| Preface |
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xv | |
| Acknowledgments |
|
xvii | |
| Editors |
|
xix | |
| Contributors |
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xxi | |
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Freshwater Bivalve Ecotoxicology |
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1 | (18) |
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Scope of Freshwater Bivalve Ecotoxicology |
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1 | (6) |
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Need for a Freshwater Bivalve Ecotoxicology Book |
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7 | (3) |
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Importance of Research on Freshwater Bivalves |
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10 | (1) |
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Roots of Bivalve Ecotoxicology |
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10 | (1) |
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A Need for Fresh Paradigms |
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11 | (3) |
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Freshwater Bivalves as Ideal Biomonitors |
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11 | (1) |
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Freshwater Bivalves as the Most Sensitive Species |
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12 | (1) |
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Biomarkers as Surrogates for Traditional Response Measures |
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13 | (1) |
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Unionids as Drivers of Bivalve Research |
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13 | (1) |
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14 | (5) |
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A Review of the Use of Unionid Mussels as Biological Indicators of Ecosystem Health |
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19 | (32) |
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19 | (1) |
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Review of Unionid Mussel Biomonitoring Literature |
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20 | (12) |
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Monitoring of Mussel Populations |
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20 | (1) |
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20 | (3) |
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Structural/Functional Indices |
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23 | (2) |
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25 | (4) |
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Laboratory Testing of Freshwater Mussels |
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29 | (3) |
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Effectiveness of Mussel Biomonitoring |
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32 | (5) |
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Mussels as Sentinels of Environmental Perturbations |
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32 | (3) |
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Mussels as Indicators of Ecological Integrity |
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35 | (2) |
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37 | (14) |
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A Brief Look at Freshwater Mussel (Unionacea) Biology |
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51 | (14) |
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51 | (1) |
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52 | (1) |
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53 | (6) |
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56 | (2) |
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58 | (1) |
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59 | (1) |
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59 | (6) |
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Propagation and Culture of Freshwater Mussels |
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65 | (30) |
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65 | (1) |
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Bivalve Life History: Understanding Early Life Stage Limitations |
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66 | (1) |
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The Need for Artificial Propagation |
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66 | (13) |
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Fish Host Techniques (in Vivo) |
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67 | (2) |
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Dependence on Fish Hosts---An Obligate Trait? |
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69 | (2) |
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Independence from Fish Hosts |
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71 | (1) |
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Artificial Media Culture (in Vitro) |
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71 | (1) |
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71 | (1) |
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72 | (1) |
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Modification of the Media |
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72 | (3) |
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Success of the in Vitro Cultured Juveniles |
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75 | (3) |
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Shipping Mussels and Glochidia |
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78 | (1) |
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79 | (1) |
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Physiological Transformation---Phases and Comparative Sensitivities of Development |
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79 | (4) |
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Fitness Beyond the ``Drop Zone'' |
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81 | (1) |
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Juvenile Culture: In-River Holding |
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82 | (1) |
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Juvenile Culture: Hatchery Conditions |
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82 | (1) |
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Restoring Declining Populations: Case Studies |
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83 | (4) |
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83 | (2) |
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Shoal Creek, Alabama and Tennessee |
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85 | (1) |
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85 | (1) |
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Middle Fork Little Red River, Arkansas |
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85 | (1) |
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Clinch, Powell, Holston, and Cumberland Rivers, Virginia |
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85 | (1) |
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85 | (1) |
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86 | (1) |
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86 | (1) |
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86 | (1) |
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Hiwassee River, Tennessee |
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86 | (1) |
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87 | (2) |
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Mammoth Spring NFH, Arkansas |
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87 | (1) |
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87 | (1) |
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Lost Valley SFH, Missouri |
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87 | (1) |
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Warm Springs NFH, Georgia |
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87 | (1) |
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87 | (1) |
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88 | (1) |
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White Sulphur Springs NFH, West Virginia |
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88 | (1) |
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88 | (1) |
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88 | (1) |
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88 | (1) |
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88 | (1) |
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Critical Uses of Early---Lifestage Unionids for Monitoring |
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89 | (1) |
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90 | (5) |
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Laboratory Toxocity Testing with Freshwater Mussels |
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95 | (40) |
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95 | (1) |
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Aquatic Toxicity Testing with Glochidia, Juvenile, and Adult Life Stages of Freshwater Mussels |
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95 | (15) |
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Methods for Conducting Acute Water-Only Toxicity Tests with Glochidia of Freshwater Mussels |
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95 | (1) |
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95 | (4) |
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Issues Regarding Use of Methods |
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99 | (5) |
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Methods for Conducting Water-Only Toxicity Tests with Juvenile Freshwater Mussels |
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104 | (1) |
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104 | (5) |
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Issues Regarding the Use of Methods |
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109 | (1) |
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Methods for Conducting Water-Only Toxicity Tests with Adult Freshwater Mussels |
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110 | (3) |
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110 | (1) |
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Issues Regarding the Use of the Methods |
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110 | (3) |
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Methods for Conducting Sediment Toxicity Tests with Freshwater Mussels |
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113 | (4) |
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113 | (3) |
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Issues Regarding Use of Methods |
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116 | (1) |
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Methods for Conducting Host Fish Exposure Toxicity Tests with Freshwater Mussels |
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117 | (2) |
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117 | (1) |
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Issues Regarding the Use of Methods |
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118 | (1) |
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Would Glochidia, While Still in Marsupium of the Adult Female Mussel, Be Exposed to Waterborne Contaminants? |
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118 | (1) |
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Methods for Conducting Toxicity Tests Using Corbicula fluminea as Surrogate Species |
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119 | (9) |
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119 | (1) |
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119 | (4) |
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Sediment Toxicity Testing |
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123 | (1) |
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Overview of Conditions Used to Conduct Toxicity Tests with Corbicula |
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123 | (3) |
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Issues Regarding the Use of the Methods |
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126 | (2) |
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Conclusions and Recommendations |
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128 | (1) |
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129 | (6) |
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In Situ Toxicity Testing of Unionids |
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135 | (16) |
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135 | (1) |
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Benefits of in Situ Testing |
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136 | (1) |
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Limitations of in Situ Testing |
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137 | (1) |
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137 | (1) |
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In Situ Testing with Freshwater Mussels |
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138 | (6) |
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Adult Unionid Mussel in Situ Testing |
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139 | (2) |
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Juvenile Unionid in Situ Testing |
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141 | (1) |
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141 | (1) |
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142 | (2) |
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144 | (1) |
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In Situ Testing with Nonunionid Bivalves |
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144 | (2) |
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145 | (1) |
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146 | (1) |
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146 | (1) |
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147 | (4) |
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Unionid Mussel Sensitivity to Environmental Contaminants |
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151 | (18) |
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151 | (1) |
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152 | (6) |
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152 | (5) |
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Sublethal Toxicity of Metals |
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157 | (1) |
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Organic Chemical Toxicity |
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158 | (4) |
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Acute Toxicity of Organic Contaminants |
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158 | (2) |
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Sublethal Effects of Organic Contaminants |
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160 | (2) |
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162 | (1) |
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162 | (1) |
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163 | (6) |
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Toxicokinetics of Environmental Contaminants in Freshwater Bivalves |
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169 | (46) |
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169 | (6) |
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170 | (1) |
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170 | (3) |
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173 | (1) |
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Metabolism and Biotransformation |
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174 | (1) |
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Bioavailability and Biotic Ligand Models |
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174 | (1) |
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Hydrophobic Organic Contaminants |
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175 | (19) |
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175 | (10) |
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185 | (2) |
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187 | (5) |
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Attainment of Steady-State |
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192 | (1) |
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Bioaccumulation and Bioavailability |
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192 | (1) |
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Implications and Potential for HOC Toxicity |
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193 | (1) |
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194 | (1) |
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194 | (1) |
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Toxic, Nonessential Metals |
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195 | (10) |
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195 | (1) |
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195 | (4) |
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Steady-State and Bioconcentration |
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199 | (1) |
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200 | (1) |
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200 | (1) |
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200 | (1) |
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201 | (1) |
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201 | (1) |
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201 | (1) |
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202 | (1) |
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202 | (1) |
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202 | (1) |
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202 | (1) |
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202 | (1) |
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203 | (1) |
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203 | (1) |
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203 | (1) |
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Metal Mixtures and Effects on Toxicokinetics |
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204 | (1) |
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204 | (1) |
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205 | (1) |
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Zinc, Calcium, Copper: Environmental Interactions |
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205 | (1) |
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205 | (1) |
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Metal Detoxification Mechanisms |
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206 | (1) |
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Implications and Potential for Metal Toxicity |
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206 | (1) |
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207 | (8) |
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Linking Bioaccumulation and Biological Effects to Chemicals in Water and Sediment: A Conceptual Framework for Freshwater Bivalve Ecotoxicology |
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215 | (42) |
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215 | (3) |
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215 | (1) |
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216 | (1) |
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Need for a Focused Conceptual Framework |
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217 | (1) |
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218 | (3) |
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218 | (2) |
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220 | (1) |
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Developing Tissue Residue Guidelines---Data Application |
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220 | (1) |
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221 | (6) |
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CBRs for Freshwater Bivalves |
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223 | (1) |
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Copper CBRs for Marine Bivalves |
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223 | (1) |
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Using Caged Bivalves to Establish Tissue Residue Effects Relationships |
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223 | (2) |
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Changes in the Relationships among Exposure, Dose, and Response |
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225 | (2) |
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227 | (6) |
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Space and Time, Site-Specific Conditions, Natural Factors |
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231 | (1) |
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232 | (1) |
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233 | (4) |
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Bivalves as Indicators of Exposure |
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234 | (1) |
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Bivalves as Indicators of Effects |
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234 | (2) |
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Biomarkers as Indicators of Exposure and Effects |
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236 | (1) |
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Refining, Integrating, and Harmonizing the Models |
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237 | (4) |
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Ecological Risk Assessment as an Umbrella Model |
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237 | (1) |
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The Exposure--Dose--Response Model |
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238 | (1) |
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Links between Tissue Residues and Effects |
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239 | (1) |
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Asking the Right Questions |
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240 | (1) |
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Examining Available Exposure--Dose--Response Data through a Different Lens |
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241 | (3) |
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Using Synoptic Data for Interpreting Results |
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241 | (1) |
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242 | (1) |
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Environmental Significance |
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243 | (1) |
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The Importance of Mechanistic Studies and Results from Different Species |
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244 | (4) |
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Dietary and Waterborne Metal Exposure in Elliptio and Mytilus |
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244 | (1) |
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Comparison of Effects on Elliptio, Musculium, and Mytilus |
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244 | (1) |
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Comparison of Sub-Cellular Partitioning in Pyganodon and Perca |
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245 | (1) |
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Integration of Unionids into a Comprehensive Monitoring Strategy |
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246 | (1) |
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Integrating Bivalve Ecotoxicology, Statistics, and Caging Studies |
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247 | (1) |
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248 | (1) |
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249 | (1) |
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Recommendations for Future Research |
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250 | (1) |
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250 | (7) |
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Biomarker Responses of Unionid Mussels to Environmental Contaminants |
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257 | (28) |
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257 | (2) |
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259 | (1) |
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Biotransformation Enzymes |
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260 | (3) |
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263 | (2) |
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265 | (2) |
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267 | (1) |
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267 | (1) |
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Reproductive and Endocrine |
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267 | (1) |
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268 | (1) |
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269 | (1) |
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Physiological and Morphological |
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270 | (8) |
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270 | (1) |
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Osmotic and Ion Regulation |
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270 | (1) |
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271 | (1) |
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271 | (2) |
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273 | (2) |
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275 | (1) |
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276 | (2) |
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Summary and Recommendations |
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278 | (2) |
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280 | (5) |
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Case Study: Comparison of Asian Clam (Corbicula fluminea) in Situ Testing to Several Nontarget Test Organism Responses to Biocidal Dosing at a Nuclear Power Plant |
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285 | (26) |
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285 | (1) |
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286 | (4) |
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286 | (1) |
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286 | (1) |
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Laboratory Toxicity Testing with Standard Test Organisms |
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287 | (1) |
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Experimental Stream Experiments |
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287 | (1) |
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288 | (1) |
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Benthic Macroinvertebrate Monitoring |
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289 | (1) |
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289 | (1) |
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290 | (11) |
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Effluent Chronic Toxicity |
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290 | (1) |
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Chironomus Sediment Toxicity |
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290 | (1) |
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Chironomus Testing in Experimental Streams |
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291 | (1) |
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Laboratory Experimental Stream Toxicity with Snails, Mayflies, Fish, and Clams |
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292 | (1) |
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293 | (1) |
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Benthic Macroinvertebrate Monitoring |
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294 | (1) |
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295 | (2) |
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In Situ 162-Day Asian Clam Test in 1992 |
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297 | (3) |
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Sampling/Toxicity Testing Efficiency |
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300 | (1) |
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301 | (4) |
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Bivalves as Indicator Species |
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302 | (3) |
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305 | (1) |
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305 | (6) |
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Case Study: Discrimination of Factors Affecting Unionid Mussel Distribution in the Clinch River, Virginia, U.S.A |
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311 | (24) |
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311 | (1) |
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312 | (4) |
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312 | (2) |
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314 | (1) |
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314 | (1) |
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315 | (1) |
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315 | (1) |
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315 | (1) |
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316 | (1) |
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316 | (6) |
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316 | (1) |
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317 | (1) |
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317 | (3) |
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320 | (1) |
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320 | (2) |
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322 | (1) |
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322 | (8) |
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330 | (1) |
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331 | (4) |
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Case Study: Impact of Partially Treated Mine Water on an Ohio River (U.S.A.) Mussel Bed---Use of Multiple Lines of Evidence in Impact Analysis |
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335 | (16) |
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335 | (1) |
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336 | (4) |
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336 | (1) |
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337 | (1) |
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338 | (1) |
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338 | (1) |
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339 | (1) |
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340 | (1) |
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340 | (5) |
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340 | (1) |
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341 | (1) |
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341 | (3) |
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344 | (1) |
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345 | (3) |
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348 | (1) |
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348 | (3) |
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Case Study: Sensitivity of Mussel Glochidia and Regulatory Test Organisms to Mercury and a Reference Toxicant |
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351 | (18) |
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351 | (3) |
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353 | (1) |
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354 | (1) |
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354 | (1) |
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Preparation of Mercury Test Solutions |
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354 | (1) |
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354 | (1) |
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355 | (1) |
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Water Chemistry and Mercury Analysis |
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355 | (1) |
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355 | (1) |
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355 | (6) |
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355 | (1) |
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356 | (1) |
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356 | (5) |
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Reference Toxicant Results |
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361 | (1) |
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Standard Regulatory Test Organisms |
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361 | (1) |
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Water Chemistry and Mercury Concentrations |
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361 | (1) |
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361 | (4) |
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361 | (3) |
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Sodium Chloride Glochidia Reference Test |
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364 | (1) |
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365 | (1) |
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365 | (4) |
| Index |
|
369 | |