ASTM D6452-99(2005) - 1.1.2005
 
Significance and Use

Wells used in ground-water quality investigations or monitoring programs are generally purged prior to sampling (Note 1). Purging is done to minimize the bias associated with stagnant water in the well, which generally does not accurately reflect ambient ground-water chemistry (Note 2).

Note 1—Some sampling methods, such as passive sampling, do not require the practice of purging prior to sample collection (1,2).3

Note 2—This guide does not address the practice of post-sample purging (purging again after sampling is completed), which is intended for purposes other than the minimization of bias associated with stagnant water in the well.

There are various methods for purging. Each purging method may have a different volume of influence within the aquifer or screened interval. Therefore, a sample collected after purging by any one method is not necessarily equivalent to samples collected after purging by the other methods. The selection of the appropriate method will be dependent on a number of factors, which should be defined during the development of the sampling and analysis plan. This guide describes the methods available and defines the circumstances under which each method may be appropriate.

 
1. Scope

Wells used in groundwater quality investigations or monitoring programs are generally purged prior to sampling (Note 1). Purging is done to minimize the bias associated with stagnant water in the well, which generally does not accurately reflect ambient groundwater chemistry (Note 2).

Note 1—Some sampling methods, such as passive sampling, do not require the practice of purging prior to sample collection (1,2).

Note 2—This guide does not address the practice of post-sample purging (purging again after sampling is completed), which is intended for purposes other than the minimization of bias associated with stagnant water in the well.

There are various methods for purging. Each purging method may have a different volume of influence within the aquifer or screened interval. Therefore, a sample collected after purging by any one method is not necessarily equivalent to samples collected after purging by the other methods. The selection of the appropriate method will be dependent on a number of factors, which should be defined during the development of the sampling and analysis plan. This guide describes the methods available and defines the circumstances under which each method may be appropriate.

 
2. Referenced Documents

D653-26a

Standard Terminology Relating to Soil, Rock, and Contained Fluids (Includes all amendments and changes 6/15/2026).

D5092-04

Standard Practice for Design and Installation of Ground Water Monitoring Wells in Aquifers

D5088-20

Standard Practice for Decontamination of Field Equipment Used at Waste Sites

D6089-19(2023)

Standard Guide for Documenting a Groundwater Sampling Event

D4750-87(2001)

Standard Test Method for Determining Subsurface Liquid Levels in a Borehole or Monitoring Well (Observation Well) (Withdrawn 2010)

D5521-05

Standard Guide for Development of Groundwater Monitoring Wells in Granular Aquifers