Hafnium

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Sunday, June 7, 2009

Texas Smelter site in Galveston shows low-level radioactive compounds as well as arsenic, cadmium, copper, lead etc......

"Case History: The 170 acre Tex-Tin Superfund site is located near La Marque, Galveston County, Texas. This facility is an inactive tin and copper smelter and contaminants were found in soils, groundwater and surface water, including the Swan Lake ecosystem and associated salt marsh habitats. Major contaminants identified were arsenic, cadmium, chromium, copper, lead and nickel as well as low-level radioactive compounds. In September, 1999, the Trustees entered into settlement negotiations with the Responsible Parties (RPs), through the Department of Justice (DOJ). A Consent Decree was signed in August 2000, with DOI-FWS concurrence..."

http://www.fws.gov/southwest/es/contaminants/NRDAR/SiteInformation/Texas/TexTin.pdf

*WHY WON'T THE EL PASO ASARCO SITE PUBLISH CHEMICAL TESTING DATA FOR ALL THOSE SAME COMPOUNDS?*

1991 El Paso Texas was recharging the Hueco aquifer with re-injection of tertiary-treated wastewater....

Brock, R.D., Buska, P.M., and Godsy, E.M., 1994, Hydrogeologic and water quality data from wells near the Hueco bolson recharge project area, El Paso, Texas, 1990 and 1991: U.S. Geological Survey Open File Report 94-329, 85 p.

Abstract Tertiary-treated wastewater currently (1991) is being injected into the Hueco bolson aquifer at a site in northeastern El Paso, Texas, to supplement the quantity of available freshwater. Hydrologic data were compiled and water-quality and bacterial data were collected from existing wells near the Hueco Bolson Recharge Project (HBRP) in August and September 1990 and 1991. Borehole tracer tests indicated upward ground-water flow in nearly all tested intervals of several observation wells. The cumulative volume of injected water was less than the volume produced from wells adjacent to the HBRP area. Water levels in three production wells, located more than 1.5 miles from the injection wells, declined at rates comparable to those observed before injection operations. Water levels in wells located within 0.75 mile of the injection-well pipeline declined at a slower rate after HBRP injection operations had begun. Between 1985 and 1991, water levels in observation wells located within 700 feet of an injection well either did not appreciably decline, or declined at smaller rates than water levels in more distant production wells. Trihalomethane compounds were detected in water from 8 of the 16 observation and production wells sampled in 1990 and in 10 of the 17 wells sampled in 1991. Concentrations trihalomethane compounds in these samples ranged from 0.05 to 1.9 mg/L in 1990 and from 0.05 to 1.4 mg/L in 1991. Concentrations of trihalomethane compounds in samples of injected water from two wells were 27.8 and 34.6 mg/L respectively, in 1991. Dibromomethane and dichloromethane were detected in water from injection wells and from observation wells within about 700 feet of the injection wells. Aerobic bacteria were determined to be the only bacteria type present in ground water except for samples from two wells, which also contained denitrifying bacteria. The populations of aerobic bacteria determined in ground water ranged from 80 to more than 160,000 most probable number of organisms per milliliter of sample.