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for a stonefly. The few data that are available indicate that the acute toxicity of
chromium (VI) decreases as hardness and pH increase. The chronic value for
rainbow and brook trout is 264.6 ug/l, and for fathead minnow it is 1.987 ug/l. In
all three fishes, a temporary reduction in growth occurred at low concentrations.
Six chronic tests with five species of daphnia have chronic values that range
from <2.5 to 40 ug/l. Growth of chinook salmon was reduced at 16 ug/l. Green
algae are quite sensitive to chromium (VI).
The ambient water quality criteria for chromium (VI) is dependent upon the
pH and hardness of the water (Federal Register 1998).
References
Eisler, R., and Hennekey, R. J. (1977). "Acute toxicities of cadmium, chromium,
mercury, nickel, and zinc to estuarine fauna," Arch. Environm. Cont. and Tox.
6, 315.
Federal Register. (1998). "USEPA national recommended water quality
criteria," 63(237), Part IV.
Integrated Risk Information System (IRIS). (1998). On-line computer database
accessed 1/99.
Olsen, K. R., and Harrel, R. C. (1973). "Effects of salinity on the toxicity of
mercury, copper, and chromium for Rangia cuneata," Contrib. Mar. Science.
17, 9.
Reish, D. J., and Carr, R. S. (1978). "The effect of heavy metals on the survival,
reproduction, development and life cycle of two species of polychaetous
annelids," Mar. Pollut. Bull. 9, 24.
U.S. Environmental Protection Agency (USEPA). (1980). "Ambient water
quality criteria for chromium," Washington, DC.
D27
Appendix D Toxicological Profiles

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