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Of the 211 shallow Urban Land-Use wells and of MTBE use in most urban areas is largely unknown- <br /> springs sampled, 73 percent had concentrations less Oxygenated fuels (which include MTBE or other <br /> . than the reporting level of 0 2 gg/L, 24 percent had oxygenates such as ethanol) have been used in all <br /> concentrations of MTBE ranging from 0 2 to gasoline sold during the wooer in Denver since 1988, <br /> 20 0 µg/L, and 3 percent had concentrations and oxygenated fuels also have been used in the <br /> exceeding 20 0 gg/L, which is the estimated lower winter in Reno, Las Vegas, and Albuquerque since <br /> limit of the USEPA(1995)draft drinking-water health 1989 (Michael Ball, USEPA, written common, 1995) <br /> advisory level (fig 4) Five of the 211 shallow urban where MTBE was detected less frequently in ground <br /> wells and springs sampled were used as a source of water The amount of MTBE used in oxygenated fuels <br /> drinking water, however, none of the samples from in these western cities is unknown Oxygenated fuels <br /> the 5 drinking-water wells had detectable concentm- were not used in eastern cities until 1992, however,to <br /> tions of MTBE In seven of the eight urban areas enhance the octane of gasoline,MTBE has been added <br /> studied, the sampled ground water was from the to premium gasoline in some areas since 1979 (Garrett <br /> uppermost part of an aquifer used for drinking water and Moreau, 1986) The use of MTBE in premium <br /> or possibly was connected to an underlying aquifer gasoline was common in New England during the <br /> that is used as a murucipal water supply In general, 1980's and may have led to its frequent detection in <br /> public-water supplies draw water from deeper parts of shallow urban ground water in 1993-94 <br /> the ground-water system, and the Study-Unit Survey <br /> data may provide a better indication of the contami- <br /> nates that presently exist in drinking-water supplies Occurrence of MTBE in deeper ground water <br /> None of the samples from the Agricultural Land-Use <br /> wells or Study-Unit Survey wells had concentrations In deeper ground water, MTBE was detected in 4 <br /> of MTBE that exceeded 20 0 gg/L of 412 Study-Unit Survey wells (1 percent)in 9 Study <br /> Units (fig 1) Three of these four wells with MTBE <br /> MTBE was detected most frequently in samples of were used for domestic or municipal water supply <br /> shallow urban ground water in Denver, Colorado, and The maximum concentration of MTBE detected was <br /> New England (fig 3), but the reason for its frequent 1 3 gg/L, and no Study-Urut Survey idenwfied more <br /> detection is not known In Denver, samples from than one well with detectable levels of MTBE The <br /> 79 percent of the shallow urban wells (23 of 29 wells) Study-Unit Survey wells had smaller concentrations <br /> had detectable concentrations of MTBE, and in New and less-frequent occurrence of MTBE than the Land- <br /> England, samples from 37 percent of the wells (13 of Use wells for three possible reasons (1) Study-Unit <br /> 35 wells) had detectable concentrations of MTBE Survey wells were not necessanly located in urban <br /> The frequent detection of MTBE to these two areas areas where MTBE is used most intensively and is <br /> may be related to the fact that the aquifer, and the most frequently detected in shallow ground water, <br /> overlying unsaturated zone, consists of very (2)Study-Unit Survey wells are deeper, and generally <br /> conductive sand and gravel and that the median depth it takes time for a recent contaminant to move into <br /> to water was very shailow-4 3 m in Denver and deeper parts of an aquifer, and (3)the concentrations <br /> 2 8 m in New England However, the mean annual of MTBE become diluted as shallow ground water <br /> precipitation is about three times greater in New mixes with deeper,generally cleaner, ground water <br /> England than in Denver (U S Geological Survey, <br /> 1970), and therefore the ground-water recharge in <br /> these two areas may be substantially different Possible sources of MTBE in ground water <br /> MTBE in ground water can originate from point <br /> Relation of MTBE in shallow urban ground and nonpomt sources Possible point sources of <br /> water to historical use MTBE include leaking gas tanks, pipelines, landfill <br /> sites, dumps, spills, industry, underground injection, <br /> It is difficult to relate the historical use of MTBE and refueling facilities Lealung underground storage <br /> with occurrence in ground water because the history tanks are a major source of contamination, about <br /> Study Results 9 <br />