ASTM E 1924 : 1997 : R2012
Withdrawn
A Withdrawn Standard is one, which is removed from sale, and its unique number can no longer be used. The Standard can be withdrawn and not replaced, or it can be withdrawn and replaced by a Standard with a different number.
Standard Guide for Conducting Toxicity Tests with Bioluminescent Dinoflagellates (Withdrawn 2013)
Hardcopy , PDF
03-31-2013
English
12-01-2012
CONTAINED IN VOL. 11.06, 2013 Defines two distinct procedures, based on similar principles, for obtaining data concerning the adverse effects of a test material (added to dilution water) on oceanic bioluminescent dinoflagellates.
Committee |
E 47
|
DocumentType |
Guide
|
Pages |
12
|
ProductNote |
Reconfirmed 2012
|
PublisherName |
American Society for Testing and Materials
|
Status |
Withdrawn
|
Supersedes |
1.1This guide covers two distinct procedures, based on similar principles, for obtaining data concerning the adverse effects of a test material (added to dilution water) on oceanic bioluminescent dinoflagellates.
1.1.1The endpoint for both procedures is based on a measurable reduction or inhibition in light output from the dinoflagellates. Both procedures are similar in that when bioluminescent dinoflagellates are exposed to toxicants, a measurable reduction in bioluminescence is observed from their cells following mechanical stimulation when compared to control cells. In the first procedure, cells of the bioluminescent dinoflagellate Gonyaulax polyedra can be tested over a range of up to seven days of exposure (or longer) to a toxicant. The second procedure uses another species, Pyrocystis lunula, for a 4 h test.
1.2Both procedures can measure the toxic effects of many chemicals, various marine and freshwater effluents, antifouling coatings, leachates, and sediments to bioluminescent dinoflagellates (1-5).3 Compounds with low water solubility such as large organic molecules may be solubilized with methanol, ethanol, and acetone solvents for testing (4) (see Guide E729).
1.3An IC50 in light output (bioluminescence) is the recommended endpoint (1). However, percent inhibition of bioluminescence is an appropriate endpoint in some cases (5).
1.4Other modifications of these procedures might be justified by special needs or circumstances. Although using appropriate procedures is more important than following prescribed procedures, results of tests conducted using unusual procedures are not likely to be comparable to results of other tests. Comparison of results obtained using modified and unmodified versions of these procedures might provide useful information concerning new concepts and procedures for conducting acute and chronic tests.
ASTM E 1850 : 2004 : R2019 | Standard Guide for Selection of Resident Species as Test Organisms for Aquatic and Sediment Toxicity Tests |
ASTM E 1733 : 1995 | Standard Guide for Use of Lighting in Laboratory Testing |
ASTM D 1141 : 1998 : EDT 1 | Standard Practice for the Preparation of Substitute Ocean Water |
ASTM E 729 : 1996 | Standard Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates, and Amphibians |
ASTM D 5196 : 2006 | Standard Guide for Bio-Applications Grade Water |
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