵŝŶƵŵ;ůͿ ŵŐͬŬŐ ϮϯϭϬϬ ϭϮϯϬϬ ϭϵϳϬϬ ϭϲϭϬϬ ϭϴϭϬϬ ϭϯϬϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŶƚŝŵŽŶLJ;^ďͿ ŵŐͬŬŐ Ϭ͘ϰϭ Ϭ͘ϯϬ Ϭ͘ϭϲ Ϭ͘ϱϮ Ϭ͘ϲϯ Ϭ͘ϴϵ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůƌƐĞŶŝĐ;ƐͿ ŵŐͬŬŐ ϱ͘ϲϵ ϭ͘ϴϰ ϯ͘ϭϵ Ϯ͘ϴϰ ϰ͘ϭϭ ϯ͘ϰϱ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂƌŝƵŵ;ĂͿ ŵŐͬŬŐ ϭϭϴ ϲϲ͘Ϯ ϵϲ͘ϯ ϴϮ͘Ϭ ϴϴ͘ϱ ϳϯ͘ϱ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĞƌLJůůŝƵŵ;ĞͿ ŵŐͬŬŐ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƐŵƵƚŚ;ŝͿ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĂĚŵŝƵŵ;ĚͿ ŵŐͬŬŐ Ϭ͘ϭϱϭ Ϭ͘ϭϭϰ Ϭ͘ϭϭϭ Ϭ͘ϮϮϱ Ϭ͘ϭϵϵ Ϭ͘ϮϱϮ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂůĐŝƵŵ;ĂͿ ŵŐͬŬŐ ϯϵϮϬ ϯϰϱϬ ϮϳϱϬ ϭϱϬϬϬ ϳϳϴϬ ϲϴϴϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŚƌŽŵŝƵŵ;ƌͿ ŵŐͬŬŐ Ϯϳ͘ϴ ϭϰ͘Ϭ ϭϵ͘ϭ ϭϳ͘ϯ Ϯϰ͘ϯ Ϯϭ͘Ϭ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŽďĂůƚ;ŽͿ ŵŐͬŬŐ ϭϬ͘ϴ ϳ͘Ϭϴ ϵ͘Ϯϯ ϴ͘Ϯϰ ϳ͘ϵϬ ϳ͘ϰϯ Ϭ͘ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽƉƉĞƌ;ƵͿ ŵŐͬŬŐ Ϯϴ͘ϳ ϮϮ͘ϯ ϮϬ͘Ϭ Ϯϳ͘ϰ Ϯϳ͘ϲ ϯϭ͘Ϯ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů/ƌŽŶ;&ĞͿ ŵŐͬŬŐ ϮϰϳϬϬ ϭϳϱϬϬ ϮϬϰϬϬ ϮϬϯϬϬ ϮϭϯϬϬ ϭϵϮϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů>ĞĂĚ;WďͿ ŵŐͬŬŐ ϯϱ͘ϲ ϮϬ͘ϭ ϭϮ͘ϴ Ϯϴ͘ϰ ϯϳ͘ϰ ϰϬ͘ϰ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂů>ŝƚŚŝƵŵ;>ŝͿ ŵŐͬŬŐ ϭϬ͘ϳ ϲ͘ϭ ϭϬ͘Ϭ ϴ͘ϱ ϴ͘ϱ ϳ͘ϳ ϱ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůDĂŐŶĞƐŝƵŵ;DŐͿ ŵŐͬŬŐ ϲϱϯϬ ϱϬϵϬ ϲϲϮϬ ϲϭϯϬ ϱϭϵϬ ϱϲϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŶŐĂŶĞƐĞ;DŶͿ ŵŐͬŬŐ ϯϲϵ Ϯϴϳ Ϯϴϳ ϯϮϯ ϯϰϮ ϯϱϮ Ϭ͘ϮϬ ϳϵϭϲϰϱϯ dŽƚĂůDĞƌĐƵƌLJ;,ŐͿ ŵŐͬŬŐ Ϭ͘Ϭϱϳ Ϭ͘Ϭϱϵ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϲϬ Ϭ͘ϬϲϮ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůDŽůLJďĚĞŶƵŵ;DŽͿ ŵŐͬŬŐ Ϭ͘ϵϴ Ϭ͘ϯϱ Ϭ͘ϲϱ Ϭ͘ϲϲ ϭ͘ϲϮ Ϭ͘ϳϳ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůEŝĐŬĞů;EŝͿ ŵŐͬŬŐ ϭϵ͘ϯ ϭϬ͘ϳ ϭϰ͘ϯ ϭϭ͘ϳ ϭϯ͘ϴ ϭϴ͘ϱ Ϭ͘ϴϬ ϳϵϭϲϰϱϯ dŽƚĂůWŚŽƐƉŚŽƌƵƐ;WͿ ŵŐͬŬŐ ϰϬϴ ϯϲϱ ϯϮϮ ϯϴϰ ϰϮϭ ϱϮϳ ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůWŽƚĂƐƐŝƵŵ;<Ϳ ŵŐͬŬŐ ϵϬϬ ϴϲϰ ϴϰϮ ϭϬϱϬ ϴϲϭ ϴϭϴ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ĞůĞŶŝƵŵ;^ĞͿ ŵŐͬŬŐ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŝůǀĞƌ;ŐͿ ŵŐͬŬŐ Ϭ͘Ϭϱϲ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϮ Ϭ͘Ϭϲϱ Ϭ͘Ϭϲϴ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŽĚŝƵŵ;EĂͿ ŵŐͬŬŐ ϰϬϴ Ϯϱϲ ϮϬϱ ϯϵϲ ϯϮϯ Ϯϰϲ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ƚƌŽŶƚŝƵŵ;^ƌͿ ŵŐͬŬŐ ϯϲ͘ϴ Ϯϴ͘ϯ ϯϮ͘ϵ ϱϵ͘ϱ ϰϮ͘ϭ ϯϴ͘ϲ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŚĂůůŝƵŵ;důͿ ŵŐͬŬŐ Ϭ͘Ϭϲϱ фϬ͘ϬϱϬ Ϭ͘Ϭϳϭ Ϭ͘Ϭϲϯ Ϭ͘Ϭϲϳ Ϭ͘Ϭϱϵ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝŶ;^ŶͿ ŵŐͬŬŐ ϭϮ͘ϱ ϭ͘ϭϱ Ϭ͘ϯϱ ϭ͘ϵϰ ϭ͘ϲϬ ϭ͘ϵϮ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝƚĂŶŝƵŵ;dŝͿ ŵŐͬŬŐ ϵϱϱ ϱϴϴ ϳϳϬ ϲϮϲ ϳϴϴ ϲϮϭ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůhƌĂŶŝƵŵ;hͿ ŵŐͬŬŐ Ϭ͘ϱϲϰ Ϭ͘ϯϬϳ Ϭ͘ϯϳϱ Ϭ͘ϰϵϮ Ϭ͘ϰϴϬ Ϭ͘ϰϭϬ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůsĂŶĂĚŝƵŵ;sͿ ŵŐͬŬŐ ϲϭ͘ϰ ϰϮ͘ϭ ϱϬ͘ϳ ϰϴ͘Ϭ ϱϯ͘ϳ ϰϰ͘ϳ Ϯ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝŶĐ;ŶͿ ŵŐͬŬŐ ϲϭ͘ϭ ϰϱ͘ϰ ϲϱ͘ϳ ϲϵ͘ϲ ϲϭ͘ϴ ϳϲ͘ϰ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝƌĐŽŶŝƵŵ;ƌͿ ŵŐͬŬŐ Ϯ͘ϰϵ Ϯ͘Ϭϱ Ϯ͘ϵϮ Ϯ͘ϰϴ ϭ͘Ϯϲ ϭ͘Ϭϲ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ EͬсEŽƚƉƉůŝĐĂďůĞ

WĂŐĞϭϬŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ ^ZͬDDd>^/E^K/>;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϵϬ D,ϴϬϵϯ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϲ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϴͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ DtϭϱͲϭͲϯ ,ϭϱͲϭϭͲϭ Z> YĂƚĐŚ WŚLJƐŝĐĂůWƌŽƉĞƌƚŝĞƐ ^ŽůƵďůĞ;Ϯ͗ϭͿƉ, Ɖ, ϴ͘ϳϬ ϲ͘ϱϬ Eͬ ϳϵϭϱϰϵϬ dŽƚĂůDĞƚĂůƐďLJ/WD^ dŽƚĂůůƵŵŝŶƵŵ;ůͿ ŵŐͬŬŐ ϱϬϭϬ ϭϳϯϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŶƚŝŵŽŶLJ;^ďͿ ŵŐͬŬŐ Ϭ͘Ϯϰ ϭ͘ϯϬ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůƌƐĞŶŝĐ;ƐͿ ŵŐͬŬŐ ϭ͘ϵϭ ϯ͘ϴϲ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂƌŝƵŵ;ĂͿ ŵŐͬŬŐ Ϯϭ͘ϵ ϴϱ͘ϳ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĞƌLJůůŝƵŵ;ĞͿ ŵŐͬŬŐ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƐŵƵƚŚ;ŝͿ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĂĚŵŝƵŵ;ĚͿ ŵŐͬŬŐ Ϭ͘ϭϭϲ Ϭ͘Ϯϭϭ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůĂůĐŝƵŵ;ĂͿ ŵŐͬŬŐ ϮϲϴϬϬ ϯϯϯϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůŚƌŽŵŝƵŵ;ƌͿ ŵŐͬŬŐ ϳ͘Ϭ ϭϲ͘Ϭ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŽďĂůƚ;ŽͿ ŵŐͬŬŐ ϯ͘ϬϮ ϱ͘ϵϬ Ϭ͘ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽƉƉĞƌ;ƵͿ ŵŐͬŬŐ ϲ͘ϱϱ ϮϮ͘ϰ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů/ƌŽŶ;&ĞͿ ŵŐͬŬŐ ϵϳϱϬ ϭϲϵϬϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů>ĞĂĚ;WďͿ ŵŐͬŬŐ ϴ͘ϴϰ ϰϴ͘ϴ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂů>ŝƚŚŝƵŵ;>ŝͿ ŵŐͬŬŐ фϱ͘Ϭ ϳ͘ϰ ϱ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůDĂŐŶĞƐŝƵŵ;DŐͿ ŵŐͬŬŐ ϮϳϳϬ ϰϮϰϬ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŶŐĂŶĞƐĞ;DŶͿ ŵŐͬŬŐ ϭϰϴ Ϯϵϰ Ϭ͘ϮϬ ϳϵϭϲϰϱϯ dŽƚĂůDĞƌĐƵƌLJ;,ŐͿ ŵŐͬŬŐ фϬ͘ϬϱϬ Ϭ͘Ϭϴϯ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůDŽůLJďĚĞŶƵŵ;DŽͿ ŵŐͬŬŐ Ϭ͘ϱϰ Ϭ͘ϲϱ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůEŝĐŬĞů;EŝͿ ŵŐͬŬŐ ϱ͘Ϭϴ ϭϭ͘ϱ Ϭ͘ϴϬ ϳϵϭϲϰϱϯ dŽƚĂůWŚŽƐƉŚŽƌƵƐ;WͿ ŵŐͬŬŐ Ϯϳϲ ϰϯϵ ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůWŽƚĂƐƐŝƵŵ;<Ϳ ŵŐͬŬŐ ϰϴϰ ϱϯϲ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ĞůĞŶŝƵŵ;^ĞͿ ŵŐͬŬŐ фϬ͘ϱϬ фϬ͘ϱϬ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŝůǀĞƌ;ŐͿ ŵŐͬŬŐ фϬ͘ϬϱϬ Ϭ͘Ϭϳϰ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŽĚŝƵŵ;EĂͿ ŵŐͬŬŐ ϰϵϲ ϭϮϱ ϭϬϬ ϳϵϭϲϰϱϯ dŽƚĂů^ƚƌŽŶƚŝƵŵ;^ƌͿ ŵŐͬŬŐ ϭϱϲ Ϯϴ͘Ϭ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŚĂůůŝƵŵ;důͿ ŵŐͬŬŐ Ϭ͘Ϭϳϴ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝŶ;^ŶͿ ŵŐͬŬŐ Ϭ͘ϯϲ ϯ͘ϳϭ Ϭ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝƚĂŶŝƵŵ;dŝͿ ŵŐͬŬŐ Ϯϴϯ ϱϴϯ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůhƌĂŶŝƵŵ;hͿ ŵŐͬŬŐ Ϭ͘ϯϲϵ Ϭ͘ϱϭϯ Ϭ͘ϬϱϬ ϳϵϭϲϰϱϯ dŽƚĂůsĂŶĂĚŝƵŵ;sͿ ŵŐͬŬŐ ϮϮ͘ϳ ϰϭ͘ϯ Ϯ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝŶĐ;ŶͿ ŵŐͬŬŐ Ϯϱ͘ϭ ϳϴ͘ϰ ϭ͘Ϭ ϳϵϭϲϰϱϯ dŽƚĂůŝƌĐŽŶŝƵŵ;ƌͿ ŵŐͬŬŐ Ϭ͘ϵϵ Ϭ͘ϱϳ Ϭ͘ϱϬ ϳϵϭϲϰϱϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ EͬсEŽƚƉƉůŝĐĂďůĞ

WĂŐĞϭϭŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ d>WDd>^;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϱϲ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϱͲϬϭ hŶŝƚƐ ,ϭϱͲϴͲϮ Z> YĂƚĐŚ DĞƚĂůƐ >,d>ĞĂĚ;WďͿ ŵŐͬ> Ϭ͘ϯϯ Ϭ͘ϭϬ ϳϵϮϳϳϯϱ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϭϮŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ ^K>h>^K/hDE,>KZ//E^K/>;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϯϳ D,ϴϬϲϬ D,ϴϬϲϵ D,ϴϬϵϭ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϰͲϬϭ ϰϲϲϯϮϱͲϬϲͲϬϭ ϰϲϲϯϮϱͲϬϳͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ DtϭϱͲϯͲϰ Z> ,ϭϱͲϴͲϲ Z> DtϭϱͲϮͲϲ Z> DtϭϱͲϭͲϰ Z> YĂƚĐŚ E/KE^ ^ŽůƵďůĞŚůŽƌŝĚĞ;ůͿ ŵŐͬ> ϭϬϱ ϱ͘Ϭ ϳϴ͘ϱ ϱ͘Ϭ ϴϱ͘ϭ ϱ͘Ϭ Ϯϵ͘ϭ ϱ͘Ϭ ϳϵϮϬϰϱϯ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ ^ŽůƵďůĞŚůŽƌŝĚĞ;ůͿ ŵŐͬŬŐ ϴϮ͘ϯ ϯ͘ϵ ϰϭ͘Ϭ Ϯ͘ϲ ϱϮ͘ϰ ϯ͘ϭ ϭϰ͘ϴ Ϯ͘ϱ ϳϵϭϰϴϭϲ ^ŽůƵďůĞ^ŽĚŝƵŵ;EĂͿ ŵŐͬŬŐ Ϯϭ͘ϲ ϯ͘ϵ ϴ͘ϴ Ϯ͘ϲ ϮϮ͘ϱ ϯ͘ϭ ϵ͘Ϯ Ϯ͘ϱ ϳϵϭϰϴϮϭ ^ŽůƵďůĞWĂƌĂŵĞƚĞƌƐ ^ĂƚƵƌĂƚŝŽŶй й ϳϴ͘ϭ ϭ͘Ϭ ϱϮ͘Ϯ ϭ͘Ϭ ϲϭ͘ϳ ϭ͘Ϭ ϱϬ͘ϵ ϭ͘Ϭ ϳϵϭϴϯϭϬ tĞƚ^ŽůƵďůĞ^ŽĚŝƵŵ;EĂͿ ŵŐͬ> Ϯϳ͘ϲ ϱ͘Ϭ ϭϲ͘ϵ ϱ͘Ϭ ϯϲ͘ϱ ϱ͘Ϭ ϭϴ͘ϭ ϱ͘Ϭ ϳϵϭϴϳϲϰ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϭϯŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ DΘ^ZsKͬ&ϭͬsW,/E^K/>Ͳ&/>WZ^;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϮϲ D,ϴϬϮϳ D,ϴϬϵϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϲ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ ,ϭϱͲϵͲϯ ,ϭϱͲϵͲϰ ,ϭϱͲϭϭͲϮ Z> YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ &ϭ;ϲͲϭϬͿͲdy ŵŐͬŬŐ фϭϬ фϭϬ фϭϬ ϭϬ ϳϵϭϰϴϭϵ sŽůĂƚŝůĞƐ sW,;s,ϲƚŽϭϬͲdyͿ ŵŐͬŬŐ фϭϬ фϭϬ фϭϬ ϭϬ ϳϵϭϰϯϱϲ ŚůŽƌŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϭϲϰ sŝŶLJůĐŚůŽƌŝĚĞ ŵŐͬŬŐ фϬ͘ϬϲϬ фϬ͘ϬϲϬ фϬ͘ϬϲϬ Ϭ͘ϬϲϬ ϳϵϭϲϭϲϰ ƌŽŵŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϯϬ фϬ͘ϯϬ фϬ͘ϯϬ Ϭ͘ϯϬ ϳϵϭϲϭϲϰ ŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϭϲϰ dƌŝĐŚůŽƌŽĨůƵŽƌŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϲϭϲϰ ϭ͕ϭͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ŝĐŚůŽƌŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϭϲϰ ƚƌĂŶƐͲϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϭͲĚŝĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ĐŝƐͲϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ŚůŽƌŽĨŽƌŵ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϭͲƚƌŝĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ĂƌďŽŶƚĞƚƌĂĐŚůŽƌŝĚĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϬϱϬ фϬ͘ϬϬϱϬ фϬ͘ϬϬϱϬ Ϭ͘ϬϬϱϬ ϳϵϭϲϭϲϰ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ŵŐͬŬŐ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽƉƌŽƉĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ dƌŝĐŚůŽƌŽĞƚŚĞŶĞ ŵŐͬŬŐ фϬ͘ϬϬϵϬ фϬ͘ϬϬϵϬ фϬ͘ϬϬϵϬ Ϭ͘ϬϬϵϬ ϳϵϭϲϭϲϰ ƌŽŵŽĚŝĐŚůŽƌŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ĐŝƐͲϭ͕ϯͲĚŝĐŚůŽƌŽƉƌŽƉĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ƚƌĂŶƐͲϭ͕ϯͲĚŝĐŚůŽƌŽƉƌŽƉĞŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϮͲƚƌŝĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ dŽůƵĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϬ фϬ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϲϭϲϰ ŚůŽƌŽĚŝďƌŽŵŽŵĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝďƌŽŵŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ dĞƚƌĂĐŚůŽƌŽĞƚŚĞŶĞ ŵŐͬŬŐ Ϭ͘Ϭϯϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϭ͕ϮͲƚĞƚƌĂĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ƚŚLJůďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϭϬ фϬ͘ϬϭϬ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϭϲϭϲϰ ŵΘƉͲyLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϰϬ фϬ͘ϬϰϬ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϲϰ ƌŽŵŽĨŽƌŵ ŵŐͬŬŐ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϲϭϲϰ ^ƚLJƌĞŶĞ ŵŐͬŬŐ фϬ͘ϬϯϬ фϬ͘ϬϯϬ фϬ͘ϬϯϬ Ϭ͘ϬϯϬ ϳϵϭϲϭϲϰ ŽͲyLJůĞŶĞ ŵŐͬŬŐ фϬ͘ϬϰϬ фϬ͘ϬϰϬ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϲϰ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϭϰŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗ DΘ^ZsKͬ&ϭͬsW,/E^K/>Ͳ&/>WZ^;^K/>Ϳ

DĂdždžĂŵ/ D,ϴϬϮϲ D,ϴϬϮϳ D,ϴϬϵϰ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϱ ϮϬϭϱͬϬϱͬϮϲ KEƵŵďĞƌ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϯͲϬϭ ϰϲϲϯϮϱͲϬϴͲϬϭ hŶŝƚƐ ,ϭϱͲϵͲϯ ,ϭϱͲϵͲϰ ,ϭϱͲϭϭͲϮ Z> YĂƚĐŚ yLJůĞŶĞƐ;dŽƚĂůͿ ŵŐͬŬŐ фϬ͘ϬϰϬ фϬ͘ϬϰϬ фϬ͘ϬϰϬ Ϭ͘ϬϰϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕Ϯ͕ϮͲƚĞƚƌĂĐŚůŽƌŽĞƚŚĂŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϯͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕ϰͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ϭ͕Ϯ͕ϯͲƚƌŝĐŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ ,ĞdžĂĐŚůŽƌŽďƵƚĂĚŝĞŶĞ ŵŐͬŬŐ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϲϭϲϰ ϭ͕Ϯ͕ϰͲƚƌŝĐŚůŽƌŽďĞŶnjĞŶĞ ŵŐͬŬŐ фϬ͘ϬϮϱ фϬ͘ϬϮϱ фϬ͘ϬϮϱ Ϭ͘ϬϮϱ ϳϵϭϲϭϲϰ s,ϲͲϭϬ ŵŐͬŬŐ фϭϬ фϭϬ фϭϬ ϭϬ ϳϵϭϲϭϲϰ ;ϲͲϭϬͿ ŵŐͬŬŐ фϭϬ ϭϬ ϳϵϭϲϭϲϰ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϭϬϭ ϭϬϬ ϵϳ ϳϵϭϲϭϲϰ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϵϲ ϵϰ ϵϮ ϳϵϭϲϭϲϰ ϭϬͲd,z>EE;ƐƵƌ͘Ϳ й ϵϵ ϴϲ ϵϴ ϳϵϭϲϭϲϰ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ й ϵϰ ϭϬϬ ϵϳ ϳϵϭϲϭϲϰ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϭϱŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

'EZ>KDDEd^

ZĞƐƵůƚƐƌĞůĂƚĞŽŶůLJƚŽƚŚĞŝƚĞŵƐƚĞƐƚĞĚ͘

WĂŐĞϭϲŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ Yh>/dz^^hZEZWKZd ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW Y^ƚĂŶĚĂƌĚ YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ ϳϵϭϲϭϬϭ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϭϬϬ ϲϬͲϭϰϬ ϭϬϭ ϲϬͲϭϰϬ ϭϬϲ й ϳϵϭϲϭϬϭ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϵϴ ϲϬͲϭϰϬ ϵϴ ϲϬͲϭϰϬ ϵϴ й ϳϵϭϲϭϬϭ ϭϬͲd,z>EE;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϴϲ ϲϬͲϭϯϬ ϴϯ ϲϬͲϭϯϬ ϴϰ й ϳϵϭϲϭϬϭ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϵϲ ϲϬͲϭϰϬ ϵϮ ϲϬͲϭϰϬ ϭϬϬ й ϳϵϭϲϭϲϰ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϭϬϬ ϳϬͲϭϯϬ ϭϬϬ ϳϬͲϭϯϬ ϭϬϬ й ϳϵϭϲϭϲϰ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϭϬϯ ϳϬͲϭϯϬ ϭϬϮ ϳϬͲϭϯϬ ϵϲ й ϳϵϭϲϭϲϰ ϭϬͲd,z>EE;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϴϴ ϱϬͲϭϯϬ ϴϭ ϱϬͲϭϯϬ ϴϯ й ϳϵϭϲϭϲϰ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϱͬϮϴ ϭϬϬ ϳϬͲϭϯϬ ϵϵ ϳϬͲϭϯϬ ϭϬϮ й ϳϵϭϵϯϯϲ KͲdZW,Ez>;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϵϬ ϱϬͲϭϯϬ ϵϮ ϱϬͲϭϯϬ ϵϰ й ϳϵϭϵϯϱϭ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϴϴ ϲϬͲϭϯϬ ϭϬϱ ϲϬͲϭϯϬ ϭϭϮ й ϳϵϭϵϯϱϭ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϴϵ ϱϬͲϭϯϬ ϵϲ ϱϬͲϭϯϬ ϵϳ й ϳϵϭϵϯϱϭ ϴͲEW,d,>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϴϲ ϱϬͲϭϯϬ ϭϬϭ ϱϬͲϭϯϬ ϵϲ й ϳϵϭϵϯϱϭ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϵϰ ϲϬͲϭϯϬ ϭϬϱ ϲϬͲϭϯϬ ϭϬϳ й ϳϵϭϰϰϴϱ DŽŝƐƚƵƌĞ ϮϬϭϱͬϬϱͬϮϴ фϬ͘ϯϬ й ϰ͘Ϭ ϮϬ ϳϵϭϱϰϵϬ ^ŽůƵďůĞ;Ϯ͗ϭͿƉ, ϮϬϭϱͬϬϱͬϮϵ ϭϬϭ ϵϳͲϭϬϯ Ϭ Eͬ ϳϵϭϲϭϬϭ ;ϲͲϭϬͿ ϮϬϭϱͬϬϱͬϮϴ ϭϮϭ ϲϬͲϭϰϬ фϭϬ ŵŐͬŬŐ ϳϵϭϲϭϬϭ ĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϵ ϳϵ ϲϬͲϭϰϬ ϴϯ ϲϬͲϭϰϬ фϬ͘ϬϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ ƚŚLJůďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϵ ϴϮ ϲϬͲϭϰϬ ϴϱ ϲϬͲϭϰϬ фϬ͘ϬϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ ŵΘƉͲyLJůĞŶĞ ϮϬϭϱͬϬϱͬϮϵ ϴϬ ϲϬͲϭϰϬ ϭϬϳ ϲϬͲϭϰϬ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ϮϬϭϱͬϬϱͬϮϵ фϬ͘ϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ ŽͲyLJůĞŶĞ ϮϬϭϱͬϬϱͬϮϵ ϳϱ ϲϬͲϭϰϬ ϳϴ ϲϬͲϭϰϬ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ ^ƚLJƌĞŶĞ ϮϬϭϱͬϬϱͬϮϴ фϬ͘ϬϯϬ ŵŐͬŬŐ ϳϵϭϲϭϬϭ dŽůƵĞŶĞ ϮϬϭϱͬϬϱͬϮϵ ϳϳ ϲϬͲϭϰϬ ϴϬ ϲϬͲϭϰϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ s,ϲͲϭϬ ϮϬϭϱͬϬϱͬϮϵ ϭϭϮ ϲϬͲϭϰϬ фϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϬϭ yLJůĞŶĞƐ;dŽƚĂůͿ ϮϬϭϱͬϬϱͬϮϵ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ;ϲͲϭϬͿ ϮϬϭϱͬϬϱͬϮϴ ϭϬϵ ϲϬͲϭϰϬ фϭϬ ŵŐͬŬŐ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϭ͕ϮͲƚĞƚƌĂĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϭ ϲϬͲϭϰϬ ϴϵ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϭͲƚƌŝĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϰ ϲϬͲϭϰϬ ϴϯ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕Ϯ͕ϮͲƚĞƚƌĂĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϭϬϲ ϲϬͲϭϰϬ ϵϵ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϭ͕ϮͲƚƌŝĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϳ ϲϬͲϭϰϬ ϵϯ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ

WĂŐĞϭϳŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW Y^ƚĂŶĚĂƌĚ YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ ϳϵϭϲϭϲϰ ϭ͕ϭͲĚŝĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϭ ϲϬͲϭϰϬ ϴϬ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϭͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϲ ϲϬͲϭϰϬ ϭϬϭ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕Ϯ͕ϯͲƚƌŝĐŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϭϬϲ ϲϬͲϭϰϬ ϵϵ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕Ϯ͕ϰͲƚƌŝĐŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϭϬϯ ϲϬͲϭϰϬ ϵϲ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝďƌŽŵŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϴ ϲϬͲϭϰϬ ϵϱ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϳ ϲϬͲϭϰϬ ϵϬ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϲ ϲϬͲϭϰϬ ϵϱ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϮͲĚŝĐŚůŽƌŽƉƌŽƉĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϱ ϲϬͲϭϰϬ ϵϯ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϯͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϮ ϲϬͲϭϰϬ ϴϵ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ϭ͕ϰͲĚŝĐŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϮ ϲϬͲϭϰϬ ϴϳ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϴ ϲϬͲϭϰϬ ϴϳ ϲϬͲϭϰϬ фϬ͘ϬϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƌŽŵŽĚŝĐŚůŽƌŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϮ ϲϬͲϭϰϬ ϵϬ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƌŽŵŽĨŽƌŵ ϮϬϭϱͬϬϱͬϮϴ ϵϳ ϲϬͲϭϰϬ ϵϱ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƌŽŵŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϳϳ ϰϬͲϭϱϬ ϲϭ ϰϬͲϭϱϬ фϬ͘ϯϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ĂƌďŽŶƚĞƚƌĂĐŚůŽƌŝĚĞ ϮϬϭϱͬϬϱͬϮϴ ϴϰ ϲϬͲϭϰϬ ϴϯ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŚůŽƌŽďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϰ ϲϬͲϭϰϬ ϴϯ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŚůŽƌŽĚŝďƌŽŵŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϲ ϲϬͲϭϰϬ ϵϯ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŚůŽƌŽĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϲϱ ϰϬͲϭϱϬ ϱϲ ϰϬͲϭϱϬ фϬ͘ϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŚůŽƌŽĨŽƌŵ ϮϬϭϱͬϬϱͬϮϴ ϴϱ ϲϬͲϭϰϬ ϴϰ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŚůŽƌŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϲϰ ϰϬͲϭϱϬ ϱϯ ϰϬͲϭϱϬ фϬ͘ϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ĐŝƐͲϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϮ ϲϬͲϭϰϬ ϵϬ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ĐŝƐͲϭ͕ϯͲĚŝĐŚůŽƌŽƉƌŽƉĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϭϬϱ ϲϬͲϭϰϬ ϭϬϮ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŝĐŚůŽƌŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϵ ϲϬͲϭϰϬ ϵϵ ϲϬͲϭϰϬ фϬ͘ϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƚŚLJůďĞŶnjĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϰ ϲϬͲϭϰϬ ϵϮ ϲϬͲϭϰϬ фϬ͘ϬϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ,ĞdžĂĐŚůŽƌŽďƵƚĂĚŝĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϳ ϲϬͲϭϰϬ ϵϭ ϰϬͲϭϱϬ фϬ͘ϮϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŵΘƉͲyLJůĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϱ ϲϬͲϭϰϬ ϵϬ ϲϬͲϭϰϬ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ϮϬϭϱͬϬϱͬϮϴ фϬ͘ϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ŽͲyLJůĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϬ ϲϬͲϭϰϬ ϴϵ ϲϬͲϭϰϬ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ^ƚLJƌĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϴ ϲϬͲϭϰϬ ϵϳ ϲϬͲϭϰϬ фϬ͘ϬϯϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ dĞƚƌĂĐŚůŽƌŽĞƚŚĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϯ ϲϬͲϭϰϬ ϴϭ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ

WĂŐĞϭϴŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW Y^ƚĂŶĚĂƌĚ YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ ϳϵϭϲϭϲϰ dŽůƵĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϴ ϲϬͲϭϰϬ ϴϳ ϲϬͲϭϰϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƚƌĂŶƐͲϭ͕ϮͲĚŝĐŚůŽƌŽĞƚŚĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϴϲ ϲϬͲϭϰϬ ϴϱ ϲϬͲϭϰϬ фϬ͘ϬϮϱ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ ƚƌĂŶƐͲϭ͕ϯͲĚŝĐŚůŽƌŽƉƌŽƉĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϭϭϲ ϲϬͲϭϰϬ ϭϬϳ ϲϬͲϭϰϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ dƌŝĐŚůŽƌŽĞƚŚĞŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϬ ϲϬͲϭϰϬ ϴϴ ϲϬͲϭϰϬ фϬ͘ϬϬϵϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ dƌŝĐŚůŽƌŽĨůƵŽƌŽŵĞƚŚĂŶĞ ϮϬϭϱͬϬϱͬϮϴ ϵϬ ϰϬͲϭϱϬ ϴϭ ϰϬͲϭϱϬ фϬ͘ϮϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ s,ϲͲϭϬ ϮϬϭϱͬϬϱͬϮϴ ϭϬϯ ϲϬͲϭϰϬ фϭϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ sŝŶLJůĐŚůŽƌŝĚĞ ϮϬϭϱͬϬϱͬϮϴ ϳϰ ϰϬͲϭϱϬ ϲϮ ϰϬͲϭϱϬ фϬ͘ϬϲϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϭϲϰ yLJůĞŶĞƐ;dŽƚĂůͿ ϮϬϭϱͬϬϱͬϮϴ фϬ͘ϬϰϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϲϰϱϯ dŽƚĂůůƵŵŝŶƵŵ;ůͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ ϯ͘ϱ ϯϱ ϭϬϰ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŶƚŝŵŽŶLJ;^ďͿ ϮϬϭϱͬϬϱͬϮϵ ϴϳ ϳϱͲϭϮϱ ϵϱ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬŬŐ ϯϮ;ϭͿ ϯϬ ϵϲ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůƌƐĞŶŝĐ;ƐͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϭ ϳϱͲϭϮϱ ϭϬϬ ϳϱͲϭϮϱ фϬ͘ϱϬ ŵŐͬŬŐ Ϯ͘ϯ ϯϬ ϵϳ ϳϬͲϭϯϬ Ϭ͘ϭϬ͕ ϳϵϭϲϰϱϯ dŽƚĂůĂƌŝƵŵ;ĂͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ ŵŐͬŬŐ ϭ͘Ϭ ϯϱ ϭϬϭ ϳϬͲϭϯϬ Z>сϬ͘ϭϬ ϳϵϭϲϰϱϯ dŽƚĂůĞƌLJůůŝƵŵ;ĞͿ ϮϬϭϱͬϬϱͬϮϵ ϭϭϯ ϳϱͲϭϮϱ ϭϭϬ ϳϱͲϭϮϱ фϬ͘ϰϬ ŵŐͬŬŐ E ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƐŵƵƚŚ;ŝͿ ϮϬϭϱͬϬϱͬϮϵ фϬ͘ϭϬ ŵŐͬŬŐ E ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůĂĚŵŝƵŵ;ĚͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϴ ϳϱͲϭϮϱ ϭϬϲ ϳϱͲϭϮϱ фϬ͘ϬϱϬ ŵŐͬŬŐ ϭϬ ϯϬ ϭϬϵ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůĂůĐŝƵŵ;ĂͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ Ϭ͘ϰϬ ϯϬ ϵϴ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŚƌŽŵŝƵŵ;ƌͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϱ ϳϱͲϭϮϱ ϭϬϴ ϳϱͲϭϮϱ фϭ͘Ϭ ŵŐͬŬŐ ϭ͘ϰ ϯϬ ϭϬϲ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽďĂůƚ;ŽͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϵ ϳϱͲϭϮϱ ϭϭϭ ϳϱͲϭϮϱ фϬ͘ϯϬ ŵŐͬŬŐ ϭ͘ϵ ϯϬ ϵϰ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŽƉƉĞƌ;ƵͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ фϬ͘ϱϬ ŵŐͬŬŐ ϭ͘ϳ ϯϬ ϵϵ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂů/ƌŽŶ;&ĞͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ Ϭ͘ϲϰ ϯϬ ϵϵ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂů>ĞĂĚ;WďͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬŬŐ Ϯ͘ϱ ϯϱ ϭϬϭ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂů>ŝƚŚŝƵŵ;>ŝͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϴ ϳϱͲϭϮϱ ϭϬϵ ϳϱͲϭϮϱ фϱ͘Ϭ ŵŐͬŬŐ E ϯϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŐŶĞƐŝƵŵ;DŐͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ Ϯ͘ϭ ϯϬ ϵϴ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůDĂŶŐĂŶĞƐĞ;DŶͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϭϮ ϳϱͲϭϮϱ фϬ͘ϮϬ ŵŐͬŬŐ ϯ͘Ϭ ϯϬ ϵϴ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůDĞƌĐƵƌLJ;,ŐͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϮ ϳϱͲϭϮϱ ϭϬϭ ϳϱͲϭϮϱ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϯϱ ϴϴ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůDŽůLJďĚĞŶƵŵ;DŽͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϱ ϳϱͲϭϮϱ ϵϵ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬŬŐ ϳ͘ϯ ϯϱ ϭϬϬ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůEŝĐŬĞů;EŝͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϳ ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ фϬ͘ϴϬ ŵŐͬŬŐ ϭ͘Ϯ ϯϬ ϭϬϯ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůWŚŽƐƉŚŽƌƵƐ;WͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬ ŵŐͬŬŐ ϱ͘Ϯ ϯϬ ϵϯ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůWŽƚĂƐƐŝƵŵ;<Ϳ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ Ϯ͘Ϭ ϯϱ

WĂŐĞϭϵŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW Y^ƚĂŶĚĂƌĚ YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ ϳϵϭϲϰϱϯ dŽƚĂů^ĞůĞŶŝƵŵ;^ĞͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϭ ϳϱͲϭϮϱ ϭϬϬ ϳϱͲϭϮϱ фϬ͘ϱϬ ŵŐͬŬŐ E ϯϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŝůǀĞƌ;ŐͿ ϮϬϭϱͬϬϱͬϮϵ ϵϲ ϳϱͲϭϮϱ ϵϰ ϳϱͲϭϮϱ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϯϱ ϵϴ ϲϬͲϭϰϬ ϳϵϭϲϰϱϯ dŽƚĂů^ŽĚŝƵŵ;EĂͿ ϮϬϭϱͬϬϱͬϮϵ фϭϬϬ ŵŐͬŬŐ E ϯϱ ϳϵϭϲϰϱϯ dŽƚĂů^ƚƌŽŶƚŝƵŵ;^ƌͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϯ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬŬŐ Ϯ͘Ϭ ϯϱ ϭϬϮ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůdŚĂůůŝƵŵ;důͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϮ ϳϱͲϭϮϱ ϵϵ ϳϱͲϭϮϱ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϯϬ ϴϱ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůdŝŶ;^ŶͿ ϮϬϭϱͬϬϱͬϮϵ ϵϬ ϳϱͲϭϮϱ ϵϭ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬŬŐ Ϯϴ ϯϱ ϳϵϭϲϰϱϯ dŽƚĂůdŝƚĂŶŝƵŵ;dŝͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϭ ϳϱͲϭϮϱ фϭ͘Ϭ ŵŐͬŬŐ Ϭ͘Ϭϵϱ ϯϱ ϭϬϳ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůhƌĂŶŝƵŵ;hͿ ϮϬϭϱͬϬϱͬϮϵ ϭϬϵ ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ фϬ͘ϬϱϬ ŵŐͬŬŐ ϭ͘ϱ ϯϬ ϭϭϬ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůsĂŶĂĚŝƵŵ;sͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϱ ϳϱͲϭϮϱ фϮ͘Ϭ ŵŐͬŬŐ Ϭ͘ϮϮ ϯϬ ϭϬϰ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŝŶĐ;ŶͿ ϮϬϭϱͬϬϱͬϮϵ E ϳϱͲϭϮϱ ϭϬϯ ϳϱͲϭϮϱ фϭ͘Ϭ ŵŐͬŬŐ ϭ͘ϳ ϯϬ ϴϵ ϳϬͲϭϯϬ ϳϵϭϲϰϱϯ dŽƚĂůŝƌĐŽŶŝƵŵ;ƌͿ ϮϬϭϱͬϬϱͬϮϵ фϬ͘ϱϬ ŵŐͬŬŐ E ϯϬ ϳϵϭϴϯϭϬ ^ĂƚƵƌĂƚŝŽŶй ϮϬϭϱͬϬϱͬϯϭ фϭ͘Ϭ й ϭ͘ϱ ϯϬ ϭϬϯ Eͬ ϳϵϭϴϳϲϰ tĞƚ^ŽůƵďůĞ^ŽĚŝƵŵ;EĂͿ ϮϬϭϱͬϬϲͬϬϭ фϱ͘Ϭ ŵŐͬ> E ϯϬ ϵϭ ϳϱͲϭϮϱ ϳϵϭϵϯϯϲ W,;ϭϬͲϭϵͿ ϮϬϭϱͬϬϲͬϬϭ ϭϭϬ ϱϬͲϭϯϬ ϭϬϱ ϱϬͲϭϯϬ фϭϬϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϵϯϯϲ W,;ϭϵͲϯϮͿ ϮϬϭϱͬϬϲͬϬϭ ϭϭϮ ϱϬͲϭϯϬ ϭϬϲ ϱϬͲϭϯϬ фϭϬϬ ŵŐͬŬŐ E ϰϬ ϳϵϭϵϯϱϭ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϭ ϱϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϬ ϱϬͲϭϯϬ ϵϰ ϱϬͲϭϯϬ фϬ͘ϬϬϱϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĐĞŶĂƉŚƚŚLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϰ ϱϬͲϭϯϬ ϵϮ ϱϬͲϭϯϬ фϬ͘ϬϬϱϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϱ ϲϬͲϭϯϬ ϭϬϬ ϲϬͲϭϯϬ фϬ͘ϬϬϰϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϴ ϲϬͲϭϯϬ ϴϳ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϳ ϲϬͲϭϯϬ ϵϬ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϵ ϲϬͲϭϯϬ ϴϴ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϰ ϲϬͲϭϯϬ ϴϬ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϰ ϲϬͲϭϯϬ ϵϯ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ŚƌLJƐĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϵ ϲϬͲϭϯϬ ϵϯ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϰ ϲϬͲϭϯϬ ϴϮ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ &ůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϵ ϲϬͲϭϯϬ ϭϬϬ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ &ůƵŽƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϮ ϱϬͲϭϯϬ ϵϭ ϱϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϲ ϲϬͲϭϯϬ ϴϯ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ EĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϬϰ ϱϬͲϭϯϬ ϴϴ ϱϬͲϭϯϬ фϬ͘ϬϭϬ ŵŐͬŬŐ E ϱϬ

WĂŐĞϮϬŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW Y^ƚĂŶĚĂƌĚ YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ ϳϵϭϵϯϱϭ WŚĞŶĂŶƚŚƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϮ ϲϬͲϭϯϬ ϴϵ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϭϵϯϱϭ WLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϴϳ ϲϬͲϭϯϬ ϭϬϭ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ŵŐͬŬŐ E ϱϬ ϳϵϮϬϰϱϯ ^ŽůƵďůĞŚůŽƌŝĚĞ;ůͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϳ ϳϱͲϭϮϱ ϭϬϱ ϴϬͲϭϮϬ фϱ͘Ϭ ŵŐͬ> ϳ͘ϴ ϯϬ ϵϭ ϳϱͲϭϮϱ ϳϵϮϲϴϲϵ &ŝŶĂůƉ,ŽĨ>ĞĂĐŚĂƚĞ ϮϬϭϱͬϬϲͬϬϵ ϰ͘ϵϯ Ɖ, ϭ͘Ϯ Eͬ ϳϵϮϲϴϲϵ /ŶŝƚŝĂůƉ,ŽĨ^ĂŵƉůĞ ϮϬϭϱͬϬϲͬϬϵ ϰ͘ϵϯ Ɖ, Ϭ͘Ϯϱ Eͬ ϳϵϮϲϴϲϵ Ɖ,ĂĨƚĞƌ,ů ϮϬϭϱͬϬϲͬϬϵ ϱ͘ϱ Eͬ ϳϵϮϲϴϲϵ Ɖ,ŽĨ>ĞĂĐŚŝŶŐ&ůƵŝĚ ϮϬϭϱͬϬϲͬϬϵ ϰ͘ϵϯ Ɖ, Ϭ Eͬ ϳϵϮϳϳϯϱ >,d>ĞĂĚ;WďͿ ϮϬϭϱͬϬϲͬϬϵ ϵϱ ϳϱͲϭϮϱ ϵϳ ϳϱͲϭϮϱ фϬ͘ϭϬ ŵŐͬ> E ϯϱ EͬсEŽƚƉƉůŝĐĂďůĞ ƵƉůŝĐĂƚĞ͗WĂŝƌĞĚĂŶĂůLJƐŝƐŽĨĂƐĞƉĂƌĂƚĞƉŽƌƚŝŽŶŽĨƚŚĞƐĂŵĞƐĂŵƉůĞ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƚŚĞǀĂƌŝĂŶĐĞŝŶƚŚĞŵĞĂƐƵƌĞŵĞŶƚ͘ DĂƚƌŝdž^ƉŝŬĞ͗ƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞŽĨŝŶƚĞƌĞƐƚŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƐĂŵƉůĞŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ Y^ƚĂŶĚĂƌĚ͗ƐĂŵƉůĞŽĨŬŶŽǁŶĐŽŶĐĞŶƚƌĂƚŝŽŶƉƌĞƉĂƌĞĚďLJĂŶĞdžƚĞƌŶĂůĂŐĞŶĐLJƵŶĚĞƌƐƚƌŝŶŐĞŶƚĐŽŶĚŝƚŝŽŶƐ͘hƐĞĚĂƐĂŶŝŶĚĞƉĞŶĚĞŶƚĐŚĞĐŬŽĨŵĞƚŚŽĚĂĐĐƵƌĂĐLJ͘ ^ƉŝŬĞĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞ͕ƵƐƵĂůůLJĨƌŽŵĂƐĞĐŽŶĚƐŽƵƌĐĞ͕ŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞŵĞƚŚŽĚĂĐĐƵƌĂĐLJ͘ DĞƚŚŽĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžĐŽŶƚĂŝŶŝŶŐĂůůƌĞĂŐĞŶƚƐƵƐĞĚŝŶƚŚĞĂŶĂůLJƚŝĐĂůƉƌŽĐĞĚƵƌĞ͘hƐĞĚƚŽŝĚĞŶƚŝĨLJůĂďŽƌĂƚŽƌLJĐŽŶƚĂŵŝŶĂƚŝŽŶ͘ ^ƵƌƌŽŐĂƚĞ͗ƉƵƌĞŽƌŝƐŽƚŽƉŝĐĂůůLJůĂďĞůĞĚĐŽŵƉŽƵŶĚǁŚŽƐĞďĞŚĂǀŝŽƌŵŝƌƌŽƌƐƚŚĞĂŶĂůLJƚĞƐŽĨŝŶƚĞƌĞƐƚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞĞdžƚƌĂĐƚŝŽŶĞĨĨŝĐŝĞŶĐLJ͘ E;DĂƚƌŝdž^ƉŝŬĞͿ͗dŚĞƌĞĐŽǀĞƌLJŝŶƚŚĞŵĂƚƌŝdžƐƉŝŬĞǁĂƐŶŽƚĐĂůĐƵůĂƚĞĚ͘dŚĞƌĞůĂƚŝǀĞĚŝĨĨĞƌĞŶĐĞďĞƚǁĞĞŶƚŚĞĐŽŶĐĞŶƚƌĂƚŝŽŶŝŶƚŚĞƉĂƌĞŶƚƐĂŵƉůĞĂŶĚƚŚĞƐƉŝŬĞĚĂŵŽƵŶƚǁĂƐƚŽŽƐŵĂůůƚŽƉĞƌŵŝƚĂƌĞůŝĂďůĞ ƌĞĐŽǀĞƌLJĐĂůĐƵůĂƚŝŽŶ;ŵĂƚƌŝdžƐƉŝŬĞĐŽŶĐĞŶƚƌĂƚŝŽŶǁĂƐůĞƐƐƚŚĂŶϮdžƚŚĂƚŽĨƚŚĞŶĂƚŝǀĞƐĂŵƉůĞĐŽŶĐĞŶƚƌĂƚŝŽŶͿ͘ E;ƵƉůŝĐĂƚĞZWͿ͗dŚĞĚƵƉůŝĐĂƚĞZWǁĂƐŶŽƚĐĂůĐƵůĂƚĞĚ͘dŚĞĐŽŶĐĞŶƚƌĂƚŝŽŶŝŶƚŚĞƐĂŵƉůĞĂŶĚͬŽƌĚƵƉůŝĐĂƚĞǁĂƐƚŽŽůŽǁƚŽƉĞƌŵŝƚĂƌĞůŝĂďůĞZWĐĂůĐƵůĂƚŝŽŶ;ŽŶĞŽƌďŽƚŚƐĂŵƉůĞƐфϱdžZ>Ϳ͘ ;ϭͿZĞĐŽǀĞƌLJŽƌZWĨŽƌƚŚŝƐƉĂƌĂŵĞƚĞƌŝƐŽƵƚƐŝĚĞĐŽŶƚƌŽůůŝŵŝƚƐ͘dŚĞŽǀĞƌĂůůƋƵĂůŝƚLJĐŽŶƚƌŽůĨŽƌƚŚŝƐĂŶĂůLJƐŝƐŵĞĞƚƐĂĐĐĞƉƚĂďŝůŝƚLJĐƌŝƚĞƌŝĂ͘

WĂŐĞϮϭŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗

s>/d/KE^/'EdhZW'

dŚĞĂŶĂůLJƚŝĐĂůĚĂƚĂĂŶĚĂůůYĐŽŶƚĂŝŶĞĚŝŶƚŚŝƐƌĞƉŽƌƚǁĞƌĞƌĞǀŝĞǁĞĚĂŶĚǀĂůŝĚĂƚĞĚďLJƚŚĞĨŽůůŽǁŝŶŐŝŶĚŝǀŝĚƵĂů;ƐͿ͘

ŶĚLJ>Ƶ͕ĂƚĂsĂůŝĚĂƚŝŽŶŽŽƌĚŝŶĂƚŽƌ

DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

WĂŐĞϮϮŽĨϯϱ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ WĂŐĞϮϯŽĨϯϱ WĂŐĞϮϰŽĨϯϱ WĂŐĞϮϱŽĨϯϱ WĂŐĞϮϲŽĨϯϱ WĂŐĞϮϳŽĨϯϱ WĂŐĞϮϴŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϮϲ ůŝĞŶƚ/͗,ϭϱͲϵͲϯ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϮϵŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϮϳ ůŝĞŶƚ/͗,ϭϱͲϵͲϰ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϬŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϯϮ ůŝĞŶƚ/͗,ϭϱͲϭϬͲϮ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϭŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϴϵ ůŝĞŶƚ/͗DtϭϱͲϭͲϮ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϮŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϵϬ ůŝĞŶƚ/͗DtϭϱͲϭͲϯ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϯŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϵϰ ůŝĞŶƚ/͗,ϭϱͲϭϭͲϮ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϰŽĨϯϱ DĂdždžĂŵ:Žďη͗ϱϰϯϰϴϵ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϭϬ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘ϬϰEtZ/',dKEZ/>> DĂdždžĂŵ^ĂŵƉůĞ͗D,ϴϬϵϰ>ĂďͲƵƉ ůŝĞŶƚ/͗,ϭϱͲϭϭͲϮ W,ŝŶ^ŽŝůďLJ'ͬ&/ŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϯϱŽĨϯϱ zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ zŽƵƌWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< ƚƚĞŶƚŝŽŶ͗ŶĚƌĞǁƌŽǁŶ zŽƵƌ͘K͘͘η͗ϰϲϲϯϭϴͲϬϭͲϬϭ ,DDZEs/ZK,D/E͘ ϭϴƚŚ&ůŽŽƌ͕ϰϳϯϬ<ŝŶŐƐǁĂLJ ƵƌŶĂďLJ͕ ĂŶĂĚĂsϱ,Ϭϲ

ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ZĞƉŽƌƚη͗ZϭϵϲϵϱϬϬ sĞƌƐŝŽŶ͗ϭͲ&ŝŶĂů

Zd/&/dK&E>z^/^ DyyD:Kη͗ϱϰϱϯϲϭ ZĞĐĞŝǀĞĚ͗ϮϬϭϱͬϬϲͬϬϭ͕ϭϮ͗ϮϬ ^ĂŵƉůĞDĂƚƌŝdž͗tĂƚĞƌ η^ĂŵƉůĞƐZĞĐĞŝǀĞĚ͗ϱ ĂƚĞ ĂƚĞ ŶĂůLJƐĞƐ YƵĂŶƚŝƚLJ džƚƌĂĐƚĞĚ ŶĂůLJnjĞĚ >ĂďŽƌĂƚŽƌLJDĞƚŚŽĚ ŶĂůLJƚŝĐĂůDĞƚŚŽĚ dyͬDd>,͕s,͕&ϭ^/DͬD^ ϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϮ zϴ^KWͲϬϬϬϭϬͬϭϭ WϴϮϲϬĐZϯŵ ,ĂƌĚŶĞƐƐ;ĐĂůĐƵůĂƚĞĚĂƐĂKϯͿ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zϳ^KWͲϬϬϬϬϮ WϲϬϮϬĂZϭŵ DĞƌĐƵƌLJ;ŝƐƐŽůǀĞĚͿďLJs& ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zϳ^KWͲϬϬϬϭϱ DK>DKĐƚϮϬϭϯŵ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚ ϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ zϴ^KWͲϬϬϬϮϵ DKW,ǁϭϮͬϬϬŵ EĂ͕<͕Ă͕DŐ͕^ďLJZ/WD^;ĚŝƐƐ͘Ϳ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zϳ^KWͲϬϬϬϬϮ WϲϬϮϬZϭŵ ůĞŵĞŶƚƐďLJZ/WD^;ĚŝƐƐŽůǀĞĚͿ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zϳ^KWͲϬϬϬϬϮ WϲϬϮϬZϭŵ W,ŝŶtĂƚĞƌďLJ'ͬD^;^/DͿ ϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ zϴ^KWͲϬϬϬϮϭ WϴϮϳϬĚZϰŵ W,ŝŶtĂƚĞƌďLJ'ͬD^;^/DͿ ϰ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϮ zϴ^KWͲϬϬϬϮϭ WϴϮϳϬĚZϰŵ dŽƚĂů>Dt͕,Dt͕dŽƚĂůW,ĂůĐ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zt/ͲϬϬϬϯϯ ƵƚŽĂůĐ &ŝůƚĞƌĂŶĚ,EKϯWƌĞƐĞƌǀĞĨŽƌDĞƚĂůƐ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zϳt/ͲϬϬϬϬϰ DKZĞƋƐϬϴͬϭϰ W,ůĞƐƐW,ŝŶtĂƚĞƌďLJ'ͬ&/ ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zt/ͲϬϬϬϯϯ ƵƚŽĂůĐ sŽůĂƚŝůĞ&ϭͲdy ϱ Eͬ ϮϬϭϱͬϬϲͬϬϮ zt/ͲϬϬϬϯϯ ƵƚŽĂůĐ

ZĞĨĞƌĞŶĐĞDĞƚŚŽĚƐƵĨĨŝdž͞ŵ͟ŝŶĚŝĐĂƚĞƐƚĞƐƚŵĞƚŚŽĚƐŝŶĐŽƌƉŽƌĂƚĞǀĂůŝĚĂƚĞĚŵŽĚŝĨŝĐĂƚŝŽŶƐĨƌŽŵƐƉĞĐŝĨŝĐƌĞĨĞƌĞŶĐĞŵĞƚŚŽĚƐƚŽŝŵƉƌŽǀĞƉĞƌĨŽƌŵĂŶĐĞ͘ Ύ ZWƐ ĐĂůĐƵůĂƚĞĚ ƵƐŝŶŐ ƌĂǁ ĚĂƚĂ͘ dŚĞ ƌŽƵŶĚŝŶŐ ŽĨ ĨŝŶĂů ƌĞƐƵůƚƐ ŵĂLJ ƌĞƐƵůƚ ŝŶ ƚŚĞ ĂƉƉĂƌĞŶƚ ĚŝĨĨĞƌĞŶĐĞ͘

Maxxam ŶĐƌLJƉƚŝŽŶ<ĞLJ 02 Jun 2015 16:58:11 -07:00

WůĞĂƐĞĚŝƌĞĐƚĂůůƋƵĞƐƚŝŽŶƐƌĞŐĂƌĚŝŶŐƚŚŝƐĞƌƚŝĨŝĐĂƚĞŽĨŶĂůLJƐŝƐƚŽLJŽƵƌWƌŽũĞĐƚDĂŶĂŐĞƌ͘ ŵĂŶĚĞĞƉEĂŐƌĂ͕ĐĐŽƵŶƚ^ƉĞĐŝĂůŝƐƚ ŵĂŝů͗EĂŐƌĂΛŵĂdždžĂŵ͘ĐĂ WŚŽŶĞη;ϲϬϰͿϲϯϵͲϮϲϬϮ сссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссс dŚŝƐƌĞƉŽƌƚŚĂƐďĞĞŶŐĞŶĞƌĂƚĞĚĂŶĚĚŝƐƚƌŝďƵƚĞĚƵƐŝŶŐĂƐĞĐƵƌĞĂƵƚŽŵĂƚĞĚƉƌŽĐĞƐƐ͘ DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

dŽƚĂůŽǀĞƌWĂŐĞƐ͗ϭ WĂŐĞϭŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: Z^h>d^K&,D/>E>z^^K&tdZ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ &ŝůƚĞƌĂŶĚ,EKϯWƌĞƐĞƌǀĂƚŝŽŶ Eͬ &/> &/> &/> &/> &/> KE^/d

WĂŐĞϮŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: DΘ^Zdyͬ&ϭͬsW,/EtdZ;tdZͿ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ Z> YĂƚĐŚ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ &ϭ;ϲͲϭϬͿͲdy ƵŐͬ> фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ ϯϬϬ ϳϵϭϵϮϵϬ sŽůĂƚŝůĞƐ sW,;s,ϲƚŽϭϬͲdyͿ ƵŐͬ> фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ ϯϬϬ ϳϵϭϵϮϵϬ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ƵŐͬ> фϰ͘Ϭ фϰ͘Ϭ фϰ͘Ϭ фϰ͘Ϭ фϰ͘Ϭ ϰ͘Ϭ ϳϵϭϵϯϴϮ ĞŶnjĞŶĞ ƵŐͬ> Ϭ͘ϴϵ фϬ͘ϰϬ ϭ͘ϯ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ dŽůƵĞŶĞ ƵŐͬ> Ϭ͘ϰϳ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ ƚŚLJůďĞŶnjĞŶĞ ƵŐͬ> Ϯ͘ϱ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ ŵΘƉͲyLJůĞŶĞ ƵŐͬ> фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ ŽͲyLJůĞŶĞ ƵŐͬ> ϭ͘ϭ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ ^ƚLJƌĞŶĞ ƵŐͬ> фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ yLJůĞŶĞƐ;dŽƚĂůͿ ƵŐͬ> ϭ͘ϭ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ фϬ͘ϰϬ Ϭ͘ϰϬ ϳϵϭϵϯϴϮ s,ϲͲϭϬ ƵŐͬ> фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ ϯϬϬ ϳϵϭϵϯϴϮ ;ϲͲϭϬͿ ƵŐͬ> фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ фϯϬϬ ϯϬϬ ϳϵϭϵϯϴϮ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϵϲ ϵϳ ϵϳ ϵϳ ϵϳ ϳϵϭϵϯϴϮ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ й ϭϭϯ ϭϭϭ ϭϭϭ ϭϭϭ ϭϭϬ ϳϵϭϵϯϴϮ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ й ϭϬϱ ϭϬϴ ϭϬϲ ϭϬϳ ϭϬϵ ϳϵϭϵϯϴϮ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϯŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: >W,Θ,W,t/d,^ZͬDW,/EtdZ;tdZͿ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ Z> DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ Z> YĂƚĐŚ WŽůLJĐLJĐůŝĐƌŽŵĂƚŝĐƐ >ŽǁDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ƵŐͬ> ϵϳ ϯ͘Ϯ ϯ͘ϲ Ϯ͘ϱ фϬ͘Ϯϰ ϯ͘ϳ Ϭ͘Ϯϰ ϳϵϭϴϳϮϴ ,ŝŐŚDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ƵŐͬ> Ϭ͘ϵϳ Ϭ͘ϬϱϬ Ϭ͘ϭϯ Ϭ͘Ϯϵ фϬ͘ϬϱϬ Ϭ͘ϭϯ Ϭ͘ϬϱϬ ϳϵϭϴϳϮϴ dŽƚĂůW, ƵŐͬ> ϵϴ ϯ͘Ϯ ϯ͘ϳ Ϯ͘ϴ фϬ͘Ϯϰ ϯ͘ϴ Ϭ͘Ϯϰ ϳϵϭϴϳϮϴ EĂƉŚƚŚĂůĞŶĞ ƵŐͬ> Ϯϱ;ϭͿ Ϭ͘ϱϬ ϭ͘ϰ Ϭ͘ϭϴ фϬ͘ϭϬ ϭ͘ϲ Ϭ͘ϭϬ ϳϵϭϵϰϮϯ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ƵŐͬ> ϱϯ;ϭͿ Ϭ͘ϱϬ Ϭ͘Ϯϵ Ϭ͘ϮϮ фϬ͘ϭϬ Ϭ͘ϯϭ Ϭ͘ϭϬ ϳϵϭϵϰϮϯ YƵŝŶŽůŝŶĞ ƵŐͬ> фϯ͘Ϯ;ϮͿ ϯ͘Ϯ фϬ͘Ϯϰ фϬ͘Ϯϰ фϬ͘Ϯϰ фϬ͘Ϯϰ Ϭ͘Ϯϰ ϳϵϭϵϰϮϯ ĐĞŶĂƉŚƚŚLJůĞŶĞ ƵŐͬ> фϭ͘ϯ;ϮͿ ϭ͘ϯ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĐĞŶĂƉŚƚŚĞŶĞ ƵŐͬ> ϲ͘ϯ Ϭ͘ϬϱϬ ϭ͘ϯ Ϭ͘ϴϬ фϬ͘ϬϱϬ ϭ͘ϯ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ &ůƵŽƌĞŶĞ ƵŐͬ> ϰ͘Ϯ Ϭ͘ϬϱϬ Ϭ͘ϯϭ Ϭ͘ϴϬ фϬ͘ϬϱϬ Ϭ͘ϯϭ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ WŚĞŶĂŶƚŚƌĞŶĞ ƵŐͬ> ϴ͘ϯ Ϭ͘ϬϱϬ Ϭ͘ϭϴ Ϭ͘ϰϲ фϬ͘ϬϱϬ Ϭ͘ϭϴ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ŶƚŚƌĂĐĞŶĞ ƵŐͬ> Ϭ͘ϳϲ Ϭ͘ϬϭϬ Ϭ͘ϬϮϱ Ϭ͘Ϭϴϴ фϬ͘ϬϭϬ Ϭ͘ϬϮϰ Ϭ͘ϬϭϬ ϳϵϭϵϰϮϯ ĐƌŝĚŝŶĞ ƵŐͬ> Ϭ͘ϬϲϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ &ůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> Ϭ͘ϯϯ Ϭ͘ϬϮϬ Ϭ͘ϬϰϮ Ϭ͘ϭϭ фϬ͘ϬϮϬ Ϭ͘Ϭϰϱ Ϭ͘ϬϮϬ ϳϵϭϵϰϮϯ WLJƌĞŶĞ ƵŐͬ> Ϭ͘ϯϳ Ϭ͘ϬϮϬ Ϭ͘Ϭϯϰ Ϭ͘ϭϭ фϬ͘ϬϮϬ Ϭ͘Ϭϯϱ Ϭ͘ϬϮϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ƵŐͬ> Ϭ͘Ϭϱϴ Ϭ͘ϬϭϬ фϬ͘ϬϭϬ Ϭ͘Ϭϯϴ фϬ͘ϬϭϬ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϭϵϰϮϯ ŚƌLJƐĞŶĞ ƵŐͬ> Ϭ͘ϭϮ Ϭ͘ϬϱϬ Ϭ͘Ϭϱϯ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϮ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> Ϭ͘Ϭϱϭ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ƵŐͬ> Ϭ͘Ϭϯϵ Ϭ͘ϬϬϵϬ фϬ͘ϬϬϵϬ Ϭ͘Ϭϯϰ фϬ͘ϬϬϵϬ фϬ͘ϬϬϵϬ Ϭ͘ϬϬϵϬ ϳϵϭϵϰϮϯ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϰϮϯ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ >W,;ϭϬͲϭϵůĞƐƐW,Ϳ ŵŐͬ> Ϯ͘Ϯ Ϭ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϵϮϴϵ ,W,;ϭϵͲϯϮůĞƐƐW,Ϳ ŵŐͬ> Ϭ͘Ϯϳ Ϭ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϵϮϴϵ džƚ͘WĞƚ͘,LJĚƌŽĐĂƌďŽŶ W,;ϭϬͲϭϵͿ ŵŐͬ> Ϯ͘ϯ Ϭ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϵϱϯϱ W,;ϭϵͲϯϮͿ ŵŐͬ> Ϭ͘Ϯϳ Ϭ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϵϱϯϱ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ KͲdZW,Ez>;ƐƵƌ͘Ϳ й ϵϰ ϴϴ ϴϴ ϴϳ ϴϲ ϳϵϭϵϱϯϱ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ й ϭϬϭ ϭϬϰ ϭϬϭ ϭϬϬ ϭϬϬ ϳϵϭϵϰϮϯ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ й ϵϱ ϭϬϯ ϭϬϭ ϵϲ ϭϬϬ ϳϵϭϵϰϮϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ ;ϭͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽĚŝůƵƚŝŽŶƚŽďƌŝŶŐĂŶĂůLJƚĞǁŝƚŚŝŶƚŚĞĐĂůŝďƌĂƚĞĚƌĂŶŐĞ͘ ;ϮͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘

WĂŐĞϰŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: >W,Θ,W,t/d,^ZͬDW,/EtdZ;tdZͿ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ Z> DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ Z> YĂƚĐŚ ϴͲEW,d,>E;ƐƵƌ͘Ϳ й ϳϯ ϴϴ ϵϬ ϴϴ ϴϴ ϳϵϭϵϰϮϯ ϵͲĐƌŝĚŝŶĞ й ϵϰ ϵϴ ϭϬϬ ϵϲ ϲϲ ϳϵϭϵϰϮϯ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ й ϴϬ ϴϬ ϵϱ ϵϭ ϳϵ ϳϵϭϵϰϮϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϱŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: D/^^K>sDd>^/EtdZ;tdZͿ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ Z> YĂƚĐŚ DŝƐĐ͘/ŶŽƌŐĂŶŝĐƐ ŝƐƐŽůǀĞĚ,ĂƌĚŶĞƐƐ;ĂKϯͿ ŵŐͬ> ϮϳϮ ϰϵϭ Ϯϱϰ ϭϲϵ ϰϵϴ Ϭ͘ϱϬ ϳϵϭϴϲϱϵ ůĞŵĞŶƚƐ ŝƐƐŽůǀĞĚDĞƌĐƵƌLJ;,ŐͿ ƵŐͬ> фϬ͘ϬϭϬ фϬ͘ϬϭϬ фϬ͘ϬϭϬ фϬ͘ϬϭϬ фϬ͘ϬϭϬ Ϭ͘ϬϭϬ ϳϵϮϬϮϮϲ ŝƐƐŽůǀĞĚDĞƚĂůƐďLJ/WD^ ŝƐƐŽůǀĞĚůƵŵŝŶƵŵ;ůͿ ƵŐͬ> Ϯϱϳ ϱϵ͘ϰ ϭϲ͘ϰ ϰϳ͘ϵ ϲϳ͘ϲ ϯ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŶƚŝŵŽŶLJ;^ďͿ ƵŐͬ> Ϯ͘ϬϮ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ фϬ͘ϱϬ Ϭ͘ϱϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚƌƐĞŶŝĐ;ƐͿ ƵŐͬ> ϳ͘ϬϬ ϯ͘Ϯϭ ϭ͘ϮϬ ϭ͘ϵϭ ϯ͘ϭϴ Ϭ͘ϭϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĂƌŝƵŵ;ĂͿ ƵŐͬ> ϭϭϱ Ϯϯϲ ϵϳ͘ϵ ϰϳ͘Ϭ Ϯϭϳ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĞƌLJůůŝƵŵ;ĞͿ ƵŐͬ> фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ фϬ͘ϭϬ Ϭ͘ϭϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝƐŵƵƚŚ;ŝͿ ƵŐͬ> фϭ͘Ϭ фϭ͘Ϭ фϭ͘Ϭ фϭ͘Ϭ фϭ͘Ϭ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽƌŽŶ;Ϳ ƵŐͬ> ϭϳϮ ϯϲϬ ϳϮ фϱϬ ϯϲϬ ϱϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĂĚŵŝƵŵ;ĚͿ ƵŐͬ> Ϭ͘ϬϭϮ Ϭ͘ϬϰϬ Ϭ͘ϬϮϬ фϬ͘ϬϭϬ Ϭ͘ϬϰϬ Ϭ͘ϬϭϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŚƌŽŵŝƵŵ;ƌͿ ƵŐͬ> ϴ͘ϭ ϭ͘ϵ фϭ͘Ϭ фϭ͘Ϭ ϭ͘ϵ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽďĂůƚ;ŽͿ ƵŐͬ> Ϭ͘ϱϵ ϴ͘ϭϰ ϭ͘ϱϬ Ϭ͘ϳϳ ϳ͘ϵϮ Ϭ͘ϱϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽƉƉĞƌ;ƵͿ ƵŐͬ> ϭ͘ϲϮ Ϭ͘ϳϬ Ϭ͘ϳϳ Ϭ͘Ϯϴ Ϭ͘ϳϰ Ϭ͘ϮϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ/ƌŽŶ;&ĞͿ ƵŐͬ> ϯϬϱϬ ϯϴϰϬϬ ϮϲϮϬ Ϯϳϭ ϯϳϲϬϬ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ>ĞĂĚ;WďͿ ƵŐͬ> Ϯ͘ϴϲ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ>ŝƚŚŝƵŵ;>ŝͿ ƵŐͬ> фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚDĂŶŐĂŶĞƐĞ;DŶͿ ƵŐͬ> ϲϬϳ ϮϲϬϬ ϭϲϯϬ ϮϮϴ ϮϳϭϬ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚDŽůLJďĚĞŶƵŵ;DŽͿ ƵŐͬ> ϱϴ͘Ϭ ϳ͘ϳ ϱ͘ϰ Ϯ͘ϴ ϳ͘ϰ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚEŝĐŬĞů;EŝͿ ƵŐͬ> ϲ͘ϰ ϭϭ͘ϭ ϯ͘Ϭ ϭ͘ϴ ϭϬ͘ϳ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ĞůĞŶŝƵŵ;^ĞͿ ƵŐͬ> Ϯ͘ϭϵ Ϭ͘ϴϰ Ϭ͘ϭϰ Ϭ͘ϮϬ Ϭ͘ϴϴ Ϭ͘ϭϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ŝůŝĐŽŶ;^ŝͿ ƵŐͬ> ϴϲϴϬ ϭϭϰϬϬ ϴϰϲϬ ϲϲϬϬ ϭϬϴϬϬ ϭϬϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ŝůǀĞƌ;ŐͿ ƵŐͬ> фϬ͘ϬϮϬ фϬ͘ϬϮϬ фϬ͘ϬϮϬ фϬ͘ϬϮϬ фϬ͘ϬϮϬ Ϭ͘ϬϮϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ƚƌŽŶƚŝƵŵ;^ƌͿ ƵŐͬ> ϲϳϵ ϭϮϲϬ ϱϬϵ ϮϮϯ ϭϮϱϬ ϭ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŚĂůůŝƵŵ;důͿ ƵŐͬ> фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŝŶ;^ŶͿ ƵŐͬ> фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŝƚĂŶŝƵŵ;dŝͿ ƵŐͬ> ϮϮ͘ϯ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ фϱ͘Ϭ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚhƌĂŶŝƵŵ;hͿ ƵŐͬ> Ϭ͘ϴϲ ϭ͘Ϯϱ Ϭ͘ϳϴ Ϭ͘ϲϯ ϭ͘ϭϵ Ϭ͘ϭϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚsĂŶĂĚŝƵŵ;sͿ ƵŐͬ> ϯϬ͘Ϯ ϱ͘ϭ фϱ͘Ϭ фϱ͘Ϭ ϱ͘ϯ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝŶĐ;ŶͿ ƵŐͬ> фϱ͘Ϭ Ϯϯ͘ϲ ϭϮ͘ϲ фϱ͘Ϭ Ϯϰ͘Ϯ ϱ͘Ϭ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝƌĐŽŶŝƵŵ;ƌͿ ƵŐͬ> Ϯ͘ϴϴ ϭ͘ϵϴ фϬ͘ϱϬ фϬ͘ϱϬ ϭ͘ϴϵ Ϭ͘ϱϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĂůĐŝƵŵ;ĂͿ ŵŐͬ> ϵϭ͘ϰ ϭϯϱ ϴϱ͘ϵ ϲϭ͘Ϯ ϭϯϳ Ϭ͘ϬϱϬ ϳϵϭϵϮϴϳ ŝƐƐŽůǀĞĚDĂŐŶĞƐŝƵŵ;DŐͿ ŵŐͬ> ϭϬ͘ϳ ϯϳ͘ϰ ϵ͘ϲϬ ϯ͘ϴϳ ϯϴ͘ϭ Ϭ͘ϬϱϬ ϳϵϭϵϮϴϳ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϲŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: D/^^K>sDd>^/EtdZ;tdZͿ

DĂdždžĂŵ/ D/ϵϭϭϭ D/ϵϭϭϮ D/ϵϭϭϯ D/ϵϭϭϰ D/ϵϭϭϱ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ϮϬϭϱͬϬϲͬϬϭ ^ĂŵƉůŝŶŐĂƚĞ Ϭϵ͗ϭϴ Ϭϵ͗Ϭϳ ϭϭ͗Ϭϵ ϭϬ͗ϯϰ Ϭϵ͗Ϭϳ KEƵŵďĞƌ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ ϰϲϲϯϭϴͲϬϭͲϬϭ hŶŝƚƐ DtϭϱͲϭ DtϭϱͲϮ DtϭϱͲϯ DtϭϱͲϰ DtϭϱͲϭϬϬ Z> YĂƚĐŚ ŝƐƐŽůǀĞĚWŽƚĂƐƐŝƵŵ;<Ϳ ŵŐͬ> ϵ͘ϳϮ ϭϯ͘ϭ Ϯ͘ϵϭ Ϯ͘ϴϭ ϭϯ͘ϯ Ϭ͘ϬϱϬ ϳϵϭϵϮϴϳ ŝƐƐŽůǀĞĚ^ŽĚŝƵŵ;EĂͿ ŵŐͬ> ϭϴϱ ϭϴϭ ϭϬ͘Ϭ ϰ͘ϯϭ ϭϴϲ Ϭ͘ϬϱϬ ϳϵϭϵϮϴϳ ŝƐƐŽůǀĞĚ^ƵůƉŚƵƌ;^Ϳ ŵŐͬ> ϭϲ͘Ϯ ϴ͘ϲ фϯ͘Ϭ ϰ͘ϭ ϳ͘ϴ ϯ͘Ϭ ϳϵϭϵϮϴϳ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϳŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

'EZ>KDDEd^

ZĞƐƵůƚƐƌĞůĂƚĞŽŶůLJƚŽƚŚĞŝƚĞŵƐƚĞƐƚĞĚ͘

WĂŐĞϴŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ Yh>/dz^^hZEZWKZd ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ ϳϵϭϵϯϴϮ ϭ͕ϰͲŝĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϵϰ ϳϬͲϭϯϬ ϭϬϬ ϳϬͲϭϯϬ ϭϬϮ й ϳϵϭϵϯϴϮ ϰͲƌŽŵŽĨůƵŽƌŽďĞŶnjĞŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϭϭϭ ϳϬͲϭϯϬ ϭϬϵ ϳϬͲϭϯϬ ϭϭϬ й ϳϵϭϵϯϴϮ ϰͲϭ͕ϮͲŝĐŚůŽƌŽĞƚŚĂŶĞ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϭϬϰ ϳϬͲϭϯϬ ϵϴ ϳϬͲϭϯϬ ϭϬϬ й ϳϵϭϵϰϮϯ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϭϬϲ ϲϬͲϭϯϬ ϭϬϯ ϲϬͲϭϯϬ ϭϬϰ й ϳϵϭϵϰϮϯ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϭϬϯ ϱϬͲϭϯϬ ϭϬϭ ϱϬͲϭϯϬ ϭϬϬ й ϳϵϭϵϰϮϯ ϴͲEW,d,>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϵϭ ϱϬͲϭϯϬ ϴϴ ϱϬͲϭϯϬ ϭϬϭ й ϳϵϭϵϰϮϯ ϵͲĐƌŝĚŝŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϵ ϱϬͲϭϯϬ ϵϳ ϱϬͲϭϯϬ ϵϭ й ϳϵϭϵϰϮϯ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϮ ϵϲ ϲϬͲϭϯϬ ϵϴ ϲϬͲϭϯϬ ϵϯ й ϳϵϭϵϱϯϱ KͲdZW,Ez>;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϭ ϵϰ ϱϬͲϭϯϬ ϵϯ ϱϬͲϭϯϬ ϴϳ й ϳϵϭϵϯϴϮ ;ϲͲϭϬͿ ϮϬϭϱͬϬϲͬϬϮ ϵϲ ϳϬͲϭϯϬ фϯϬϬ ƵŐͬ> ϳϵϭϵϯϴϮ ĞŶnjĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϬϲ ϳϬͲϭϯϬ ϵϵ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ ƚŚLJůďĞŶnjĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϭϭ ϳϬͲϭϯϬ ϭϬϰ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ ŵΘƉͲyLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϬϵ ϳϬͲϭϯϬ ϭϬϭ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ DĞƚŚLJůͲƚĞƌƚͲďƵƚLJůĞƚŚĞƌ;DdͿ ϮϬϭϱͬϬϲͬϬϮ ϵϴ ϳϬͲϭϯϬ ϵϭ ϳϬͲϭϯϬ фϰ͘Ϭ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ ŽͲyLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϬϮ ϳϬͲϭϯϬ ϵϳ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ ^ƚLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϭϬϵ ϳϬͲϭϯϬ ϭϬϮ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ dŽůƵĞŶĞ ϮϬϭϱͬϬϲͬϬϮ ϵϵ ϳϬͲϭϯϬ ϵϯ ϳϬͲϭϯϬ фϬ͘ϰϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ s,ϲͲϭϬ ϮϬϭϱͬϬϲͬϬϮ ϵϭ ϳϬͲϭϯϬ фϯϬϬ ƵŐͬ> E ϯϬ ϳϵϭϵϯϴϮ yLJůĞŶĞƐ;dŽƚĂůͿ ϮϬϭϱͬϬϲͬϬϮ фϬ͘ϰϬ ƵŐͬ> ϭϳ ϯϬ ϳϵϭϵϰϮϯ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϴ ϱϬͲϭϯϬ ϳϬ ϱϬͲϭϯϬ фϬ͘ϭϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĐĞŶĂƉŚƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϴϯ ϱϬͲϭϯϬ ϳϱ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĐĞŶĂƉŚƚŚLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϴϮ ϱϬͲϭϯϬ ϳϱ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĐƌŝĚŝŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϴ ϱϬͲϭϯϬ ϳϭ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϴϰ ϲϬͲϭϯϬ ϳϳ ϲϬͲϭϯϬ фϬ͘ϬϭϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϱ ϲϬͲϭϯϬ ϲϴ ϲϬͲϭϯϬ фϬ͘ϬϭϬ ƵŐͬ> E ϰϬ Ϭ͘ϬϬϵϭ͕ ϳϵϭϵϰϮϯ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϴϬ ϲϬͲϭϯϬ ϳϮ ϲϬͲϭϯϬ ƵŐͬ> E ϰϬ Z>сϬ͘ϬϬϵϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϵ ϲϬͲϭϯϬ ϳϭ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϲ ϲϬͲϭϯϬ ϲϵ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϬ ϲϬͲϭϯϬ ϲϱ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ

WĂŐĞϵŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ ϳϵϭϵϰϮϯ ŚƌLJƐĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϱ ϲϬͲϭϯϬ ϲϵ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϮ ϲϬͲϭϯϬ ϲϲ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ &ůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϳ ϲϬͲϭϯϬ ϲϵ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ &ůƵŽƌĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϴ ϱϬͲϭϯϬ ϳϭ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϳ ϲϬͲϭϯϬ ϲϵ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ EĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϮ ϱϬͲϭϯϬ ϲϰ ϱϬͲϭϯϬ фϬ͘ϭϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ WŚĞŶĂŶƚŚƌĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϵ ϲϬͲϭϯϬ ϳϭ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ WLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϭ ϳϳ ϲϬͲϭϯϬ ϲϵ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ƵŐͬ> E ϰϬ ϳϵϭϵϰϮϯ YƵŝŶŽůŝŶĞ ϮϬϭϱͬϬϲͬϬϭ ϴϲ ϱϬͲϭϯϬ ϴϭ ϱϬͲϭϯϬ фϬ͘Ϯϰ ƵŐͬ> E ϰϬ ϳϵϭϵϱϯϱ W,;ϭϬͲϭϵͿ ϮϬϭϱͬϬϲͬϬϭ ϵϴ ϱϬͲϭϯϬ ϵϰ ϱϬͲϭϯϬ фϬ͘ϮϬ ŵŐͬ> E ϯϬ ϳϵϭϵϱϯϱ W,;ϭϵͲϯϮͿ ϮϬϭϱͬϬϲͬϬϭ ϭϭϭ ϱϬͲϭϯϬ ϭϬϭ ϱϬͲϭϯϬ фϬ͘ϮϬ ŵŐͬ> E ϯϬ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚůƵŵŝŶƵŵ;ůͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϳ ϴϬͲϭϮϬ ϭϭϬ ϴϬͲϭϮϬ фϯ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŶƚŝŵŽŶLJ;^ďͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϭ ϴϬͲϭϮϬ ϭϬϮ ϴϬͲϭϮϬ фϬ͘ϱϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚƌƐĞŶŝĐ;ƐͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϵ ϴϬͲϭϮϬ ϭϬϯ ϴϬͲϭϮϬ фϬ͘ϭϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĂƌŝƵŵ;ĂͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϮ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĞƌLJůůŝƵŵ;ĞͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϭ ϴϬͲϭϮϬ ϭϬϱ ϴϬͲϭϮϬ фϬ͘ϭϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝƐŵƵƚŚ;ŝͿ ϮϬϭϱͬϬϲͬϬϮ ϵϳ ϴϬͲϭϮϬ ϭϬϭ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽƌŽŶ;Ϳ ϮϬϭϱͬϬϲͬϬϮ фϱϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚĂĚŵŝƵŵ;ĚͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϯ ϴϬͲϭϮϬ ϵϴ ϴϬͲϭϮϬ фϬ͘ϬϭϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŚƌŽŵŝƵŵ;ƌͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϯ ϴϬͲϭϮϬ ϵϵ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽďĂůƚ;ŽͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϯ ϴϬͲϭϮϬ ϵϵ ϴϬͲϭϮϬ фϬ͘ϱϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŽƉƉĞƌ;ƵͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϱ ϴϬͲϭϮϬ ϵϵ ϴϬͲϭϮϬ фϬ͘ϮϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ/ƌŽŶ;&ĞͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϱ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ>ĞĂĚ;WďͿ ϮϬϭϱͬϬϲͬϬϮ ϵϴ ϴϬͲϭϮϬ ϵϳ ϴϬͲϭϮϬ фϬ͘ϮϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ>ŝƚŚŝƵŵ;>ŝͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϰ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚDĂŶŐĂŶĞƐĞ;DŶͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϬ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚDŽůLJďĚĞŶƵŵ;DŽͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϬ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚEŝĐŬĞů;EŝͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϮ ϴϬͲϭϮϬ ϭϬϬ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ĞůĞŶŝƵŵ;^ĞͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϵ ϴϬͲϭϮϬ ϵϮ ϴϬͲϭϮϬ фϬ͘ϭϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ŝůŝĐŽŶ;^ŝͿ ϮϬϭϱͬϬϲͬϬϮ фϭϬϬ ƵŐͬ>

WĂŐĞϭϬŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ŝůǀĞƌ;ŐͿ ϮϬϭϱͬϬϲͬϬϮ ϭϮϲ;ϭͿ ϴϬͲϭϮϬ ϭϬϬ ϴϬͲϭϮϬ фϬ͘ϬϮϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚ^ƚƌŽŶƚŝƵŵ;^ƌͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϵϴ ϴϬͲϭϮϬ фϭ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŚĂůůŝƵŵ;důͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϮ ϴϬͲϭϮϬ ϵϳ ϴϬͲϭϮϬ фϬ͘ϬϱϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŝŶ;^ŶͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϱ ϴϬͲϭϮϬ ϭϬϮ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚdŝƚĂŶŝƵŵ;dŝͿ ϮϬϭϱͬϬϲͬϬϮ ϭϭϰ ϴϬͲϭϮϬ ϵϲ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚhƌĂŶŝƵŵ;hͿ ϮϬϭϱͬϬϲͬϬϮ ϭϬϬ ϴϬͲϭϮϬ ϵϬ ϴϬͲϭϮϬ фϬ͘ϭϬ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚsĂŶĂĚŝƵŵ;sͿ ϮϬϭϱͬϬϲͬϬϮ ϵϵ ϴϬͲϭϮϬ ϭϬϭ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝŶĐ;ŶͿ ϮϬϭϱͬϬϲͬϬϮ E ϴϬͲϭϮϬ ϭϬϱ ϴϬͲϭϮϬ фϱ͘Ϭ ƵŐͬ> ϳϵϭϵϴϭϮ ŝƐƐŽůǀĞĚŝƌĐŽŶŝƵŵ;ƌͿ ϮϬϭϱͬϬϲͬϬϮ фϬ͘ϱϬ ƵŐͬ> ϳϵϮϬϮϮϲ ŝƐƐŽůǀĞĚDĞƌĐƵƌLJ;,ŐͿ ϮϬϭϱͬϬϲͬϬϮ ϴϯ ϴϬͲϭϮϬ ϴϳ ϴϬͲϭϮϬ фϬ͘ϬϭϬ ƵŐͬ> E ϮϬ ƵƉůŝĐĂƚĞ͗WĂŝƌĞĚĂŶĂůLJƐŝƐŽĨĂƐĞƉĂƌĂƚĞƉŽƌƚŝŽŶŽĨƚŚĞƐĂŵĞƐĂŵƉůĞ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƚŚĞǀĂƌŝĂŶĐĞŝŶƚŚĞŵĞĂƐƵƌĞŵĞŶƚ͘ DĂƚƌŝdž^ƉŝŬĞ͗ƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞŽĨŝŶƚĞƌĞƐƚŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƐĂŵƉůĞŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ ^ƉŝŬĞĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞ͕ƵƐƵĂůůLJĨƌŽŵĂƐĞĐŽŶĚƐŽƵƌĐĞ͕ŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞŵĞƚŚŽĚĂĐĐƵƌĂĐLJ͘ DĞƚŚŽĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžĐŽŶƚĂŝŶŝŶŐĂůůƌĞĂŐĞŶƚƐƵƐĞĚŝŶƚŚĞĂŶĂůLJƚŝĐĂůƉƌŽĐĞĚƵƌĞ͘hƐĞĚƚŽŝĚĞŶƚŝĨLJůĂďŽƌĂƚŽƌLJĐŽŶƚĂŵŝŶĂƚŝŽŶ͘ ^ƵƌƌŽŐĂƚĞ͗ƉƵƌĞŽƌŝƐŽƚŽƉŝĐĂůůLJůĂďĞůĞĚĐŽŵƉŽƵŶĚǁŚŽƐĞďĞŚĂǀŝŽƌŵŝƌƌŽƌƐƚŚĞĂŶĂůLJƚĞƐŽĨŝŶƚĞƌĞƐƚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞĞdžƚƌĂĐƚŝŽŶĞĨĨŝĐŝĞŶĐLJ͘ E;DĂƚƌŝdž^ƉŝŬĞͿ͗dŚĞƌĞĐŽǀĞƌLJŝŶƚŚĞŵĂƚƌŝdžƐƉŝŬĞǁĂƐŶŽƚĐĂůĐƵůĂƚĞĚ͘dŚĞƌĞůĂƚŝǀĞĚŝĨĨĞƌĞŶĐĞďĞƚǁĞĞŶƚŚĞĐŽŶĐĞŶƚƌĂƚŝŽŶŝŶƚŚĞƉĂƌĞŶƚƐĂŵƉůĞĂŶĚƚŚĞƐƉŝŬĞĚĂŵŽƵŶƚǁĂƐƚŽŽƐŵĂůůƚŽƉĞƌŵŝƚĂƌĞůŝĂďůĞ ƌĞĐŽǀĞƌLJĐĂůĐƵůĂƚŝŽŶ;ŵĂƚƌŝdžƐƉŝŬĞĐŽŶĐĞŶƚƌĂƚŝŽŶǁĂƐůĞƐƐƚŚĂŶϮdžƚŚĂƚŽĨƚŚĞŶĂƚŝǀĞƐĂŵƉůĞĐŽŶĐĞŶƚƌĂƚŝŽŶͿ͘ E;ƵƉůŝĐĂƚĞZWͿ͗dŚĞĚƵƉůŝĐĂƚĞZWǁĂƐŶŽƚĐĂůĐƵůĂƚĞĚ͘dŚĞĐŽŶĐĞŶƚƌĂƚŝŽŶŝŶƚŚĞƐĂŵƉůĞĂŶĚͬŽƌĚƵƉůŝĐĂƚĞǁĂƐƚŽŽůŽǁƚŽƉĞƌŵŝƚĂƌĞůŝĂďůĞZWĐĂůĐƵůĂƚŝŽŶ;ŽŶĞŽƌďŽƚŚƐĂŵƉůĞƐфϱdžZ>Ϳ͘ ;ϭͿZĞĐŽǀĞƌLJŽƌZWĨŽƌƚŚŝƐƉĂƌĂŵĞƚĞƌŝƐŽƵƚƐŝĚĞĐŽŶƚƌŽůůŝŵŝƚƐ͘dŚĞŽǀĞƌĂůůƋƵĂůŝƚLJĐŽŶƚƌŽůĨŽƌƚŚŝƐĂŶĂůLJƐŝƐŵĞĞƚƐĂĐĐĞƉƚĂďŝůŝƚLJĐƌŝƚĞƌŝĂ͘

WĂŐĞϭϭŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: s>/d/KE^/'EdhZW'

dŚĞĂŶĂůLJƚŝĐĂůĚĂƚĂĂŶĚĂůůYĐŽŶƚĂŝŶĞĚŝŶƚŚŝƐƌĞƉŽƌƚǁĞƌĞƌĞǀŝĞǁĞĚĂŶĚǀĂůŝĚĂƚĞĚďLJƚŚĞĨŽůůŽǁŝŶŐŝŶĚŝǀŝĚƵĂů;ƐͿ͘

ŶĚLJ>Ƶ͕ĂƚĂsĂůŝĚĂƚŝŽŶŽŽƌĚŝŶĂƚŽƌ

DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

WĂŐĞϭϮŽĨϭϴ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ WĂŐĞϭϯŽĨϭϴ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ DĂdždžĂŵ^ĂŵƉůĞ͗D/ϵϭϭϭ ^ŝƚĞZĞĨĞƌĞŶĐĞ͗EtZ/',dKEWZ< ůŝĞŶƚ/͗DtϭϱͲϭ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϭϰŽĨϭϴ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ DĂdždžĂŵ^ĂŵƉůĞ͗D/ϵϭϭϮ ^ŝƚĞZĞĨĞƌĞŶĐĞ͗EtZ/',dKEWZ< ůŝĞŶƚ/͗DtϭϱͲϮ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϭϱŽĨϭϴ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ DĂdždžĂŵ^ĂŵƉůĞ͗D/ϵϭϭϯ ^ŝƚĞZĞĨĞƌĞŶĐĞ͗EtZ/',dKEWZ< ůŝĞŶƚ/͗DtϭϱͲϯ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϭϲŽĨϭϴ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ DĂdždžĂŵ^ĂŵƉůĞ͗D/ϵϭϭϰ ^ŝƚĞZĞĨĞƌĞŶĐĞ͗EtZ/',dKEWZ< ůŝĞŶƚ/͗DtϭϱͲϰ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϭϳŽĨϭϴ DĂdždžĂŵ:Žďη͗ϱϰϱϯϲϭ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϮ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ DĂdždžĂŵ^ĂŵƉůĞ͗D/ϵϭϭϱ ^ŝƚĞZĞĨĞƌĞŶĐĞ͗EtZ/',dKEWZ< ůŝĞŶƚ/͗DtϭϱͲϭϬϬ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚŚƌŽŵĂƚŽŐƌĂŵ

EŽƚĞ͗dŚŝƐŝŶĨŽƌŵĂƚŝŽŶŝƐƉƌŽǀŝĚĞĚĨŽƌƌĞĨĞƌĞŶĐĞƉƵƌƉŽƐĞƐŽŶůLJ͘^ŚŽƵůĚĚĞƚĂŝůĞĚĐŚĞŵŝƐƚŝŶƚĞƌƉƌĞƚĂƚŝŽŶ ŽƌĨŝŶŐĞƌƉƌŝŶƚŝŶŐďĞƌĞƋƵŝƌĞĚ͕ƉůĞĂƐĞĐŽŶƚĂĐƚƚŚĞůĂďŽƌĂƚŽƌLJ͘

WĂŐĞϭϴŽĨϭϴ zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ zŽƵƌWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< ƚƚĞŶƚŝŽŶ͗:ĞƌĞŵLJŚƵĂ zŽƵƌ͘K͘͘η͗'ϭϬϮϵϰϮ ,DDZEs/ZK,D/E͘ ϭϴƚŚ&ůŽŽƌ͕ϰϳϯϬ<ŝŶŐƐǁĂLJ ƵƌŶĂďLJ͕ ĂŶĂĚĂsϱ,Ϭϲ

ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ZĞƉŽƌƚη͗Zϭϵϳϯϰϲϰ sĞƌƐŝŽŶ͗ϭͲ&ŝŶĂů

Zd/&/dK&E>z^/^ DyyD:Kη͗ϱϰϳϭϵϴ ZĞĐĞŝǀĞĚ͗ϮϬϭϱͬϬϲͬϬϱ͕ϭϬ͗ϯϱ ^ĂŵƉůĞDĂƚƌŝdž͗tĂƚĞƌ η^ĂŵƉůĞƐZĞĐĞŝǀĞĚ͗ϭ ĂƚĞ ĂƚĞ ŶĂůLJƐĞƐ YƵĂŶƚŝƚLJ džƚƌĂĐƚĞĚ ŶĂůLJnjĞĚ >ĂďŽƌĂƚŽƌLJDĞƚŚŽĚ ŶĂůLJƚŝĐĂůDĞƚŚŽĚ W,ŝŶtĂƚĞƌǁŚĞŶW,ƌĞƋƵŝƌĞĚ ϭ ϮϬϭϱͬϬϲͬϬϴ ϮϬϭϱͬϬϲͬϬϴ zϴ^KWͲϬϬϬϮϵ DKW,ǁϭϮͬϬϬŵ W,ŝŶtĂƚĞƌďLJ'ͬD^;^/DͿ ϭ ϮϬϭϱͬϬϲͬϬϴ ϮϬϭϱͬϬϲͬϬϵ zϴ^KWͲϬϬϬϮϭ WϴϮϳϬĚZϰŵ dŽƚĂů>Dt͕,Dt͕dŽƚĂůW,ĂůĐ ϭ Eͬ ϮϬϭϱͬϬϲͬϬϵ zt/ͲϬϬϬϯϯ ƵƚŽĂůĐ W,ůĞƐƐW,ŝŶtĂƚĞƌďLJ'ͬ&/ ϭ Eͬ ϮϬϭϱͬϬϲͬϬϵ zt/ͲϬϬϬϯϯ ƵƚŽĂůĐ

ZĞĨĞƌĞŶĐĞDĞƚŚŽĚƐƵĨĨŝdž͞ŵ͟ŝŶĚŝĐĂƚĞƐƚĞƐƚŵĞƚŚŽĚƐŝŶĐŽƌƉŽƌĂƚĞǀĂůŝĚĂƚĞĚŵŽĚŝĨŝĐĂƚŝŽŶƐĨƌŽŵƐƉĞĐŝĨŝĐƌĞĨĞƌĞŶĐĞŵĞƚŚŽĚƐƚŽŝŵƉƌŽǀĞƉĞƌĨŽƌŵĂŶĐĞ͘ Ύ ZWƐ ĐĂůĐƵůĂƚĞĚ ƵƐŝŶŐ ƌĂǁ ĚĂƚĂ͘ dŚĞ ƌŽƵŶĚŝŶŐ ŽĨ ĨŝŶĂů ƌĞƐƵůƚƐ ŵĂLJ ƌĞƐƵůƚ ŝŶ ƚŚĞ ĂƉƉĂƌĞŶƚ ĚŝĨĨĞƌĞŶĐĞ͘

Maxxam ŶĐƌLJƉƚŝŽŶ<ĞLJ 09 Jun 2015 17:16:47 -07:00

WůĞĂƐĞĚŝƌĞĐƚĂůůƋƵĞƐƚŝŽŶƐƌĞŐĂƌĚŝŶŐƚŚŝƐĞƌƚŝĨŝĐĂƚĞŽĨŶĂůLJƐŝƐƚŽLJŽƵƌWƌŽũĞĐƚDĂŶĂŐĞƌ͘ ŵĂŶĚĞĞƉEĂŐƌĂ͕ĐĐŽƵŶƚ^ƉĞĐŝĂůŝƐƚ ŵĂŝů͗EĂŐƌĂΛŵĂdždžĂŵ͘ĐĂ WŚŽŶĞη;ϲϬϰͿϲϯϵͲϮϲϬϮ сссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссссс dŚŝƐƌĞƉŽƌƚŚĂƐďĞĞŶŐĞŶĞƌĂƚĞĚĂŶĚĚŝƐƚƌŝďƵƚĞĚƵƐŝŶŐĂƐĞĐƵƌĞĂƵƚŽŵĂƚĞĚƉƌŽĐĞƐƐ͘ DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

dŽƚĂůŽǀĞƌWĂŐĞƐ͗ϭ WĂŐĞϭŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: >W,Θ,W,t/d,^ZͬDW,/EtdZ;tdZͿ

DĂdždžĂŵ/ D:ϴϬϬϲ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϲͬϬϱ KEƵŵďĞƌ 'ϭϬϮϵϰϮ hŶŝƚƐ DtϭϱͲϭ Z> YĂƚĐŚ WŽůLJĐLJĐůŝĐƌŽŵĂƚŝĐƐ >ŽǁDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ƵŐͬ> ϭϮϬ Ϭ͘ϲϳ ϳϵϮϰϭϰϱ ,ŝŐŚDŽůĞĐƵůĂƌtĞŝŐŚƚW,ǭƐ ƵŐͬ> Ϭ͘ϰϰ Ϭ͘ϬϱϬ ϳϵϮϰϭϰϱ dŽƚĂůW, ƵŐͬ> ϭϮϬ Ϭ͘ϲϳ ϳϵϮϰϭϰϱ EĂƉŚƚŚĂůĞŶĞ ƵŐͬ> Ϯϵ;ϭͿ Ϭ͘ϱϬ ϳϵϮϲϱϴϵ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ƵŐͬ> ϳϭ;ϭͿ Ϭ͘ϱϬ ϳϵϮϲϱϴϵ YƵŝŶŽůŝŶĞ ƵŐͬ> фϬ͘ϲϳ;ϮͿ Ϭ͘ϲϳ ϳϵϮϲϱϴϵ ĐĞŶĂƉŚƚŚLJůĞŶĞ ƵŐͬ> фϬ͘Ϯϲ;ϯͿ Ϭ͘Ϯϲ ϳϵϮϲϱϴϵ ĐĞŶĂƉŚƚŚĞŶĞ ƵŐͬ> ϳ͘ϯ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ &ůƵŽƌĞŶĞ ƵŐͬ> ϱ͘Ϭ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ WŚĞŶĂŶƚŚƌĞŶĞ ƵŐͬ> ϴ͘ϵ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ŶƚŚƌĂĐĞŶĞ ƵŐͬ> Ϭ͘ϳϮ Ϭ͘ϬϭϬ ϳϵϮϲϱϴϵ ĐƌŝĚŝŶĞ ƵŐͬ> Ϭ͘Ϭϴϯ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ &ůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> Ϭ͘ϭϴ Ϭ͘ϬϮϬ ϳϵϮϲϱϴϵ WLJƌĞŶĞ ƵŐͬ> Ϭ͘ϮϮ Ϭ͘ϬϮϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ƵŐͬ> Ϭ͘ϬϮϰ Ϭ͘ϬϭϬ ϳϵϮϲϱϴϵ ŚƌLJƐĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ƵŐͬ> Ϭ͘Ϭϭϱ Ϭ͘ϬϬϵϬ ϳϵϮϲϱϴϵ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ƵŐͬ> фϬ͘ϬϱϬ Ϭ͘ϬϱϬ ϳϵϮϲϱϴϵ ĂůĐƵůĂƚĞĚWĂƌĂŵĞƚĞƌƐ >W,;ϭϬͲϭϵůĞƐƐW,Ϳ ŵŐͬ> Ϯ͘Ϭ Ϭ͘ϮϬ ϳϵϮϰϴϮϬ ,W,;ϭϵͲϯϮůĞƐƐW,Ϳ ŵŐͬ> фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϮϰϴϮϬ džƚ͘WĞƚ͘,LJĚƌŽĐĂƌďŽŶ W,;ϭϬͲϭϵͿ ŵŐͬ> Ϯ͘Ϭ Ϭ͘ϮϬ ϳϵϮϲϱϵϯ W,;ϭϵͲϯϮͿ ŵŐͬ> фϬ͘ϮϬ Ϭ͘ϮϬ ϳϵϮϲϱϵϯ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ ;ϭͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽĚŝůƵƚŝŽŶƚŽďƌŝŶŐĂŶĂůLJƚĞǁŝƚŚŝŶƚŚĞ ĐĂůŝďƌĂƚĞĚƌĂŶŐĞ͘ ;ϮͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ ;ϯͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ĞƚĞĐƚŝŽŶůŝŵŝƚƐ ƌĂŝƐĞĚĚƵĞƚŽĚŝůƵƚŝŽŶƚŽďƌŝŶŐĂŶĂůLJƚĞǁŝƚŚŝŶƚŚĞĐĂůŝďƌĂƚĞĚƌĂŶŐĞ͘

WĂŐĞϮŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: >W,Θ,W,t/d,^ZͬDW,/EtdZ;tdZͿ

DĂdždžĂŵ/ D:ϴϬϬϲ ^ĂŵƉůŝŶŐĂƚĞ ϮϬϭϱͬϬϲͬϬϱ KEƵŵďĞƌ 'ϭϬϮϵϰϮ hŶŝƚƐ DtϭϱͲϭ Z> YĂƚĐŚ ^ƵƌƌŽŐĂƚĞZĞĐŽǀĞƌLJ;йͿ KͲdZW,Ez>;ƐƵƌ͘Ϳ й ϴϵ ϳϵϮϲϱϵϯ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ й ϭϬϯ ϳϵϮϲϱϴϵ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ й ϭϬϭ ϳϵϮϲϱϴϵ ϴͲEW,d,>E;ƐƵƌ͘Ϳ й ϵϰ ϳϵϮϲϱϴϵ ϵͲĐƌŝĚŝŶĞ й ϭϬϰ ϳϵϮϲϱϴϵ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ й ϴϰ ϳϵϮϲϱϴϵ Z>сZĞƉŽƌƚĂďůĞĞƚĞĐƚŝŽŶ>ŝŵŝƚ

WĂŐĞϯŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

'EZ>KDDEd^

ZĞƐƵůƚƐƌĞůĂƚĞŽŶůLJƚŽƚŚĞŝƚĞŵƐƚĞƐƚĞĚ͘

WĂŐĞϰŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ Yh>/dz^^hZEZWKZd ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ ϳϵϮϲϱϴϵ ϭϬͲEd,ZE;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϴ ϵϰ ϲϬͲϭϯϬ ϭϬϭ ϲϬͲϭϯϬ ϭϬϭ й ϳϵϮϲϱϴϵ ϴͲEW,d,z>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϴ ϭϬϭ ϱϬͲϭϯϬ ϭϬϰ ϱϬͲϭϯϬ ϵϵ й ϳϵϮϲϱϴϵ ϴͲEW,d,>E;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϴ ϵϳ ϱϬͲϭϯϬ ϵϵ ϱϬͲϭϯϬ ϵϯ й ϳϵϮϲϱϴϵ ϵͲĐƌŝĚŝŶĞ ϮϬϭϱͬϬϲͬϬϴ ϭϬϱ ϱϬͲϭϯϬ ϭϬϮ ϱϬͲϭϯϬ ϭϬϬ й ϳϵϮϲϱϴϵ dZW,Ez>Ͳϭϰ;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϴ ϵϯ ϲϬͲϭϯϬ ϵϯ ϲϬͲϭϯϬ ϵϯ й ϳϵϮϲϱϵϯ KͲdZW,Ez>;ƐƵƌ͘Ϳ ϮϬϭϱͬϬϲͬϬϴ ϭϬϯ ϱϬͲϭϯϬ ϭϬϱ ϱϬͲϭϯϬ ϴϬ й ϳϵϮϲϱϴϵ ϮͲDĞƚŚLJůŶĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϮ ϱϬͲϭϯϬ ϵϳ ϱϬͲϭϯϬ фϬ͘ϭϬ ƵŐͬ> ϯ͘ϴ;ϭͿ ϰϬ ϳϵϮϲϱϴϵ ĐĞŶĂƉŚƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϱ ϱϬͲϭϯϬ ϵϴ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> ϯ͘ϳ ϰϬ ϳϵϮϲϱϴϵ ĐĞŶĂƉŚƚŚLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϲ ϱϬͲϭϯϬ ϵϵ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E;ϯͿ ϰϬ ϳϵϮϲϱϴϵ ĐƌŝĚŝŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϱ ϱϬͲϭϯϬ ϵϳ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϮ ϲϬͲϭϯϬ ϵϰ ϲϬͲϭϯϬ фϬ͘ϬϭϬ ƵŐͬ> Ϯ͘Ϭ ϰϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ĂͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϰ ϲϬͲϭϯϬ ϴϳ ϲϬͲϭϯϬ фϬ͘ϬϭϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ĂͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϯ ϲϬͲϭϯϬ ϵϲ ϲϬͲϭϯϬ фϬ͘ϬϬϵϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ďΘũͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϰ ϲϬͲϭϯϬ ϵϰ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;Ő͕Ś͕ŝͿƉĞƌLJůĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϵ ϲϬͲϭϯϬ ϵϭ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ĞŶnjŽ;ŬͿĨůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϴϳ ϲϬͲϭϯϬ ϴϯ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ŚƌLJƐĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϳ ϲϬͲϭϯϬ ϵϭ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ ŝďĞŶnj;Ă͕ŚͿĂŶƚŚƌĂĐĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϬ ϲϬͲϭϯϬ ϵϯ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ &ůƵŽƌĂŶƚŚĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϭ ϲϬͲϭϯϬ ϴϯ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ƵŐͬ> ϰ͘ϱ ϰϬ ϳϵϮϲϱϴϵ &ůƵŽƌĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϴ ϱϬͲϭϯϬ ϵϭ ϱϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> ϭ͘Ϯ ϰϬ ϳϵϮϲϱϴϵ /ŶĚĞŶŽ;ϭ͕Ϯ͕ϯͲĐĚͿƉLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϱ ϲϬͲϭϯϬ ϵϱ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> E ϰϬ ϳϵϮϲϱϴϵ EĂƉŚƚŚĂůĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϯ ϱϬͲϭϯϬ ϴϵ ϱϬͲϭϯϬ фϬ͘ϭϬ ƵŐͬ> Ϯ͘ϴ;ϭͿ ϰϬ ϳϵϮϲϱϴϵ WŚĞŶĂŶƚŚƌĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϲ ϲϬͲϭϯϬ ϵϲ ϲϬͲϭϯϬ фϬ͘ϬϱϬ ƵŐͬ> ϰ͘ϲ ϰϬ ϳϵϮϲϱϴϵ WLJƌĞŶĞ ϮϬϭϱͬϬϲͬϬϵ ϵϮ ϲϬͲϭϯϬ ϴϯ ϲϬͲϭϯϬ фϬ͘ϬϮϬ ƵŐͬ> Ϭ͘ϰϲ ϰϬ ϳϵϮϲϱϴϵ YƵŝŶŽůŝŶĞ ϮϬϭϱͬϬϲͬϬϵ ϭϬϵ ϱϬͲϭϯϬ ϭϬϳ ϱϬͲϭϯϬ фϬ͘Ϯϰ ƵŐͬ> E;ϮͿ ϰϬ ϳϵϮϲϱϵϯ W,;ϭϬͲϭϵͿ ϮϬϭϱͬϬϲͬϬϴ ϭϬϳ ϱϬͲϭϯϬ ϭϭϮ ϱϬͲϭϯϬ Ϭ͘ϮϮ͕Z>сϬ͘ϮϬ ŵŐͬ> ϴ͘ϱ ϯϬ

WĂŐĞϱŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ Yh>/dz^^hZEZWKZd;KEdΖͿ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗:

DĂƚƌŝdž^ƉŝŬĞ ^ƉŝŬĞĚůĂŶŬ DĞƚŚŽĚůĂŶŬ ZW YĂƚĐŚ WĂƌĂŵĞƚĞƌ ĂƚĞ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ йZĞĐŽǀĞƌLJ Y>ŝŵŝƚƐ sĂůƵĞ hŶŝƚƐ sĂůƵĞ;йͿ Y>ŝŵŝƚƐ ϳϵϮϲϱϵϯ W,;ϭϵͲϯϮͿ ϮϬϭϱͬϬϲͬϬϴ ϭϭϬ ϱϬͲϭϯϬ ϭϭϳ ϱϬͲϭϯϬ фϬ͘ϮϬ ŵŐͬ> E ϯϬ ƵƉůŝĐĂƚĞ͗WĂŝƌĞĚĂŶĂůLJƐŝƐŽĨĂƐĞƉĂƌĂƚĞƉŽƌƚŝŽŶŽĨƚŚĞƐĂŵĞƐĂŵƉůĞ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƚŚĞǀĂƌŝĂŶĐĞŝŶƚŚĞŵĞĂƐƵƌĞŵĞŶƚ͘ DĂƚƌŝdž^ƉŝŬĞ͗ƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞŽĨŝŶƚĞƌĞƐƚŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞƐĂŵƉůĞŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ ^ƉŝŬĞĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžƐĂŵƉůĞƚŽǁŚŝĐŚĂŬŶŽǁŶĂŵŽƵŶƚŽĨƚŚĞĂŶĂůLJƚĞ͕ƵƐƵĂůůLJĨƌŽŵĂƐĞĐŽŶĚƐŽƵƌĐĞ͕ŚĂƐďĞĞŶĂĚĚĞĚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞŵĞƚŚŽĚĂĐĐƵƌĂĐLJ͘ DĞƚŚŽĚůĂŶŬ͗ďůĂŶŬŵĂƚƌŝdžĐŽŶƚĂŝŶŝŶŐĂůůƌĞĂŐĞŶƚƐƵƐĞĚŝŶƚŚĞĂŶĂůLJƚŝĐĂůƉƌŽĐĞĚƵƌĞ͘hƐĞĚƚŽŝĚĞŶƚŝĨLJůĂďŽƌĂƚŽƌLJĐŽŶƚĂŵŝŶĂƚŝŽŶ͘ ^ƵƌƌŽŐĂƚĞ͗ƉƵƌĞŽƌŝƐŽƚŽƉŝĐĂůůLJůĂďĞůĞĚĐŽŵƉŽƵŶĚǁŚŽƐĞďĞŚĂǀŝŽƌŵŝƌƌŽƌƐƚŚĞĂŶĂůLJƚĞƐŽĨŝŶƚĞƌĞƐƚ͘hƐĞĚƚŽĞǀĂůƵĂƚĞĞdžƚƌĂĐƚŝŽŶĞĨĨŝĐŝĞŶĐLJ͘ E;ƵƉůŝĐĂƚĞZWͿ͗dŚĞĚƵƉůŝĐĂƚĞZWǁĂƐŶŽƚĐĂůĐƵůĂƚĞĚ͘dŚĞĐŽŶĐĞŶƚƌĂƚŝŽŶŝŶƚŚĞƐĂŵƉůĞĂŶĚͬŽƌĚƵƉůŝĐĂƚĞǁĂƐƚŽŽůŽǁƚŽƉĞƌŵŝƚĂƌĞůŝĂďůĞZWĐĂůĐƵůĂƚŝŽŶ;ŽŶĞŽƌďŽƚŚƐĂŵƉůĞƐфϱdžZ>Ϳ͘ ;ϭͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽĚŝůƵƚŝŽŶƚŽďƌŝŶŐĂŶĂůLJƚĞǁŝƚŚŝŶƚŚĞĐĂůŝďƌĂƚĞĚƌĂŶŐĞ͘ ;ϮͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ ;ϯͿĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽŵĂƚƌŝdžŝŶƚĞƌĨĞƌĞŶĐĞ͘ĞƚĞĐƚŝŽŶůŝŵŝƚƐƌĂŝƐĞĚĚƵĞƚŽĚŝůƵƚŝŽŶƚŽďƌŝŶŐĂŶĂůLJƚĞǁŝƚŚŝŶƚŚĞĐĂůŝďƌĂƚĞĚƌĂŶŐĞ͘

WĂŐĞϲŽĨϭϬ DĂdždžĂŵŶĂůLJƚŝĐƐ/ŶƚĞƌŶĂƚŝŽŶĂůŽƌƉŽƌĂƚŝŽŶŽͬĂDĂdždžĂŵŶĂůLJƚŝĐƐƵƌŶĂďLJ͗ϰϲϬϲĂŶĂĚĂtĂLJsϱ'ϭ<ϱdĞůĞƉŚŽŶĞ;ϲϬϰͿϳϯϰͲϳϮϳϲ&Ădž;ϲϬϰͿϳϯϭͲϮϯϴϲ DĂdždžĂŵ:Žďη͗ϱϰϳϭϵϴ ,DDZEs/ZK,D/E͘ ZĞƉŽƌƚĂƚĞ͗ϮϬϭϱͬϬϲͬϬϵ ůŝĞŶƚWƌŽũĞĐƚη͗ϯϬϮͲϬϯϱ͘Ϭϰ ^ŝƚĞ>ŽĐĂƚŝŽŶ͗ EtZ/',dKEWZ< zŽƵƌW͘K͘η͗ϱϭϵϱϮϬϬϬ ^ĂŵƉůĞƌ/ŶŝƚŝĂůƐ͗: s>/d/KE^/'EdhZW'

dŚĞĂŶĂůLJƚŝĐĂůĚĂƚĂĂŶĚĂůůYĐŽŶƚĂŝŶĞĚŝŶƚŚŝƐƌĞƉŽƌƚǁĞƌĞƌĞǀŝĞǁĞĚĂŶĚǀĂůŝĚĂƚĞĚďLJƚŚĞĨŽůůŽǁŝŶŐŝŶĚŝǀŝĚƵĂů;ƐͿ͘

ZŽďZĞŝŶĞƌƚ͕ĂƚĂsĂůŝĚĂƚŝŽŶŽŽƌĚŝŶĂƚŽƌ

DĂdždžĂŵŚĂƐƉƌŽĐĞĚƵƌĞƐŝŶƉůĂĐĞƚŽŐƵĂƌĚĂŐĂŝŶƐƚŝŵƉƌŽƉĞƌƵƐĞŽĨƚŚĞĞůĞĐƚƌŽŶŝĐƐŝŐŶĂƚƵƌĞĂŶĚŚĂǀĞƚŚĞƌĞƋƵŝƌĞĚΗƐŝŐŶĂƚŽƌŝĞƐΗ͕ĂƐƉĞƌƐĞĐƚŝŽŶϱ͘ϭϬ͘ϮŽĨ/^Kͬ/ ϭϳϬϮϱ͗ϮϬϬϱ;Ϳ͕ƐŝŐŶŝŶŐƚŚĞƌĞƉŽƌƚƐ͘&Žƌ^ĞƌǀŝĐĞ'ƌŽƵƉƐƉĞĐŝĨŝĐǀĂůŝĚĂƚŝŽŶƉůĞĂƐĞƌĞĨĞƌƚŽƚŚĞsĂůŝĚĂƚŝŽŶ^ŝŐŶĂƚƵƌĞWĂŐĞ͘

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