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• <br />scientific literature. How does the recent <br />toxicology compare with the existing <br />toxicology, and what, if anything, did we <br />learn? <br />2,4-D toxicology <br />The latest studies confirm what existing <br />toxicology hes shown for some time. For <br />example, the new toxicology and <br />environmental toxicology (114 studies) <br />confirms: <br />I. 2,4-D has moderate to (ow acute <br />toxicity. The LD50 (rats) ranges <br />from 699 mg per kg of body weight <br />(2,4-D acid) to 896 mg/kg for the <br />ester. From an LD50 standpoint, <br />2,4-D is less toxic than caffeine and <br />slightly more toxic than aspirin. <br />2. 2,4-D has low reproductive toxicity. <br />3. 2,4-D does not cause birth defects. <br />4. Based on the extensive toxicology, it <br />is highly improbable that 2,4-D <br />causes cancer. <br />5. 2,4-D has low potential to cause <br />neurotoxicity in both short- and long- <br />term exposures. <br />6. 2,4-D does not cause genetic <br />damage. <br />7. At the concentrations which may be <br />found in the environment, 2,4-D is <br />highly unlikely to present a threat to <br />wildlife. <br />Environmental fate <br />The seventy-eight environmental fate <br />studies again confirm that 2,4-D has a <br />relatively short half-life and is rather <br />immobile in the soil. In thirty-five <br />studies across the U.S., the average <br />lowest depth ranged from six to twelve <br />inches in soils of the Southern United <br />States to sixteen to twenty-four inches in <br />tow organic-matter soils. Soils were <br /> <br />sampled to a depth of forty~ight inches. <br />Its average half-life in soils ranged from <br />6.4 days in Southern soils to 8.3 days in <br />high organic- matter soils. As a result, <br />2,4-D is unlikely to get into ground <br />water. The average half-life in grass was <br />6.1 days and 6.9 days in thatch. The half- <br />life in natural water was two to four <br />weeks, although in areas where soil <br />microbes were conditioned to 2,4-D, <br />such as a treated rice paddy, the half-life <br />was as short as one day. The acid form <br />of 2,4-D, as wel[ as the amine and ester <br />chemical groups, metabolized to <br />compounds of nontoxicological <br />significance and ultimately to form of <br />cazbon. Thus, 2,4-D is considered a <br />biodegradable compound, and under <br />normal conditions, 2,4-D residues are not <br />persistent in soil, water, or vegetation. <br />2,4-D and past problems <br />ff the toxicology of 2,4-D has always <br />been essentially clean, why aze there still <br />per+eeived problems? Any suggestions <br />that 2,4-D may cause cancer, for <br />example, were never based on controlled, <br />laboratory-animal feeding studies. <br />Rather, they came from what are known <br />as case-control studies in the field of <br />epidemiology. These studies are based on <br />interviews, often by telephone, with <br />populations of cancer cases who may <br />have had an exposure of interest. The <br />results of these interviews are then <br />compared to interviews with non-cancer <br />cases. <br />There aze more than 100 epidemiologic <br />studies pertinent to 2,4-D. Taken <br />together, the results aze equivocal or <br />ambiguous, with some studies suggesting <br />a relationship between 2,4,-D and non- <br />Hodgkins lymphoma (NHL.), a form of <br />