From: | Lenny Siegel <lsiegel@cpeo.org> |
Date: | 6 Dec 2003 00:32:05 -0000 |
Reply: | cpeo-military |
Subject: | [CPEO-MEF] Splitting the perchlorate problems in half |
The more I learn about perchlorate, the more I'm convinced that there are two sets of perchlorate problems, not one. From a policy point of view, perchlorate in drinking water is different than the perchlorate in environmental media - soil, groundwater, and surface water - that release the contaminant into drinking water. Perchlorate is thus different, in most locations, than volatile organic compounds (VOCs), such as trichloroethylene (TCE). At most VOC sites, extraction pumps are turned off when the contaminant is found, not just to block the exposure pathway, but to minimize the chemical's migration. At some sites, water with low levels of contamination is blended with water from other sources. Only at a few sites do people actually drink treated (or even untreated) TCE-laden water. Our ability to detect perchlorate pollution, however, has outpaced our ability to regulate it. Furthermore, in the three states (Nevada, California, and Arizona) that drink water apparently contaminated by perchlorate from the Las Vegas Wash, contamination is so overwhelming that there is nothing else to drink. While at most VOC sites we focus on the detection of, regulation of, treatment of, and liability for contamination in the environment, perchlorate raises issues both in the environment AND within water distribution systems. First and foremost, it's important to recognize that a health-based standard for perchlorate ingestion means something different at the point of drinking water delivery than when making remedial decisions. In drinking water, the standard tends to be absolute. If pollution exceeds the standard, we find other supplies, remove the contaminant, or as a less desirable solution, blend in cleaner water to reduce the concentration. For perchlorate, this means that water systems will be installing treatment systems, regardless of how much cleanup is required upstream. In cleanup the standard serves as a more flexible goal that guides risk management decisions. The point of compliance may be far from the source - at a property boundary, fox example. In selecting the remedy, decision-makers may determine that excessive costs will prevent full remediation to the health-based goal. Or as is often the case with TCE, it may turn out that standard remedial technologies are incapable of reducing contamination to the level of the standard. Even if achievable, the goal may be decades away. In my work with community groups, I tend to push for cleanups to achieve stringent standards, but I recognize that risk management decisions are more complex. This is particularly important in regulating the release of perchlorate into the environment. While reasonable steps should be taken to manage waste and substitutes should be developed to prevent its generation, the establishment of a stringent health-based standard does not mean that the use of perchlorate will never be permitted to deposit localized concentrations above that standard. The treatment strategy for drinking water may also be different. I've recently viewed presentations arguing that bio-treatment tends to be more effective and efficient than ion exchange. However, water vendors who historically have gone to great expense to keep microbes out of drinking water are reluctant to utilize any microbes, no matter how benign, to treat their product. In remediation, however, public support for active bioremediation tends to be strong. It may also turn out that it is easier to sample for perchlorate in drinking water supplies than in the environment. Both government and industry scientists are now saying that the standard analytic method for perchlorate detection generates false positives - that is, it finds perchlorate where it isn't, or at least it reports inaccurately high concentrations. As I understand it, this is largely due to interference from other substances in the water. To the extent that drinking water contains lower concentrations of other minerals, the measurements may be more accurate. Finally, at most environmental sites, the remedial response, including treatment, is paid for by polluters and other responsible parties. In the drinking water system, cleanup is paid for by water vendors. Unless they can find a sugar daddy in Congress to help pay the bills, that cost is passed on to the customers. Although they may have a case for cost recovery - that is, to make polluters pay for the treatment system - at most sites that is unlikely to occur until long after the expenses are made. In no way am I suggesting that just by splitting the perchlorate problem in half can we resolve the enormous challenge we face. Rather, I do think, if we're careful to make the proper analytical distinctions, that we should be better able to better comprehend the problems and negotiate over solutions. Lenny Siegel -- 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 ~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~ CPEO: A DECADE OF SUCCESS. Your generous support will ensure that our important work on military and environmental issues will continue. Please consider one of our donation options. Thank you. http://www.groundspring.org/donate/index.cfm?ID=2086-0|721-0 | |
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