From: | "Laura Olah" <olah@speagle.com> |
Date: | 16 Sep 1997 14:34:43 |
Reply: | cpeo-military |
Subject: | WHY HARDWOOD RANGE EXPANSION IS STUPID! |
Aimee, Please post. THANKS! Laura CSWAB Comment on the draft EIS for the Proposed Expansion of the Hardwood Bombing Range in Northern Wisconsin: A proposal to withdraw 6,000 acres of County Forest land and add it to the existing Hardwood Bombing Range in Juneau County. WHY THE HARDWOOD RANGE EXPANSION IS STUPID! "Construction and maintenance and bombing could possibly have the following effect on wetlands: altering groundwater discharge/recharge characteristics, reduced potential for filtering and treatment for water quality protection, reduced potential for attenuation and storage of stream and floodwater, loss of floral diversity, and loss of fishery and wildlife habitat." Source: Draft Environmental Impact Statement Addressing the Hardwood Range Expansion and Associated Airspace Action, Wisconsin Air National Guard, August 1997. VIABLE ENVIRONMENTALLY AND ECONOMICALLY SUPERIOR ALTERNATIVES WERE ELIMINATED FROM CONSIDERATION EARLY IN THE EIS PROCESS AND NOT CARRIED FORWARD FOR DETAILED STUDY. Utilizing electronic scoring of simulated weapons delivery and increasing flight simulator training is actively and successfully used by the U.S. Air Force, contrary to statements in the draft EIS. These technologies are currently able to meet the "accuracy parameters" required by the USAF, contrary to the draft EIS. Just last year, Kelly Air Force Base in San Antonio, Texas, installed a Unit Training Device (UTD) flight simulator. The UTD is one of 65 such units currently utilized by the USAF at bases across the nation. According to the UTD program manager for the Air Force, a "quality, full-mission trainer used to cost as much as the F-16 it simulated; now we are purchasing trainers for less than $1 million each and experiencing a 95 percent cost reduction in comparison to traditional mission simulators." The UTD simulator is used by the 182nd Fighter Squadron of the Texas Air National Guard's 149th Fighter Wing to train its F-16 pilots -- the same aircraft used at the Hardwood Range -- in emergency procedures, avionics, air-to-air and air-to-ground combat, and tactical fighting in a dense threat environment. According to the facility's press release, the Guard pilots are also able to practice acquiring and identifying targets and accurately delivering weapons in adverse weather conditions at day or night. Unlike previous F-16 simulators, which have had to be housed in gymnasium-sized high bays, UTD trainers can be operated within a standard squadron office environment. While operating a traditional F-16 weapon system trainer in a specially designed facility has cost about $50,000 a month, today individual UTD simulators can be operated for a fraction of the amount. The base reports these cost savings are being driven by a leap in computer technology that also has enabled UTD simulators to maintain a high degree of flight training realism. The UTD program, the report concludes, began to take shape when the Air National Guard identified the need for a unit-level pilot trainer. At the time its units did not have simulators, which required aircrews to travel to distant Air Force bases where F-16 simulators were located. THE POTENTIAL ENVIRONMENTAL, ECOLOGICAL AND HEALTH IMPACTS OF USING CHAFF ON PUBLIC, PRIVATE, AND TRIBAL LANDS WERE OMITTED FROM THE EIS. Chaff is an airborne radar-detection countermeasure consisting of extremely fine fibers of aluminum coated fiberglass. A typical burst Chaff bundle contains approximately 2.1 million human hair size fiberglass strands. After its dispersal and use in military training exercises it becomes a waste material that falls to the ground. The use of chaff at Fallon Naval Air Station, Nellis Air Force Base, Mountain Home Air Force Base, and at military installations across the nation is a growing concern for rural residents. According to the Rural Alliance for Military Accountability (RAMA), rural residents and the Bureau of Land Management officials are finding clumps of chaff on public and private lands throughout central Nevada. The Nevada Division of Environmental Protection noted two primary concerns: "The first concern is from inhalable particulate below PM10 which may occur from the decomposition and resuspension of fiber particulate by mechanical means. The Division's second concern deals with the physical deposition of what could be considered solid waste on public and private lands in the State of Nevada. There is very little information on the amounts of chaff currently deposited and how these fibers decompose in the environment." The Nevada Division of Environmental Protection concluded, "The Division does not feel that adequate studies have been done to assure that there are no environmental risks posed by the fibers." The mechanical breakdown of these silicate fibers can be defined as asbestos-like, tiny filaments, and could, if inhaled or ingested, lodge in body tissue. The health risks associated with inhalation or ingestion have never been independently researched. According to Department of Defense studies, "The minimum dimension of a chaff fiber is 0.0003 inches, which converts to 7.6 micrometers. This is less than the 10 micrometer maximum size cutoff in EPA's standard for inhalable particulate." Moreover, the National Institute for Occupational Safety and Health (NIOSH) considers crystalline silica (as a respirable dust) "a potential human carcinogen." The Air Force report Identifying and Evaluating the Effects of Chaff from Military Aircraft documented the lack of information on potential health risks, saying: "There is no documentation of human exposure studies to chaff." The report continued by noting: "Detailed authoritative data concerning the impacts of chaff on land is lacking...The long-term effects of chaff are unknown." The Army in 1992 concluded: "The potential of weathering fibers to respirable geometries in the environment and the potential exposure from resuspension of these fibers need to be determined to evaluate long-term risk and chronic exposure scenarios." The report continued: "Glass and carbon fibers and, likely iron fibers deposited on soils are susceptible to wind resuspension until immobilization occurs. However, even those fibers immobilized on soil surfaces can be resuspended by physical forces such as foot and/or vehicular traffic. Thus, there is a persistent risk of fiber inhalation and mitigation efforts will likely be required for areas containing high fiber concentrations. . ." THE PRESENCE OF EXTENSIVE WETLANDS, TOGETHER WITH A FACILITY-WIDE SHALLOW WATER TABLE, ELIMINATES THE HARDWOOD SITE AS A VIABLE TRAINING AREA. The draft EIS clearly states: "Extensive wetlands are located within the Hardwood Range, proposed expansion area, and Restricted Area R-6904A." (Page 3-38). Moreover, the EIS characterizes ordnance impact as "significant surface disturbance." And lastly, the EIS says construction and maintenance and bombing could effect wetlands by "altering groundwater discharge/recharge characteristics, reduced potential for filtering and treatment for water quality protection, reduced potential for attenuation and storage of storm and floodwater, loss of floral diversity, and loss of fishery and wildlife habitat." One of the most inane statements in the entire draft EIS is on page 4-27: "None of the activities associated with the Proposed Action would have an impact on groundwater resources underlying the expanded Hardwood Range." As groundwater is hydrologically connected to adjacent wetlands, this would seem impossible. The Watershed Protection Approach, as recognized by the USEPA, is "a management approach for more effectively protecting and restoring aquatic ecosystems and protecting human health. The EPA Office of Water is using this approach to focus on hydrologically defined resource areas, watersheds, and aquifers. The EWPA recognizes that water quality management must embrace human and ecosystem health and that managing for one without considering the other can be detrimental to both." (Emphasis added.) (Source: Watershed Protection: A Statewide Approach, EPA Office of Wetlands, Oceans and Watersheds, USEPA, August, 1995.) EPA Administration also supports this approach saying: "The EPA's overall goal is to prevent adverse effect to human health and the environment and protect the nation's groundwater resources in accord with federal laws. It will counter adverse effects (significant and reasonable risks) to the resource and the pollution in the near and long-term. Prevention is emphasized because groundwater cleanup is costly and difficult. Safe drinking water is the primary goal, along with the protection of interconnected surface water resources and ecosystems." (Source: Protecting the Nation's Groundwater: EPA strategy for the 1990s. July 1991. Final Report of the EPA Ground Water Task Force.) THE MUNITIONS DISPOSAL SITE SHOULD BE CLOSED AND REMEDIATED AS SOON AS POSSIBLE. The draft EIS states no live ordnance is utilized at Hardwood, subsequently there is no apparent need for keeping this site open. The draft EIS reports: "One Defense Installation Restoration Project is located on the Hardwood Range. This site has been used since 1976 for annual burning and burial of spent munitions. A small plume of contaminated groundwater has been identified in that area...No monitoring is currently being performed at the site." THE CHARACTERIZATION OF THE COMBUSTION PRODUCTS IN THE EIS IS BASED ON OBSOLETE, INCOMPLETE INFORMATION. In an attempt to measure and identify emissions from the burning of propellants, Sandia National Lab recently conducted the so-called "Bang Box" tests. According to this report, emission factors from these tests included toxic and carcinogenic substances such as carbon monoxide, methane, benzene, 2,4 dinitrotoluene, 2,6 dinitrotoluene, and nitrogen oxides. Potential toxic emissions include lead, cadmium, and chromium -- standard constituents of conventional propellants. According to the Overview of the Health Effects of Selected Munitions Chemicals published by the USEPA and the Department of the Army. "DNT is classified B2 (probable human carcinogen) and thus a Lifetime HA is not recommended. The cancer potency is associated with hepatocellular and mammary gland carcinogenic activity in rats after 2,4-DNT treatment. 2,4-DNT also may be a promoter. There is some evidence which suggests that 2,6-DNT has both initiation and promotion activity and, therefore, may be a complete carcinogen." The Army's Health Risk Assessment for the Open Burn Facility at Badger Army Ammunition Plant describes the incremental carcinogenic risk for exposure to DNT's from open burning of propellants. Of considerable concern are the multiple potential exposure pathways including inhalation, soil ingestion, dermal contact, and food ingestion and the increased and additive risks associated with each of these exposure pathways. Non-carcinogenic health risk are increased as well; toxic metals-contaminated ash, disbursed by open burning, exposes soldiers and nearby residents through inhalation, soil ingestion, dermal contact, and food ingestion. Other pollutants including NOx, CO, VOC's and TSP increase and compound risks to human health. In addition to fire hazards, burning red phosphorus emits toxic fumes of oxides of phosphorus and can react with reducing materials. THE CHARACTERIZATION OF POTENTIAL ECOLOGICAL, ENVIRONMENTAL AND HUMAN HEALTH IMPACTS OF TITANIUM TETRACHLORIDE IN THE DRAFT EIS IS INCOMPLETE, AND THEREFORE INCORRECT. Titanium Tetrachloride is a colorless or light yellow, fuming liquid with a pungent odor. Signal charges used in training ordnance at Hardwood reportedly each contain 17 cubic centimeters of titanium tetrachloride. The "smoke" described in the draft EIS is actually poisonous gases, according to the US Department of Health and Human Services (USDHHS) Toxicological Profiles. In a fire, poisonous emissions include titanium oxides and hydrochloric acid. Titanium Tetrachloride is classified by the Department of Transportation and the US Environmental Protection Agency as a Hazardous Substance, and is on the Special Health Hazard Substance List because it is corrosive. According to the USDHHS, breathing Titanium Tetrachloride can irritate the nose, throat and air passages, causing cough and phlegm. Repeated exposure can cause chronic bronchitis and may cause emphysema. Higher exposures can cause fluid in the lungs, a medical emergency, and even death. Skin contact can cause burns. The USDHHS reports acute (short-term) ecological effects may include "the death of animals, birds, or fish, and death or low growth rate in plants. Acute effects are seen two to four days after animals or plants come in contact with a toxic chemical substance. Insufficient data are available to evaluate or predict the acute, short-term effects of Titanium Tetrachloride to aquatic life, plants, birds, or land animals." Chronic toxic ecological effects may include shortened lifespan, reproductive problems, lower fertility, and changes in appearance or behavior. Chronic effects can be seen long after first exposure(s) to a toxic chemical. Insufficient data are available to evaluate or predict the chronic, long-term effects of Titanium Tetrachloride to aquatic life, plants, birds, or land animals. Laura Olah, Executive Director Citizens for Safe Water Around Badger E12629 Weigand's Bay South Merrimac, Wisconsin 53561 olah@speagle.com Phone (608)643-3124 Fax (608)643-0005 Website http://www.speagle.com/cswab | |
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