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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. -
Sources and Emissions of Air Pollutants
© Jones & Bartlett Learning, LLC. NOT FOR SALE OR DISTRIBUTION Chapter 2 Sources and Emissions of Air Pollutants LEArning ObjECtivES By the end of this chapter the reader will be able to: • distinguish the “troposphere” from the “stratosphere” • define “polluted air” in relation to various scientific disciplines • describe “anthropogenic” sources of air pollutants and distinguish them from “natural” sources • list 10 sources of indoor air contaminants • identify three meteorological factors that affect the dispersal of air pollutants ChAPtEr OutLinE I. Introduction II. Measurement Basics III. Unpolluted vs. Polluted Air IV. Air Pollutant Sources and Their Emissions V. Pollutant Transport VI. Summary of Major Points VII. Quiz and Problems VIII. Discussion Topics References and Recommended Reading 21 2 N D R E V I S E 9955 © Jones & Bartlett Learning, LLC. NOT FOR SALE OR DISTRIBUTION 22 Chapter 2 SourCeS and EmiSSionS of Air PollutantS i. IntrOduCtiOn level. Mt. Everest is thus a minute bump on the globe that adds only 0.06 percent to the Earth’s diameter. Structure of the Earth’s Atmosphere The Earth’s atmosphere consists of several defined layers (Figure 2–1). The troposphere, in which all life The Earth, along with Mercury, Venus, and Mars, is exists, and from which we breathe, reaches an altitude of a terrestrial (as opposed to gaseous) planet with a per- about 7–8 km at the poles to just over 13 km at the equa- manent atmosphere. The Earth is an oblate (slightly tor: the mean thickness being 9.1 km (5.7 miles). Thus, flattened) sphere with a mean diameter of 12,700 km the troposphere represents a very thin cover over the (about 8,000 statute miles). -
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. -
DOE-HDBK-1122-99; Radiological Control Technician Training
DOE-HDBK-1122-99 Module 1.11 External Exposure Control Study Guide Course Title: Radiological Control Technician Module Title: External Exposure Control Module Number: 1.11 Objectives: 1.11.01 Identify the four basic methods for minimizing personnel external exposure. 1.11.02 Using the Exposure Rate = 6CEN equation, calculate the gamma exposure rate for specific radionuclides. 1.11.03 Identify "source reduction" techniques for minimizing personnel external exposures. 1.11.04 Identify "time-saving" techniques for minimizing personnel external exposures. 1.11.05 Using the stay time equation, calculate an individual's remaining allowable dose equivalent or stay time. 1.11.06 Identify "distance to radiation sources" techniques for minimizing personnel external exposures. 1.11.07 Using the point source equation (inverse square law), calculate the exposure rate or distance for a point source of radiation. 1.11.08 Using the line source equation, calculate the exposure rate or distance for a line source of radiation. 1.11.09 Identify how exposure rate varies depending on the distance from a surface (plane) source of radiation, and identify examples of plane sources. 1.11.10 Identify the definition and units of "mass attenuation coefficient" and "linear attenuation coefficient". 1.11.11 Identify the definition and units of "density thickness." 1.11.12 Identify the density-thickness values, in mg/cm2, for the skin, the lens of the eye and the whole body. 1.11.13 Calculate shielding thickness or exposure rates for gamma/x-ray radiation using the equations. 1.11-1 DOE-HDBK-1122-99 Module 1.11 External Exposure Control Study Guide INTRODUCTION The external exposure reduction and control measures available are of primary importance to the everyday tasks performed by the RCT. -
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. -
Physics 1CL · WAVE OPTICS: INTERFERENCE and DIFFRACTION · Winter 2010
Physics 1CL · WAVE OPTICS: INTERFERENCE AND DIFFRACTION · Winter 2010 Introduction An important property of waves is interference. You are familiar with some simple examples of interference of sound waves. This interference effect produces positions having large amplitude oscillations due to constructive interference or no oscillations due to destructive interference which can be considered to arise from superposition plane waves (waves propagating in one dimension). A more complicated behavior occurs when we consider the superposition of waves that propagate in two (or three dimensions), for instance the waves that arise from the two slits in Young’s double slit experiment. Here, interference produces a two (or three) dimensional pattern of minima and maxima that depends on the relative position of the interfering sources and on the wavelength of the wave. The Young’s double slit experiment clearly shows that light has wave properties. Interference effects are important because they are the basis for determining the positions of atoms in molecules using x-ray diffraction. An interference pattern arises from x- rays scattered from the individual atoms in a molecule. Each atom acts as a coherent source and the interference pattern is used to determine the spatial arrangement of the atoms in the molecule. In this lab you will study the interference pattern of a pair of coherent sources. Coherent sources have a fixed phase relationship at all times. Several pairs of transparences are provided to facilitate the understanding and analysis of constructive and destructive interference. The transparencies are constructed to mimic the behavior of a pair of harmonic point source wave trains. -
Section 401 of the Clean Water Act and Its Application to Nonpoint Source Pollution in California Scott Mithlines
Golden Gate University Law Review Volume 30 Article 7 Issue 1 Ninth Circuit Survey January 2000 Section 401 of the Clean Water Act and its Application to Nonpoint Source Pollution in California Scott mithlineS Follow this and additional works at: http://digitalcommons.law.ggu.edu/ggulrev Part of the Environmental Law Commons Recommended Citation Scott mithlS ine, Section 401 of the Clean Water Act and its Application to Nonpoint Source Pollution in California, 30 Golden Gate U. L. Rev. (2000). http://digitalcommons.law.ggu.edu/ggulrev/vol30/iss1/7 This Note is brought to you for free and open access by the Academic Journals at GGU Law Digital Commons. It has been accepted for inclusion in Golden Gate University Law Review by an authorized administrator of GGU Law Digital Commons. For more information, please contact [email protected]. Smithline: Clean Water Act NOTE SECTION 401 OF THE CLEAN WATER ACT AND ITS APPLICATION TO NONPOINT SOURCE POLLUTION IN CALIFORNIA I. INTRODUCTION The Ninth Circuit Court of Appeals recently held in Oregon Natural Desert Ass'n v. Dombeck I ("Dombeck") that "certifica tion under Section 401 of the Clean Water Act is not required for grazing permits or other federal licensed activities that may cause pollution solely from nonpoint sources. "2 The court not only excluded grazing from the certification requirement under Section 401 of the Clean Water Act (the Act), but also ruled that all discharges from solely nonpoint sources are ex cluded from the state certification process.3 By upholding the validity of the grazing permit in the absence of state certifica tion, the court substantially limited states' ability to regulate nonpoint source pollution originating on federal lands. -
Lesson 2. Pollution and Water Quality Pollution Sources
NEIGHBORHOOD WATER QUALITY Lesson 2. Pollution and Water Quality Keywords: pollutants, water pollution, point source, non-point source, urban pollution, agricultural pollution, atmospheric pollution, smog, nutrient pollution, eutrophication, organic pollution, herbicides, pesticides, chemical pollution, sediment pollution, stormwater runoff, urbanization, algae, phosphate, nitrogen, ion, nitrate, nitrite, ammonia, nitrifying bacteria, proteins, water quality, pH, acid, alkaline, basic, neutral, dissolved oxygen, organic material, temperature, thermal pollution, salinity Pollution Sources Water becomes polluted when point source pollution. This type of foreign substances enter the pollution is difficult to identify and environment and are transported into may come from pesticides, fertilizers, the water cycle. These substances, or automobile fluids washed off the known as pollutants, contaminate ground by a storm. Non-point source the water and are sometimes pollution comes from three main harmful to people and the areas: urban-industrial, agricultural, environment. Therefore, water and atmospheric sources. pollution is any change in water that is harmful to living organisms. Urban pollution comes from the cities, where many people live Sources of water pollution are together on a small amount of land. divided into two main categories: This type of pollution results from the point source and non-point source. things we do around our homes and Point source pollution occurs when places of work. Agricultural a pollutant is discharged at a specific pollution comes from rural areas source. In other words, the source of where fewer people live. This type of the pollutant can be easily identified. pollution results from runoff from Examples of point-source pollution farmland, and consists of pesticides, include a leaking pipe or a holding fertilizer, and eroded soil. -
Currents Status, Challenges, and Future Directions in Identifying Critical Source Areas for Non-Point Source Pollution in Canadian Conditions
agriculture Review Currents Status, Challenges, and Future Directions in Identifying Critical Source Areas for Non-Point Source Pollution in Canadian Conditions Ramesh P. Rudra 1,*, Balew A. Mekonnen 1, Rituraj Shukla 1 , Narayan Kumar Shrestha 1, Pradeep K. Goel 2 , Prasad Daggupati 1 and Asim Biswas 3 1 School of Engineering, University of Guelph, Guelph, ON N1G 2W1, Canada; [email protected] (B.A.M.); [email protected] (R.S.); [email protected] (N.K.S.); [email protected] (P.D.) 2 Ontario Ministry of the Environment, Conservation and Parks, Etobicoke, ON M9P 3V6, Canada; [email protected] 3 School of Environmental Sciences, University of Guelph, ON N1G 2W1, Canada; [email protected] * Correspondence: [email protected]; Tel.: +519-824-4120 (ext. 52110) Received: 9 September 2020; Accepted: 5 October 2020; Published: 12 October 2020 Abstract: Non-point source (NPS) pollution is an important problem that has been threatening freshwater resources throughout the world. Best Management Practices (BMPs) can reduce NPS pollution delivery to receiving waters. For economic reasons, BMPs should be placed at critical source areas (CSAs), which are the areas contributing most of the NPS pollution. The CSAs are the areas in a watershed where source coincides with transport factors, such as runoff, erosion, subsurface flow, and channel processes. Methods ranging from simple index-based to detailed hydrologic and water quality (HWQ) models are being used to identify CSAs. However, application of these methods for Canadian watersheds remains challenging due to the diversified hydrological conditions, which are not fully incorporated into most existing methods. The aim of this work is to review potential methods and challenges in identifying CSAs under Canadian conditions.