ASTM D 3977 : 1997 : R2013
Superseded
A superseded Standard is one, which is fully replaced by another Standard, which is a new edition of the same Standard.
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Standard Test Methods for Determining Sediment Concentration in Water Samples
Hardcopy , PDF
11-11-2014
English
01-01-2013
CONTAINED IN VOL. 11.02, 2017 Defines the determination of sediment concentrations in water and wastewater samples collected from lakes, reservoirs, ponds, streams, and other water bodies.
Committee |
D 19
|
DocumentType |
Test Method
|
Pages |
7
|
ProductNote |
Reconfirmed 2013
|
PublisherName |
American Society for Testing and Materials
|
Status |
Superseded
|
SupersededBy | |
Supersedes |
1.1These test methods cover the determination of sediment concentrations in water and wastewater samples collected from lakes, reservoirs, ponds, streams, and other water bodies. In lakes and other quiescent-water bodies, concentrations of sediment in samples are nearly equal to concentrations at sampling points; in most instances, sample concentrations are not strongly influenced by collection techniques. In rivers and other flowing-water bodies, concentrations of sediment in samples depend upon the manner in which the samples are collected. Concentrations in isokinetically-collected samples can be multiplied by water discharges to obtain sediment discharges in the vicinity of the sampling points.
1.2The procedures given in these test methods are used by the Agricultural Research Service, Geological Survey, National Resources Conservation Service, Bureau of Reclamation, and other agencies responsible for studying water bodies. These test methods are adapted from a laboratory-procedure manual2 and a quality-assurance plan.3
Sections | |
Test Method A—Evaporation | 8 to 13 |
Test Method B—Filtration | 14 to 19 |
Test Method C—Wet-sieving-filtration | 20 to 25 |
1.4Test Method A can be used only on sediments that settle within the allotted storage time of the samples which usually ranges from a few days to a few weeks. A correction factor must be applied if dissolved-solids concentration exceeds about 10 % of the sediment concentration.
1.5Test Method B can be used only on samples containing sand concentrations less than about 10 000 ppm and clay concentrations less than about 200 ppm. The sediment need not be settleable because filters are used to separate water from the sediment. Correction factors for dissolved solids are not required.
1.6Test Method C can be used if two concentration values are required: one for sand-size particles and one for the combination of silt and clay-size particles. The silt-clay fraction need not be settleable.
1.7These test methods must not be confused with turbidity measurements discussed in Test Method D1889. Turbidity is the optical property of a sample that causes light rays to be scattered and absorbed; it is not an accurate measure of the mass or concentration of sediment in the sample.
1.8These test methods contain some procedures similar to those in Test Methods D1888 which pertains to measuring particulate and dissolved matter in water.
ASTM D 7512 : 2009 : R2015 | Standard Guide for Monitoring of Suspended-Sediment Concentration in Open Channel Flow Using Optical Instrumentation |
ASTM D 7726 : 2011 : R2016 : EDT 1 | Standard Guide for The Use of Various Turbidimeter Technologies for Measurement of Turbidity in Water |
ASTM D 4411 : 2003 : R2014 : EDT 1 | Standard Guide for Sampling Fluvial Sediment in Motion |
ASTM D 7100 : 2011 | Standard Test Method for Hydraulic Conductivity Compatibility Testing of Soils with Aqueous Solutions |
ASTM D 1129 : 2013 : REDLINE | Standard Terminology Relating to Water |
ASTM D 2777 : 2013 : REDLINE | Standard Practice for Determination of Precision and Bias of Applicable Test Methods of Committee D19 on Water |
ASTM E 11 : 2017 : REDLINE | Standard Specification for Woven Wire Test Sieve Cloth and Test Sieves |
ASTM D 1888 : 1978 | Methods of Test for Particulate and Dissolved Matter in Water (Withdrawn 1989) |
ASTM D 4410 : 2016 : REDLINE | Terminology for Fluvial Sediment |
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