Using High Density Poly Ethylene (HDPE) Sheets

Total Page:16

File Type:pdf, Size:1020Kb

Using High Density Poly Ethylene (HDPE) Sheets Experimental study on Leachate movement control and treatment using High Density Poly Ethylene (HDPE) Sheets Aravind TPA ( [email protected] ) Sri Krishna College of Technology https://orcid.org/0000-0002-6135-3550 Pranesh K K Sri Krishna College of Technology Parameshwaran B Sri Krishna College of Technology Research Keywords: Landll, Leachate, HDPE, pH, Turbidity, BOD, COD, TSS, TDS Posted Date: April 28th, 2020 DOI: https://doi.org/10.21203/rs.3.rs-22373/v1 License: This work is licensed under a Creative Commons Attribution 4.0 International License. Read Full License 1 Experimental study on Leachate movement control and treatment 2 using High Density Poly Ethylene (HDPE) Sheets 3 4 Aravind T P A1, Pranesh K K2 and Parameshwaran B3 5 1 Assistant Professor, Sri Krishna College of Technology, [email protected] 6 2Student, Department of Civil Engineering, Sri Krishna College of Technology, [email protected] 7 3Student, Dept. of Civil Engineering, Sri Krishna College of Technology, [email protected] 8 ABSTRACT 9 Nowadays, in India, the incidents such as fire, groundwater contamination and 10 emission of methane due to the open dumping of municipal solid wastes have become very 11 common. To overcome these issues and also to reduce the foul smell emanating from the 12 yards due to rain drenching the piles of accumulated wastes, sanitary landfills with proper 13 leachate movement control facilities and recycling of leachates should be adapted. When 14 landfill squanders (Municipal solid waste) debases and downpour washes through the solid 15 wastes, the leachate is formed. The Leachate is a dark fluid containing organic and inorganic 16 chemicals, heavy metals and pathogens. Leachate may permeate through the landfill liners 17 and subsoil, causing contamination of surface water and sub - surface waters, which results to 18 several health hazards. The synthesis of waste changes drastically over the life of the landfill 19 because of the presence of organic and inorganic substances. This paper focuses towards the 20 control of leachate movement in a sanitary landfill and partial treatment 21 of leachate using HDPE (High Density Poly Ethylene) sheets, such that the partially 22 treated leachate meets the standards prescribed for the quality of Irrigation water. In this 23 paper, the characteristics of leachate were studied by filtering it through 1, 2 and 3 layers 24 of HDPE sheets respectively. When analyzed, the characteristics of leachate such as pH, 25 Turbidity, BOD, COD, TSS and TDS shows that the leachate collected from 3 layered HDPE 26 filtration system has better quality than the other two systems and it could be used for 27 irrigation purposes as a tool to ensure sustainability by contributing towards the reduction of 28 water scarcity issue. 29 Keywords: Landfill, Leachate, HDPE, pH, Turbidity, BOD, COD, TSS and TDS. 30 1. INTRODUCTION 31 Sanitary landfill is a method of disposing the Municipal Solid wastes. These sanitary 32 landfills prevent the contact between the wastes and the environment. It contains liners to 33 delineate the trash from permeating into the ground soil causing contamination of ground 34 water. At present the survey from waste management points out that Sanitary Landfill method 35 is the effective method to be considered in the Disposal process. Sanitary landfills with 36 proper lining and leachate collection systems are based on circular economy, as it reduces the 37 scarcity of natural resources by recycling the leachates into the water cycle without 38 contaminating the groundwater. As the municipal solid wastes disposed in landfills comes in 39 mere contact with storm water or any run offs, it results in the formation of leachate. The 1 40 Leachate is a dark fluid containing both organic and inorganic chemicals, heavy metals and 41 pathogens. A clay liner used as a boundary of landfill cell acts as a hydraulic barrier for the 42 fluids to flow in and it has been determined by finding the moisture content of the clay taken 43 from the sides of the landfill cell case and around the landfill cell case used in the lining 44 system. The gases released from landfill contain 92% to 95% of carbon dioxide and methane 45 while the rest is comprised of gases like oxygen, nitrogen, ammonia, sulphides and hydrogen. 46 The basic characteristics of leachate to be studied are pH, Turbidity, Chemical oxygen 47 demand, Biological oxygen demand, Turbidity, TDS and TSS. 48 2. MATERIALS 49 The materials used for setting up the Sanitary landfill Prototype are discussed here. 50 2.1 HDPE sheets 51 High Density Polyethylene (HDPE) or polyethylene high-thickness (HDPE) is a 52 thermoplastic polymer created from the monomer ethylene. With a high solidarity to- 53 thickness proportion, HDPE is utilized in the creation of plastic containers, consumption safe 54 funnelling, geo films and plastic wood. It offers an amazing protection from most solvents 55 and also from alcohol, weaken acids, oil, oils, salts low temperature, etc., It has extremely 56 low water assimilation limit. The characteristics of HDPE sheets used are shown in Table 1. 57 2.2 Mesh 58 A mesh is an obstruction made of associated strands of metal, fibre, or other adaptable or 59 malleable materials. A mesh resembles a web or a net which has many added or woven 60 strands. The characteristics of mesh used are shown in Table 2. 61 2.3 PVC Pipe 62 PVC refers to Poly Vinyl Chloride, and it's become a common swap for metal piping. 63 It's the white plastic channel normally utilized for plumbing and collection of leachate from 64 the landfill. A PVC pipe with numerous perforations and wrapped with the mesh is supplied. 65 The characteristics of PVC pipe used are shown in Table 3. 66 2.4 Clay 67 Clay is a soil that contains an elevated level of fine particles and colloidal substance 68 and become tenacious when wet and decline as far as possible compared to various soils. The 69 dirt is utilized as a covering material in our clean landfill. 70 The moisture content of the clay used in the landfill lining is determined to be 9.5%. 71 2.5 Municipal Solid Wastes 2 72 The municipal solid wastes collected are analysed in order to determine the 73 composition and characteristics. The composition of solid wastes is found to be as shown in 74 Fig 1. 75 76 Fig 1 Composition of Solid Waste Sample 77 The characteristics of collected solid wastes to be used in landfills are as given in 78 Table 4. 79 3. RESULTS AND DISCUSSION 80 3.1 Irrigation Water Quality 81 As per The Environmental Protection act - 1986, the water quality required for 82 Irrigation should satisfy the standards prescribed in Table 5. The partially treated leachate 83 characteristics are compared with these standards to identify the best treatment system among 84 1, 2 and 3 layered HDPE filtration of leachate from the landfills. 85 3.2 pH 86 The pH values of the leachate obtained from the landfills with 1, 2 and 3 layers of 87 HDPE sheet filtration systems shows that leachate from 2 and 3 layered filtration systems 88 meets with the standards prescribed for the quality of Irrigation water as shown in Fig 2. 8 7.22 6.61 7 6 4.82 5 pH 4 3 2 1 0 1-HDPE 2-HDPE 3-HDPE 89 3 90 Fig 2 Comparison of pH values 91 3.3 Chemical Oxygen Demand (COD) 92 The COD values of the leachate obtained from the landfills with 1, 2 and 3 layers of 93 HDPE sheet filtration systems, shows that leachate from all the 3 filtration systems meets 94 with the standards prescribed for the quality of Irrigation water as shown in the Fig 3. 1350 1316 1300 ) ) 1250 1221 COD (mg/l COD 1200 1144 1150 1100 1050 1-HDPE 2-HDPE 3-HDPE 95 96 Fig 3 Comparison of COD values 97 3.4 Biological Oxygen Demand (BOD5) 98 The BOD values of the leachate obtained from the landfills with 1, 2 and 3 layers of 99 HDPE sheet filtration systems shows that only the leachate from 3 layered filtration systems 100 meets with the standards prescribed for the quality of Irrigation water as shown in the Fig 4. 4 1600 1341.85 1400 1200 973.15 1000 BOD (mg/l) BOD 800 600 304.16 400 200 0 1-HDPE 2-HDPE 3-HDPE 101 102 Fig 4 Comparison of BOD values 103 3.5 Turbidity 104 The turbidity values of the leachate obtained from the landfills with 1, 2 and 3 layers 105 of HDPE sheet filtration systems, shows that leachate from all the 3 filtration systems layered 106 filtration systems meets with the standards prescribed for the quality of Irrigation water as 107 shown in Fig 5. 3 2.51 2.5 2 1.8 Turbidity (NTU) Turbidity 1.5 1.27 1 0.5 0 1-HDPE 2-HDPE 3-HDPE 108 109 Fig 5 Comparison of Turbidity values 110 3.6 Total Dissolved Solids (TDS) 5 111 The TDS values of the leachate obtained from the landfills with 1, 2 and 3 layers of 112 HDPE sheet filtration systems, shows that leachate from 3 layered filtration systems meets 113 with the standards prescribed for the quality of Irrigation water as shown in the Fig 6. 16000 14620 14000 12000 10000 7200 8000 TDS (mg/l) (mg/l) TDS 6000 4000 2000 400 0 1-HDPE 2-HDPE 3-HDPE 114 115 Fig 6 Comparison of TDS values 116 3.8 Discussion 117 From the various parameters which are studied and compared, it is clear that the 118 landfill setup developed with 3 layered filtration system satisfies all the criteria required to be 119 used for the Irrigation practices (Table 6).
Recommended publications
  • World Bank Document
    WATER GLOBAL PRACTICE QUALITY UNKNOWN BACKGROUND PAPER Public Disclosure Authorized Determinants of Public Disclosure Authorized Essayas Ayana Declining Water Quality Public Disclosure Authorized Public Disclosure Authorized About the Water Global Practice Launched in 2014, the World Bank Group’s Water Global Practice brings together financing, knowledge, and implementation in one platform. By combining the Bank’s global knowledge with country investments, this model generates more firepower for transformational solutions to help countries grow sustainably. Please visit us at www.worldbank.org/water or follow us on Twitter at @WorldBankWater. About GWSP This publication received the support of the Global Water Security & Sanitation Partnership (GWSP). GWSP is a multidonor trust fund administered by the World Bank’s Water Global Practice and supported by Australia’s Department of Foreign Affairs and Trade, the Bill & Melinda Gates Foundation, the Netherlands’ Ministry of Foreign Affairs, Norway’s Ministry of Foreign Affairs, the Rockefeller Foundation, the Swedish International Development Cooperation Agency, Switzerland’s State Secretariat for Economic Affairs, the Swiss Agency for Development and Cooperation, U.K. Department for International Development, and the U.S. Agency for International Development. Please visit us at www.worldbank.org/gwsp or follow us on Twitter #gwsp. Determinants of Declining Water Quality Essayas Ayana © 2019 International Bank for Reconstruction and Development / The World Bank 1818 H Street NW, Washington, DC 20433 Telephone: 202-473-1000; Internet: www.worldbank.org This work is a product of the staff of The World Bank with external contributions. The findings, interpretations, and conclusions expressed in this work do not necessarily reflect the views of The World Bank, its Board of Executive Directors, or the governments they represent.
    [Show full text]
  • Plants in Constructed Wetlands Help to Treat Agricultural Processing Wastewater
    UC Agriculture & Natural Resources California Agriculture Title Plants in constructed wetlands help to treat agricultural processing wastewater Permalink https://escholarship.org/uc/item/67s9p4z8 Journal California Agriculture, 65(2) ISSN 0008-0845 Authors Grismer, Mark E Shepherd, Heather L Publication Date 2011 Peer reviewed eScholarship.org Powered by the California Digital Library University of California ReseaRch aRticle ▼ Plants in constructed wetlands help to treat agricultural processing wastewater by Mark E. Grismer and Heather L. Shepherd Over the past three decades, winer- ies in the western United States and sugarcane processing for ethanol in Central and South America have experienced problems related to the treatment and disposal of pro- cess wastewater. Both winery and sugarcane (molasses) wastewaters are characterized by large organic loadings that change seasonally and are detrimental to aquatic life. We examined the role of plants for treating these wastewaters in constructed wetlands. In the green- house, subsurface-flow flumes with agricultural processing wastewaters may have high concentrations of organic matter that volcanic rock substrates and plants contaminate surface waters when discharged downstream. at imagery estate Winery in Glen ellen, constructed wetlands with plants were tested for their ability to remove pollutants. steadily removed approximately 80% of organic-loading oxygen demand Shepherd et al. (2001) described the sugarcane and winery wastewater from sugarcane process wastewater negative impacts of winery wastewater Sugarcane, food-processing, winery after about 3 weeks of plant growth; downstream, which led to requirements and other distilleries generate waste- for its control and on-site treatment. waters from processing and equipment unplanted flumes removed about Similarly, downstream degradation wash-down.
    [Show full text]
  • Great Salt Lake Brine Chemistry Database, 1966–2011
    GREAT SALT LAKE BRINE CHEMISTRY DATABASE, 1966–2011 by Andrew Rupke and Ammon McDonald OPEN-FILE REPORT 596 UTAH GEOLOGICAL SURVEY a division of UTAH DEPARTMENT OF NATURAL RESOURCES 2012 GREAT SALT LAKE BRINE CHEMISTRY DATABASE, 1966–2011 by Andrew Rupke and Ammon McDonald Cover photo: The Southern Pacific Railroad rock causeway. The view is to the east, and the north arm of Great Salt Lake is on the left. OPEN-FILE REPORT 596 UTAH GEOLOGICAL SURVEY a division of UTAH DEPARTMENT OF NATURAL RESOURCES 2012 STATE OF UTAH Gary R. Herbert, Governor DEPARTMENT OF NATURAL RESOURCES Michael Styler, Executive Director UTAH GEOLOGICAL SURVEY Richard G. Allis, Director PUBLICATIONS contact Natural Resources Map & Bookstore 1594 W. North Temple Salt Lake City, UT 84116 telephone: 801-537-3320 toll-free: 1-888-UTAH MAP website: mapstore.utah.gov email: [email protected] UTAH GEOLOGICAL SURVEY contact 1594 W. North Temple, Suite 3110 Salt Lake City, UT 84116 telephone: 801-537-3300 website: geology.utah.gov This open-file release makes information available to the public that may not conform to UGS technical, edito- rial, or policy standards; this should be considered by an individual or group planning to take action based on the contents of this report. Although this product represents the work of professional scientists, the Utah Department of Natural Resources, Utah Geological Survey, makes no warranty, expressed or implied, regarding its suitability for a particular use. The Utah Department of Natural Resources, Utah Geological Survey, shall not be liable under any circumstances for any direct, indirect, special, incidental, or consequential damages with respect to claims by users of this product.
    [Show full text]
  • Total Dissolved Solids in Drinking-Water
    WHO/SDE/WSH/03.04/16 English only Total dissolved solids in Drinking-water Background document for development of WHO Guidelines for Drinking-water Quality __________________ Originally published in Guidelines for drinking-water quality, 2nd ed. Vol. 2. Health criteria and other supporting information. World Health Organization, Geneva, 1996. © World Health Organization 2003 All rights reserved. Publications of the World Health Organization can be obtained from Marketing and Dissemination, World Health Organization, 20 Avenue Appia, 1211 Geneva 27, Switzerland (tel: +41 22 791 2476; fax: +41 22 791 4857; email: [email protected]). Requests for permission to reproduce or translate WHO publications - whether for sale or for noncommercial distribution - should be addressed to Publications, at the above address (fax: +41 22 791 4806; email: [email protected]). The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or of certain manufacturers’ products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. The World Health
    [Show full text]
  • Investigation of Total Dissolved Solids Regulation In
    Investigation of Total Dissolved Solids Regulation in the Appalachian Plateau Physiographic Province: A Case Study from Pennsylvania and Recommendations for the Future by Mark Wozniak A project submitted to the Graduate Faculty of North Carolina State University in partial fulfillment of the requirements for the degree of Masters of Environmental Assessment Raleigh, North Carolina 2011 Advisory Chair: Linda Taylor ii ABSTRACT WOZNIAK, MARK. Investigation of Total Dissolved Solids Regulation in the Appalachian Plateau Physiographic Province: A Case Study from Pennsylvania and Recommendations for the Future. (Under the direction of Linda Taylor and Dr. Chris Hofelt). Total dissolved solids (TDS) are a natural constituent of surface water throughout the world. The World Health Organization, U.S. Environmental Protection Agency, and most states regulate TDS as a secondary drinking water criteria, affecting taste and odor, limiting discharges to 500 mg/L. This method of regulation fails to account for the conservative nature of TDS, with in-stream concentrations increasing with each addition, as well as impacts to aquatic life. New sources of TDS are further stressing historically contaminated waterways throughout the Appalachian Plateau, leaving them unable to assimilate additional TDS. With these new sources only projected to increase, it is necessary, now more than ever, for the states to develop total maximum daily loads for the affected waterways. This is the most effective method for regulating TDS to ensure the sustained health of the regional aquatic communities and human health. iii BIOGRAPHY Mark Wozniak has lived in western Pennsylvania all his life, where he attained an interest in all aspects of the natural environment at an early age.
    [Show full text]
  • Treatability of a Highly-Impaired, Saline Surface Water for Potential Urban Water Use
    water Article Treatability of a Highly-Impaired, Saline Surface Water for Potential Urban Water Use Frederick Pontius Department of Civil Engineering and Construction Management, Gordon and Jill Bourns College of Engineering, California Baptist University, Riverside, CA 92504, USA; [email protected]; Tel.: +1-951-343-4846 Received: 14 January 2018; Accepted: 14 March 2018; Published: 15 March 2018 Abstract: As freshwater sources of drinking water become limited, cities and urban areas must consider higher-salinity waters as potential sources of drinking water. The Salton Sea in the Imperial Valley of California has a very high salinity (43 ppt), total dissolved solids (70,000 mg/L), and color (1440 CU). Future wetlands and habitat restoration will have significant ecological benefits, but salinity levels will remain elevated. High salinity eutrophic waters, such as the Salton Sea, are difficult to treat, yet more desirable sources of drinking water are limited. The treatability of Salton Sea water for potential urban water use was evaluated here. Coagulation-sedimentation using aluminum chlorohydrate, ferric chloride, and alum proved to be relatively ineffective for lowering turbidity, with no clear optimum dose for any of the coagulants tested. Alum was most effective for color removal (28 percent) at a dose of 40 mg/L. Turbidity was removed effectively with 0.45 µm and 0.1 µm microfiltration. Bench tests of Salton Sea water using sea water reverse osmosis (SWRO) achieved initial contaminant rejections of 99 percent salinity, 97.7 percent conductivity, 98.6 percent total dissolved solids, 98.7 percent chloride, 65 percent sulfate, and 99.3 percent turbidity.
    [Show full text]
  • Summary of Water Quality Indicators-Surface Waters Page 2 Around 9 Mg/L
    HOW WATER QUALITY INDICATORS WORK Following are summaries of water quality indicators from several sources collated by the International Water Institute. They provide information about how the specific water quality indicators describe river health and factors affecting them. Other sources: http://ga.water.usgs.gov/edu/characteristics.html, and http://bcn.boulder.co.us/basin/data/NUTRIENTS/info/ *************************************************************************************** Following from FM RIVER at: http://www.undeerc.org/watman/FMRiver/PPTV/factsheets.asp Electrical Conductivity The electrical conductivity of water is directly related to the concentration of dissolved solids in the water. Ions from the dissolved solids in water influence the ability of that water to conduct an electrical current, which can be measured using a conductivity meter. When correlated with laboratory TDS measurements, electrical conductivity can provide an accurate estimate of the TDS concentration. Conductivity measurements for the Red River correlate very closely to the TDS determinations. Water in the Red River is usually below the 900 microsiemens/cm (red line on graph) set for drinking water by EPA's National Secondary Water Standards even before entering the local The Red River contains 1/70th the water treatment plants. dissolved minerals found in seawater. Graph of electrical conductivity (μS/cm) for the Red River in the FM metro area for the period July 2001 to April 2003 in relation to the EPA guideline (900 μS/cm; red line) for drinking water. Dissolved Oxygen Dissolved oxygen (DO) refers to the amount of oxygen (O2) dissolved in water. Because fish and other aquatic organisms cannot survive without oxygen, DO is one of the most important water quality parameters.
    [Show full text]
  • Revising Criteria for Chloride, Sulfate and Total Dissolved Solids
    Understanding Iowa’s Water Quality Standards Revising Criteria for Chloride, Sulfate and Total Dissolved Solids By revising Iowa’s water quality standards, the Iowa Department of Natural Resources (DNR) is working for improved water quality and safety in Iowa. Water Quality Standards are the goals that we set for Iowa’s streams, rivers and lakes. Water Quality Standards have three components: • Designate the use or uses of the waterbody Proposed chloride criteria To calculate the applicable acute and chronic criteria for chloride, (aquatic life and recreational uses) use the equations below. Statewide default values for hardness • Set the criteria for protecting those uses and sulfate will be used unless site specific data is available. The • Protect and maintain existing water quality DNR updated its proposed chloride criteria on March 3, 2009, based on new EPA toxicity data. Recently, the DNR began to compile all research related to toxicity of total dissolved solids, chloride Acute Chloride Criteria Equation and sulfate. The purpose was to update and develop 287.8(Hardness)0.205797(Sulfate)-0.07452 = Acute Criteria Value (mg/L) criteria for these parameters to better protect aquatic Chronic Chloride Criteria Equation life based on new scientific information. 177.87(Hardness)0.205797(Sulfate)-0.07452 = Chronic Criteria Value (mg/L) The DNR worked with the U.S. Environmental Protection Agency to ensure that the research compiled The following statewide background values were met certain scientific standards. Gaps were identified determined by analyzing DNR ambient water monitoring in the research and resulted in new toxicity tests being data from 2000 to 2007: performed in 2008.
    [Show full text]
  • Differences in the Composition of Leachate from Active and Non
    water Article Differences in the Composition of Leachate from Active and Non-Operational Municipal Waste Landfills in Poland Aleksandra Wdowczyk * and Agata Szyma ´nska-Pulikowska Faculty of Environmental Engineering and Geodesy, Institute of Environmental Engineering, Wrocław University of Environmental and Life Sciences, pl. Grunwaldzki 24, 50-363 Wrocław, Poland; [email protected] * Correspondence: [email protected]; Tel.: +48-71-320-5544 Received: 27 September 2020; Accepted: 5 November 2020; Published: 8 November 2020 Abstract: Leachate formation is one of the many environmental hazards associated with landfilling. The leachate may migrate from the landfill to surface water and groundwater, posing a potential threat to aquatic ecosystems. Moreover, its harmful effect on human health and life has been proven. Due to the risks that landfill leachates may pose, it is necessary to control the state of the environment in their surroundings. The paper presents an example of the application of selected statistical methods (basic statistics, statistical tests, principal component analysis) to assess the impact of individual pollution indicators on the quality of landfill leachates. The conducted analysis showed the existence of significant differences between the surveyed active (Legnica, Jawor) and non-operational (Wrocław, Bielawa) landfills in Poland. These differences were especially visible in the cases of the following: electric conductivity (EC) (non-operational landfills 1915–5075 µS/cm, active 5093–11,370 µS/cm), concentrations of total Kjeldahl nitrogen (TKN) (non-operational landfills 0.18–294.5 mg N/dm3, active 167.56–907.4 mg N/dm3), chemical oxygen demand (COD), organic nitrogen (ON), ammonium nitrogen (AN), total solids (TS), total dissolved solids (TDS), total suspended solids (TSS), sulfates, chlorides, sodium, potassium, calcium, magnesium and nickel.
    [Show full text]
  • Irrigation Water Quality: Total Dissolved Solids
    P.O. Box 82 Golf, IL 60029-0082 Phone: 847-579-3090 Fax: 847-724-8212 Irrigation Water Quality: Total Dissolved Solids Total Dissolved Solids All water contains some dissolved mineral salts and chemicals. Some soluble salts are nutrients and are beneficial to grass and other plant growth, others however may be toxic to plants or may become so when present in high concentrations. The rate at which salts accumulate in soil depends on their concentration in the irrigation water, the amount of water applied annually, annual precipitation (rain plus snow), and the soil’s physical/chemical characteristics. Throughout our area many businesses use recycled water for irrigation. Water from retention ponds and/or wells is used for irrigation initially and then the excess water runs off into the pond. With each pass over the landscape the water picks up more dissolved material. Much of the recycled water used for irrigation contains high concentrations of dissolved salts that are potentially toxic to turf grasses and other plants. Water analysis and periodic monitoring are key components of irrigation management at such sites. Analyses of irrigation water provide data on many parameters. The most important parameters for irrigation purposes are: total suspended solids (salinity); sodium (Na); relative proportion of sodium to calcium (Ca) and magnesium (Mg) (Sodium Adsorption Ratio); chloride (Cl), boron (B), bicarbonate (HCO3), and carbonate (CO3) content; and pH. Water Reclamation: Reverse-osmosis water filtration units are the best method of total suspended solids removal. Osmosis is a special case of diffusion in which the molecules are water and the concentration gradient occurs across a semi-permeable membrane.
    [Show full text]
  • Wastewater Management for High-TDS Wastewaters In
    WastewaterWastewater ManagementManagement forfor HighHigh--TDSTDS WastewatersWastewaters inin PennsylvaniaPennsylvania TotalTotal DissolvedDissolved SolidsSolids (TDS):(TDS): • Are a measurement of inorganic salts, organic matter and other dissolved materials in water. • Are a secondary drinking water contaminant. • Can cause operational problems for drinking water systems. • Can cause toxicity to aquatic life through increases in salinity, changes in the ionic composition of the water, and the toxicity of individual ions. LargeLarge SourcesSources ofof TDSTDS • Steel Industry • Pharmaceutical Manufacturing • Mining Operations • Oil & Gas Extraction • Some Power Plants • Landfills • Food Processing Facilities • Others WaterWater QualityQuality ConsiderationsConsiderations • Water quality analyses show that Pennsylvania’s rivers and streams have a very limited ability to assimilate additional TDS. • Growing demand for assimilative capacity strains our ability to protect water quality. • Fall 2008, actual water quality issues related to TDS emerged in the Monongahela River basin. WestWest BranchBranch SusquehannaSusquehanna RiverRiver • TDS in the West Branch is already 48% of the 500 mg/L water quality criterion during design-flow conditions. TDS REGRESSION WQN 401 WEST BRANCH FLOW DATA FROM WEST BRANCH AT LEWISBURG, PA Q7-10 of 764 cfs is equivalent to 242 mg/L TDS 350 300 y = -38.302Ln(x) + 496.68 R2 = 0.6338 250 200 150 TDS (mg/L) TDS 100 50 0 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 Flow (CFS) BeaverBeaver RiverRiver
    [Show full text]
  • Guidelines for Drinking-Water Quality, Fourth Edition
    10 Acceptability aspects: Taste, odour and appearance A conceptual framework for Introduction implementing the Guidelines (Chapter 1) (Chapter 2) he provision of FRAMEWORK FOR SAFE DRINKING-WATER SUPPORTING Tdrinking-water that INFORMATION is not only safe but also Health-based targets Public health context Microbial aspects (Chapter 3) and health outcome acceptable in appear- (Chapters 7 and 11) Water safety plans Chemical aspects ance, taste and odour is (Chapter 4) (Chapters 8 and 12) of high priority. Water System Management and Radiological Monitoring that is aesthetically un- assessment communication aspects (Chapter 9) acceptable will under- Acceptability Surveillance mine the confi dence of aspects (Chapter 5) consumers, will lead to (Chapter 10) complaints and, more importantly, could lead Application of the Guidelines in specific circumstances to the use of water from (Chapter 6) sources that are less safe. Climate change, Emergencies, Rainwater harvesting, Desalination To a large extent, systems, Travellers, Planes and consumers have no ships, etc. means of judging the safety of their drinking-water themselves, but their attitude towards their drinking- water supply and their drinking-water suppliers will be affected to a considerable ex- tent by the aspects of water quality that they are able to per- The appearance, taste and odour of drinking-water ceive with their own senses. It should be acceptable to the consumer. Water that is is natural for consumers to re- aesthetically unacceptable can lead to the use of water gard with suspicion water that from sources that are aesthetically more acceptable, appears dirty or discoloured or but potentially less safe. that has an unpleasant taste or smell, even though these characteristics may not in themselves be of direct conse- quence to health.
    [Show full text]