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time, such as turbidity, or at a minimum, the visual appearance of the discharge water; and (5) <br />information about well characteristics, such as the total depth of the well, the well diameter, the <br />depth(s) to the screened or open intervals, and the water level in the well. <br />Information collected during development can be used to evaluate requirements for sam- <br />pling. Estimates of the recovery rate and recovery time of the water level in the well after pump- <br />ing can be used to estimate the time required for purging the well prior to sampling. If the <br />recovery rate of the water level in the well is slow even after development, it might be necessary <br />to plan purging of the well on one day and sampling the well on the following day. The recovery <br />time can be used to determine the pumping rates to purge and sample the well and to determine <br />if an alternative method of pumping the well is required. <br />Factors that affect the well development and the effort required depend on aquifer charac- <br />teristics, the drilling method used to install the well, and well characteristics. Traditionally, <br />methods of well development are selected to optimize on the capacity of a well. Because a pri- <br />mary objective for wells used in the NAWQA Program is water-quality sampling, methods for <br />developing wells must be evaluated and selected on the basis of the probable effect on ground- <br />water chemistry. The best development techniques to restore the chemical quality of aquifer <br />pore water to its predrilled condition are those that avoid the introduction of air, foreign water, <br />and other foreign fluids into the aquifer during the development process. This reduces well- <br />development options, but is critical to ensuring that the effect of development on ground-water <br />chemistry is minimized. The following methods for well development in the NAWQA Program, <br />in the order of recommended use, are: bailing; mechanical surging; pumping or overpumping, <br />and backwashing; indirect eduction jetting; backwashing; and jetting and surging with water or <br />air (W. Lapham, U.S. Geological Survey, written commun., 1995--see footnote 1; U.S. Bureau <br />of Reclamation, 1977; Anderson, 1984; Driscoll, 1986; Aller and others, 1989; and Shuter and <br />Teasdale, 1989). <br />Documentation <br />The criteria for well selection and information about wells selected for sampling are to be <br />documented in permanent files. Careful and complete documentation aids in interpretation of <br />ground-water data and provides historical reference for future use of the well. In addition, doc- <br />umentation of network-design information for each Study-Unit Survey, Land-Use Study, and <br />Flowpath Study is required. Types of network-design information include network identifica- <br />tion, personnel involved, well selection and installation information, and field activities. An <br />example form is provided in an internal document entitled "gw.network.documentation" <br />(P. Leahy, U.S. Geological Survey, written commun., February 4, 1994). <br />A paper or electronic well site file should be maintained for each well sampled by NAWQA <br />Study Units. Information in this file begins with a well-information check list (fig. 7). As infor- <br />mation about the well site is collected, it is added to the site file. <br />It is USGS policy,,that all of the routine ground-water data collected must be stored in the <br />computer files of the National Water Information System. The USGS, Office of Ground Water, <br />interprets "routine" data collection of the USGS to include "all ground-water data collected by <br />WRD basic-data programs and district projects" (Office of Ground Water Technical Memoran- <br />dum No. 93-03, written commun., 1993). <br />40