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Drilling and Production Operations  3S


 2,1.4 Reserves Pits

   The most common method for the disposal of drilling wastes for
 onshore wells is in on-site reserves pits. The contents of reserves pits vary,
 depending on the drilling mud and the types of formations drilled.
 Reserves pits, however, can cause local environmental impact, particu-
 larly older pits that contain materials that are currently banned from
 such disposal or that were not constructed according to current regula-
 tions. The environmental impact of modern reserves pits are minimal.
   The composition of the fluid in a reserves pit may be different from
 that of the original drilling fluid. Chemical and physical alterations
 of drilling fluids can occur during and after drilling from the heat and
 pressure encountered during drilling or from the addition of formation
 materials. Other materials may also be added to the pit before closure,
 either deliberately or inadvertently. Such materials include caustic
 soda, rig wash, diesel fuel, waste oil from machinery, metal and plastic
 containers, and other refuse (Powter, 1990). Bad storage and disposal
 practices associated with reserves pits have lead to their being a source
 of benzene, lead, arsenic, and fluoride, even when these components
 were not detected in the active mud system (Wojtanowicz, 1991).
   The heavy metals and other dissolved solids contents in both the
 water and mud (sludge) phases of 125 reserves pits scattered around
 the United States were measured in one study, and the total and water-
 soluble (leachable) concentrations were determined (Leuterman et ah,
 1988), The mean metals concentrations of all of the pits varied
 significantly with species, with mean concentrations on the order of
 a few tens of mg/L. These data are summarized in Table 2-3. It was
 found that the metals concentrations in the mud phase were generally
 higher than in the water phase, indicating that most of the metals were
 probably bound to the organic and clay particles and were not readily
 available for leaching.
   In separate studies, the heavy metals contents of reserves pits in
 the U.S. Gulf Coast were also analyzed and found to vary significantly
 (Wojtanowicz et ah, 1989 and Deuel and Holliday, 1990). In the latter
 study, the pit contents were analyzed by the U.S. Environmental
 Protection Agency, the American Petroleum Institute, and in a private
 study under Louisiana State guidelines. The analysis protocols and
 procedures differed in the three studies and yielded somewhat different
 results. The results are summarized in Tables 2-4 and 2-5.
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