United States Environmental Protection Agency Robert S. Kerr Environmental Research Laboratory Ada OK 74820 Research and Development EPA-600/S2-84-108 July 1984 c/ERA Project Summary Laboratory Assessment of Potential Hydrocarbon Emissions from Land Treatment of Refinery Oily Sludges R.G. Wetherold, J.L. Randall, and K.R. Williams Volatile organic emissions were characterized when oily petroleum sludges from refineries were incorpo- rated in soils under controlled labora- tory conditions. The sludges tested included three of the five listed hazard- ous wastes for the refining industry: dissolved air flotation float, slop oil emulsion solids, and API separator sludge. The volatile components of the sludges were first identified. Then the effects of air temperature and humidity, wind speed, soil type, temperature and moisture, sludge loading and volatility, and method of waste application were studied. The volatile components iden- tified in the sludge were also present in the emissions from the soil-waste mixtures. The quantity of emissions was most affected by the sludge volatil- ity, sludge loading, application method, and atmospheric humidity; the cumula- tive emissions at a given period of time could be correlated with these opera- tional variables. The emission rate or level was not significantly affected by soil type or soil moisture. An expression for estimating the rate of emissions as a function of elapsed time after applica- tion could not be developed from the data. Although every effort was made to simulate actual land treatment conditions, it was not possible to apply these laboratory findings directly to predict full-scale results. This Project Summary was developed by EPA's Robert S. Kerr Environmental Research Laboratory. Ada, OK, to an- nounce key findings of the research project that is fully documented in a separate report of the same title (see Project Report ordering information at back). The research effort was jointly funded by the US EPA and the American Petroleum Institute. Introduction Land treatment has been used exten- sively by the petroleum refining industry to attenuate oily sludges, predominantly on company property. In the current process of renewing land treatment permits, there has been an increasing interest in addressing the characteristics and magnitude of volatile organic emis- sions occurring in land treatment opera- tions. This laboratory study was performed to assess the atmospheric emissions from the land treatment of refinery sludges, particularly those listed as hazardous wastes for petroleum refining in 40 CFR 261.32 and which are routinely land treated by the industry. The wastes studied were API separator sludge, slop oil emulsion solids, and dissolved air flotation (DAF) float. The magnitude and characteristics of the emissions and the variables affecting them were investi- gated using sludges and soils collected from participating refineries. Procedures The volatile organic constituents of the sludges were identified by using a purging device, trapping the emitted organics, and performing analyses by gas chromatography 'mass spectrometry ------- (GC/MS). A laboratory land treatment simulator apparatus was constructed to measure air emissions from soil/waste mixtures while controlling and mea- suring air velocity, humidity, and tem- perature, and soil temperature and mois- ture. A series of tests was conducted with this simulator using eight soil samples and nine sludges obtained from eight participating refineries. Initially, nine variables were evaluated with the simulator (Table 1). Based on these preliminary studies, the five variables indicated by asterisks in Table 1 were chosen for further intensive study. Table 2 is the experimental matrix for evaluating these variables, where one variable was studied while holding the four others constant. The remaining variables in Table 1 were held constant: air and soil temperatures at 90°F, wind velocity 3 mph, and sludge application mode being to the surface. Emissions measurements consisted of total hydrocarbons as measured by a Byron Instruments 401 Total Hydrocarbon Analyzer and indivi- dual compound identification by collec- tion in steel cylinders and dual detector GC analysis using normalized toluene response as the indicator of the compound present.1 Results and Discussion The sludge characteristics are presented in Table 3 (nonspecific organic content) and in Table 4 (specific organic compounds identified). Fifty-two runs were made with the land treatment simulator. Statis- tical interpretation identified the param- Table 1. Operational Variables Studied with the Land Treatment Simula- tion Apparatus Table 3. Nonspecific Organic Composition of Sludges *Sludge Volatility Application Mode "So/1 Loading Air Temperature Soil Temperature *Soil Type *Soil Moisture *Air Humidity Air Flow Sludge SL-11 SL-12 SL-13 SL-14 Type API Sludge DAF Float Slop Oil API Sludge Oil & Grease (wt. %) 22 1 2 2 Volatilized hydrocarbons" (PPM /ml sludge) 820 70 125 103 Sum of volatilized compounds identified'' (ug/gm) 6,100 760 2,910 850 "A verage total hydrocarbon concentration in vapor phase over 4 hrs. nitrogen purging using 1 ml sludge (expressed as hexane). "Total concentration of emitted compounds identified by GC/MS (see Table 4). Table 4. Major Organic Compounds Identified in Sludges Sludges SL-11 SL-12 SL-13 SL-14 Compound Benzene Toluene M/P-Xylene 0-Xylene CyBenzene CyBenzene Napthalene Anthr./Phen. C9-H.C. (alkane) Ciz-H.C. (alkane) C,i-H.C. (alkane) Cn-H.C. (alkanej (pristane) Cig-MC. Cso-H.C. 540 1,700 7OO 330 /, 7OO 890 230 150 13O 140 84 66 31 2 32 58 58 28 150 120 34 20 30 57 72 72 26 NM 18 98 11O SO 4OO 40O 350 1,100 14 210 84 24 4O ^ 16 5 14 30 16 160 140 64 92 36 J2O 68 68 28 14 eters having the most significant affects on emission levels: sludge volatility, sludge loading, and air humidity. The emission rate or level is not significantly affected by type of soil or its moisture content. In general, the results showed that the more volatile components identified in the sludges are emitted to the air, specifically C9 - Ci2 alkanes, xylenes. C3-benzenes, toluene, and benzene. The more volatile compounds were present in Table 2. Experimental Matrix for Evaluating Operational Variables Sludge ID Sludge Volatility: Low Medium High SL-12 SL-13. SL-14 SL-11 Soil ID Soil Type: Sludge Loadings: Soil Moisture: Air Relative Humidity: D-1 D-8 D-7 Silty sand Silty clay Sandy Silt 5 levels (0.05 - 2.0 Ib oil/ft2 soil) 5 levels (5 - 25 wt. %) 3 levels (30 - 80%) the emissions at relatively higher con- centrations compared to the concentra- tions in the sludges that were the respective sources of the emissions. The cumulative emissions at a given period in time (four to seven hours after application) can be correlated with sludge volatility, sludge loading, and atmospheric humidity. During the two phases of the study, the hydrocarbon volatilization ranges, expressed as % oil content in sludges applied, were 0 - 3.6% after 30 minutes and 0-6% after 4 hours applied. An expression for estimating rate of emissions as a function of elapsed time after sludge application could not be developed from the data obtained. Alt of the specific organic compounds identified in the emissions from each of the runs is tabulated in the report to- gether with the measured concentra- tions in parts per million by volume expressed as carbon (ppmv-C). References 1Cox, R.D. and R.D. Earp "Determination of Trace Level-Organics in Ambient Air ------- by High-Resolution Gas Chromatogra- phy with Simultaneous Photoioniza- tion and Flame lonization Detection," Anal. Chem. 54 (13) 2266, November, 1982. R. G. Wetherold, J. L Randall, and K. R. Williams are with Radian Corporation. Austin, TX 78766. Fred M. Pfeffer is the EPA Project Officer (see below). The complete report, entitled "Laboratory Assessment of Potential Hydrocarbon Emissions from Land Treatment of Refinery Oily Sludges," (Order No. PB 84- 209 766; Cost: $13.00, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at: Robert S. Kerr Environmental Research Laboratory U.S. Environmental Protection Agency Ada, OK 74820 U S. GOVERNMENT PRINTING OFFICE, 1984 — 759-015/7755 ------- United States Center for Environmental Research Environmental Protection Information Agency Cincinnati OH 45268 Official Business Penalty for Private Use $300 0000329 4 < ------- |