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Bob Bastian U.S. EPA, Office of Wastewater Management Washington, D.C.

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Presentation on theme: "Bob Bastian U.S. EPA, Office of Wastewater Management Washington, D.C."— Presentation transcript:

1 Bob Bastian U.S. EPA, Office of Wastewater Management Washington, D.C.

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3 History-EPA Guidelines For Water Reuse First Guidelines for Water Reuse-1980 Research Report by CDM for EPA/ORD 1992 Guidelines update format-purple design manual series 2004 Guidelines incorporated: – 3 National Academy studies – UV disinfection alternative – Emerging contaminants – Case studies intended for state regulatory use

4 1980 Guidelines Objective To Make Water Managers and Resource Planners Aware of the Proven Possibilities of Water Reclamation

5 1992

6 1992 Update to the Guidelines A Major Rewrite (increased from 106 to 254 pages) Water Resource Driven Level of Treatment Guidelines International Issues Major Changes from 1980 to 1992 Guidelines Inventory of State Regulations Expanded Case Studies Included a Section on International Reuse Truly Provided Treatment Guidelines

7 2004 Guidelines for Water Reuse EPA 625/R-04/108; August

8 2004 Update Updating the Inventory of State Regulations, Adding State Contacts Expanded Discussion of Potable Reuse Issues Emphasizing Recent Studies and Projects Emerging Pathogens R&D/Issues Emerging Chemical Constituents (NDMAs, Endocrine Disrupters, etc.) Updating USGS Data on National Water and Reuse Practices New Case Studies

9 What the 2004 Guideline Wasnt A Design Manual A Treatment Manual A Scope of Work for Reuse Projects A Land Application/Effluent Disposal Manual

10 2004 Chapters 1. Introduction 2. Technical Issues in Planning Water Reuse Systems 3. Types of Reuse Applications 4. Water Reuse Regulations and Guidelines in the U.S. 5. Legal and Institutional Issues 6. Funding Alternatives for Water Reuse Systems 7. Public Information Programs 8. Water Reuse Outside the U.S.

11 Who Was the Intended Audience? Municipal Wastewater and Water Supply Agencies International, State, Regional and Local Regulatory Agencies Reclaimed Water Users (Public and Private)

12 States with Reuse Regulations and Guidelines in 1992 Hawaii Alaska Regulations Guidelines

13 Status in 2003 Hawaii Alaska Guidelines Regulations

14 Reuse Categories Unrestricted Urban Reuse Unrestricted Urban Reuse Restricted Urban Reuse Restricted Urban Reuse Agricultural Reuse for Food Crops Agricultural Reuse for Food Crops Agricultural Reuse for Nonfood Crops Agricultural Reuse for Nonfood Crops Recreational Impoundments Recreational Impoundments Intrusion Barrier Intrusion Barrier u Environmental – e.g., Wetlands u Industrial Reuse u Groundwater Recharge u Indirect Potable Reuse - Spreading Basins - Spreading Basins - Injection - Injection - Surface Water Augmentation - Surface Water Augmentation

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18 Suggested Guidelines for Water Reuse

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20 Projected Growth in the U.S

21 2012 Update Effort Cooperative Research and Development Agreement (CRADA ) – CDM-EPA/OWM-EPA/NRMRL Federal Cooperators – EPA – U.S. AID – USDA/NIFA Participate on Project Management Committee, Steering Committee and TRC Review

22 Goals For 2012 Guidelines Update Total Water Management Approach Reflect Integrated Water Resources Management Recognize technology and regulations for higher quality uses Utilize current knowledge base – supplement with recent experience Increased focus on international project economic benefits International development standards and guidelines (WHO, EU, IWA)

23 Drivers For 2012 Guidelines Update Presidential Executive Order – increased water and energy efficiency at federal facilities LEED certified facility criteria Sponsor interest in updating Guidelines National Academy Study-role of reuse in water supply CWA/SDWA linkage to TWM Wetland buffers to polish water Advanced treatment technologies like OC-GWR promote interest in IPR

24 Format for Updating the Guidelines Forums/Workshops/Web meetings for input International Forums –Jordan –March IWA 6th Efficiency Conference – Singapore – July International Water Week Web-based e-Room for participants Expanded contents, increased web linkage Volunteer Authors/Reviewers

25 Contents – Types of Reuse Applications Increased agricultural use discussion – federal food safety Soil science / salinity issues Wetlands polishing and stream augmentation Groundwater augmentation (managed aquifers/ASR) Indirect potable reuse (IPR) applications Potable reuse applications Public health considerations Regional technical focus

26 Expanded International Chapter Technical guide for U.S. AID mission staff Roadmap for policy makers in foreign countries Promote linkage between environmental, public health, and economic benefits of reuse Cross-reference best practice case studies Identify knowledge gaps in scale of application Application of small scale onsite/decentralized options Create reuse system development checklist On-ramping water reuse globally

27 Schedule

28 National Research Council Committee on the Assessment of Water Reuse as an Approach to Meeting Future Water Supply Needs Water Reuse: Potential for Expanding the Nations Water Supply Through Reuse of Municipal Wastewater

29 Committee Membership RHODES TRUSSELL, Chair, Trussell Technologies, Pasadena, California HENRY ANDERSON, Wisconsin Division of Public Health, Madison, Wisconsin ED ARCHULETA, El Paso Water Utilities, El Paso, Texas JAMES CROOK, Environmental Engineering Consultant, Norwell, Massachusetts JÖRG DREWES, Colorado School of Mines, Golden, Colorado DENISE FORT, University of New Mexico, Albuquerque, New Mexico CHARLES HAAS, Drexel University, Philadelphia, Pennsylvania BRENT HADDAD, University of California, Santa Cruz, California DUANE HUGGETT, University of North Texas, Denton, Texas SUNNY JIANG, University of California, Irvine, California DAVID SEDLAK, University of California, Berkeley, California SHANE SNYDER, University of Arizona, Tucson, Arizona MARGARET WHITTAKER, ToxServices LLC, Washington, D.C. DALE WHITTINGTON, University of North Carolina, Chapel Hill, North Carolina NRC Staff: Stephanie Johnson (Study Director), Sarah Brennan, and Stephen Russell

30 Study Charge 1. Contributing to the nation's water supplies. What are the potential benefits of expanded water reuse and reclamation? What is the suitability of processed wastewaters for various purposes? Focused on municipal wastewater. 2.Assessing the state of technology. What is the current state-of-the-technology in wastewater treatment and production of reclaimed water? What are the current technology challenges and limitations? 3.Assessing risks. What are the human health risks of using reclaimed water? What are the risks of using reclaimed water for environmental purposes? How effective are monitoring, control systems, and the existing regulatory framework in assuring the safety and reliability of wastewater reclamation practices?

31 Study Charge (cont.) 4. Costs. How do the costs (including environmental costs) and benefits of water reclamation and reuse generally compare with other supply alternatives? 5.Barriers to implementation. What implementation issues limit the applicability of water reuse to help meet the nation's water needs and what, if appropriate, are means to overcome these challenges? 6. Research needs. What research is needed to advance the safe, reliable, and cost-effective reuse of municipal wastewater where traditional sources of water are inadequate? What are appropriate roles for governmental and non-governmental entities? 15 sponsors, including EPA, NSF, USBR and 9 water utilities.

32 Study Process 8 meetings (5 information gathering): 1. Irvine, CA - Dec San Francisco, CA - Jun Golden, CO - Jul Orlando, FL - Oct Washington, D.C. - Jan Woods Hole, MA - Jun Irvine, CA - Sept Dallas/Ft. Worth, TX - Jan Briefings/presentations from many individuals, agencies and organizations Included original data analysis and survey of utilities for reuse costs Peer-reviewed consensus report

33 Context for Wastewater Reuse New water supplies and improved efficiency needed to meet demands of shifting populations and changing climate US Population & Growth trends One block for each Co. in U.S. Height of Block = Population density Color = Pop between 1970 & 2030

34 Wastewater Reuse Potential Out of 32 BGD wastewater effluent, 12 BGD discharged directly to ocean or estuary in U.S. Inland discharges may also be available for reuse. Thus, reuse offers significant potential to increase total available water resources.

35 Water Reuse in Context Nonpotable reuse well established, generally accepted. Potable reuse projects represent a fraction of all reuse Reuse projects are estimated to be <1% of total U.S. water use ADD FL HERE Florida Reuse In 2010

36 Water Reuse in Context De facto reuse is common De facto reuse = where reuse is practiced but not officially recognized or permitted as a reuse project 9

37 Water Reuse in Context De facto reuse* is common Updated analysis of extent of de facto reuse needed River Ouse, UK Sewage Treatment Works Percentage Effluent [90th Percentile] 0 – 5% 6 – 15% 16 – 25% 26 – 50% > 50% From Johnson & Williams, 2009

38 Water Reuse Treatment Technology A portfolio of treatment options exists to mitigate microbial and chemical contaminants in reclaimed water. –Includes engineered treatment and natural processes –The lack of guidance for design and operation of natural processes is the biggest deterrent to their expanded use in engineered reuse systems.

39 Reuse Treatment Technology (cont.) Treatment can be tailored to meet specific water quality objectives for intended applications. Membrane-based processes are particularly attractive for reuse applications. However, membranes are not a panacea

40 Environmental Buffers Natural systems are employed in most potable water reuse systems to provide an environmental buffer. May provide: (1) retention time, (2) attenuation of contaminants, and (3) blending (or dilution) But, the science required to design for uniform protection from one environmental buffer to the next is not available. Engineered processes can be designed to achieve these same functions. It cannot be demonstrated that such natural barriers provide public health protection that is not also available by other engineered processes. The potable reuse of highly treated reclaimed water without an environmental buffer is worthy of consideration, if adequate protection is engineered within the system. The distinction between indirect and direct potable reuse is not scientifically meaningful to product water quality.

41 Understanding the Risks Health risks remain difficult to fully characterize and quantify through epidemiological or toxicological studies However, well-established methods exist for estimating the risks of various water reuse applications. The occurrence of a contaminant at a detectable level does not necessarily indicate a significant risk. Risk assessment screening methods can be used to estimate human health effects where dose-response data are lacking.

42 Understanding the Risks To quantify uncertainty in risk assessments, a better understanding of the performance of reuse systems is needed including failures and variability of treatment and distribution system The potential for unintended or inappropriate uses should be assessed and mitigated. i.e., procedures to detect cross connections. Guidance and user-friendly risk assessment tools needed.

43 Evaluating the Risks in Context It is appropriate to compare the risk from water produced by potable reuse projects with the risk associated with the water supplies that are presently in use. Committees Risk Exemplar: Original comparative analysis of three scenarios: 1 de facto example and 2 typical potable reuse projects

44 Risk Exemplar Scenarios Scenario 1: De facto reuse 5% effluent in pristine surface water, no degradation in stream 18

45 Risk Exemplar Scenarios Scenario 2: Soil-Aquifer Treatment (SAT) Secondary treatment, filtration, no disinfection, SAT, 6 mo retention in subsurface, no dilution, wellhead Cl 2 disinfection. 19

46 Risk Exemplar Scenarios Scenario 3: Advanced Water Treatment Secondary treatment, chloramination, MF, RO, UV/AOP, direct injection, 6 mo retention in subsurface, no dilution, wellhead Cl 2 disinfection. 20

47 Risk Exemplar Contaminants Pathogens: Adenovirus Norovirus Salmonella Cryptosporidium Disinfection Byproducts Bromate Bromoform Chloroform Dibromoacetic acid (DBCA) Dibromoacetonitrile (DBAN) Dibromochloromethane (DBCM) Dichloroacetic acid (DCAA) Dichloroacetonitrile (DCAN) Haloacetic acid (HAA5) Trihalomethanes (THMs) N-Nitrosodimethylamine (NDMA) Hormones and Pharmaceuticals 17β-Estradiol Acetaminophen (paracetamol) Ibuprofen Caffeine Carbamazepine Gemfibrozil Sulfamethoxazole Meprobamate Primidone Others Triclosan Tris(2-chloroethyl)phosphate (TCEP) Perfluorooctanesulfonic acid (PFOS) Perfluorooctanoic acid (PFOA)

48 Risk Exemplar Methods (Detailed in Appendix A) Contaminant concentrations: Estimated initial concentration of contaminants in source waters based on literature review Estimated removal efficiencies and fate assumptions for steps in 3 scenarios (based on literature review) Microbial Risk Assessment: Used dose response equations shown in App. A. Assumed 1 L/d water consumption (unboiled). Chemical risk assessment: Risk based action levels (RBALs) determined for chemicals based on 2 L/d consumption (Table A-12) Margin of Safety = RBAL / drinking water conc. MOS > 1 not considered to be a significant health risk Verification

49 Risk Exemplar Results: Pathogens * The risks for Salmonella and Cryptosporidium in Scenario 3 were below the limits that could be assessed by the model.

50 Risk Exemplar Results: Chemicals

51 Risk Exemplar Conclusions The risk from 24 selected chemical contaminants in the two potable reuse scenarios does not appear to exceed the risk in common existing water supplies. With respect to pathogens, although there is a great degree of uncertainty, the committees analysis suggests the risk from potable reuse does not appear to be any higher, and may be orders of magnitude lower than currently experienced in at least some current (and approved) drinking water treatment systems (i.e., de facto reuse).

52 Ecological Enhancement Via Reuse Few studies have documented the environmental risks associated with the purposeful use of reclaimed water for ecological enhancement. risk issues not expected to exceed those encountered with the normal surface water discharge of wastewater. Trace organic chemicals have raised some concerns, because aquatic organisms can be more sensitive to trace organic chemicals than humans. Sensitive ecosystems may necessitate more rigorous analysis of ecological risks before proceeding with ecological enhancement projects with reclaimed water.

53 Costs Financial costs of water reuse are widely variable and dependent on site-specific factors Distribution system costs can be the most significant component of costs for nonpotable reuse systems. To determine the most socially, environmentally, and economically feasible alternative, water managers and planners should consider nonmonetized costs and benefits of reuse projects in their comparative cost analyses of water supply alternatives. Example benefits: Improved supply reliability Reduce dependence on imported water. Example costs: Reuse projects may have a larger (or smaller) carbon footprint than existing supply alternatives. Can reduce water flows to downstream users and ecosystems.

54 Social, Legal, and Regulatory Issues Water rights laws, which vary by state, affect the ability of water authorities to reuse wastewater. Enhanced public knowledge of water supply and treatment are important to informed decision making. The public, decision makers, and media need access to credible scientific and technical materials on water reuse to help them evaluate proposals and frame the issues. Public debate on water reuse is evolving and maturing as more projects are implemented.

55 Social, Legal, and Regulatory Issues Risk-based federal regulations for nonpotable reuse would provide nationwide minimum acceptable standards of health protection –could facilitate broader implementation of reuse. Modifications to the structure or implementation of the SDWA would increase public confidence in the potable water supply and ensure the presence of appropriate controls in potable reuse projects. –SDWA does not include specific requirements for treatment or monitoring when source water consists mainly of municipal wastewater effluent. –Such requirements could enhance public health protection and provide nationwide consistency when planned or de facto potable reuse is practiced.

56 Social, Legal, and Regulatory Issues EPA should fully consider the advantages and disadvantages of federal reuse regulations to the future application of water reuse to address the nations water needs while appropriately protecting public health. Application of legislative tools to effluent- impacted water supplies could improve the protection of public health. These could include: Updates to the National Pretreatment Programs list of priority pollutants. Increased designated use of surface waters for public water supplies.

57 Research Needs Health, Social, and Environmental Issues 1. Quantify the extent of de facto reuse in the U.S. 2. Address critical gaps in the understanding of health impacts of human exposure to constituents in reclaimed water. 3. Enhance methods for assessing the human health effects of chemical mixtures and unknowns. 4. Strengthen waterborne disease surveillance, investigation methods, governmental response infrastructure, and epidemiological research tools and capacity. 5. Assess the potential impacts of environmental applications of reclaimed water in sensitive ecological communities. 6. Quantify the nonmonetized costs and benefits of potable and nonpotable water reuse compared with other water supply sources to enhance water management decision making. 7. Examine the public acceptability of engineered multiple barriers compared with environmental buffers for potable reuse.

58 Research Needs Treatment Efficiency and Quality Assurance Develop a better understanding of contaminant attenuation in environmental buffers. Develop a better understanding of the formation of hazardous transformation products during water treatment for reuse and ways to minimize or remove them. Develop a better understanding of pathogen removal efficiencies and the variability of performance in various unit processes and multibarrier treatment and develop ways to optimize these processes. Quantify the relationships between polymerase chain reaction (PCR) detections and viable organisms in samples at intermediate and final stages. Develop improved techniques and data to consider hazardous events or system failures in risk assessment of water reuse. Identify better indicators and surrogates that can be used to monitor process performance in reuse scenarios and develop online real-time or near real-time analytical monitoring techniques for their measurement. Analyze the need for new reuse approaches and technology in future water management.

59 Federal and Nonfederal Roles in Research Addressing the research needs will require the involvement of several federal agencies as well as support from nongovernmental research organizations. Improved coordination is needed. If national water reuse regulations are developed, a more robust research effort will be needed with enhanced coordination among federal and nonfederal entities. Such an effort would benefit from the leadership of a single federal agency.

60 Overall Summary Expanding water reuse could significantly increase the nations water resource, particularly in coastal communities. Available technology can reduce chemical and microbial contaminants to levels comparable to or lower than those present in many current drinking water supplies. Modifications to the CWA and SDWA could ensure public health protection for both reuse projects and de facto reuse while increasing public confidence in water reuse. Improved coordination among federal and nonfederal entities could more effectively address key research needs.

61 Future Studies: Greywater? A follow-up NRC study could address: Quantity and suitability. How much greywater use occurs in the U.S. and for what applications? What is the suitabilityin terms of water quality and quantityof greywater for various purposes? Treatment. What types of treatment are available at a household level, and how do these treatment methods compare in terms of cost and energy use? What research should be pursued to produce improved technologies? Assessing costs and benefits. What are the costs and benefits of greywater use (including nonmonitized costs and benefits, such as impacts on wastewater infrastructure and effects on water and energy conservation)? Assessing risks. What are the human health and environmental risks of using greywater for various purposes? What existing state and regulatory frameworks address greywater use, and how effective are they in assuring the safety and reliability of greywater use practices?

62 62 U.S. Environmental Protection Agency Office of Wastewater Management Washington, D.C tele:


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