United States Environmental Protection Agency Office of Environmental Processes Effects Research Washington DC 20460 Research and Development EPA/600/S8-86/004 Aug. 1986 c/ERA Project Summary EPA Ground-Water Research Programs Brana Lobel This document describes the U.S. En- vironment^ Protection Agency's (EPA's) ground-water research pro- grams. The programs focus on protec- tion of ground-water resources by elim- inating or controlling sources of contamination; understanding and pre- dicting the movement and attenuation of contaminants in the subsurface; monitoring for contamination; restor- ing polluted aquifers; and ensuring that research findings are conveyed to pub- lic officials, field managers, and the sci- entific community. This Project Summary was devel- oped by EPA's Office of Environmental Processes and Effects Research, Wash- ington, DC, to announce key findings of the research project that is fully docu- mented in a separate report of the same title (see Project Report ordering infor- mation at back). Introduction Ground water is a vast and important resource. In the United States, approxi- mately 15 quadrillion gallons (56 quadrillion liters) of water are stored within 0.5 miles (0.8 kilometers) of the land surface. Ground water supplies about 25 percent of all fresh water used. Fifty percent of U.S. citizens obtain all or part of their drinking water from ground water; and 95 percent of rural house- holds depend totally upon it. Commer- cially, ground water is extensively em- ployed in agricultural practices, particularly for irrigation, and in various industries. Contaminants may leak, percolate, or be injected into aquifers. As contami- nants travel through the soil and into a ground-water system, they may be slowed down or degraded by processes that are complex and not completely understood, but these natural proc- esses are not totally effective for all con- taminants. For example, soils were once believed to be capable of binding and holding all chemicals. This is now known to be false for some important and widely used classes of chemicals, like organic solvents such as tri- and tet- rachloroethylene, benzenes, and carbon tetrachloride. Other contaminants such as heavy metals are not degradable at all but may be immobilized. Depending on the nature of the discharge arid the type of pollutant, contaminants may en- ter ground water as slugs (isolated masses) or localized plumes. ORD administers fourteen laborato- ries throughout the United States, four of which conduct research directly re- lated to protecting ground water (Fig- ure 1). Other ORD labs study drinking water quality, health effects, treatment technologies, analytical methods for water samples, and techniques for qual- ity assurance. These investigations, which often address contaminants oc- curring in both surface and ground water, also provide valuable informa- tion and control tools. In recent years, scientific knowledge about ground-water systems has been increasing rapidly. The ability to take uncontaminated samples in the subsur- face—previously a major limitation in research—has been greatly improved. At ORD, researchers have developed techniques that allow them to enumer- ate and characterize subsurface mi- crobes. ORD scientists have also stimu- lated the aerobic biodegradation of trichloroethylene (TCE). Improvements have been made in technology for as- sessing the subsurface, in adapting techniques from other disciplines to successfully identify specific contami- nants in ground water, and in assessing the behavior of certain chemicals in some geologic materials. Each of these research areas is discussed in detail in the full report. ------- t'' Source Control Control of contaminant sources on the land surface represents both the be- ginning and end point of current ground-water research efforts. Until more is known about subsurface proc- esses and their interactions with specific contaminants, source control remains the primary method for pre- venting ground-water contamination. At the same time, source control tech- niques are also used where contamina- tion has already occurred, for example, in the cleanup of unregulated dump sites or in emergency response to acci- dental spills. ORD supports two source control re- search programs through the Haz- ardous Waste Engineering Research Laboratory in Cincinnati, Ohio (HWERL- CIN). Both programs develop and evalu- ate state-of-the-art technology for haz- ardous waste management, storage, and disposal. The Hazardous Waste Land Disposal Program, in support of RCRA disposal regulations and guide- lines, investigates landfills, surface im- poundments, and underground storage facilities. The Removal and Remedial Action Program develops technology for emergency and ongoing hazardous waste site cleanup in support of CERCLA (Superfund). Table 1 lists cur- rent source control projects for both programs. A major issue for almost all in situ treatment processes is to develop a means of employing them quickly and efficiently. As one answer, HWERL engi- neers and contractors are currently field-testing a prototype mobile in situ containment and treatment unit (ISCTU). This is a 45-foot-long (14- meter-long) drop-deck trailer capable of treating approximately 80,000 square feet (7,500 square meters) of contami- nated soil approximately 25 feet (8 me- ters) deep per month. The system has the capacity to treat a variety of contam- inants in several different soils. The full report presents complete in- formation on these other source control projects: Hazardous waste land dis- posal; landfill cover systems; clay soil and synthetic liners; waste modifica- tion; system evaluation; and insitu re- moval and remedial action. Prediction Predicting pollutant behavior in the subsurface is one of the most difficult— but also one of the most important— tasks for ground-water protection pro- grams. Many interacting variables can influence the transport and fate of con- taminants: for example, the source o1 contamination, the type of pollutants climatic conditions, topography, anc the geological and biological character istics of the subsurface. The relative influences of various processes anc conditions on the behavior of a contam ADEMQA/HQ = Office of Acid Deposition, Environmental Monitoring and Quality Assurance EMSL/LV = Environmental Monitoring Systems Laboratory in Las »•/:/ Vegas 1 ERL/ATH - Environmental Research Laboratory in Athens HWERL/CIN = Hazardous Waste Engineering Research Laboratory in Cincinnati OEET/HQ = Office of Environmental Engineering and Technology in Washington OEPER/HQ = Office of Environmental Processes and Effects Research in Washington OER/HQ = Office of Exploratory Research in Washington HWERL/CIN, RSKERL/ADA = Robert S. Kerr Environmental Research Laboratory in Ada Source Control S^ y "X ^ n • Washington, DC / <(DEMQA/H< OEET/HQ OEPER/HQ OER/HQ RSKERL/ADA • Ada. Oklahoma — Production — Monitoring — In Situ Aquifer Cleanup Figure J. EPA offices and laboratories involved in ground-water research programs. of the Office of Research and Development. All offices and laboratories shown here are ------- inant can vary, dramatically affecting the accuracy of predictions. Knowledge of these interactions must be refined in order to develop and improve mathe- matical models to predict chemical transport and fate. In order to gain this knowledge, continued research is needed to obtain representative sam- ples, to develop more accurate labora- tory simulations (microcosms) of envi- ronmental systems, to conduct field verification studies, to refine tools and procedures used to measure chemical and physical reactions, and to deter- mine chemistry and biology in situ. At EPA's Robert S. Kerr Environmen- tal Research Laboratory in Ada, Okla- homa (RSKERL-AOA), researchers are investigating the movement of water in the ground (hydrogeology) and the var- ious physical, chemical, and biological attenuation processes that degrade or destroy contaminants. In addition, RSKERL scientists and engineers are in- vestigating methods for determining the mechanical integrity of injection wells and the interaction of injected fluids with geologic materials. The Environmental Research Labora- tory in Athens, Georgia (ERL-ATH) re- searches subsurface transport and transformation processes for organic pollutants and heavy metals, develops and tests leaching models for unsatu- rated zone transport to ground water, and provides technical assistance and methodology to support proposed RCRA regulations. Table 2 summarizes current predic- tion research at RSKERL and ERL-ATH. The full report describes all key predic- tion projects listed in Table 2. Monitoring Monitoring provides information on Table 1. Source Control Research Hazardous Waste Engineering Research Laboratory—Cincinnati, OH Area of Concern Project Title Purpose Goals and Products Land Disposal Office of Environmental Engi- neering and Technology (OEET)—Hazardous Waste- Surface Impoundments Land Disposal OEET—Hazardous Waste Technical Resource Docu- ments Land Disposal Support to Land Disposal Remedial Action Chemical Treatment Methods for Dioxins and Dibenzofurans Remedial Action Dioxin Assessment and Con- trol Research Assess and develop improved design, operation, and closure components for landfills, surface impoundments, and waste piles used for haz- ardous waste management. Areas covered in- clude gas and VOC (volatile organic chemical) emission control technologies, clay soil and FML (flexible membrane liner) liner performance, cover performance, contaminant/soil interaction, leachates, leak detection techniques, and dike construction criteria. Develop and update technical manuals for land- filling and surface impoundment of hazardous wastes, including information such as design, construction, and operating and monitoring pro- cedures. The manuals will address the design and installation of liners, the design of landfill covers to prevent infiltration, and closure proce- dures for surface impoundments. Develop design, operation, maintenance, and closure procedures for landfills. Research topics include the effects of subsidence on cover per- formance, chemical compatibility and service life prediction for synthetic liners, leachate col- lection and treatment efficiency, cost effective- ness of multi-layer cover systems, assessment of maintenance-free cover systems, and the im- pact of designing secure landfills in saturated soils. Develop and evaluate methods for the destruc- tion of dioxins and other chemically related wastes in soils, sediments, and contained waste streams. Laboratory and field studies will ad- dress the feasibility of UV photolysis and APFEG reagents for treatment of dioxin-contaminated soils, the removal of chlorinated dioxins from contaminated soils, the application of alkali polyethylene glycolate complexes to destroy dioxins in Missouri soils, and the supercritical extraction of chlorinated dioxins from soils. Evaluate the feasibility of incineration for on site detoxification of dioxin-contaminated liquid wastes and soils. • Technical Resource Docu- ments (TRDs) • Computer programs to review land disposal permit applica- tions. • "Expert Information" comput- erized systems on contain- ment technologies. • Technical assistance to RCRA permit writers. • Improved design and technol- ogy. • Provide state-of-the-art techni- cal information to field man- agers and Federal, state, and local officials. Develop and improve the per- formance of components and the unit operations of secure landfills to comply with RCRA regulations. Improve chemical and physi- cal contaminant destruction technology. Improve contamination de- struction processes. ------- Table 1. (Continued) Area of Concern Project Title Purpose Goals and Products Remedial Action Engineering Support for Site and Situation Assessment Remedial Action Provide Technical Support to Enforcement Program and Re- gional Offices Apply engineering expertise to assessments of hazardous waste site situations (e.g., waste characteristics, hydrology, geology, and soil characteristics) to assist in developing corrective measures. Develop criteria for conducting site assessments. Prepare feasibility studies regard- ing data requirements for remedial action deci- sions. Provide scientific information and analyses in support of litigation on corrective actions at Su- perfund sites. Support areas include review of designs for remedial actions, review of data submitted by liable parties, expert witness testi- mony, technology transfer, emergency response assistance at releases and waste sites, supervi- sion of cleanup operations involving ORD equip- ment, analytical support using mobile and cen- tral laboratories, and technical support regarding the designation of hazardous sub- stances and assignment of reportable quantities. Technical assistance at haz- ardous waste sites. • Technical assistance to EPA regional and state and local officials. Removal and Reme- dial Action Evaluate Technology to Man- age Uncontrolled Waste Sites Removal Action Prevent and Contain Haz- ardous Material Releases Removal Action Special Biodegradation Proc- esses for Detoxifying Contam- inated Soils Evaluate improved and new technologies for emergency and remedial actions for hazardous material spills and newly discovered releases of hazardous substances from uncontrolled waste sites. Topics include field evaluation of prototyp- ical mobile equipment and innovative commer- cially available equipment, the use of chemicals for mitigation of the effects of hazardous sub- stance releases, fugitive dust control proce- dures, and the fixation of contaminated soils. Develop new and improved technology for the prevention and control of pollution from haz- ardous material releases by adapting related in- dustrial technologies. Research topics include spill or accidental release prevention, ore- response planning, containment and confine- ment, separation and concentration, the destruc- tion of collected cleanup residuals, and the selection of chemicals to control releases of floating hazardous substances. Develop and evaluate biological methods for the destruction or detoxification of chemicals in soils. Genetic engineering and other biological techniques will be used to determine if living or- ganisms such as plants, yeast, and microbes can be employed to successfully transform or degrade such substances as organochlorine compounds, 2,4,5-trichlorophenoxyacetic acid, chlorinated dioxins, and halogenated hydrocar- bons. • Provide most effective tech- nology for spill control and i lease cleanup. Improve technology for emt gency handling of hazardou releases. • Cost-effective decontamina tion techniques. potential or known contamination. Many types of monitoring may be per- formed for a variety of reasons to deter- mine probable contaminant pathways, to map actual contaminant flow, to lo- cate sources of contamination, to iden- tify contaminant plumes, and to detect leaching, percolation, or leaks. Monitor- ing research, conducted at the Environ- mental Monitoring Systems Laboratory in Las Vegas, Nevada (EMSL-LV), with assistance from the Robert S. Kerr Envi- ronmental Research Laboratory in Ada, Oklahoma (RSKERL-ADA), focuses on developing ground-water monitoi and sampling techniques and geoph cal monitoring techniques, and refii methods for interpretive analysi) data. These techniques and meth are used to define the nature, local and movement of subsurface conti ------- Table 2. Ground-Water Prediction Research Robert S. Kerr Environmental Research Laboratory—Ada, OK Environmental Research Laboratory—Athens, GA Area of Concern Project Title Purpose Goals and Products Biological Processes Determination of Subsurface Microbial Activity Biological Processes Hydrogeologic Proc- esses Management Aids Management Aids Management Aids Management Aids Management Aids Management Aids Prediction of Microbial Con- taminant Concentrations Determination of Dispersion Coefficient Processes Determination of Waste Mo- bility by the Use of Micro- cosms Enforcement and Other Tech- nical Support Evaluating Ground-Water Contamination Risks from Hazardous Waste Disposal Methods to Determine the Im- pact of Geology on Ground- Water Quality Standard System for Evaluat- ing Ground-Water Pollution Potential Using Hydrogeologic Settings Validation of Predictive Tech- niques for Environmental Ex- posure Adapt methods such as electron and epifluores- cence microscopy and muramic acid assays to determine the abundance and metabolic activi- ties of indigenous microflora in subsurface habi- tats. Develop methods to estimate the propor- tion of metabolically active bacteria to determine their nutritional state. Develop and evaluate predictive models describ- ing the movement and survival of viruses and pathogenic bacteria in ground water. Conduct field investigations to develop an understanding of physical and chemical compo- nents of dispersion. Evaluate soil profile and aquifer microcosms for their capacity to predict hazardous waste move- ment. Test protocols using selected chemicals from RCRA Section 3001. Compare results with field verification studies. Provide consultation, project supervision, testi- mony, and analytical support for Superfund ac- tivities involving ground-water contamination. Investigate the processes that govern the trans- port rates, transformation, and fates of haz- ardous waste constituents in the subsurface. Evaluate mathematical models describing solute transport in the subsurface. Assess validity through field experiments. Develop techniques for determining the impact of geology, including the impact of surface de- velopment and water use, on ground-water quality. Develop methods for detecting geologi- cal areas within an aquifer that should not be developed for public water use because of natu- rally occurring contaminants such as chromium, selenium, uranium, and arsenic. Develop a protocol to determine the pollution potential of any United States aquifer or area within an aquifer based on hydrogeologic crite- ria. Provide training and guidance in the use of the protocol. Develop an extensive field data base to estab- lish parameters to test exposure assessment models. These models are designed to assess pesticide migration through the saturated and unsaturated zones. Physical and Chemi- Mathematical Models for Sub- Create or modify a range of models for predict- cal Processes surface Transport and Fate ing concentrations of toxic chemicals in the sub- surface. Develop improved methods for identifying and characteriz- ing subsurface microflora. • Provide methods and data for predicting chemical concentra- tions in ground water at a point of use. • Determine the physical and chemical components of dis- persion as used in solute transport models. • Increase applicability of pre- diction equations. • Develop screening methods to assess hazardous waste expo- sure potential. • Provide technical support. • Provide field-evaluated meth- ods and data to predict con- centrations of contaminants from the treatment, storage, and disposal of hazardous wastes. • Develop methods for deter- mining impact of naturally oc- curring geological materials and conditions on ground- water quality. Provide technical basis for planning the location of land disposal sites. Preliminary system has been published, current field evaluations will lead to the development of the protocol. Validate pesticide exposure assessment models, including PRZM, PESTANS, SESOIL, and SWAG. • Provide a choice of mathemat- ical models of contaminant transport and fate, suitable for a variety of computers, to aid in estimating exposure of hu- mans, animals, and plant life. ------- Table 2. (Continued) Area of Concern Project Title Purpose Goals and Products Physical and Chemi- cal Processes Physical, Chemical, and Biological Proc- esses Movement and Persistence of Dioxins in Soils and Ground Water Prediction of Chemical Con- taminant Concentrations Determine batch sorption isotherms using la- beled dioxins. Evaluate successive additions and extractions of dioxins to determine desorption characteristics and sorption kinetics in the sub- surface. Validate transport potential using unsat- urated microcosms. Examine sorption/retardation of organic contam- inants in the subsurface in terms of subsurface characteristics and organic chemical properties. Define the subsurface microbial population and investigate capability to transform organic pollu- tants. Study abiotic transformations of organics and concentration effects on sorption and trans- port. • Provide capability to predict the rate of movement and transformation of dioxins in soils and ground water. • /Assess potential for human exposure to dioxin. • Provide methods and data to predict concentrations of microbial contamination in ground water. nation. Table 3 lists current monitoring projects. The laboratories also provide operational guidance and technical sup- port to EPA program and regional of- fices, and to state and local agencies. The full report describes each of the projects listed in Table 3. In Situ Aquifer Cleanup Restoring a polluted aquifer is gener- ally an extremely expensive enterprise. Nevertheless, in some instances, restor- ation is the option of choice, for exam- ple, when there is no other local drink- ing water source, when the cost of transporting water from an alternative source equals or surpasses the cost of restoration, or when the damage to the aquifer has serious human health or ecological implications. The decision to attempt restoration of a polluted aquifer is rarely simple or clear-cut. Technical feasibility is only one aspect to consider and is often not the most pressing one. Economic, health, social, political, and other factors must be weighed against one another. Until a range of inexpensive, effective cleanup methods is developed, man- agers who must decide whether to re- store an aquifer face a series of difficult decisions. Serious thought, good man- agement skills, and a solid information base are required. To meet these needs, researchers at RSKERL are concentrat- ing on two approaches to improve exist- ing cleanup methods: they are examin- ing ways of making restoration techniques less expensive and more easily applicable, and they are examin- ing case histories of restoration efforts to identify factors that influenced their success or failure. From this base, they are developing guidelines for decision- making. Table 4 summarizes current re- search projects at RSKERL. The full re- port describes several other key insitu aquifer cleanup projects. Information Transfer and Technical Assistance Transmitting information about cur- rent research to decision makers, field managers, and the scientific community is an important part of EPA's ground- water research programs. New research findings are communicated directly to the scientific, technical, and manage- ment community via information trans- fer mechanisms such as articles, docu- ments, symposia, conferences, and training programs. In addition, ORD staff offer technical assistance to a vari- ety of sources (for example, EPA re- gional and program offices, other fed- eral and state agencies) to solve specific environmental problems. The Robert S. Kerr Environmental Re- search Laboratory (RSKERL) conducts many information transfer activities and, in recent years, has provided tech- nical assistance at over a dozen haz- ardous waste field sites in nine states. At the Environmental Monitoring Sys- tems Laboratory (EMSL), technical sup- port investigations and training in geophysics are an important part of lab- oratory activities. Hazardous Waste En- gineering Research Laboratory (HWERL) researchers provide scientific information and analysis in support of corrective actions at Superfund sites, as well as producing a series of technical handbooks on source control technol- ogy in support of CERCLA, and technical resource documents (TRDs) on specific areas of landfill design. HWERL has also recently established the Technical Infor- mation Exchange (TIX), a specialized reference center that provides state-of- the-art information on hazardous waste cleanup and emergency response tech nology. In addition to its technical sup port for the 1984 RCRA amendmen land disposal banning rule, the Environ mental Research Laboratory in Athens Georgia (ERL-ATH) maintains the Cen ter for Water Quality Modeling. ORD also supports two centers tha specialize in ground-water informatiot transfer. The National Ground-Water In formation Center (NGWIC) in Worthing ton, Ohio, houses the world's larges catalogued and retrievable collection o ground-water literature, concentratini on hydrogeology and water-well tech nology. It contains more than 10,00' volumes, including state publication? technical reports, government docu ments, maps, reference books, and re lated literature, plus over 120 periodic* subscriptions. The NGWIC maintains it own computerized data base, with mor than 35,000 references, and has the abi ity to search two international retriev< systems with access to over 150 add tional data bases. The Internatiom Ground Water Modeling Cente (IGWMC) serving North, Central, an South America, is located in Indian; polis, Indiana. The Center, supports largely by the EPA and in part by tr Holcomb Research Institute at Butli University, operates a clearinghouse f< more than 600 ground-water model organizes and conducts short coursi and seminars, and conducts a researc program on ground-water modeling. second IGWMC office in Delft, tf Netherlands, not directly supported I EPA, serves Europe, Asia, Africa, at Australia. Synergism in Research: the Stanford/Waterloo Project Of necessity, ground-water r ------- Table 3. Ground-Water Monitoring Research Environmental Monitoring Systems Laboratory—Las Vegas, NV Robert S. Kerr Environmental Research Laboratory—Ada, OK Area of Concern Project Title Purpose Coals and Products Monitoring and Sampling Geophysical Surveys of Haz- ardous Waste Sites Monitoring and Sampling Ground-Water Quality Protec- tion from Injection Wells Provide geophysical and geochemical monitor- ing support to EPA regional offices and EPA's Emergency Response Team for assessment of CERCLA hazardous waste sites. Test the mechanical integrity of injection wells. Develop an overview of contamination cases as- sociated with Class II and V injection wells. • Meet RCRA land disposal reg- ulations for ground-water de- tection and compliance moni- toring for contaminants leaking from permitted facili- ties. • Provide cost-effective monitor- ing techniques. • Support remedial and removal actions at CERCLA sites. • Establish standard procedures for the application of geophysical and geochemical techniques. • Conduct geophysical surveys on request. • Provide technical support in the implementation of Under- ground Injection Control (UIC) regulations. Monitoring and Sampling Monitoring and Sampling Methods for Monitoring Well Construction Monitoring Ground Water with Fiber Optics Technology Monitoring and Sampling Unsaturated Zone Monitoring for Hazardous Waste Sites Monitoring and Sampling Geophysics Well Construction and Sam- pling for Ground-water Qual- ity Analyses Detection of Leachate Plumes in Ground Water with Geophysics Assess alternative methods for constructing monitoring wells to determine problems with surface and subsurfce contamination; select and field-test recommended monitoring options. Evaluate the feasibility of performing contaminant-specific ground-water monitoring using fiber optics technology combined with laser fluorescence spectroscopy. Evaluate agricultural equipment and methods for monitoring in the vadose zone to detect leaching and percolation of pollutants from haz- ardous wastes. Determine the relative effective- ness of suction and gravity lysimeters. Develop methods for constructing, completing, and sampling ground-water monitoring wells to obtain representative physical, chemical, and bi- ological data. Evaluate geophysical and geochemical methods to detect and map organic and inorganic leachate plumes at hazardous waste sites, em- phasizing soil-gas sampling techniques for map- ping organic plumes. Determine and recommend preferred well drilling and sealing techniques to derive accurate ground-water sam- ples. Develop methodology and hardware to monitor organic and Inorganic chloride con- centrations. Conduct field demonstration to identify weaknesses in the methodology. Improve response time and lower cost of monitoring tech- nology. Adapt existing technology to meet RCRA regulations for monitoring at permitted land treatment or land farming dis- posal areas. Provide guidance for lysimeter performance for permit writers. Develop technical resource document on unsaturated zone monitoring at hazardous waste land treatment units. Update manual for sampling ground-water quality parame- ters Establish guidelines for the number of sample points re- quired to map a plume. Develop quality assurance guidelines for the calibration of equipment and procedures for mapping hazardous waste sites. ------- Tab/0 3. (Continued) Area of Concern Project Title Purpose Goals and Products Provide guidance on the appli- cation of geophysical and geochemical techniques to hazardous waste sites. Recommend procedures for hazardous waste site investi- gations. Geophysics Downhole Sensing for Haz- ardous Waste Site Monitoring Geophysics Interpretive Analysis Geophysical Sensing of Fluid Movement from Injection Wells Locating Abandoned Wells with Historical Photographs Interpretive Analysis Indicator Methods for Ground-Water Detection Mon- itoring Design, build, modify, and evaluate sensing devices and methods used to obtain geohydro- logic data from monitoring wells. Map the migration of wastes from injection wells at depths of 1,000+ feet at several field sites, using the time-domain electromagnetic method. Identify abandoned oil and gas wells through historical aerial photographs and verify by com- parison with conventional records. Determine parameters that indicate the presence of hazardous constituents in ground water at land disposal sites, using existing data from Consent Decree, Super-fund, and RCRA site monitoring files. Develop new technology or modify existing technology fa typical small-diameter, shallow-depth, plastic-cased monitoring wells. Develop procedural manual for use by site operators and regulatory personnel. Make conference presenta- tions on project efforts. Assess the applicability of time-domain EM technology to meet Underground Injec- tion Control (UIC) regulation requirements. Develop a technical transfer report. Assist EPA regional officials examining large areas for abandoned gas and oil wells to comply with UIC regula- tions. Provide reports with area maps indicating photo- identified oil and gas well to cations. Evaluate performance of se- lected indicator parameters. Meet RCRA requirements fo detection and compliance monitoring as part of land c posal ground-water monitoi ing programs. Identify "missed classes" o; hazardous constituents. Develop a short list of parameters that are (1) reli- able indicators of leakage, < (2) inexpensive to measure. searchers often examine discrete sub- ject areas (for instance, dispersion in certain immiscible fluids), and study them on a small scale (for instance, in a laboratory microcosm). Because ground water is a complex subject, this is often the best way to gain a clearer comprehension of individual processes. However, researchers must consider whether the results of short-term, dis- crete, small-scale studies will validly translate to the long-term realities of contaminant movement in ground water. The question arises: How to take the small pieces of the puzzle and fit them into a larger, coherent whole? In one effort to address this question, ORD has sponsored the Stanford/ Waterloo project, an attempt to provide new understanding of the long-term be- havior of contaminants in ground water. This project is an extramural ef- fort monitored by the RSKERL labora- tory and conducted jointly by Stanford University and the University of Water- loo, Ontario, Canada. It has two compo- nents: a large-scale study of orga contaminant transport, and an inve gation of leachate from municipal Se tary landfills. Each of these studies described in detail in the full report. Future Directions Ground water presents a series complex issues for study. Our indusl society, with its plethora of chemi< and by-products, combined with oui verse topography, geohydrology, climate, create an intricate matrix ------- Table 4. In Situ Aquifer Cleanup Research Robert S. Kerr Environmental Research Laboratory—Ada, OK Area of Concern Project Title Purpose Goals and Products Case History/Cost- Benefit Analysis Case History/Cost- Benefit Analysis Technology Technology Technology Technology Methods for Protecting Public Water Supplies from Existing Ground-Water Contamination Analysis of Cost-Effectiveness of Aquifer Restoration Tech- niques Feasibility of Enhancing the In Situ Biodegradation of Con- taminants in Ground Water Laboratory and Field Evalua- tion of Methodology for In Situ Aquifer Restoration Simulated Aquifer Restoration Monitoring the Development of Active Subsurface Organ- isms During Bioreclamation of Polluted Aquifers Determine cost-effectiveness and feasibility of alternate aquifer cleanup methods by examining social, political, institutional, and technical is- sues in case studies. Evaluate incremental benefits versus incremen- tal costs of cleaning up a range of waste sites, considering political, social, economic, and med- ical issues, as well as cleanup effectiveness. Detect the presence of plasmid DNA in ground- water bacteria and evaluate the ability of ground-water bacteria to act as hosts for specific plasmid DNA associated with biodegra- dation. Evaluate the behavior of the plasmids in subsurface material. Evaluate selected cleanup methods, including physical removal, chemical treatment, and en- hanced biodegradation for feasibility and cost- effectiveness. Test aquifer restoration methods under simu- lated conditions by creating an artificial aquifer that can be mathematically represented. Evaluate existing methods for determining the population sizes of bacterial groups that may be used to biodegrade contaminants in aquifers. • Provide states and localities with methods of assessing technology to protect public water supplies. • Determine the effectiveness of various aquifer restoration techniques. • Develop hierarchical decision- making set to determine "how clean is clean?" • Evaluate the feasibility of en- hancing in situ biological degradation of ground-water contaminants. • Develop cleanup protocols using the results of the proj- ect. • Develop the process for aero- bic degradation of TCE (trichloroethylene) for use in the field. • Use artificial aquifer systems to develop aquifer restoration methods. • Increase scientific information that will lead to effective bioreclamation techniques. contamination scenarios. Physical and chemical theories must be modified to apply to variable and often inaccessible conditions in the subsurface. The rela- tive newness of ground-water investi- gation, combined with its complexity, point to several basic research priori- ties: • Identify and study major existing and potential contamination sources and agents. • Invent and/or refine effective, inex- pensive technology for monitoring and sampling, source control, and basic predictive research. • Develop reliable mathematical models to predict the movement and transformation of contaminants in ground water. • Provide ground-water training for EPA, state, and local officials. • Transmit information quickly. The time lag between the verification of research findings and practical ap- plication should be made as narrow as possible. To supplement these recommenda- tions, Appendix A of the full report pre- sents the principal findings and recom- mendations by the Ground-Water Research Review Committee of EPA's Science Advisory Board. The commit- tee's recommendation covers staffing, the Superfund, accelerated research, technology and training. Ground-Water Research in Other Federal Agencies Several Federal agencies sponsor re- search programs that examine ground- water-related issues. The descriptions of their research given in the full report are not intended to be comprehensive but rather to provide a general context in which to place EPA's research pro- grams. For more detailed information, the reader should contact the specific agencies mentioned. The ground-water research of other Federal agencies is summarized in Table 5. EPA integrates its research ef- forts with these other agencies through joint projects, work groups, committee participation, and informal information exchange. The United States Geological Survey (USGS) is the major Federal agency doing ground-water research, and receives the bulk of Federal fund- ing. Since 1981, EPA has operated under a general memorandum of understanding (MOD) with the USGS. As a result of EPS's Ground-Water Pro- tection Strategy (of which the research program are a part), an MOU specifi- cally on ground water was signed in June 1985. It addresses data collection and technical assistance as well as re- search coordination. Appendix B of the full report describes in detail the re- search programs listed in Table 5. ------- Table S. Ground-Water Research In Other Federal Agencies Research Category Agency Source Control Prediction Monitoring Cleanup Objective U.S. Air Force U.S. Army Corps of Engineers U.S. Department of Agricul- ture U.S. Department of Energy U.S. Geological Survey National Science Foundation' U.S. Navy2 Tennessee Valley Authority Develop methods for predicting the impact oi Air Force activities on ground water. Develop cost-effective ground-water pollutior control and monitoring systems; provide en- vironmental and health effects data on Army- unique pollutants; develop environmental management systems and data bases. Provide basis for evaluating effects of changes in agricultural techniques on ground-water quality. Provide information on mechanisms con- tributing to transport and long-term fate of energy-related contaminants in ground water. Provide research to describe, assess, and de velop ground-water resources. Perform basic research. Provide data needed for assessing the signh cance of potential Tennessee Valley ground- water contamination sources and for pre- venting and isolating contamination. 1 Fundamental researach will contribute to all areas, although it is not necessarily specifically directed toward ground-water projection. ^Program just beginning to be defined. The EPA author Brana Lobel is with the Office of Environmental Processes and Effects Research, Washington, DC 20460. The complete report, entitled "EPA Ground-Water Research Programs,"(Order No. PB 86-212 552/AS; Cost: $9.95, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephone: 703-487-4650 The EPA author can be contacted at: Office of Environmental Processes and Effects Research U.S. Environmental Protection Agency Washington, DC 20460 10 ------- rtwrn MOCTt o »-» O o O o O ZZ oo < »r WMTJ ODOXJ 3DXIO -4 H M5O HI f"«I O ill Z O <^ 0i rn o z *. o ------- |