Abstract
<div class="line" id="line-5"> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> Ephemeral wetlands are characterized by temporal changes in abiotic characteristics that could ameliorate or exacerbate contaminant effects on resident species. The goal of this study was to determine the effects of temperature and naturally occurring suspended solids and organic carbon on the response of </span> <i style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> Daphnia pulex </i> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> , and the calanoid copepod, </span> <i style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> Diaptomus clavipes </i> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> , to a copper reference toxicant. Organisms were exposed to copper at 10, 20 and 30 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> ∘ </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> C in 48-h static renewal tests with a diluent of either reconstituted laboratory water or water from a wetland that had elevated levels of both suspended solids and organic carbon. 48-h LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> values were calculated for both total and free ion copper concentrations. When wetland water was used as the diluent, LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> values based on total copper concentrations were significantly greater than free ion LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> s for both species. This difference was not as great in laboratory water, indicating that binding of the metal was greater in the wetland diluent and the free ion was largely responsible for toxicity. While </span> <i style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> D. clavipes </i> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> was significantly less sensitive to the metal than </span> <i style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> D. pulex </i> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> (48-h LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> for total copper in laboratory water at 20 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> ∘ </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> C 607.4 μg/L vs. 10.7 μg/L, respectively), the copepod exhibited a much greater response to increasing temperature. When the Biotic Ligand Model was used to generate free ion concentrations, it was found that measured concentrations exceeded the predicted values at each test condition; however measured LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> values for </span> <i style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> D. pulex </i> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> were within a factor of two of the predicted LC </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 13.5px;"> 50 </span> <span style="color: rgb(51, 51, 51); background-color: rgb(252, 252, 252); font-family: Georgia, Palatino, serif; font-size: 18px;"> 's at all temperatures and in both diluents. </span></div>
| Original language | American English |
|---|---|
| Journal | Water Air and Soil Pollution |
| Volume | 171 |
| DOIs | |
| State | Published - Mar 15 2006 |
| Externally published | Yes |
Keywords
- aquatic invertebrates
- copper toxicity
- organic carbon
- suspended solids
- temperature
Disciplines
- Environmental Engineering
- Environmental Chemistry
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