Water Pollution Guiding Question: How Does Water Pollution Affect Humans and LESSON 3 Ecosystems?
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Section 1: Introduction (PDF)
SECTION 1: Introduction SECTION 1: INTRODUCTION Section 1 Contents The Purpose and Scope of This Guidance ....................................................................1-1 Relationship to CZARA Guidance ....................................................................................1-2 National Water Quality Inventory .....................................................................................1-3 What is Nonpoint Source Pollution? ...............................................................................1-4 Watershed Approach to Nonpoint Source Pollution Control .......................................1-5 Programs to Control Nonpoint Source Pollution...........................................................1-7 National Nonpoint Source Pollution Control Program .............................................1-7 Storm Water Permit Program .......................................................................................1-8 Coastal Nonpoint Pollution Control Program ............................................................1-8 Clean Vessel Act Pumpout Grant Program ................................................................1-9 International Convention for the Prevention of Pollution from Ships (MARPOL)...................................................................................................1-9 Oil Pollution Act (OPA) and Regulation ....................................................................1-10 Sources of Further Information .....................................................................................1-10 -
Water Quality Attribution and Simulation of Non-Point Source Pollution Load Fux in the Hulan River Basin Yan Liu1,2, Hongyan Li1,2*, Geng Cui3 & Yuqing Cao1,2
www.nature.com/scientificreports OPEN Water quality attribution and simulation of non-point source pollution load fux in the Hulan River basin Yan Liu1,2, Hongyan Li1,2*, Geng Cui3 & Yuqing Cao1,2 Surface water is the main source of irrigation and drinking water for rural communities by the Hulan River basin, an important grain-producing region in northeastern China. Understanding the spatial and temporal distribution of water quality and its driving forces is critical for sustainable development and the protection of water resources in the basin. Following sample collection and testing, the spatial distribution and driving forces of water quality were investigated using cluster analysis, hydrochemical feature partitioning, and Gibbs diagrams. The results demonstrated that the surface waters of the Hulan River Basin tend to be medium–weakly alkaline with a low degree of mineralization and water-rock interaction. Changes in topography and land use, confuence, application of pesticides and fertilizers, and the development of tourism were found to be important driving forces afecting the water quality of the basin. Non-point source pollution load fuxes of nitrogen (N) and phosphorus (P) were simulated using the Soil Water and Assessment Tool. The simulation demonstrated that the non-point source pollution loading is low upstream and increases downstream. The distributions of N and P loading varied throughout the basin. The fndings of this study provide information regarding the spatial distribution of water quality in the region and present a scientifc basis for future pollution control. Rivers are an important component of the global water cycle, connecting the two major ecosystems of land and sea and providing a critical link in the biogeochemical cycle. -
The Effect of Water Temperature on Aquatic Organisms: a Review of Knowledge and Methods for Assessing Biotic Responses to Temperature
The effect of water temperature on aquatic organisms: a review of knowledge and methods for assessing biotic responses to temperature Report to the Water Research Commission by Helen Dallas The Freshwater Consulting Group Freshwater Research Unit Department of Zoology University of Cape Town WRC Report No. KV 213/09 30 28 26 24 22 C) o 20 18 16 14 Temperature ( 12 10 8 6 4 Jul '92 Jul Oct '91 Apr '92 Jun '92 Jan '93 Mar '92 Feb '92 Feb '93 Aug '91 Nov '91 Nov '91 Dec Aug '92 Sep '92 '92 Nov '92 Dec May '92 Sept '91 Month and Year i Obtainable from Water Research Commission Private Bag X03 GEZINA, 0031 [email protected] The publication of this report emanates from a project entitled: The effect of water temperature on aquatic organisms: A review of knowledge and methods for assessing biotic responses to temperature (WRC project no K8/690). DISCLAIMER This report has been reviewed by the Water Research Commission (WRC) and approved for publication. Approval does not signify that the contents necessarily reflect the views and policies of the WRC, nor does mention of trade names or commercial products constitute endorsement or recommendation for use ISBN978-1-77005-731-9 Printed in the Republic of South Africa ii Preface This report comprises five deliverables for the one-year consultancy project to the Water Research Commission, entitled “The effect of water temperature on aquatic organisms – a review of knowledge and methods for assessing biotic responses to temperature” (K8-690). Deliverable 1 (Chapter 1) is a literature review aimed at consolidating available information pertaining to water temperature in aquatic ecosystems. -
Limitation of Primary Productivity in a Southwestern
37 MO i LIMITATION OF PRIMARY PRODUCTIVITY IN A SOUTHWESTERN RESERVOIR DUE TO THERMAL POLLUTION THESIS Presented to the Graduate Council of the North Texas State University in Partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE By Tom J. Stuart, B.S. Denton, Texas August, ]977 Stuart, Tom J., Limitation of Primary Productivity in a Southwestern Reseroir Due to Thermal Pollution. Master of Sciences (Biological Sciences), August, ]977, 53 pages, 6 tables, 7 figures, 55 titles. Evidence is presented to support the conclusions that (1) North Lake reservoir is less productive, contains lower standing crops of phytoplankton and total organic carbon than other local reservoirs; (2) that neither the phytoplankton nor their instantaneously-determined primary productivity was detrimentally affected by the power plant entrainment and (3) that the effect of the power plant is to cause nutrient limitation of the phytoplankton primary productivity by long- term, subtle, thermally-linked nutrient precipitation activities. ld" TABLE OF CONTENTS Page iii LIST OF TABLES.................. ----------- iv LIST OF FIGURES ........ ....- -- ACKNOWLEDGEMENTS .-................ v Chapter I. INTRODUCTION. ...................... 1 II. METHODS AND MATERIALS ........ 5 III. RESULTS AND DISCUSSION................ 11 Phytoplankton Studies Primary Productivity Studies IV. CONCLUSIONS. ............................ 40 APPENDIX. ............................... 42 REFERENCES.........-....... ... .. 49 ii LIST OF TABLES Table Page 1. Selected Comparative Data from Area Reservoirs Near North Lake.............................18 2. List of Phytoplankton Observed in North Lake .. 22 3. Percentage Composition of Phytoplankton in North Lake. ................................. 28 4. Values of H.Computed for Phytoplankton Volumes and Cell Numbers for North Lake ............ 31 5. Primary Production Values Observed in Various Lakes of the World in Comparison to North Lake. -
Determination of Thermal Pollution Effect on End Part of Stream Mahmoud, Amaal, O
International Journal of Innovative Technology and Exploring Engineering (IJITEE) ISSN: 2278-3075, Volume-9 Issue-3, January 2020 Determination of Thermal Pollution Effect on End Part of Stream Mahmoud, Amaal, O. F., El Nadi, M.H., Nasr, N. A.H., Ezat, M.B. In view of these developments, a variety of new ABSTRACT-The present study was conducted to evaluate the energy infrastructures to meet the demands for population environmental impact of thermal effluent sources on the main growth that lead the decision makers to redirect the rudder water quality parameters at the low flow conditions. The low flow towards the power plants. That was in order to provide a causes the flow velocity to be low which causes accumulation of continuous source of electricity as a clean and renewable any pollutant source. The study was performed by creating a 2-d model of the last reach of Rosetta branch at winter closure. Delft source of energy. Contrariwise, Power plants might cause 3d software is used to create a hydro-dynamic model to simulate Intensive damages on the environment. If these damages the flow pattern within a 5 km of the branch upstream Edfina were not studied and carefully planned before construction regulator. Water quality model is coupled afterwards to simulate and operation, therefore impact assessment of power plants the water quality parameters. A base case scenario of the current is nesses. Egypt also faced same challenges in consuming state at the low flow condition is set up and calibrated. Another the massive amount of energy in the past few years, can be scenario is performed after adding a thermal pollutant source. -
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. -
Thermal Pollution Abatement Evaluation Model for Power Plant Siting
THERMAL POLLUTION ABATEMENT EVALUATION MODEL FOR POWER PLANT SITING P. F. Shiers D. H. Marks Report #MIT-EL 73-013 February 1973 a" pO ENERGY LABORATORY The Energy Laboratory was established by the Massachusetts Institute of Technology as a Special Laboratory of the Institute for research on the complex societal and technological problems of the supply, demand and consumptionof energy. Its full-time staff assists in focusing the diverse research at the Institute to permit undertaking of long term interdisciplinary projects of considerable magnitude. For any specific program, the relative roles of the Energy Laboratory, other special laboratories, academic departments and laboratories depend upon the technologies and issues involved. Because close coupling with the nor- .ral academic teaching and research activities of the Institute is an important feature of the Energy Laboratory, its principal activities are conducted on the Institute's Cambridge Campus. This study was done in association with the Electric Power Systems Engineering Laboratory and the Department of Civil Engineering (Ralph H. Parsons Laboratory for Water Resources and Hydrodynamics and the Civil Engineering Systems Laboratory). -Offtl -. W% ABSTRACT A THERMAL POLLUTION ABATE.ENT EVALUATION MODEL FOR POWER PLANT SITING A thermal pollution abatement model for power plant siting is formulated to evaluate the economic costs, resource requirements, and physical characteristics of a particular thermal pollution abatement technology at a given site type for a plant alternative. The model also provides a screening capability to determine which sites are feasible alternatives for development by the calculation of the resource requirements and a check of the applicable thermal standards, and determining whether the plant alternative could be built on the available site in compliance with the thermal standards. -
Brief for Petitioner ————
No. 18-260 IN THE Supreme Court of the United States ———— COUNTY OF MAUI, Petitioner, v. HAWAI‘I WILDLIFE FUND; SIERRA CLUB - MAUI GROUP; SURFRIDER FOUNDATION; WEST MAUI PRESERVATION ASSOCIATION, Respondents. ———— On Writ of Certiorari to the United States Court of Appeals for the Ninth Circuit ———— BRIEF FOR PETITIONER ———— COUNTY OF MAUI HUNTON ANDREWS KURTH LLP MOANA M. LUTEY ELBERT LIN RICHELLE M. THOMSON Counsel of Record 200 South High Street MICHAEL R. SHEBELSKIE Wailuku, Maui, Hawai‘i 96793 951 East Byrd Street, East Tower (808) 270-7740 Richmond, Virginia 23219 [email protected] (804) 788-8200 COLLEEN P. DOYLE DIANA PFEFFER MARTIN 550 South Hope Street Suite 2000 Los Angeles, California 90071 (213) 532-2000 Counsel for Petitioner May 9, 2019 WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – WASHINGTON, D. C. 20002 i QUESTION PRESENTED In the Clean Water Act (CWA), Congress distin- guished between the many ways that pollutants reach navigable waters. It defined some of those ways as “point sources”—namely, pipes, ditches, and other “discernible, confined and discrete conveyance[s] … from which pollutants are or may be discharged.” 33 U.S.C. § 1362(14). The remaining ways of moving pollutants, like runoff or groundwater, are “nonpoint sources.” The CWA regulates pollution added to navigable waters “from point sources” differently than pollution added “from nonpoint sources.” It controls point source pollution through permits, e.g., id. § 1342, while nonpoint source pollution is controlled through federal oversight of state management programs, id. § 1329. Nonpoint source pollution is also addressed by other state and federal environmental laws. The question presented is: Whether the CWA requires a permit when pollu- tants originate from a point source but are conveyed to navigable waters by a nonpoint source, such as groundwater. -
Point Sources of Pollution - Yuhei Inamori, Naoshi Fujimoto
WATER QUALITY AND STANDARDS - Vol. II - Point Sources of Pollution - Yuhei Inamori, Naoshi Fujimoto POINT SOURCES OF POLLUTION Yuhei Inamori National Institute for Environmental Studies, Tsukuba, Japan, and Naoshi Fujimoto Faculty of Applied Bioscience, Tokyo University of Agriculture, Tokyo, Japan Keywords: organic matter, nitrogen, phosphorus, heavy metals, domestic wastewater, food industry, chemical industry, activated sludge process, biofilm process, anaerobic treatment Contents 1. Introduction 2. Kind of point sources 2.1. Percentage of point source loading to total pollution loading 2.2. Domestic wastewater 2.3. Industrial wastewater 2.3.1. Food industry 2.3.2. Chemical industry 2.3.3. Livestock industry and fish farm 3. Countermeasures for point sources 4. Wastewater treatment processes 4.1. Activated sludge process and modified process 4.2. Biofilm process 4.3. Anaerobic treatment 4.4. Thermophilic oxic process Glossary Bibliography Biographical Sketches Summary Point source loading refers to pollutants produced by identified pollution sources. Point source loadings include treated and untreated wastewater from factories, domestic wastewater,UNESCO treated water from sewerage – treatment EOLSS plants, and wastewater from feedlots and fish farms. Organic matter, nitrogen and phosphorus are discharged into water bodies by inflowSAMPLE of domestic wastewater andCHAPTERS industrial wastewater causing organic pollution and eutrophication. The point source loading of organic matter, nitrogen, and phosphorus as percentages of the total loading in Lake Kasumigaura in Japan are 55%, 58%, and 77% respectively. Among point source loadings, the largest loading is domestic wastewater, which supplies 33% of CODMn, 34% of nitrogen and 45% of phosphorus. In Japan, the amount of wastewater, BOD, nitrogen and phosphorus were calculated approximately to 200 L, 40g, 10g, and 1g, respectively, per person per day. -
Keeping the Clean Water Act Cooperatively Federal—Or, Why the Clean Water Act Does Not Directly Regulate Groundwater Pollution
William & Mary Environmental Law and Policy Review Volume 42 (2017-2018) Issue 2 Article 3 February 2018 Keeping the Clean Water Act Cooperatively Federal—Or, Why the Clean Water Act Does Not Directly Regulate Groundwater Pollution Damien Schiff Follow this and additional works at: https://scholarship.law.wm.edu/wmelpr Part of the Environmental Law Commons, and the Water Resource Management Commons Repository Citation Damien Schiff, Keeping the Clean Water Act Cooperatively Federal—Or, Why the Clean Water Act Does Not Directly Regulate Groundwater Pollution, 42 Wm. & Mary Envtl. L. & Pol'y Rev. 447 (2018), https://scholarship.law.wm.edu/wmelpr/vol42/iss2/3 Copyright c 2018 by the authors. This article is brought to you by the William & Mary Law School Scholarship Repository. https://scholarship.law.wm.edu/wmelpr KEEPING THE CLEAN WATER ACT COOPERATIVELY FEDERAL—OR, WHY THE CLEAN WATER ACT DOES NOT DIRECTLY REGULATE GROUNDWATER POLLUTION DAMIEN SCHIFF* INTRODUCTION The Clean Water Act1 is the leading federal environmental law regulating water pollution.2 In recent years, its scope and application to normal land-use activities have become extremely contentious.3 Yet, despite the growing controversy, the environmental community contin- ues to try to extend the Act’s reach.4 One of its most recent efforts has focused on expanding the Act to groundwater pollution.5 In this Article * Senior Attorney, Pacific Legal Foundation. 1 33 U.S.C. §§ 1251–1388. The Act’s formal title is the Federal Water Pollution Control Act Amendments of 1972. See Pub. L. No. 92-500, § 1, 86 Stat. 816 (Oct. 18, 1972). -
Modeling Spatial Distributions of Point and Nonpoint Source Pollution Loadings in the Great Lakes Watersheds
International Journal of Environmental Science and Engineering 2:1 2010 Modeling Spatial Distributions of Point and Nonpoint Source Pollution Loadings in the Great Lakes Watersheds ∗ Chansheng He and Carlo DeMarchi Examples of the models include ANSWERS (Areal Nonpoint Abstract—A physically based, spatially-distributed water quality Source Watershed Environment Simulation) [3], CREAMS model is being developed to simulate spatial and temporal (Chemicals, Runoff and Erosion from Agricultural distributions of material transport in the Great Lakes Watersheds of Management Systems) [22], GLEAMS (Groundwater Loading the U.S. Multiple databases of meteorology, land use, topography, Effects of Agricultural Management Systems) [23], AGNPS hydrography, soils, agricultural statistics, and water quality were used (Agricultural Nonpoint Source Pollution Model) [39], EPIC to estimate nonpoint source loading potential in the study watersheds. HSPF Animal manure production was computed from tabulations of animals (Erosion Productivity Impact Calculator) [34], by zip code area for the census years of 1987, 1992, 1997, and 2002. (Hydrologic Simulation Program in FORTRAN) [5], and SWAT Relative chemical loadings for agricultural land use were calculated (Soil and Water Assessment Tool) [2], to name a few. from fertilizer and pesticide estimates by crop for the same periods. However, these models are either empirically based, or Comparison of these estimates to the monitored total phosphorous spatially lumped or semi-distributed, or do not consider load indicates that both point and nonpoint sources are major nonpoint sources from animal manure and combined sewer contributors to the total nutrient loads in the study watersheds, with overflows (CSOs). To meet this need, the National Oceanic nonpoint sources being the largest contributor, particularly in the rural and Atmospheric Administration (NOAA) Great Lakes watersheds. -
Phytoplankton Communities Impacted by Thermal Effluents Off Two Coastal Nuclear Power Plants in Subtropical Areas of Northern Taiwan
Terr. Atmos. Ocean. Sci., Vol. 27, No. 1, 107-120, February 2016 doi: 10.3319/TAO.2015.09.24.01(Oc) Phytoplankton Communities Impacted by Thermal Effluents off Two Coastal Nuclear Power Plants in Subtropical Areas of Northern Taiwan Wen-Tseng Lo1, Pei-Kai Hsu1, Tien-Hsi Fang 2, Jian-Hwa Hu 2, and Hung-Yen Hsieh 3, 4, * 1 Institute of Marine Biotechnology and Resources, National Sun Yat-sen University, Kaohsiung, Taiwan, R.O.C. 2 Department of Marine Environmental Informatics, National Taiwan Ocean University, Keelung, Taiwan, R.O.C. 3 Graduate Institute of Marine Biology, National Dong Hwa University, Pingtung, Taiwan, R.O.C. 4 National Museum of Marine Biology and Aquarium, Pingtung, Taiwan, R.O.C. Received 30 December 2014, revised 21 September 2015, accepted 24 September 2015 ABSTRACT This study investigates the seasonal and spatial differences in phytoplankton communities in the coastal waters off two nuclear power plants in northern Taiwan in 2009. We identified 144 phytoplankton taxa in our samples, including 127 diatoms, 16 dinoflagellates, and one cyanobacteria. Four diatoms, namely, Thalassionema nitzschioides (T. nitzschioides), Pseudo-nitzschia delicatissima (P. delicatissima), Paralia sulcate (P. sulcata), and Chaetoceros curvisetus (C. curvisetus) and one dinoflagellate Prorocentrum micans (P. micans) were predominant during the study period. Clear seasonal and spatial differences in phytoplankton abundance and species composition were evident in the study area. Generally, a higher mean phytoplankton abundance was observed in the waters off the First Nuclear Power Plant (NPP I) than at the Second Nuclear Power Plant (NPP II). The phytoplankton abundance was usually high in the coastal waters during warm periods and in the offshore waters in winter.