United States Environmental Protection Agency Industrial Environmental Research^' Laboratory Research Triangle Park NC 27711 Research and Development EPA-600/S9-82-017 Feb. 1983 Project Summary Proceedings: Symposium on Environmental Aspects of Fuel Conversion Technology—VI, A Symposium on Coal-Based Synfuels—October 1981 F. A. Ayer and N. S. Jones The document summarizes or con- tains an abstract of each presentation made at the EPA-sponsored sympo- sium, October 26-30, 1981, in Den- ver, CO. The symposium provided a forum for the exchange of ideas and for discussion of environmentally re- lated information on coal gasification and liquefaction. Process developers and users, research scientists, and government officials reported on re- sults achieved from research projects, synfuels process development, inter- agency programs, control technology evaluation, and regulatory actions. The program included sessions on en- vironmental source test and evalua- tion results for gasification, indirect liquefaction, and direct liquefaction processes, and water-, air-, solid waste-, multimedia-, and product- related environmental considerations. Approx- imately 215 participants attended the 5-day symposium. This Project Summary was devel- oped by EPA's Industrial Environmen- tal Research Laboratory, Research Tri- angle Park. NC, to announce key find- ings of the research project that is fully documented in a separate report of the same title (see Project Report ordering information at back). This report summarizes speakers' presentations contained in the proceed- ings of the EPA-sponsored Symposium on the Environmental Aspects of Fuel Conversion Technology - VI, a Sympo- sium on Coal-Based Synfuels, Denver, CO, October 26-30, 1981. The sym- posium provided a forum for the ex- change of ideas and for discussion of environmentally related information on cba) gasification and liquefaction. Pro- cess developers and users, research scientists, and government officials re- ported on results from research proj- ects, synfuels process development, interagency programs, control technol- ogy evaluation, and regulatory actions. The program included sessions on environmental source test and evalua- tion results for gasification, indirect liquefaction, and direct liquefaction pro- cesses, and water-, air-, solid waste-, multimedia- and product-related en- vironmental considerations. Approxi- mately 215 participants attended the symposium. Abstracts of speakers' remarks follow: Session I, Part A. Environmental Source Test and Evaluation Results, Gasification and Indirect Liquefaction Characterization of Process Liquids and Organic ------- Condensates from the Lurgi Coal Gasification Plant at Kosovo, Yugoslavia K.J. Bombaugh, K.W. Lee, and R.G. Oldham, Radian Corp. Austin, TX 78766 S. Kapor, Institut za Primenu Nuklearne Energy Beograd-Zemun, Yugoslavia Process liquids and gaseous stream condensates from the Lurgi Coal gasifi- cation plant at Kosovo were character- ized to define theirorganiccomposition. Samples of entrained liquids and condensates were collected during Phase II of the Kosovo source test that was described at the preceding synfuels symposium. These samples were char- acterized 'by liquid chromatographic fractionation using EPA's protocol for a Level I source assessment. In addition, GC/MS analyses were per- formed on key samples to quantify their levels of potentially hazardous PNAs, and GC with selective detection was used to characterize sulfur- and nitrogen-bearing species. This presentation discussed the analytical results and impact that these condensates had on the plant's dis- charge stream severity. It also compared the composition of liquids from the Lurgi process with that of liquids from other processes. Application of Kosovo (Lurgi) Gasification Plant Test Results to Pollution Control Process Design G.C. Page, W.E. Corbett, and R.A. Magee, Radian Corp. Austin, TX 78766 This paper describes a test program performed by Radian Corporation to obtain process data to define the pollution control technology require- ments for Lurgi-based coal gasification plants. This program was sponsored by EPA's Industrial Environmental Research Laboratory (Research Triangle Park) and conducted at a Lurgi-based gasification plant in the Kosovo region of Yugoslavia. It should be emphasized that the Kosovo plant does not reflect state-of-the-art Lurgi technology especially in pollution control practices. However, the uncon- trolled process discharge streams from the Kosovo plant are representative of those from Lurgi-based gasification plants. From an assessment of the Kosovo data, the following discharge streams were selected to be key based on flow rate and/or concentration of pollutants: (1) high- and low-pressure coal lock vent gases and ash from the gas production section, (2) liquid depressur- ization gases and surge tank vent gases from tar/oil separation section, (3) HaS- and C02-rich vent gases from the Rectisol acid gas removal section, and (4) extracted wastewater from the Phenosolvan unit. The conclusions of an engineering evaluation of the components in those key discharge streams and the effects those components may have on pollution control processes were: (1) pollution control processes are commercially available for treating these streams; (2) the effects of minor and trace compo- nents on the performance of those control processes have not been dem- onstrated, and there may be problems in the direct transfer of technology from other industries (e.g., coke ovens); (3) the design and selection of pollution control processes during transient and normal operation should occur in parallel with the base plant design; and (4) the variability of the components in the discharge streams must be determined and included in pollution control process design. Environmental Aspects of the GKT Coal Gasification Process R.E. Wetzel, GKT 43 Essen, Federal Republic of Germany K.W. Crawford, TRW Redondo Beach, CA 90278 W.C. Yee, TVA Chattanooga, TN 37401 Thermal conversion of coal is always accompanied by the production of: pyrolysis products; solid wastes like ash, slag, or fly dust; different sulfur compounds; and a number of undesired trace compounds in the gas. The quality and quantity of these components depend on the applied process principle, the composition of the reactants, and the main process parameters (e.g., temperature and pressure). The GKT high-temperature, entrained coal gas- ification process, well-established commercially for 30 years, offers coa conversion with minimum environmen tal impact. To evaluate the operating condition; and environmental impact when gasify ing American coal, TVA and GK1 conducted a large-scale test with abou 5,000 short tons of Illinois No. 6 coal in < commercial coal-to-ammonia plant ir Greece. TRW, funded by TVA, cooperatec in the extensive test program regarding the environmental aspects. The favor able results of the test runs, carried ou in March/April 1981, and the extraordi narily low environmental impact demon strated, have led to TVA's decision t< build its Murphy Hill plant based 01 GKT's technology. Source Test of the Texaco Gasification Process Located at Oberhausen-Holten, West Germany R.G. Wetherold and R.M. Mann, Radian Corp. Austin, TX 78766 J. Morgan and W.C. Yee, TVA Chattanooga, TN 37401 P. Ruprecht, Ruhrchemie AG 4200 Oberhausen-Holten, Federal Republic of Germany R. Diirfield, Ruhrkohle 01 und Gas GmbH 4250 Bottrop, Federal Republic of Germany A comprehensive environmente characterization of water and solid from the Ruhrkohle/Ruhrchemie co< gasification pilot plant in Oberhauser Holten, West Germany, has bee conducted. Coal is gasified at the plar with a high-pressure, entrained-be coal gasification process. The pilot plat tests were conducted in Novembe 1980 during gasification of Illinois No. coal. A test plan was prepared includin stream selection, sample collection an chemical analyses. Multiple samples < process waters and solids were collects during two 12-hour environment! balance periods. Normal pilot plat operation was maintained during th first period; the second incorporate water recycle to minimize makeu water requirements. Samples of liquid and solid proce; streams have been subjected to compr hensive analyses. These efforts, undi contract with TVA, have been perform( ------- to provide support information on both the process operation and environmen- tal impact associated with a 10,000-ton per day coal gasification plant proposed by TVA for a northern Alabama site. Topics addressed in the presentation included pilot plant configuration and operation, treatment of the process water, and RCRA testing of solids from the gasification and water treatment processes. Source Test and Evaluation of a Riley Gas Producer Firing North Dakota Lignite F.L Jones, American Natural Service Co. Detroit, Ml 48226 W.P. Earley, Riley Stoker Corp. Worcester, MA 01613 M.R. Fuchs, Radian Corp. Austin, TX 78766 V.A. Kolesh, Riley Stoker Corp. Worcester, MA 01613 A 10-ft 6-in. diameter Riley Morgan gasifier was operated for 14 days to convert North Dakota lignite to low Btu gas. During that period, the gasifier was operated at a range of load conditions, and the product gas was transported to a commercial-scale kiln burner in a large combustion test chamber. Process stream conditions and compositions were recorded throughout the test and were submitted to an SAM/IA analysis. Gaseous effluent streams were found to be well controlled due to the unique Riley coal-feed and poke-hole systems. Solid wastes from the process (gasifier ash and cyclone dust) were found to be nontoxic, noncarcinogenic, and nonmu- tagenic. Gasifier wastewater effluent (ash pan water) was similarly found to be nonhazardous. Although combustion stack gases were not monitored, sulfur and particulate loadings in the gasifier product gas indicated that the stack gases would comply with current EPA New Source Performance Standards. If all reduced nitrogen compounds were converted to NOx, however, these emissions would exceed New Source Performance Standards. Session I, Part B. Environmental Source Test and Evaluation Results, Direct Liquefaction Environmental Program and Plans for the EDS Coal Liquefaction Project R.L Thomas, Exxon Research and Engineering Co. Florham Park, NJ 07932 The Exxon Donor Solvent (EDS) coal liquefaction project is a unique govern- ment/industry arrangement for devel- oping EDS technology to the point that commercial plants can be designed with an acceptable level of risk. A broad environmental program is being advanced within the project to address plant emission, occupational health, and product-related environmental concerns associated with the direct liquefaction of coal. The current plans, status, and outlook for the EDS environmental program provide an overall strategy for the acquisition of data relating to these concerns early in the technology development cycle. Sampling and Analysis of Process and Effluent Streams from the Exxon Donor Solvent Coal Liquefaction Pilot Plant M.D. Notich and J.I. Kim, Hittman Associates, Inc. Columbia, MD 21045 Under contract to the U.S. EPA, Hittman Associates performed a sam- pling and analysis of process discharge streams from the Exxon Donor Solvent (EDS) coal liquefaction plant in Baytown, TX. Twenty-four streams were sampled and 2,200 samples were returned to Hittman's laboratory for analysis. The chemical analyses of these samples included water quality parameters, GC/MS, GC/FID, and bioassays. Analyses were also performed to determine the accuracy and precision of the data and to determine the variability of stream components due to process variations. Preliminary results are available and data for the source test and evaluation report are being evaluated. Health and Environmental Studies of H-Coal Process K.E. Cowser, J.L Epler, C.W. Gehrs, M.R. Guerin, and J.A. Klein Oak Ridge National Laboratory Oak Ridge, TN 37830 With the implementation of the Energy Security Act of 1980, coal and oil shale are expected to be principal sources for petroleum and natural gas substitutes. H-Coal is one of several processes under intensive study for the direct conversion of coal to the desired synthetic fuels. This paper describes the health and environmental study program of H-Coal, sponsored by the Department of Energy. Presented are the results of the chemical, biological, and ecological characteriza- tion of products and by-products derived from the operation of a process devel- opment unit. These initial results provide an informed basis for subse- quent monitoring and testing of the nominal 200- to 600-ton/d pilot plant at Catlettsburg, KY. Chemical Characterization and Bioassay of SRC Process Materials W.D. Felix, D.D. Mahlum, B.W. Wilson, W.C. Weimer, and R.A. Pelroy Battelle Pacific Northwest Laboratory Richland, WA 99352 Bioassay techniques have shown that certain coal liquefaction process streams and products are both mutagenic (Ames assay) and carcinogenic. These materials have been chemically fractionated using a number of techniques (solvent extraction, alumina column separation, HPLC, Sephadex LH-20) in an attempt to identify the constituents responsible for the biological activity. These studies have shown that primary aromatic amines (PAAs) account for more than 90% of the mutagenic response in the Ames test. Long-term skin painting and initiation-promotion assays indicate that the PAAs may also play a role in the carcinogenicity of the coal-derived materials. However, while the PAAs can be designated as the determinant mutagens in coal liquids, they cannot be assigned a determinant role in skin ------- carcinogenesis. Thus far, carcinogenicity appears to better correlate with increas- ing molecular weight and boiling point. Our results also suggest that benzo(a)py- rene is not a reliable marker compound for carcinogenic activity. (Only the abstract is published in the proceedings.) Session II. Water-Related Environmental Considerations Coal Conversion Wastewater Treatment/Reuse - An Overview F.E. Witmer, U.S. Department of Energy Washington, DC 20545 Environmentally, synfuels can be produced from coal by either low- or high-temperature processes. Low- temperature processes produce high boiling liquids and tars which tend to retain the multiple-ring structure of the original coal "molecule," while high- temperature processes typically produce synthesis gas, methane, and/or light liquids. Dry-ash moving-bed gasification and direct liquefaction processes are representative of low-temperature conversion processes. Entrained gasifi- cation is an example of high-tempera- tures processes. Fluid-bed gasification processes that operate at temperatures just below the ash slagging point may produce limited heavy liquids and fall intermediate within the classification regime. Depending on the process, process steam which is subsequently condensed and/or gas cleanup quench waters come into direct contact with the raw gaseous product stream. As a conse- quence, the resultant wastewater associated with the low-temperature processes is highly contaminated with organics. The production of ammonia in the high-temperature processes is generally suppressed and reduced due to "cracking." Condensate waters from high-temperature processes usually contain little or negligible NH3, while the condensate waters from low-tempera- ture processes contain high levels of NH3. The condensate waters from both low- and high-temperature processes generally contain volatized and entrained mineral matter, trace elements, and salts, as well as adsorbed H2S, C02, and cyanates. Treatment of the condensate waters from low-temperature processes poses a special challenge due to the high and variable level and toxic nature of the gross organics. A portion of the total organic carbon is biorefractory, also causing concern. Laboratory treatability tests have demonstrated that, with appropriate dilution and/or pretreat- ment (e.g., gas stripping, organic extraction, and/or the addition of powdered activated carbon), activated sludge treatment processes do a reason- able job of reducing biological oxygen demands (BOD) and total organic carbon (TOC) levels, and coupled with activated carbon treatment, relatively high quality effluent can be produced. In a "zero discharge" mode, subsequent concentration and reuse of the effluent must be effected to ultimately produce a concentrated brine or dry salt. The questions that remain center on the capability of this rather elaborate treatment train to accommodate variabil- ities in the rawfeed and on the reliability and costs of such a system; i.e., do viable alternatives exist? Options are outlined with special emphasis on: (1) improvements to biological treatment, and (2) purely physical/chemical sys- tems. The effect of more stringent standards with respect to the control of biorefractory ring-structure compounds, trace elements, ammonia, etc., is discussed relative to the state-of-the- art biotreatment and these environmen- tal control options. Areas of uncertainty and future research are delineated based on a recent synfuel wastewater workshop conducted in June 1981. Characterization of Coal Conversion Wastewaters Using On-Site GC/MS C.J. Thielen and R.V. Collins, Radian Corp. Austin, TX 78766 This paper discusses a characteriza- tion of a wastewater stream from a coal gasification facility using on-siteextrac- tion and GC/MS analysis. The objectives of the program were to: • Characterize the wastewater organic components primarily for selected priority pollutants. Ap- pendix C, and synfuels com- pounds. • Investigate the stability of these compounds during refrigerated and ambient storage. • Evaluate the destruction of or- ganics by wet oxidation. Extractable material in the wastewa ter consisted primarily of phenols am alkylphenols. These compounds ac counted for about 98% of the tota organic mass identified. Several polynu clear aromatic (PNA) compounds wen also identified. Deterioration in thi composition of the sample was observe* over a 1 -month period. This was mos evident in the concentration of dimethyl phenols which dropped approximate!' 75% during 2 weeks of refrigerate* storage. Ambient sample storage pro duced a greater decrease in the concen tration of phenol but did not appear t< affect the alkylphenols or the base/ neutral compounds as much as phenols It is expected that the observed change: in composition would hamper any off site wastewater treatability studies will water of this type. Treatment of.thi wastewater by wet oxidation was alsi evaluated and found to remove greate than 90% of the extractable organics. Treatment of Wastewater from a Fixed-Bed Atmospheric Coal Gasifier P.C. Singer and E. Miller, University of North Carolina Chapel Hill, NC 27514 Previous studies using a simulate coal conversion wastewater hav demonstrated the feasibility of treatih this type of waste by an activated sludg process. Phenol concentrations wer reduced to levels below 1 mg/l, andth toxicity and mutagenicity of the simi lated wastewater were reduced sut stantially by the biological treatmen This paper gives results of an evaluatio of the biological and subsequent physica chemical treatability of a real co< conversion wastewater, along with comparison of the results with thos obtained using the simulated waste water. Coal gasification wastewater wa obtained from a Chapman gasifier at th Holston Army Ammunition Plant i Kingsport, TN. The wastewater wa diluted to 25% of full strength, supple mented with phosphate, and subjecte to aerobic biological treatment in 22.5-liter completely mixed activate sludge reactor. The reactor was operate at a solids retention time of 20 days an a hydraulic detention time of 10 days. I addition to characterizing the quality < the effluent using various chemical ar bioassay procedures, the effluent fro the biological reactor was subjected to ------- series of physical-chemical treatment steps consisting of chemical coagulation, ammonia stripping, ozonation, and activated carbon adsorption. The chemi- cal quality and bioassay characteristics of these various samples are presented. Treatment of Fossil Fuel Derived Wastewaters With Powdered Activated Carbon/Activated Sludge Technology R.B. Ely and C.L Berndt, Zimpro, Inc. Mercer Island, WA 98040 The treatment of high-strength fuel conversion wastewaters by convention- al biological treatment processes may be operationally troublesome and only marginally effective from the standpoint of treatment system stability and performance. The addition of powdered activated carbon to the activated sludge process not only greatly improves pro- duct water quality but also provides cost savings compared to more conventional waste treatment and carbon regenera- tion processes. This paper describes the powdered carbon/activated sludge wastewater treatment process, discusses the advan- tages of powdered carbon addition including performance obtained on fossil fuel derived wastewaters, and presents cost comparison data for wastewater treatment and spent carbon regeneration. Land Treatment of Coal Conversion Wastewaters R.C. Sims (now with Utah State University, Logan, UT 84322) and M.R. Overcash, North Carolina State University Raleigh, NC 27650 This research project investigated the treatment potential of soil systems for polynuclear aromatic compounds (PNAs) present in aqueous wastes from coal conversion processes. A protocol for obtaining the soil assimilative capacities for mutagenic and recalcitrant PNA compounds was developed and, for a subset of compounds, data were obtained to describe: (1) rates of transformation, including degradation, detoxication, and possible intoxication; (2) effect of PNA structure on transformation rate; (3) effect of engineering management options, including nutrient addition, analog enrichment, surfactant addition, and pH adjustment on transformation rates; and (4) soil acclimation to PNAs. A three-step protocol—including: (1) incubation, (2) identification, and (3) determination of mutagenic potential— involves interfacing high-performance liquid chromatography (HPLC) for com- pound and metabolite identification with the Ames Salmonella typhimurium/ mammalian microsome mutagenicity assay for determining genotoxic po- tential of PNA compounds and trans- formation products in soil. Identification (HPLC) and mutation (Ames assay) were quantified. Session III. Air-related Environmental Considerations Removal of Acid Gases and Other Contaminants from Coal Gas Using Refrigerated Methanol J.K. Ferrell, R.M. Kelly, R.W. Rousseau, and R.M. Felder North Carolina State University Raleigh, NC 27650 The steam-oxygen gasification of a New Mexico subbituminous coal was carried out in a pilot-scale fluidized-bed gasifier. Gas cleaning was accomplished by a hot cyclone, a water-quench venturi scrubber, filters, and an acid gas removal system using refrigerated methanol as the solvent. Results of both gasification and gas cleaning are described. Refrigerated methanol proved to be effective in cleaning the gasifier- make gas; however, several reduced sulfur species and hydrocarbons were detected in the absorber, flash tank, and stripper exit gas streams over a wide range of operating conditions. While a variety of simple aromatics accumulated in the recirculating methanol, essentially no polynuclear aromatic (PNA) com- pounds were detected. Most PNAs were evidently removed in the gas quenching process. Advanced Techniques for Flue Gas Desulfurization C.C. Masser, M.A. Maxwell, and T.G. Brna Industrial Environmental Research Laboratory, U.S. EPA Research Triangle Park, NC 27711 In 1979 the combustion of sulfur- bearing fuels accounted for more than 80% of the SO2 emissions in the U.S. These emissions can be controlled to a degree by burning low-sulfur fuels or by pretreating the fuel to lower its sulfur content. Currently the most widely practiced technological control involves scrubbing the combustion flue gases to remove the SO2. Flue gas desulfuriza- tion systems can be categorized as nonregenerable (or "throwaway") and regenerable (or producing a salable product). The advantages and disadvan- tages of several systems in each category are discussed. Several recent developments in waste disposal and enhanced S02 removal are also pre- sented. Health and Environmental Studies of Coal Gasification Process Streams and Effluents C.A. Reilly, Jr., A.S. Boparai, S. Bourne, R.D. Flotard, D.A. Haugen, R.E. Jones, F.R. Kirchner, T. Matsushita, M.J. Peak, V.C. Stamoudis, J.R. Stetter, and K.E. Wilzbach, Argonne National Laboratory Argonne, II 60439 The synfuels environmental research program at Argonne National Laboratory is investigating the impact of high-Btu coal gasification on health and the environment. Activities include a toxico- logic and chemical characterization of process streams in the gasifier and pretreater sections of the Hygas coal gasification pilot plant, and process streams and workplace air from the Grand Forks Energy Technology Center's slagging fixed-bed gasifier facility. Cellular assays for mutagenicity, cyto- toxicity, and functional impairment are performed to determine relative toxicity. Various acute and chronic whole- animal lexicological evaluations, includ- ing skin tumorigenesis, are performed for streams found to contain potential toxicants (e.g., oils and tars). The chemical characteristics of vapor-phase and airborne particulate-associated organics, as well as biologically active materials isolated from process streams, are investigated by physical and chemi- cal fractionation of the samples, with biological monitoring and detailed GC and GC/MS analyses of the fractions. Present data indicate that toxicants are ------- present, but their levels of activity are relatively low. As a result of these studies, it is tentatively concluded that with appropriate control technology and industrial hygiene procedures, no serious health or environmental prob- lems appear to be associated with coal gasification. Gaseous Fugitive Emissions from SynfueJs Production - Sources and Controls R.L Honerkamp, Radian Corp. Austin, TX 78766 Fugitive emissions are generally defined as emissions that are not released through an enclosure such as a duct or vent pipe. Fugitive emissions of volatile organic compounds (VOCs) are caused by process fluid leakage from seals (valves, pumps, etc.), process fluid purges (sampling, equipment cleaning), and secondary emission sources (drains, wastewater systems, towers). Most sources of fugitive VOC emissions in the U.S. are currently found in petroleum production and refining facilities, organic chemical manufacturing plants, and coke by-product plants. Synfuels production facilities will also have VOC fugitive emission sources. The paper describes the potential sources and control options for fugitive VOC emissions in synfuels production facilities. Fugitive emission regulations have been applied to California petroleum refineries for several years, and U.S. New Source Performance Standards (NSPS) are currently under development for several industries. These regulations are based on the need to reduce fugitive emissions because VOCs are photo- chemical ozone precursors. Some fugitive emissions also need to be controlled because compounds released in the emissions may be hazardous. U.S. National Emission Standards for Hazard- ous Air Pollutants (NESHAP) have been developed for controlling fugitive emis- sions of vinyl chloride and benzene. VOC emissions from synfuels produc- tion facilities may require control because they contribute to atmospheric ozone formation and/or because they contain hazardous compounds. The nature of potential hazardous compounds will depend on variables such as the type of process, feedstock character- istics, and operating parameters Fugitive emission controls can be categorized as work practices or engi- neering controls. Work practices would include leak detection and leak repair programs and good housekeeping practices. Leak detection and repair programs involve periodic testing to locate significant VOC leaks and subse- quent repairs to reduce or eliminate the leakage. Housekeeping practices would include procedures to minimize process fluid spills and to expedite spill cleanup. Engineering controls are generally equipment substitution strategies. For example, closed-loop sampling connec- tions eliminate process fluid purge emissions, and double mechanical pump seals can be operated to minimize emission potential. These types of equipment would be used instead of equipment with a greater potential to leak VOC. Because the emission sources (pumps, valves, etc.) on synfuels plants will be similar to those in existing U.S. indus- tries, the emission control techniques will also be applicable. The experience that has been gained in applying fugitive VOC emission controls will be valuable in developing VOC control strategies for synfuels-plants. Control Systems for Air Emissions from Coal Gasification S. Thomson, Fluor Engineers and Constructors, Inc. Irvine, CA 92730 This paper discusses control systems for air emissions on coal conversion projects. Topics include the control of emissions from acid gas treatment processes and the control of emissions from gasification reactors. Alternate control systems as well as the difficulties involved in establishing the Best Available Control Technology (BACT) are also covered. Session IV. Solid Waste- Related Environmental Considerations Health Effects Bioassay Results from Coal Conversion Solid Wastes M.P. Maskarinec, F.W. Larimer, J.L Epler, and C.W. Francis Oak Ridge National Laboratory Oak Ridge, TN 37830 To assist EPA and DOE in identifying solid wastes that may pose a potential hazard to human health and environ- ment, the Oak Ridge National Labora- tory has conducted studies on extracts from solid wastes obtained from various coal liquefaction and gasification pro- cesses. Analytical procedures to chem- ically characterize and separate the or- ganic and inorganic constituents were developed. Various approaches to ex- traction were compared. Batteries ol health effects and environmental as- says were applied to the extracts or theii fractions to indicate chronic hazards The applicability and compatibility of the coupled chemical and biological proce dures are evaluated with particulai emphasis on the Ames mutageniciti test. A Comparison of RCRA Leachates of Solid Wastes from Coal-Fired Utilities and Low- and Medium-Btu Gasification Processes M.R. Fuchs, D.L Heinrich, L.J. Holcombe, and K.T. Ajmera, Radian Corp. Austin, TX 78766 EPA has promulgated regulation which temporarily exclude utility waste (including fly ash and bottom ash fror coal-fired generating stations) fror Subtitle C of the Resource Conservatio and Recovery Act (RCRA) regulations EPA, using broad interpretation c amendments to the Act, has als excluded coal gasification solid waste from Subtitle C regulations, and thes wastes are listed as nonhazardou pending further data evaluation. Thi paper gives comparative results ( RCRA leachates of the solid waste from two low-Btu gasification processe and coal-fired utility solid wastes. Th three facilities from which solid waste were obtained used the same lignil feedstock. Also presented are compare ble RCRA leachate results of soli wastes from a medium-Btu gasificatio process and a coal-fired power plan both fueled with identical lignil feedstocks. The results indicate thi solid wastes from coal-fired utilities ar those generated directly by low- ar medium-Btu gasification processes ai nonhazardous according to RCR protocol and limits. 6 ------- Characterization of Solid Wastes from Indirect Liquefaction Facilities C.A. Hunter, K.Y.Yu, and K.W. Crawford, TRW Redondo Beach, CA 90278 Gasification ash and slag are the major solid wastes generated in indirect coal liquefaction facilities. Smaller amounts of spent catalysts and pollution control sludges may also be generated. There is a limited amount of data on the hazardous and nonhazardous character- istics of these solid wastes. Leachate data for gasifier ash and slag from Lur- gi, Wellman-Galusha, and Texaco gasi- fication have been presented elsewhere. The RCRA leaching characteristics of quenched gasifier slag and dust from commercial scale Koppers-Totzek gasi- fication tests in Greece are presented in this paper. The potential accumulation of trace elements in the sludges from biological oxidation of Lurgi gasification condensates are estimated. Koppers- Totzek and Texaco gasification conden- sates will contain negligible amounts of organics (compared to the Lurgi gasifi- cation condensates) and will not require biological oxidation. The potential accu- mulation of trace elements on high temperature shift catalyst are examined as a function of degree of gasification and feed coal characteristics. Ash/Slag Residuals and Wastewater Treatment Plant Sludges from Synfuels Facilities: Characterizations and Implications for Disposal R.D. Neufeld, G. Keleti, J. Bern, C. Moretti, S. Wallach, and H. Erdogen University of Pittsburgh Pittsburgh, PA 15261 This paper gives an overview of research conducted at the University of Pittsburgh in the area of coal conversion ash and slag. Residuals were obtained from the GFETC "slagging Lurgi type" gasifier (two different runs), METC (Wellman-Galusha type) pressurized gasifier, DOE-Chapman gasifier fly ash, and two H-Coal vacuum bottoms resid- uals. A first screen bioassay of SRC-II Fort Lewis coal liquefaction residuals and sludges is also presented. In addition, research has been conducted at the University of Pittsburgh for the past few years in the area of developing a stable pretreatment and biological treatment facility for the processing of phenolic type coal gasification waste- waters. During the processing of wastewaters, sludges are produced which are assessed for toxicity, muta- genicity, and overall disposability. Update on EPA's Regulatory Views on Coal Conversion Solid Wastes Y.M. Garbe, U.S. EPA Washington, DC 20460 The Resource Conservation and Recovery Act of 1976 (RCRA) charges EPA with the responsibility for establish- ing a program for the management of hazardous solid wastes. This paper summarizes current and anticipated RCRA regulations affecting thesynfuels industry. Included in the various RCRA issues pertaining to the synfuels indus- try is a discussion of the RCRA mining exemption. An overview is given of the Of- fice of Solid Waste's planned research activities to support future synfuels solid waste regulations. (Only the abstract is published in the proceedings.) Session V. Multimedia Environmental Considerations A Permittees View of Synfuel Commercialization G.L Harlow, U.S. EPA Region 4 Atlanta, GA 30365 The EPA is responsible for issuing permits to synfuels plants for the control of various liquid, gaseous, and solid waste streams. These permits comprise the Prevention of Significant Deteriora- tion (PSD) under the Clean Air Act of 1977, the National Pollutant Discharge Elimination System (NPDES) and the Section 404 Dredge and Fill permits under the Clean Water Act of 1977, and the hazardous waste permits under the Resource Conservation and Recovery Act (RCRA) of 1976. Since there will likely not be federal regulations established by EPA set- ting standards on requirements for first-generation synfuels plants, the environmental permits will have to be individually negotiated, case by case, with each applicant using best engineer- ing practice. This places an unusual burden on the permit writer who will be negotiating with the discharger from an uninformed and defenseless position. To overcome this burden and to avoid long, time-consuming delays in the permit process, the company should disclose in its application for permit exactly what steps will be taken to control air emissions, water discharges, and hazardous wastes. (Only the abstract is published in the proceedings.) Comparison of Environmental Design Aspects of Some Lurgi-Based Synfuels Plants M.R. Beychok, Consultant Irvine, CA92715 WJ. Rhodes, Industrial Environmental Research Laboratory, U.S. EPA Research Triangle Park, NC 27711 This paper summarizes the current status of proposed projects in the U.S. which involve synfuels production based on utilizing Lurgi coal gasification technology. For some Lurgi-based synfuel proj- ects where actual plant design informa- tion has been made available, acompar- ison of their environmental designs is discussed. The primary focus of the environmental'design comparison is on the facilities to be included for the control and abatement of air pollutant emissions and wastewater pollutant discharges. Insofar as possible, the paper also focuses on commercial-scale project designs. Session VI. Product-Related Environmental Considerations Risk Assessment of Synfuel Technology A.A. Moghissi, U.S. EPA Washington, DC 20460 (No paper or abstract available.) Premanufacture Review of Synfuels Under TSCA M. Hale, Jr. and C. Mazza U.S. EPA Washington, DC 20460 The Toxic Substances Control Act (TSCA) requires manufacturers to notify EPA at least 90 days before they ------- produce a new chemical substance for commercial purposes. Once notified, EPA has 90 days, extendable for good cause to 180 days, to review the chemical. During the review period, the Agency can act to prohibit or limit the manufacture, processing, or use of a new chemical substance where it finds that the information available on the substance is insufficient for a reasoned evaluation of its risks and that (1) the chemical may present an unreasonable risk to human health or the environment or (2) significant human or environmen- tal exposure can reasonably be ex- pected. Certain synthetic fuel products (including certain by-products and intermediates) may be new chemical substances under TSCA and therefore potentially subject to premanufacture notice requirements. This paper outlines TSCA premanufacture notification requirements; it describes how "new" chemical substances are defined; and it discusses the types of data that might be provided to EPA with a premanufacture notice on a synfuel. Methanol as a Clean Major Fuel P.W. Spaite, Consultant Cincinnati, OH 45213 Methanol is considered as an alterna- tive fuel that could be produced using available technology to displace major petroleum fuels in a relatively short time. The major factors considered are: 1. Potential environmental conse- quences of introducing methanol. 2. Status of development of meth- anol fuel technology. 3. Cost and efficiency of synfuels processes. 4. Potential markets. 5. Prospects of commercialization of methanol fuels. The paper develops an overview perspective by identifying all important factors in each category and presenting enough quantitative data to permit relative comparisons without excessive detail. Methanol as an Alternative Transportation Fuel R. Rykowski, R.D. Atkinson, D. Heiser, J. McGuckin, D. Fletcher, J. Alson, and M. Rosenfeld, U.S. EPA Ann Arbor, Ml 48105 Over the remaining years of this century, synthetic fuels will play a key role in the nation's drive for energy independence. Although self-reliance is indeed a desirable goal, many people believe that it cannot be achieved without significant compromises in environmental quality. This may not be the case. One synfuel, methanol, could be used to replace both gasoline and diesel fuel and yield environmental benefits. This pa per compares methanol with synthetic fuels from other coal liquefaction processes in terms of the environmental and economic conse- quences of their use. Project Summary—A Compendium of Synfuel End Use Testing Programs M. Ghassemi, S.C. Quinlivan, and M. Haro, TRW Redondo Beach, CA 90278 A "Compendium of Synfuel End Use Testing Programs," which provides information on major recently com- pleted, current, and planned synfuels end use testing projects, has been devel- oped. The compendium is intended to promote flow of information among various synfuels testing programs, thereby reducing chances for duplica- tion of effort and enabling design and implementation of cost-effective and systematic approaches to the collection of appropriate environmental data in conjunction with ongoing and planned performance testing projects. EPA intends to update this compendium to include results from current and future testing programs. Projects described in the compendium involve testing of shale-derived fuels, SRC-II middle distillates, EDS fuel oils, H-coal liquids, and methanol/indolene mixtures in various equipment such as utility boilers, steam generators, diesel engines (laboratory-and full-scale), auto engines, and various other combustors. Published reports on various testing efforts and discussions with test sponsors/contractors are the sources of data for the compendium. Based on the data in this compendium, the thrust of the synfuels testing program which has been carried out to date has been to assess equipment performance and fuel handling charac- teristics. Where some emissions moni- toring has been conducted, such efforts have been limited in scope and have primarily emphasized measurement of criteria pollutants (NOx, SOx, particu lates, etc.). Essentially no data havi been collected on emissions of noncri teria/nonregulated pollutants. Comparative Testing of Emissions from Combustion of Synthetic and Petroleum Fuels W.G. Tucker and J.A. McSorley, Industrial Environmental Research Laboratory, U.S. EPA Research Triangle Park, NC 27711 Procedures are being developed fc the comparative testing of combustio products from liquid synthetic fuels an petroleum-based analogs. Combustio tests at EPA's research facility in Nort Carolina are measuring differences i emissions from petroleum-, coal-, an shale-derived fuels in stationary corr bustors. Data from these tests will b used in refining procedural guidance o combustion testing of synfuels for Prt manufacturing Notice (PMN) applies tions. Unpresented Papers Two papers, not presented at tr symposium, are published in the pn ceedings. Problems Associated with th Analysis of Synfuels Product Process, and Wastewater Streams H.C. Higman, O.K. Rohrbaugh, R.H. Colleton, and R.A. Auel Hittman Associates, Inc. Columbia, MD21045 Hittman Associates, as part of i environmental assessment of co liquefaction technology sponsored the U.S. EPA, performed various anal ses on samples from the Solve Refined Coal II (SRC-II) plant in I Lewis, WA, and the Exxon Don Solvent (EDS) plant in Baytown, TX. Tl paper describes several probler encountered in these analyses a methods taken to mitigate them. Reco mendations are made on approaches avoiding such problems. ------- Solvent Extraction Processing for Coal Conversion Wastewaters J.R. Campbell and R.G. Luthy, Carnegie-Mellon University Pittsburgh, PA 15213 M.J.T. Corrondo, New University of Lisbon Lisboa, Portugal This paper outlines experimental and modeling techniques being used to evaluate solvent extraction processing of coal conversion wastewaters. The project includes characterization of organic contaminants in slagging fixed- bed gasification process wastewater, as well as screening studies to evaluate removal efficiencies for these contami- nants. Experiments are also in progress to measure distribution coefficients for several solvent types with phenol and representative base- and neutral- fraction aromatic solutes. These experi- ments are being performed with both clean water and wastewater systems. Results from these experiments are being evaluated in light of three techniques for estimating distribution coefficients: modified regular solution theory as used in chemical engineering processing, expanded solubility param- eter approach as used in liquid-liquid chromatography, and estimation of octanol-water partition coefficient as employed in environmental science. This paper reviews results obtained to date and explains direction for work during the coming year. F.A. Ayer ana N.S. Jones are with Research Triangle Institute, P. O. Box 12194, Research Triangle Park. NC 27709 N. Dean Smith is the EPA Project Officer (see below). The complete report, entitled "Proceedings: Symposium on Environmental Aspects of Fuel Conversion Technology—Ml, A Symposium on Coal-Based Synfuels-October 1981,"(Order No. PB83-128 181; Cost: $40.00; 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 Project Officer can be contacted at: Industrial Environmental Research Laboratory U.S. Environmental Protect/on Agency Research Triangle Park, NC 27711 U.S. GOVERNMENT PRINTING OFFICE: 1983/659 -095/581 ------- " c CO c v> 0) CO 8 > m 03 3 (0 < si ID 3 r* 9L T) o ^* CD O 3? 11 - o O3 I & ro o> oo r m > TJ •n m "^ m CO n - O O CD CD Cfl ._ .. O O -n CO •< A3 l» w §|s ------- |