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The No-Purge Scetuarno � <br /> (Lessons Learned) <br /> Thomas Wayne„ Kabis <br /> Background <br /> The essential importance of groundwater quality is now recognized as development of <br /> groundwater continues to expand Monitoring of groundwater quality is becoming increasingly <br /> more important due to public worries over chemical contamination The development of new <br /> equipment and techniques for measuring contaminants in minute concentrations without the <br /> additional production of hazardous and toxic wastes has been added to a list of sampling <br /> concerns. Accuracy and cost savings top the list of concerns surrounding the sampling and <br /> monitoring of groundwater <br /> The measure of cost savings when engaging in groundwater sampling is calibrated with many <br /> standards The most common standards involve the expenditure of manpower and raw <br /> materials for the collection of any one sample, suite of samples or for the conduct of an entire <br /> program of groundwater sampling. The expenditure of manpower and use of raw materials <br /> takes on a much more complicated meaning when viewed through an established sampling <br /> plan and to a greater extant, when compiling and publishing a sampling plan. <br /> First and foremost, it is necessary to understand the medium to be sampled, the environment in <br /> which the sampling is to take place, and exactly what is to be expected from the sampling event. <br /> It is also pertinent to consider the consequences of using any particular type of equipment or <br /> procedure, either based on the equipment itself, or on imposed standards. Current sampling <br /> standards are based on antiquated equipment and involve the production of large amounts of <br /> additional hazardous waste as a result of the sampling event, in order to obtain a repeatable <br /> average sample This produced waste, must then be discharged elsewhere or treated and <br /> discharged, generally adding greatly to the confusion of exactly what the regional chemical <br /> composition of groundwater is at any one site <br /> There has been much study completed on the problem of obtaining representative groundwater <br /> samples from rapidly recovering ground-water monitoring wells Scalf, et. al. reported in a <br /> 1981 paper that bacterial activity can dramatically affect VOC analysts results Dissolved VOCs <br /> can effervesce in as little as 2 hours after sample acquisition. Seanor and Brannaka noted in <br /> their 1983 paper that water in ground-water monitoring wells is stagnant, this means that, <br /> typically, water standing in a well is usually considerably above the screened interval and this <br /> water is not in communication with formational water This standing water is subject to <br /> different chemical equilibria and often has different pH, Eh, temperature, and dissolved solids <br /> Wilson and Dworkin reported in their 1984 paper that rust and scale from ground-water <br /> monitoring wells may interfere with laboratory analyses, as may the presence of colloids and <br /> clay platelets Barcelona and Helfrich concluded in 1986, that no or improper purging of a <br /> ground-water monitoring well was a greater cause for sampling error than was sampling . <br /> method, well construction materials, or sampler materials They went so far as to state that <br /> improper purging was the dominant error factor <br />