Physical and Chemical Water Testing
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Cryptosporidium and Water
Cryptosporidium and Water: A Public Health Handbook 1997 WG WCWorking Group on Waterborne Cryptosporidiosis Suggested Citation Cryptosporidium and Water: A Public Health Handbook. Atlanta, Georgia: Working Group on Waterborne Cryptosporidiosis. CDCENTERS FOR DISEASEC CONTROL AND PREVENTION For additional copies of this handbook, write to: Centers for Disease Control and Prevention National Center for Infectious Diseases Division of Parasitic Diseases Mailstop F-22 4770 Buford Highway N.E. Atlanta, GA 30341-3724 CONTENTS Executive Summary Introduction 1- Coordination and Preparation 2- Epidemiologic Surveillance 3- Clinical Laboratory Testing 4- Evaluating Water Test Results Drinking Water Sources, Treatment, and Testing Environmental Sampling Methods Issuing and Rescinding a Boil Water Advisory 5- Outbreak Management Outbreak Assessment News Release Information Frequently Asked Questions Protocols for Special Audiences and Contingencies 6- Educational Information Preventing Cryptosporidiosis: A Guide for Persons With HIV and AIDS Preventing Cryptosporidiosis: A Guide for the Public Preventing Cryptosporidiosis: A Guide to Water Filters and Bottled Water 7- Recreational Water Appendix Selected Articles Key Words and Phrases Figures A-F Index Working Group on Waterborne Cryptosporidiosis (WGWC) Daniel G. Colley and Dennis D. Juranek, Coordinators, WGWC Division of Parasitic Diseases (DPD) National Center for Infectious Diseases Centers for Disease Control and Prevention Scott A. Damon, Publications Coordinator, WGWC, Centers for Disease Control and Prevention Margaret Hurd, Communications Coordinator, WGWC, Centers for Disease Control and Prevention Mary E. Bartlett, DPD Editor, Centers for Disease Control and Prevention Leslie S. Parker, Visual Information Specialist, Centers for Disease Control and Prevention Task Forces and Other Contributors: The draft materials for this handbook were developed through the work of multiple task forces and individuals whose names appear at the beginning of each chapter/section. -
National Primary Drinking Water Regulations
National Primary Drinking Water Regulations Potential health effects MCL or TT1 Common sources of contaminant in Public Health Contaminant from long-term3 exposure (mg/L)2 drinking water Goal (mg/L)2 above the MCL Nervous system or blood Added to water during sewage/ Acrylamide TT4 problems; increased risk of cancer wastewater treatment zero Eye, liver, kidney, or spleen Runoff from herbicide used on row Alachlor 0.002 problems; anemia; increased risk crops zero of cancer Erosion of natural deposits of certain 15 picocuries Alpha/photon minerals that are radioactive and per Liter Increased risk of cancer emitters may emit a form of radiation known zero (pCi/L) as alpha radiation Discharge from petroleum refineries; Increase in blood cholesterol; Antimony 0.006 fire retardants; ceramics; electronics; decrease in blood sugar 0.006 solder Skin damage or problems with Erosion of natural deposits; runoff Arsenic 0.010 circulatory systems, and may have from orchards; runoff from glass & 0 increased risk of getting cancer electronics production wastes Asbestos 7 million Increased risk of developing Decay of asbestos cement in water (fibers >10 fibers per Liter benign intestinal polyps mains; erosion of natural deposits 7 MFL micrometers) (MFL) Cardiovascular system or Runoff from herbicide used on row Atrazine 0.003 reproductive problems crops 0.003 Discharge of drilling wastes; discharge Barium 2 Increase in blood pressure from metal refineries; erosion 2 of natural deposits Anemia; decrease in blood Discharge from factories; leaching Benzene -
A Public Health Legal Guide to Safe Drinking Water
A Public Health Legal Guide to Safe Drinking Water Prepared by Alisha Duggal, Shannon Frede, and Taylor Kasky, student attorneys in the Public Health Law Clinic at the University of Maryland Carey School of Law, under the supervision of Professors Kathleen Hoke and William Piermattei. Generous funding provided by the Partnership for Public Health Law, comprised of the American Public Health Association, Association of State and Territorial Health Officials, National Association of County & City Health Officials, and the National Association of Local Boards of Health August 2015 THE PROBLEM: DRINKING WATER CONTAMINATION Clean drinking water is essential to public health. Contaminated water is a grave health risk and, despite great progress over the past 40 years, continues to threaten U.S. communities’ health and quality of life. Our water resources still lack basic protections, making them vulnerable to pollution from fracking, farm runoff, industrial discharges and neglected water infrastructure. In the U.S., treatment and distribution of safe drinking water has all but eliminated diseases such as cholera, typhoid fever, dysentery and hepatitis A that continue to plague many parts of the world. However, despite these successes, an estimated 19.5 million Americans fall ill each year from drinking water contaminated with parasites, bacteria or viruses. In recent years, 40 percent of the nation’s community water systems violated the Safe Drinking Water Act at least once.1 Those violations ranged from failing to maintain proper paperwork to allowing carcinogens into tap water. Approximately 23 million people received drinking water from municipal systems that violated at least one health-based standard.2 In some cases, these violations can cause sickness quickly; in others, pollutants such as inorganic toxins and heavy metals can accumulate in the body for years or decades before contributing to serious health problems. -
Water Quality Monitoring
Intermediate Student Guide to Water Quality Monitoring Developed in cooperation with the Texas Stream Team. Guadalupe-Blanco River Authority flowing solutions Monitoring Manual Intermediate School Level Introduction to Student Field Guide The Guadalupe-Blanco River Authority and Texas Stream Team encourages ordinary folks to be curious about how clean the water is in their creeks, rivers, and ponds. The program teaches citizens how to spot problems in water quality. Before we get started, we should discuss the term “water quality”. When we observe a water body like a creek or river, we look at the condition of the water – does it appear clear? Does it have a smell? Is the water moving, or is it still? Answering these types of questions tell us about the quality of the water. Did you ever stop to think about water as being healthy or non-healthy? Sure you did! Just think about it…. You’ve likely seen nice clean streams or rivers…. These are examples of ‘good’ water quality. You may have also observed water that is not too appealing…or ‘poor’ water quality. When you make these simple observations, you are judging the health of the water. Ok, we’ve made it pretty clear -- when we are involved in water quality studies, we are determining the health of a body of water. This guide will assist you in learning how to identify if there are any problems in water quality. You will work with a nearby creek, river, or lake – your teacher will decide what your study area will be. You will learn how to conduct simple tests. -
Standard Methods for the Examination of Water and Wastewater
Standard Methods for the Examination of Water and Wastewater Part 1000 INTRODUCTION 1010 INTRODUCTION 1010 A. Scope and Application of Methods The procedures described in these standards are intended for the examination of waters of a wide range of quality, including water suitable for domestic or industrial supplies, surface water, ground water, cooling or circulating water, boiler water, boiler feed water, treated and untreated municipal or industrial wastewater, and saline water. The unity of the fields of water supply, receiving water quality, and wastewater treatment and disposal is recognized by presenting methods of analysis for each constituent in a single section for all types of waters. An effort has been made to present methods that apply generally. Where alternative methods are necessary for samples of different composition, the basis for selecting the most appropriate method is presented as clearly as possible. However, samples with extreme concentrations or otherwise unusual compositions or characteristics may present difficulties that preclude the direct use of these methods. Hence, some modification of a procedure may be necessary in specific instances. Whenever a procedure is modified, the analyst should state plainly the nature of modification in the report of results. Certain procedures are intended for use with sludges and sediments. Here again, the effort has been to present methods of the widest possible application, but when chemical sludges or slurries or other samples of highly unusual composition are encountered, the methods of this manual may require modification or may be inappropriate. Most of the methods included here have been endorsed by regulatory agencies. Procedural modification without formal approval may be unacceptable to a regulatory body. -
Interpreting Your Water Test Report Kathleen Parrott, Extension Specialist, Housing Blake Ross, Extension Specialist, Biological Systems Engineering
PUBLICATION 356-489 Interpreting Your Water Test Report Kathleen Parrott, Extension Specialist, Housing Blake Ross, Extension Specialist, Biological Systems Engineering Obtaining a water analysis from a testing laboratory is to measure concentration are even smaller. In these cases, a necessary first step toward solving household water parts per billion (ppb) is used. Some contaminants have quality** problems. Before seeking testing, you may units that are specific to the test like those used forradon , have had concerns about the safety of the water used in hardness, conductance, and turbidity. Others, such as the household. Or you may have noticed objectionable pH, are expressed as an index number and not in terms of symptoms when using the water for drinking, cooking, concentration, and therefore have no units. or other household purposes. Perhaps you have routinely Even with modern techniques and expensive equipment, monitored your household water quality through periodic there are limits to which a water testing laboratory may testing and have recently noticed differing results between determine the amount of a given contaminant in water. If tests for one or more indicators. To positively identify the the amount of a substance is so small it cannot be mea- source of contamination problems, as well as to determine sured, the laboratory will usually indicate that the result is the type of corrective action to take, a properly interpreted “below detection limit” (b.d.l.) or “not detected” (n.d.), or water analysis report is essential. it may provide the actual detection limit value for a given Besides providing a laboratory report of the analysis for contaminant by using a “less than” (<) symbol. -
EMERGING CONTAMINANTS in ARIZONA WATER a Status Report September 2016
EMERGING CONTAMINANTS IN ARIZONA WATER A Status Report September 2016 CONTAMINANT ASSESSMENT • MONITORING • RESEARCH OPPORTUNITIES • IMPACTS • RESOURCES • COMMUNICATION & OUTREACH Acknowledgements Misael Cabrera APEC Sponsor, ADEQ Director Henry Darwin APEC Sponsor, ADEQ Director (former) Trevor Baggiore APEC Chair, ADEQ Water Quality Division Director Mike Fulton APEC Chair, ADEQ Water Quality Division Director (former) Randy Gottler APEC Co-Chair, City of Phoenix Committee Chairs/Co-chairs* Dan Quintanar Chair, Outreach and Education Committee Tucson Water John Kmiec Chair, Chemical EC Committee Town of Marana Dr. Jeff Prevatt Chair, Microbial EC Committee Pima County Regional Wastewater Reclamation Dept. Cindy Garcia (M) Co-chair, Outreach and Education Committee City of Peoria Jamie McCullough Co-chair, Outreach and Education Committee City of El Mirage Dr. Channah Rock Co-chair, Outreach and Education Committee University of Arizona, Maricopa Agricultural Center Laura McCasland (O) Co-chair, Chemical EC Committee City of Scottsdale Steve Baker Co-chair, Microbial EC Committee Arizona Dept. of Health Services, Division of Public Health Services Additional APEC Members* Dr. Morteza Abbaszadegan (M) Arizona State University, Dept. of Civil and Environmental Engineering Dr. Leif Abrell (C,M) University of Arizona, Arizona Laboratory for Emerging Contaminants Jennifer Botsford (C,O) Arizona Dept. of Health Services, Office of Environmental Health Dr. Kelly Bright (M) University of Arizona, Soil, Water & Environmental Science Al Brown (O) Arizona State University, The Polytechnic School Dr. Mark Brusseau (C,O) University of Arizona, School of Earth & Environmental Sciences Alissa Coes (C) U.S. Geological Survey, Arizona Water Science Center Nick Paretti U.S. Geological Survey, Arizona Water Science Center Patrick Cunningham (O) The Law Office of Patrick J. -
Private Water Wells
Chapter I PRIVATE WATER WELLS INTRODUCTION 4 WELL LOCATION 4 MICROORGANISM PROTECTION 4 PROTECTION FROM OTHER CONTAMINANTS 10 CONE OF DEPRESSION 10 LOCATING A NEW WELL 12 WELL CONSTRUCTION 12 DRILLED WELLS 14 DRIVEN WELLS 14 DUG WELLS 14 WELL CASING 14 WELL GROUTING 18 WELL SCREEN AND GRAVEL PACK 19 WELL DEVELOPMENT 19 SANITARY WELL SEAL 20 DISINFECTION OF WELL 20 WELL PUMPS 23 POWER PUMPS 23 HAND PUMPS 26 FREEZE PROTECTION 27 WELL PUMP HOUSE 27 PITLESS INSTALLATIONS 28 WELL MAINTENANCE 31 WATER TESTING 33 DRINKING WATER STANDARDS 33 PROTECTION OF WELLS (WELLHEAD PROTECTION) 34 PRESSURE TANKS 36 WATER STORAGE TANK 37 CROSS-CONNECTION CONTROL 38 COMPLAINT INVESTIGATION AND EVALUATION OF EXISTING WELLS 40 PLUGGING ABANDONED WELLS 40 REFFERENCES AND READING MATERIALS 41 PROTOCOLS EVALUATION OF A NEW WELL SITE OR AN EXISTING PRIVATE WELL 44 APPENDICES APPENDIX A. WELL DISINFECTION 50 APPENDIX B. COMMON INORGANIC DRINKING WATER QUALITY PARAMETERS 52 APPENDIX C. KDHE PRIVATE WELL WATER QUALITY SCREENING RESULTS INTERPRETATION 60 APPENDIX D. EVALUATION OF TASTE AND ODOR COMPLAINTS (TROUBLE SHOOTING GUIDE) 62 TABLES I-1. PUBLIC AND PRIVATE WATER SYTEMS IN KANSAS 6 I-2. MINIMUM AND RECOMMENDED SEPARATION DISTANCES FROM PRIVATE WELLS 8 I-3. PRIVATE WELL 12-POINT MAINTENANCE CHECK 32 I-4. RELATIVE CONTAMINATION RISKS FOR HOME AND FARMSTEAD ACTIVITIES 35 FIGURES I-1. SITE FEATURES SHOWING MINIMUM AND RECOMMENDED SEPARATION DISTANCES 9 I-2. CONE OF DEPRESSION FOR A PUMPING WELL 11 I-3. GOOD WELL LOCATION AND SEPARATION DISTANCES FOR A FARMSTEAD 13 I-4. CONSTRUCTION OF A DRILLED WELL IN AN UNCONSOLIDATED FORMATION 15 I-5. -
A Mini Project: Monitoring and Assessment for Water Quality of Study Area, Gombak River
MOJ Ecology & Environmental Sciences Research Article Open Access A mini project: monitoring and assessment for water quality of study area, gombak river Abstract Volume 3 Issue 2 - 2018 The proposal for this project was submitted to the National River Care Fund, Malaysia on Sept-Oct 2016 by a group of students from the UCSI University Aquatic Science Regina LZL,1,2 Teo SS,1,2 Tennat A,3 Lim LH1,2 Student Association (AQSA). The location of the project was selected as a continuation 1Aquatic Science Programme, Department of Applied Sciences, of the community services carried out by a previous batch of students. The seven UCSI University, Malaysia month project was used to measure water quality parameters for the Gombak river 2Aquatic Science Student Association, Department of Applied at the Batu 12 village location. Samples were collected each month from February Sciences, UCSI University, Malaysia 2017 until August 2017. Based on the water quality testing which indicated that 3Stella Maris International School, Malaysia the water is not contaminated or polluted, it was decided that an aquaponic system would be constructed instead of the hydroponic system mentioned in the proposal Correspondence: Lim LH, Department of Applied Sciences, because the water quality is good enough for both vegetables and fish to grow and the UCSI University, No.1 Jalan Menara Gading, UCSI Heights, community can benefit from this system. A suitable area for setting the systems up was 56000 Cheras, Kuala Lumpur, W. P. Kuala Lumpur, Malaysia, Tel: identified and site preparation activities were commenced immediately. The water in 603-910-188-80, Email [email protected] the aquaponic system was quarantined for a month before the fish were transfered to it from the laboratory. -
EPA's Recreational Water Quality Criteria
OFFICE OF WATER 820-F-12-058 Recreational Water Quality Criteria NOTICES This document has been drafted and approved for publication by the Health and Ecological Criteria Division, Office of Science and Technology, United States (U.S.) Environmental Protection Agency (EPA), and is approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. FOREWORD Under §304(a)(l) of the Clean Water Act (CWA) of 1977 (P.L. 95-217) the Administrator of the EPA is directed to develop and publish water quality criteria (WQC) that accurately reflect the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare that might be expected from the presence of pollutants in any body of water, including groundwater. CWA §304(a)(9) directs the Administrator to publish new or revised WQC for pathogens and pathogen indicators (including a revised list of testing methods, as appropriate), based on the results of the studies conducted under §104(v) of the CWA, for the purpose of protecting human health in coastal recreation waters. Coastal recreation waters (“coastal waters”) are defined under §502(21) of the CWA as the Great Lakes and marine coastal waters (including coastal estuaries) that are designated by a state for use for swimming, bathing, surfing, or similar water contact activities. This document includes WQC recommendations for pathogens and pathogen indicators based on the results of the studies conducted under §104(v) of the CWA for both coastal recreational waters and other waters designated for primary contact recreation (“non-coastal waters”). -
Testing Drinking Water for Coliphage As a Fecal Quality Indicator
Testing Drinking Water for Coliphage as a Fecal Quality Indicator Advances in Rapid Coliphage Detection Robert Salter 09/8/2012 Testing Drinking Water for Coliphage as a Quality Indicator Drinking water production includes a series of processing steps designed to reduce the risk of chemical and biological contamination(1, 2). The most common source of biological contamination is sewage pollution from human or animal waste. Raw sewage may contain pathogenic bacteria and viruses that cause illness but it also contains a higher prevalence of innocuous fecal indicators, such as enteric bacteria and bacteriophages (3). These are used as fecal indicators to assess water processing quality and integrity based on the assumption that by controlling the indicators, one controls for the less prevalent pathogens. The most common fecal indicators used in water testing for regulatory compliance are coliform and E. coli bacteria. In 2006, fecal enterococci bacteria and coliphage (bacteriophage in the coliform group of bacteria) were listed as equivalent fecal markers to E. coli in the Ground Water Rule (GWR) (4). Figure 1. Coliphage infection of E. coli produces multiple progeny that are released during the lytic cycle after replication. The multiple progeny can then re- infect and replicate to produce a detectable reaction between 4-6 hours after first infection. Coliphage were added to the GWR as an equivalent indicator to E. coli based on 20 years of epidemiological data showing that over 50% of waterborne illnesses in the US were viral in origin (5). Coliphage are bacterial viruses and some types are structurally similar to pathogenic enteric viruses. -
WATER SAMPLING & TESTING Introduction
WATER SAMPLING & TESTING Introduction: According to the well code, all new drinking water wells are required to be sampled for the presence of coliform bacteria prior to being placed into service. The well owner is ultimately responsible for collecting the samples, and the well contractor is responsible for notifying the well owner of their need to collect the samples. Some local health departments may require additional sampling such as partial chemical or arsenic. This additional sampling will typically be described on the well construction permit. General Rules: • The sampling location selected should reflect the quality of water coming from that portion of the water supply being evaluated. • For new installations, the sampling tap at the pressure tank is most commonly used. • For routine monitoring of both existing and new installations, the sampling tap at the kitchen sink is often used. • Sampling from the well head is the most practical method of determining the quality of water from the well itself. This eliminates the influence from service lines, pressure tanks, valves, etc. Sampling at the pressure tank evaluates the following: 1. piping (drop pipe and service line) 2. pressure tank 3. pump 4. well structure 5. aquifer Sampling at the kitchen sink evaluates the following: 1. piping (drop pipe and service line) 2. treatment equipment 3. hot water tank 4. pressure tank 5. pump 6. well structure 7. aquifer Coliform Bacteria Sampling Procedures: 1. Flush sampling tap (into pail if at pressure tank). 2. Reduce flow. 3. Obtain correct sample container. 4. Remove seal from sampling container. 5. Carefully remove cap and do not set down.