Effect of Copper (II) Sulfate Pentahydrate on Simocephalus serrulatus Reproduction Tyler Freeman, Brad Kroyer, Leena Rani. Baylor University Waco, TX 76798 Abstract This experiment determined the effects copper (II) sulfate pentahydrate on Simocephalus serrulatus reproduction. Both samples of organisms and wetland water to grow them came from the Waco Wetlands. Samples of Simocephalus serrulatus were divided among 16 containers (Three concentrations and a control). The organisms were allowed to reproduce for 20 days. Pipette sub-sampling was used to analyze the copper’s effects on reproduction. Data did not supports our original hypothesis that increased copper has a negative effect on reproduction. Results showed that the optimal copper level for reproduction was approximately 1.487 ppm. Introduction Results Copper (II) sulfate pentahydrate is used in a variety of herbicides, fungicides, and pesticides. Because of this widespread use, copper leakage into the ground water, streams, and lakes occurs frequently (Bae & Freeman, 2007). Copper in high concentrations is toxic for most organisms because of its ability to create molecules that damage proteins, lipids and DNA. Daphnia sp., has been used extensively to measure aquatic population tolerance of pollutants, so Simocephalus serrulatus, a similar organism, has been chosen to investigate the affects of copper (II) sulfate pentahydrate on their reproductive fitness (United, 2001). Figure 3: Mean population of Simocephalus serrulatus at varying concentrations of copper (II) sulfate pentahydrate after a 20 day growth period Materials and Methods Organisms were placed in 16 plastic containers filled with 1.4 L of Lake Waco Wetlands filtered water (120 micromesh), a minimal amount of algae for food, and a count of 7 Simocephalus serrulatus per container on a 12-12 day-night cycle at 22 C (Fig. 1). Using the DR-890 Colorimeter, we obtained the concentration of copper in the wetland water (Fig. 2). Control, 0.895 ppm, 1.487 ppm, and 2.975 ppm concentrations were established. Each concentration had 4 separate containers to remove outliers (Bylsma & O’Meara, 2006). To support the growing populations with a continuous supply of nutrients, we added 1.4 L more of filtered wetland water weekly along with the corresponding value of copper necessary to keep a constant concentration. After 20 days, data was obtained on the reproductive success of each cell by pipette sub-sampling. Water from each container was siphoned off leaving a more concentrated 150 mL sample. A 5 mL portion of that was pipetted in a petri dish and organisms were counted. Contrary to the initial hypothesis, populations of Simocephalus serrulatus exhibited heightened reproductive success in increased concentrations of copper (II) sulfate pentahydrate. In comparison with the inversely proportional relationship between the fitness of Daphnia sp. and increasing levels of copper concentration (Bylsma & O’Meara, 2006), data supported the notion that Simocephalus serrulatus prefer an environment with a slightly higher copper concentration than that of the Waco wetlands. Further investigation is needed to determine the tolerance of Simocephalus serrulatus in environments of even higher copper concentrations. In regard to the regulation of water-bourne heavy-metal pollutants (specifically copper), slight increases may be tolerable by aquatic populations. However, more drastic levels of heavy metal toxicity could pose a threat to populations of Simocephalus serrulatus. Further experimentation is necessary to determine if excessive copper levels, far beyond those used in this experiment, have a detrimental effect on aquatic populations; the data is insufficient in making this assessment. Acknowledgements After counting Simocephalus serrulatus in each container using pipette sub-sampling, our results showed an unexpected affinity for higher concentrations of copper (II) sulfate pentahydrate. While the control groups and groups with lower concentrations of copper demonstrated moderate reproductive success, the Simocephalus serrulatus thrived in medium-high concentrations. Figure 2 Figure 1 Discussion & Conclusion Marty L. Harvill, Ph.D.; Baylor University Biology Department; Ms. Nora Schell; Lake Waco Wetlands; Baylor University Dean of Arts and Science; URSA; Alissa Wiseman, Statistics Graduate Student; Baoqin Ding, Laboratory Assistant Literature Cited Bae, Jin-Seok. Freeman, Harold S. “Aquatic toxicity evaluation of copper-complexed direct dyes to the Daphnia magna”, Dyes and Pigments, Volume 73, Issue 1, 2007, Pages 126132 Bylsma, Amanda, O’Meara, Teri. "Copper-Washed Soil Toxicity and the Aquatic Arthropod Daphnia magna: Effects of Copper Sulfate Treatments." Web. 1 Mar. 2012. <http://www.the-macc.org/wpcontent/uploads/2009/09/2006_Effects-of-Copper-SulfateTreatments.pdf>. United States Department of Agriculture. "Copper Sulfate." Agricultural Marketing Service. Department of Agriculture, 21 Sept. 2001. 1 Mar. 2012. <http://www.ams.usda.gov>.
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