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POTASSIUM CHLORIDE CAS N°: 7447-40-7

POTASSIUM CHLORIDE CAS N°: 7447-40-7

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OECD SIDS<br />

<strong>POTASSIUM</strong> <strong>CHLORIDE</strong><br />

Date: 30-MAR-2003<br />

4. Ecotoxicity Substance ID: <strong>7447</strong>-<strong>40</strong>-7<br />

AQUATIC ORGANISMS<br />

4.1 Acute/Prolonged Toxicity to Fish<br />

Type of test: static<br />

Species:<br />

Pimephales promelas (Fathead minnows)<br />

Exposure period: 24, 48, 96 hours<br />

Unit: mg/l Analytical monitoring: yes<br />

LC50/24 hours: = 950<br />

LC50/48 hours: = 910<br />

LC50/96 hours: = 880<br />

Method:<br />

other: EPA/600/4-90/027<br />

Year: 1997 GLP: no<br />

Test substance: as prescribed by 1.1-1.4; reagent grade<br />

Remarks:<br />

All organisms, 1 to 7 days old, were obtained from<br />

in-house cultures. Brood stock were cultured at<br />

20-25 degrees C in tap water pretreated with<br />

activated carbon. Larva were fed Artemia sp. twice<br />

daily until they were used in testing.<br />

The toxicity tests followed the general guidance<br />

of the U.S. Environmental Protection Agency. All<br />

tests were conducted in 30-ml plastic beakers<br />

containing 10 ml test solution and five organisms<br />

per chamber. Tests were conducted under a 16-h:8-h<br />

light-dark photoperiod at 25 degrees C.<br />

Dilution/control water for all tests was<br />

moderately hard reconstituted water (MHRW).<br />

Exposure period was 96 hours, with daily<br />

observations of mortality. The criteria for death<br />

were no visible movement and no response to<br />

prodding. 100 µl of concentrated brine shrimp<br />

nauplii was added after 48 hours of exposure.<br />

Test solutions were prepared by dissolving 10,000<br />

mg/l KCl salt in MHRW, and diluting with MHRW to a<br />

series of 5 test concentrations spaced on 0.5<br />

dilution factor. As testing proceeded, test<br />

concentrations were spaced much more closely to<br />

better define responses near the effect threshold.<br />

All ion concentrations measured in stock solutions<br />

were compared to nominal values. If measured<br />

concentration differed from the nominal value by<br />

more than 20 %, the actual measured concentrations<br />

were substituted for the nominal concentrations.<br />

Background KCl content in the dilution water MHRW<br />

were added to the calculated contributions from<br />

the stock solutions.<br />

Dissolved oxygen (DO) and pH were measured in<br />

selected test solutions during actual toxicity<br />

testing: Measured DO concentrations were always ><br />

<strong>40</strong> % saturation; measured pH was between 7.5-9.0.<br />

3 replicate tests were conducted, and average LC50<br />

values were calculated as the arithmetic mean of<br />

the values; SD = 15, range 1.4-62.<br />

46<br />

UNEP PUBLICATIONS

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