Freshwater Bivalve Ecotoxoicology - Chapter 12 pdf

... 4 Cu-diss. m g/L 51111 3121 1 1 ! 11 Total m g/L 15 14 725144823231515142229 Mn-diss. m g/L ! 10 25 ! 10 10 ! 10 ! 10 10 ! 10 10 ! 10 12 12 124 0 Total m g/L 128 0 452 310 1120 768 727 760 773 515 ... 0.634 a Bend-to-bend ratio K 0.633 a K 0.481 K 0.496 STPs K 0.663 b K 0.484 K 0.499 a Significantat P ! .05. b Significant at P ! .01. Freshwater BivalveEcotoxicology322 4284X CHAPTER 12 1...

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... 1994. Metcalfe-Smith, J. L. and Green, R. H., Aging studies on three species of freshwater mussels from ametal- polluted watershed in Nova Scotia, Canada, Can. J. Zool.,70, 128 4 129 1, 1992. Metcalfe-Smith, ... Juvenile freshwater mussel (Bivalvia: Unionidae) responses to acute toxicity testing with copper, Environ. Toxicol. Chem. ,12, 879–883, 1993. Freshwater BivalveEcotoxicology42...

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... the state-of-the-art of freshwater bivalveecotoxicologybysome of the leading scientistsinthe field. The intent fromthe outset,among the authorscollaborating on this bookaboutfreshwater bivalveecotoxicology, ... 119 SedimentToxicity Testing 123 Overview of Conditions Used to Conduct Toxicity Tests with Corbicula 123 Issues Regarding the Use of the Methods 126 Conclusions and Recommendat...

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... Strayer1981;Holland-Bartels 1990).Itappears that Juvenile Growth Sperm Glochidia FIGURE 3.1 Atypical freshwater mussel life cycle. Freshwater BivalveEcotoxicology52 4284X CHAPTER 3—17/10/2006—09:42—JEBA—XML ... them. Freshwater BivalveEcotoxicology54 4284X CHAPTER 3—17/10/2006—09:42—JEBA—XML MODEL C–pp. 51–64 © 2007 by the Society of Environmental Toxicology and Chemistry (SETAC) stre...

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... algaetodetermine their response to 0 10 20 30 40 50 60 70 80 90 Control (C) New-lowNew-med. New-high Combo-lowCombo-med. Combo-high Glochidial Treatment (day6inglochidial culture) %Transformation %Alive %Dead FIGURE ... several weeks have been reported to range in length from 700 to 120 0 m m (a 7-to -1 2- fold increaseinsize from the newly-transformed juvenile) at the time of their releasei...

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... 16L:8D 12L:12D NR 16L:8D 16L:8D 16L:8D 8Test chamber 100-mL beaker 250-mL or 30 0- ml beaker 400-mL beakerBasket of mesh netting in 4-L chamber 1 2- well plate 6-well plate 1 2- well plate 1 2- well ... 24 D12L:12D or 16L:8D 16L:8D NR NR NR 16L:8D 24D 24D 16L:8D 12L:12D 16L:8D 16L:8D 16L:8D 8Test chamber 125 -mL beaker 1 2- well plate Covered 250-mL crystallizing dish Petri dish Petri...

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... that was cut awayand fitted with 105 m mnylon screening to create aflow-through holding chamber (Figure6.2). Eight 1-to-2-week- old V. iris were placed in each tube that was then fitted with acotton ... for long-term, in-situ tests with freshwater and marine bivalves, In Proceedings, 29th Annual Aquatic Toxicity Workshop,October 20–23, Fairmount Chateau Whistler, Whistler, BC, 2002. Sasson-Bri...

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... LC50s Mala- thion ( m g/L) Pyrene (mg/L) Anthr- acene (mg/L) PCP ( m g/L) Toxa- phene ( m g/L) Chlor- dane ( m g/L) Aqua- thol ( m g/L) Hydr- othol ( m g/L) Bayth- roid (Mg/L) 2,4-D (Mg/L) Atra- zine ( ... December,1999b,EPA 822-R-9 9-0 14. U.S. Environmental Protection Agency, National Recommended Water Quality Criteria,Office of Water, Office of Science and Technology, Washington, DC, 2002....

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... (1996) M. edulis Water and algae PAH, P0 20-day exposure, 14-day elimination Bjork and Gilek (1996) C. virginica Field PAH, PCB 2 8- to 50-day uptake, 50-day elimination Sericano, Wade, and Brooks ... 14 5-day uptake, 32-day elimination Gewurtz et al. (2002) E. complanata Water only and sediment PAH, 34–48 20-day exposure, 20-day elimination Thorsen(2003) Marine Oysters No. 2Fuel oil 60-da...

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... Effects-based, (b) EcoRisk-based, and (c) Harmonization of guidelines-based approaches to show the relative importance in the use of bioaccumulation. Freshwater BivalveEcotoxicology240 4284X CHAPTER ... Report No.: ISBN 0-7 77 8-0 22 8-7 , 1992. Richman, L. A., Niagara River Mussel Biomonitoring Program, 1995, Ontario: Queen’s Printer for Ontario, November 1997, Report No.: ISBN 0-7...

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