Manganese is a toxic element frequently overlooked when assessing toxicity
of effluents, sediments, and pore waters. Manganese can be present at toxic
levels in anoxic solutions due to increased solubility under chemically re
ducing conditions, and it can remain at those levels for days in aerated te
st waters due to slow precipitation kinetics. Ceriodaphnia dubin and Hyalel
la azteca are freshwater organisms often used for toxicity testing and reco
mmended for assessments of effluents and pore waters. Lethal and reproducti
ve-inhibition concentrations of Mn were determined for C. dubia in acute 48
-h tests and chronic three-brood tests using animals < 24 h old and between
24 and -48 h old. Sensitivity of H. azteca to Mn was determined with 7-day
-old animals in acute 96-h tests. Tests were run at three levels of water h
ardness to assess the amelioratory effect, which was often significant. Man
ganese concentrations were measured analytically at test initiation and aft
er 96 h for calculation of toxicity and determination of Mn precipitation d
uring the tests. Minimal amounts of Mn (less than or equal to 3%) precipita
ted within 96 h. LC(50)s determined for H. azteca progressively increased f
rom 3.0 to 8.6 to 13.7 mg Mn/L in soft, moderately hard, and hard waters, r
espectively. The tolerance of C. dubia to Mn was not significantly differen
t between moderately hard and hard waters, but was significantly lower in s
oft water. Manganese sensitivity of C. dubia was not significantly differen
t between the ages tested. Acute LC50 values for C. dubia averaged 6.2, 14.
5 and 15.2 mg Mn/L and chronic IC50 values averaged 3.9, 8.5 and 11.5 mg Mn
/L for soft, moderately-hard and hard waters. respectively. Manganese toxic
ity should be considered when assessing solutions with concentrations appro
aching these levels.