From: | Lenny Siegel <lsiegel@cpeo.org> |
Date: | 22 Jul 2005 23:34:25 -0000 |
Reply: | cpeo-military |
Subject: | [CPEO-MEF] Wide-spread, low concentration perchlorate |
"Evaluation of Alternative Causes of Wide-Spread, Low Concentration Perchlorate Impacts to Groundwater," prepared by GeoSyntec Consultants for the Strategic Environmental Research and Development Program (SERDP) and officially dated May 5, 2005, is available on line at a 54-page, 424 K PDF file at http://www.serdp.org/research/cp/cp-1429.pdf Here is the EXECUTIVE SUMMARY The frequency of detection of perchlorate in groundwater and drinking water supplies has been steadily increasing since its initial identification as a chemical of concern in 1997. It is currently estimated that perchlorate is present in groundwater in at least 30 states and affects the drinking water supplies of more than 20 million people in the southwestern United States (U.S.). The source of perchlorate in water supplies has typically been attributed to U.S. Department of Defense (DOD), National Aeronautics & Space Administration (NASA) and/or defense contractor facilities that have used ammonium perchlorate (AP) in rocket and missile propellants. Perchlorate impacts to groundwater and surface waters in southern Nevada and southern California have also been attributed to the historic production and release of perchlorate from a former chemical manufacturing facility in the Las Vegas, Nevada area (Hogue, 2003), which has impacted the surface waters of Lake Mead and the Colorado River. As a result of its high profile and its addition to the Unregulated Contaminant Monitoring Rule (UCMR List 1), which requires perchlorate analysis by large public water suppliers and selected small water utilities, most public water supplies are now being routinely analyzed for perchlorate. Through monitoring activities, perchlorate has been detected at low levels (typically less than 50 µg/L) in a significant number of areas without apparent military sources. Investigation activities have linked these perchlorate impacts to various non-military sources, including use of perchlorate-containing blasting agents for quarrying and construction, manufacture of road flares, manufacture and use of fireworks and pyrotechnics, use of perchloric acid in industrial manufacturing, and use of Chilean nitrate fertilizers. Perchlorate is known to be present in a significant number of products and processes. Unfortunately, it has proven exceedingly difficult to obtain records of perchlorate handling related to production and use of many of these products and processes. As such, this review focuses on five major perchlorate-containing products for which significant quantity and use information is available: Chilean nitrate fertilizers; fireworks; safety flares; blasting explosives; and electrochemically-prepared (ECP) chlorine products. The key findings of this review for each of these major perchlorate-containing products can be summarized as follows: Chilean Nitrate Fertilizer: Between 1909 and 1929 (the period for which detailed information could be obtained), the U.S. imported an estimated 19 million tons of Chilean nitrate (Goldenwieser,1919; Howard, 1931), of which an average of 65% was used as fertilizer (Brand, 1930). Assuming an average perchlorate content of about 0.2% in Chilean nitrate (based on U.S. Environmental Protection Agency research results), approximately 49 million pounds of perchlorate may have been unknowingly applied to agricultural soils during this time period, for fertilization of crops such as cotton, tobacco, fruits and vegetables. While the use of Chilean nitrate fertilizers has steadily declined since about the 1930s, there is evidence of continued use through the present day. Additional evaluation of soils and groundwater in agricultural areas that have used (and may still be using) Chilean nitrate fertilizers seems warranted to evaluate whether past and/or present fertilizer practices can be expected to be the cause of long-term, low concentration perchlorate impacts to groundwater in some agricultural areas and watersheds. Fireworks: In 2003, 221 million pounds of fireworks were consumed in the U.S., with an estimated 3% produced domestically and the remainder imported from China (APA, 2004a). Although perchlorate is widely used as an oxidizer in firework formulations, there is little information related to the amount of perchlorate residue remaining after burning of fireworks and/or statistics on dud rates and blind stars that occur during fireworks displays. As such, it is difficult to estimate potential perchlorate inputs from fireworks to the environment. Recent studies have detected perchlorate in soils, groundwater and/or surface water following fireworks displays, and therefore, the potential environmental impact of perchlorate from fireworks displays warrants further scientific study. Safety Flares: Preliminary research by Silva (2003a, 2003b) of the Santa Clara Valley Water District in California indicates that 3.6 grams of perchlorate can potentially leach from an unburned, damaged (i.e., run over by a motor vehicle) 20-minute road flare. While numbers are not available for total domestic flare production, assuming an average cost per flare of $0.50 to $1.00 per flare and annual sales of $20 million by the largest domestic manufacturer, some 20 to 40 million flares may be sold annually. Given this estimate, up to 237,600 pounds of perchlorate could leach from road flares annually. Surface runoff from highways and roads represents a potentially significant and largely uninvestigated impact to surface water and groundwater quality. Additional evaluation of the potential for perchlorate impacts to surface waters and groundwater from safety flare use appears warranted. Blasting Explosives: Some water gels, emulsions, and non-electric detonators can contain substantial amounts of perchlorate (e.g., up to 30% by weight). While, most of the perchlorate in the explosives is expected to be consumed in the detonation, poor housekeeping practices (i.e., spillage), improper use, or misfires can potentially result in perchlorate contamination of surface and ground waters, as has been reported for multiple sites in Massachusetts. Given that the U.S produces approximately 2.5 million tons of explosives annually, perchlorate could potentially be released into the environment nationwide in substantial amounts. Currently, no publicly-available data exist to quantify potential perchlorate impacts from blasting. More studies are required to assess and quantify the potential impact of blasting explosives on perchlorate contamination of surface and ground waters. ECP Chlorine Chemicals: During the electrochemical manufacture of chlorine products, such as chlorate, from chloride brine feedstocks, perchlorate may be formed as an impurity at concentrations of 50 to 500 mg/kg. The estimated North American annual chlorate manufacturing capacity is 2.4 million tons, whereas the total annual consumption of sodium chlorate in the U.S. is approximately 1.2 million tons. The pulp and paper industry uses approximately 94% of all sodium chlorate consumed in the U.S. for on-site production of chlorine dioxide to bleach cellulose fibers. Effluents from pulp mills have been reported to contain chlorate (1 to 70 mg/L) but there is little information available as to the potential for perchlorate release from these facilities. Sodium chlorate is also used as a non-selective contact herbicide and a defoliant for cotton, sunflowers, sundangrass, safflower, rice, and chili peppers. The use of sodium chlorate in the pulp and paper industry and as a defoliant has the potential to contribute perchlorate to the environment and needs to be better understood. The United States DoD, NASA and related defense contractors are likely to be the most significant domestic users of perchlorate, and as such, a significant percentage of identified groundwater perchlorate impacts are likely to be attributable to DoD, NASA, and related defense contractor facilities. However, cases exist, and many more are likely to surface, where perchlorate impacts result from combinations of military, non-military, and/or natural inputs. The ability of DoD, NASA, and defense contractors to accurately apportion the relative contributions from these varying sources, and hence to properly determine liability and control cleanup cost, lies in having a good understanding of the wide variety of products and processes that may contribute perchlorate to the environment and through the development and validation of appropriate forensic tools. This review is intended to assist DOD, NASA, and defense contractors in identifying the significant number of industrial and commercial processes and products that contain perchlorate and to estimate the potential contribution of perchlorate to the environment (past and/or present) from non-military products or processes. -- Lenny Siegel Director, Center for Public Environmental Oversight c/o PSC, 278-A Hope St., Mountain View, CA 94041 Voice: 650/961-8918 or 650/969-1545 Fax: 650/961-8918 <lsiegel@cpeo.org> http://www.cpeo.org _______________________________________________ Military mailing list Military@list.cpeo.org http://www.cpeo.org/mailman/listinfo/military | |
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