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An important concern associated with the environmental assessment of agricultural properties is <br /> the issue of buried pesticide containers. It was an occasional practice to dispose of containers by <br /> this method many years ago. To detect these types of underground artifacts is difficult even with <br /> the use of ground penetrating radar or other types of non-intrusive, subsurface analyses. The <br /> land surface did not exhibit visual indicators for buried containers such as surfacing of product <br /> residue, soil mounding or soil depressions. In addition, 84 acres of the site was recently deep- <br /> ripped to six feet. Normally, this procedure would uncover buried artifacts. <br /> The static groundwater is found approximately 60 feet under the property. This is considered a <br /> comparatively deep groundwater elevation. Deep groundwater is not as easily impacted from <br /> pesticides or nitrogen in the form of nitrates. The groundwater directional flow is probably <br /> towards the northeast. The on-site soils consist of a medium clay content sandy loam soil which <br /> can attenuate agrichemical contamination in comparison to a sandy soil. <br /> To evaluate agrichemical residues as a nonpoint source of potential contamination, pesticide <br /> records from the previous two years were obtained. The science of pesticide residues in soil, air, <br /> surface water and groundwater is extremely complex and variable. Environmental models which <br /> attempt to predict pesticide behavior and transport in the environment are beyond the scope of <br /> this investigation. It has been clearly evident over the last four decades that the riskibenefit ratio <br /> regarding pesticides has been overwhelming benefit and comparatively low risk to the United <br /> States population, as a whole. <br /> Environmental fate data for the following pesticides which were applied to the subject property <br /> was obtained from the Illustrated Handbook of Physical-Chemical Properties and Environmental <br /> Fate for Organic Pesticide Chemicals: <br /> Imidan. Common name: Phosmet. Half-lives in the environment: Surface water: 33 days <br /> (d). Soil: field half-life of 10 d. Phytolysis half-life 53.25 hrs. <br /> Glyphos. Half-lives in the environment: Air: 0.469-4.69 hrs. Surface water: 70 d. <br /> Soil: <28 d. <br /> CONCLUSIONS AND RECOMMENDATIONS <br /> From visual observations,there is no surface contamination. The probability of subsurface <br /> contamination from pesticides can be considered low, considering the environmental fate data <br /> and soil type. Groundwater testing for nitrate and DBCP will be performed next month to <br /> complete the requirements of the Soil Suitability Study. Therefore, at this point in time, no <br /> corrective action is required within the boundaries of the subject property. <br /> 4 <br /> `vaffey Jg Prsearch <br />