Global Drinking Water Quality Index: Development and Sensitivity Analysis
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Pomorskie Voivodeship Development Strategy 2020
Annex no. 1 to Resolution no. 458/XXII/12 Of the Sejmik of Pomorskie Voivodeship of 24th September 2012 on adoption of Pomorskie Voivodeship Development Strategy 2020 Pomorskie Voivodeship Development Strategy 2020 GDAŃSK 2012 2 TABLE OF CONTENTS I. OUTPUT SITUATION ………………………………………………………… 6 II. SCENARIOS AND VISION OF DEVELOPMENT ………………………… 18 THE PRINCIPLES OF STRATEGY AND ROLE OF THE SELF- III. 24 GOVERNMENT OF THE VOIVODESHIP ………..………………………… IV. CHALLENGES AND OBJECTIVES …………………………………………… 28 V. IMPLEMENTATION SYSTEM ………………………………………………… 65 3 4 The shape of the Pomorskie Voivodeship Development Strategy 2020 is determined by 8 assumptions: 1. The strategy is a tool for creating development targeting available financial and regulatory instruments. 2. The strategy covers only those issues on which the Self-Government of Pomorskie Voivodeship and its partners in the region have a real impact. 3. The strategy does not include purely local issues unless there is a close relationship between the local needs and potentials of the region and regional interest, or when the local deficits significantly restrict the development opportunities. 4. The strategy does not focus on issues of a routine character, belonging to the realm of the current operation and performing the duties and responsibilities of legal entities operating in the region. 5. The strategy is selective and focused on defining the objectives and courses of action reflecting the strategic choices made. 6. The strategy sets targets amenable to verification and establishment of commitments to specific actions and effects. 7. The strategy outlines the criteria for identifying projects forming part of its implementation. 8. The strategy takes into account the specific conditions for development of different parts of the voivodeship, indicating that not all development challenges are the same everywhere in their nature and seriousness. -
Water Quality Conditions in the United States a Profile from the 1998 National Water Quality Inventory Report to Congress
United States Office of Water (4503F) EPA841-F-00-006 Environmental Protection Washington, DC 20460 June 2000 Agency Water Quality Conditions in the United States A Profile from the 1998 National Water Quality Inventory Report to Congress States, tribes, territories, and interstate commissions report that, in 1998, about 40% of U.S. streams, lakes, and estuaries that were assessed were not clean enough to support uses such as fishing and swimming. About 32% of U.S. waters were assessed for this national inventory of water quality. Leading pollutants in impaired waters include siltation, bacteria, nutrients, and metals. Runoff from agricultural lands and urban areas are the primary sources of these pollu- tants. Although the United States has made significant progress in cleaning up polluted waters over the past 30 years, much remains to be done to restore and protect the nation’s waters. Findings States also found that 96% of assessed Great Lakes shoreline miles are impaired, primarily due to pollut- Recent water quality data find that more than ants in fish tissue at levels that exceed standards to 291,000 miles of assessed rivers and streams do not protect human health. States assessed 90% of Great meet water quality standards. Across all types of water- Lakes shoreline miles. bodies, states, territories, tribes, and other jurisdictions report that poor water quality affects aquatic life, fish Wetlands are being lost in the contiguous United consumption, swimming, and drinking water. In their States at a rate of about 100,000 acres per year. Eleven 1998 reports, states assessed 840,000 miles of rivers states and tribes listed sources of recent wetland loss; and 17.4 million acres of lakes, including 150,000 conversion for agricultural uses, road construction, and more river miles and 600,000 more lake acres than residential development are leading reasons for loss. -
2021 Water Quality Report
2021 WATER QUALITY REPORT 2021 WATER QUALITY REPORT CITY OF NEWARK: SOUTH WELL FIELD TREATMENT PLANT AIR STRIPPER BUILDING Annual Water Quality Report The Environmental Protection Agency (EPA) Newark meets or exceeds the water quality requires public water suppliers to provide standards of the Delaware Division of Public consumer confidence reports (CCR) to their Health Office of Drinking Water and the customers . These reports are also known as Environmental Protection Agency. The tables on annual water quality reports. The below report pages 4-6 of this report list those substances summarizes information regarding the sources found in our finished water during calendar year used (i.e. rivers, reservoirs, or aquifers), any 2020. detected contaminants, compliance and educational efforts. How the Water is Treated The City’s 317 million gallon reservoir provides a Drinking water, including bottled water, may At the Curtis Water Treatment Plant (CWTP), reliable source of raw water which can be treated reasonably be expected to contain at least small water from the White Clay Creek is clarified with and ready for drinking in times of heavy rain or amounts of some substances. The presence of alum and polymer and then filtered to remove drought. In an effort to keep sediment these substances does not necessarily indicate impurities. Chlorine is added to kill harmful accumulation in our water mains to a minimum, that water poses a health risk. In order to ensure bacteria and viruses. Finally, fluoride is added to we flush the entire system yearly. that tap water is safe to drink, the EPA prescribes the water to protect your teeth. -
Impact of the Artificial Strait in the Vistula Spit on the Hydrodynamics
water Article Impact of the Artificial Strait in the Vistula Spit on the Hydrodynamics of the Vistula Lagoon (Baltic Sea) Michał Szydłowski * , Tomasz Kolerski and Piotr Zima Faculty of Civil and Environmental Engineering, Gda´nskUniversity of Technology, Narutowicza 11/12, 80-233 Gda´nsk,Poland; [email protected] (T.K.); [email protected] (P.Z.) * Correspondence: [email protected]; Tel.: +48-58-347-1809 Received: 25 March 2019; Accepted: 8 May 2019; Published: 10 May 2019 Abstract: In the Vistula Lagoon, storm surges are induced by variable sea levels in the Gulf of Gda´nsk and wind action. The rising of the water level in the southern part of the basin, exceeding 1.0 m above mean sea level, can be dangerous for the lowland area of Zuławy˙ Elbl ˛askie,causing the inundation of the polders adjacent to the lagoon. One of the potential possibilities to limit the flood risk is to decrease the water level in the lagoon during strong storm surges by opening an artificial canal to join the lagoon with the Gulf of Gda´nsk.The decision to build a new strait in the Vistula Spit was made in 2017. In order to analyze the impact of the artificial connection between the sea and the lagoon during periods of high water stages in the southern part the lagoon, mathematical modelling of the hydrodynamics of the Vistula Lagoon is required. This paper presents the shallow water equations (SWEs) model adapted to simulate storm surges driven by the wind and sea tides, and the numerical results obtained for the present (without the new strait) and future (with the new strait) configuration of the Vistula Lagoon. -
Evaluating Residential Indoor Air Quality Concerns1
Designation: D7297 – 06 Standard Practice for Evaluating Residential Indoor Air Quality Concerns1 This standard is issued under the fixed designation D7297; the number immediately following the designation indicates the year of original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A superscript epsilon (´) indicates an editorial change since the last revision or reapproval. 1. Scope 2. Referenced Documents 1.1 This standard practice describes procedures for evaluat- 2.1 ASTM Standards:2 ing indoor air quality (IAQ) concerns in residential buildings. D1356 Terminology Relating to Sampling and Analysis of 1.2 The practice primarily addresses IAQ concerns encoun- Atmospheres tered in single-family detached and attached (for example, D1357 Practice for Planning the Sampling of the Ambient townhouse or duplex design) residential buildings. Limited Atmosphere guidance is also included for low- and high-rise multifamily D4861 Practice for Sampling and Selection of Analytical dwellings. Techniques for Pesticides and Polychlorinated Biphenyls 1.3 The IAQ evaluation procedures are comprised of inter- in Air views with the homeowner or resident(s) (including telephone D4947 Test Method for Chlordane and Heptachlor Residues interviews and face-to-face meetings) and on-site investiga- in Indoor Air tions (including walk-through, assessment, and measure- D5197 Test Method for Determination of Formaldehyde ments). For practicality in application, these procedures are and Other Carbonyl Compounds in Air (Active Sampler dividing into three separate phases. Methodology) 1.4 The procedures described in this standard practice are D5438 Practice for Collection of Floor Dust for Chemical aimed at identifying potential causes contributing to the IAQ Analysis concern. -
Diffuse Pollution, Degraded Waters Emerging Policy Solutions
Diffuse Pollution, Degraded Waters Emerging Policy Solutions Policy HIGHLIGHTS Diffuse Pollution, Degraded Waters Emerging Policy Solutions “OECD countries have struggled to adequately address diffuse water pollution. It is much easier to regulate large, point source industrial and municipal polluters than engage with a large number of farmers and other land-users where variable factors like climate, soil and politics come into play. But the cumulative effects of diffuse water pollution can be devastating for human well-being and ecosystem health. Ultimately, they can undermine sustainable economic growth. Many countries are trying innovative policy responses with some measure of success. However, these approaches need to be replicated, adapted and massively scaled-up if they are to have an effect.” Simon Upton – OECD Environment Director POLICY H I GH LI GHT S After decades of regulation and investment to reduce point source water pollution, OECD countries still face water quality challenges (e.g. eutrophication) from diffuse agricultural and urban sources of pollution, i.e. pollution from surface runoff, soil filtration and atmospheric deposition. The relative lack of progress reflects the complexities of controlling multiple pollutants from multiple sources, their high spatial and temporal variability, the associated transactions costs, and limited political acceptability of regulatory measures. The OECD report Diffuse Pollution, Degraded Waters: Emerging Policy Solutions (OECD, 2017) outlines the water quality challenges facing OECD countries today. It presents a range of policy instruments and innovative case studies of diffuse pollution control, and concludes with an integrated policy framework to tackle this challenge. An optimal approach will likely entail a mix of policy interventions reflecting the basic OECD principles of water quality management – pollution prevention, treatment at source, the polluter pays and the beneficiary pays principles, equity, and policy coherence. -
Sediment Transport Along the Vistula Spit (The Baltic Sea)
Russian Science Foundation Project No 14-17-00547 “A forecast development for evolution of accumulative Russian coasts of tideless seas” Laboratory for Coastal Systems Study Sediment transport along the Vistula Spit (the Baltic Sea) Boris Chubarenko, Aleksander Babakov Laboratory for Coastal System Study, Atlantic Branch of P.P.Shirshov Institute of Oceanology Russian Academy of Sciences EMECS11 – Sea Coasts XXVI Joint Conference, August 22-27, 2016 Study area Vistula Lagoon and Vistula Spit belong to the sediment-system of the Gulf of Gdansk Gulf of Gdansk Kaliningrad RUSSIA (Kaliningrad Oblast) Gdansk POLAND Chubarenko B.V., Babakov A.N. Sediment transport along the Vistula Spit (the Baltic Sea). EMECS11 – Sea Coasts XXVI Joint Conference, Sain-Petersburg (Russia), August 22-27, 2016 Study area Historical changes in hydrographic scheme of the Visula Lagoon New outlet of the Vistula River was artificially Pregola River constructed between 1889 and 1895 and officially opened on 31 March 1895 RU Nogat River took up to 85% from the Vistula PL River discharge. Sluice ‘Biala Gora Lock’ was constructed Old Vistula River Delta at the Visla-Nogat divergence point in 1915. It finally separated the Vistula Lagoon from the Vistula River. (Presentation of P. Margonsku, MIR, ARTWEI Project) Motivation Convergence of fluxes at the Yantarny- Unidirectional flux to south Convergence of fluxes at the Baltiysk concave [Beloshapkov, [Zenkovich, 1958] Vistula Lagoon inlet [Boldyrev, Beloshapkova, Brasavs, 1984] Zenkovich, 1982] [Ostrowski, Pruszak, Skaja, [Leontjev, 2012] Convergence of fluxes at the Szmytkiewicz, 2010] central part of the Vistula Spit [Babakov, 2003] Convergence of fluxes at the southern part of the Vistula Spit Chubarenko B.V., Babakov A.N. -
Monitoring Water Quality & Quantity in Mining
SURFACE & GROUNDWATER / ENVIRONMENT & ECOSYSTEMS DHI SOLUTION MONITORING WATER QUALITY & QUANTITY IN MINING Environmental monitoring - tailor-made! ENVIRONMENTAL MONITORING - THE KEY TO KNOWLEDGE SUMMARY Regardless of the project, monitoring is a crucial element of gaining knowledge CLIENT about environmental conditions. When it comes to monitoring water, it is essential The mining industry and associated to do this in an optimal way so as to provide only the necessary information, which companies can be used for specific actions. Too many monitoring programmes have been established with the aim to know everything, which eventually leads to enormous CHALLENGE amount of data but not knowledge. Assessment of water quality and quantity Water is linked to nearly every type of mining industry, whether as groundwater, Collect the right variables surface water coastal water, or process/wastewater and accordingly there is a Fulfill the regulations substantial need to assess water quality and quantity conditions in all phases of Ensure scientifically sound judgement of mining: exploration, operation/production and decommissioning. impacts We at DHI work with tailor-made monitoring, which enables the client to get all the SOLUTION relevant data - and only those. To provide tailor-made monitoring based on the relevant data Changes in water quality can Applying state-of-the-art technologies as lead to many types of impacts part of the monitoring and the mining industry unfortunately creates various VALUE such problems. One of the Optimisation of monitoring costs standard impacts comes from Fast delivery of data acid drainage of the mines or Easier compliance with permits the mine-tailing and has multiple impacts on not just the biology but also on water which is taken downstream for domestic or industrial use. -
Modification of the Water Quality Index (WQI)
water Review Modification of the Water Quality Index (WQI) Process for Simple Calculation Using the Multi-Criteria Decision-Making (MCDM) Method: A Review Naseem Akhtar 1 , Muhammad Izzuddin Syakir Ishak 1,2,*, Mardiana Idayu Ahmad 1 , Khalid Umar 3 , Mohamad Shaiful Md Yusuff 1, Mohd Talha Anees 4, Abdul Qadir 5 and Yazan Khalaf Ali Almanasir 1 1 School of Industrial Technology, Division of Environmental Technology, Universiti Sains Malaysia, Gelugor 11800, Pulau Pinang, Malaysia; [email protected] (N.A.); [email protected] (M.I.A.); [email protected] (M.S.M.Y.); [email protected] (Y.K.A.A.) 2 Centre for Global Sustainability Studies, Universiti Sains Malaysia, Gelugor 11800, Pulau Pinang, Malaysia 3 School of Chemical Sciences, Universiti Sains Malaysia, Gelugor 11800, Pulau Pinang, Malaysia; [email protected] 4 Department of Geology, Faculty of Science, University of Malaya, Petaling Jaya 50603, Kuala Lumpur, Malaysia; [email protected] 5 School of Physics, Universiti Sains Malaysia, Gelugor 11800, Pulau Pinang, Malaysia; [email protected] * Correspondence: [email protected] Abstract: Human activities continue to affect our water quality; it remains a major problem world- wide (particularly concerning freshwater and human consumption). A critical water quality index Citation: Akhtar, N.; Ishak, M.I.S.; (WQI) method has been used to determine the overall water quality status of surface water and Ahmad, M.I.; Umar, K.; Md Yusuff, groundwater systems globally since the 1960s. WQI follows four steps: parameter selection, sub- M.S.; Anees, M.T.; Qadir, A.; Ali indices, establishing weights, and final index aggregation, which are addressed in this review. -
The Lower Vistula in the Aspect of the E40 and E70 International Shipping Routes
Ż. Marciniak | Acta Energetica 2/15 (2013) | 153–161 The lower Vistula in the aspect of the E40 and E70 international shipping routes Author Żaneta Marciniak Keywords shipping route, waterways, inland navigation, E40 international waterway, E70 international waterway Abstract Throughout the history of Europe and the world, shipping routes have determined the develop- ment of many civilisations, since it was along them that settlements and commerce developed, goods and people were transported, and later, industry was located. Currently, shipping routes are an important element in inland transport corridors. The European Union puts particular emphasis on the development of inland and rail transport to balance road transport, which is drastically expanding. Development of inland waterway transport routes in Poland has allies in intensely developing sea ports. The allies of the lower Vistula (dolna Wisła) are the ports in Gdańsk and Gdynia, for which construction of inland ports up-country is an opportunity to increase the trans-shipment capacity. Poland uses the potential of international inland waterways poorly when compared to other European Union countries, which results for instance from the bad technical condition of river engineering structures and from years of neglect in water management. The situation is further amplified by the lack of consistent laws regarding inland navigation and water management, as the responsibility for those issues is shared by several ministries, the institutions they are in charge of and local governments. Governments of the voivodeships situated along the planned international waterways E40 between Warsaw and Gdańsk (Mazowieckie, Kujawsko-Pomorskie, Pomorskie voivodeships) and E70 (Lubuskie, Wielkopolskie, Kujawsko-Pomorskie, Warmińsko-Mazurskie, Pomorskie voivode- ships) can see both the transport and the tourism potential of Polish waterways. -
Water Quality Criteria
Office of Water EPA 823 -B -17 -001 2017 Water Quality Standards Handbook Chapter 3: Water Quality Criteria The WQS Handbook does not impose legally binding requirements on the EPA, states, tribes or the regulated community, nor does it confer legal rights or impose legal obligations upon any member of the public. The Clean Water Act (CWA) provisions and the EPA regulations described in this document contain legally binding requirements. This document does not constitute a regulation, nor does it change or substitute for any CWA provision or the EPA regulations. Water Quality Standards Handbook Chapter 3: Water Quality Criteria (40 CFR 131.11) Table of Contents Introduction .................................................................................................................................................. 1 3.1 Water Quality Criteria ............................................................................................................................. 1 Toxic and Priority Pollutants ..................................................................................................................... 1 3.2 Forms of Water Quality Criteria .............................................................................................................. 4 3.2.1 Numeric Water Quality Criteria ....................................................................................................... 4 3.2.2 Narrative Water Quality Criteria ..................................................................................................... -
Water Quality and Biodiversity of Lønningsbekk Creek
Lønningsbekk 2014 WATER QUALITY AND BIODIVERSITY OF LØNNINGSBEKK CREEK Group 6 Siri Vatsø Haugum Eihab Idris Eugene Kitsios Imelda Rantty Kåre Andreas Thorsen The University of Bergen BIO 300 UiB Group 6 : Siri Vatsø Haugum, Eihab Idris, Eugene Kitsios, Imelda Rantty, Kåre Andreas Thorsen 1 Lønningsbekk 2014 Table of Contents 1. Introduction………………………………………………………………………………….. 4 1.1 The environmental impact of concrete production……………………….. 4 1.2 Abiotic factors ………………………………………………………………………………. 5 1.3 Thermotolerant Coliform Bacteria ………………………………………………… 6 1.4 Phosphorus ………………………………………………………………………………….. 6 1.5 Benthic macroinvertebrates as ecological indicators …………………… 7 1.6 Aim of study 8 2. Materials and Methods ……………………………………………………………….. 9 2.1 Study area ……………………………………………………………………………………. 9 2.2 Sampling Procedures ……………………………………………………………………. 12 2.2.1 Thermotolerant Coliform Bacteria ………………………………………………… 12 2.2.2 Phosphorus…………………………………………………………………………………… 12 2.2.3 Temperature, conductivity, pH, dissolved oxygen, salinity and 13 velocity ………………………………………………………………………………………… 2.2.4 Creek Flow Rate …………………………………………………………………………… 13 2.2.5a Biodiversity …………………………………………………………………………………. 14 2.2.5b Laboratory investigations ……………………………………………………………. 14 2.2.5c Biodiversity analysis ……………………………………………………………………. 15 3. Results …………………………………………………………………………………………. 17 3.1 Thermotolerant Coliform Bacteria ………………………………………………… 17 3.2 Phosphorus ………………………………………………………………………………….. 18 3.3 Temperature, conductivity, pH, dissolved oxygen, salinity and 20 velocity ………………………………………………………………………………………….