Bioaccumulation and toxicity of copper in outdoor freshwater microcosms
This study characterizes the effects of copper (Cu) on Florida apple snails ( Pomacea paludosa) and mosquito fish ( Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (...
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| Published in: | Ecotoxicology and environmental safety Vol. 74; no. 4; pp. 1011 - 1020 |
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| Abstract | This study characterizes the effects of copper (Cu) on Florida apple snails (
Pomacea paludosa) and mosquito fish (
Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (AGLR) in St. Lucie County and Sunrise Boys property (SRB) in Palm Beach County) and a reference site (Equus property) in St. Lucie County. The study included a 5-week aging phase, an 11 month exposure phase, and a 3 month post-treatment (exposure) phase. The aging phase was initiated by flooding agricultural soils with rainwater in 4
m
3 fiberglass microcosm tanks. Introducing juvenile apple snails (≤7
d old) and mosquito fish (2–3
cm) into the microcosm tanks initiated the exposure phase. Survival, growth, and reproduction of apple snails and fish, and Cu uptake in apple snails, fish, and periphyton were determined in this study. Water chemistry (e.g., dissolved Cu concentration, dissolved organic carbon and dissolved oxygen concentrations, pH, hardness, alkalinity, etc.) was measured daily or weekly during the study. Initial soil Cu concentrations in Equus, SRB, and AGLR microcosms were 7, 55, and 99
mg/kg dw, respectively. Dissolved Cu concentrations in Equus, SRB and AGLR microcosms at the beginning of the study were 3, 82, and 43
μg/L, respectively and decreased to low saturation levels of about ≤9
μg/L Cu after the first 3 months of the study. The decrease of dissolved Cu concentrations was likely due to the dilution of rainwater. Snail and fish mortality appeared to be higher in SRB microcosms than in Equus and AGLR microcosms. There was no significant difference in growth of the snails between treatments. Snail growth data followed the von Bertalanffy Model. The maximum shell length, shell height, and shell width of the snails calculated by the von Bertalanffy Model (
L
∞) were 2.76, 2.05, and 2.18
cm, respectively. The maximum wet weight was 9.38
g. Growth rate (
k) of the snails increased in order of shell height (0.459), shell length (0.550), and shell weight (0.598). There was no reproduction in the snails in any treatments including the reference during the exposure phase. However, Cu did not affect reproduction of fish during this period. Copper concentrations in periphyton from Equus, SRB, and AGLR microcosms ranged from 2 to 62, 31 to 371, and 13 to 478
mg/kg, respectively. Copper concentrations in fish at the beginning, days 30 and 150 of the study ranged from 3.19 to 7.53
mg/kg and were not significantly different from the different treatments. Average Cu concentrations in the soft tissue of dead snails from SRB and AGLR microcosms were 4602
mg/kg dw (ranged from 2913 to 8370
mg/kg dw) and 2824
mg/kg dw (ranged from 2118 to 3600
mg/kg dw), respectively. The Cu concentrations in the soft tissue of dead snails found in this study were higher than the tissue Cu concentrations in live aquatic organisms reported in the literature. These high Cu concentrations in edible apple snail soft tissue might pose a risk to Florida apple snail predators, including the snail kite. The post-exposure phase, with snails exposed to only water (i.e., no soils) showed depuration of copper from apple snails and reproduction in all treatments. |
|---|---|
| AbstractList | This study characterizes the effects of copper (Cu) on Florida apple snails (Pomacea paludosa) and mosquito fish (Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (AGLR) in St. Lucie County and Sunrise Boys property (SRB) in Palm Beach County) and a reference site (Equus property) in St. Lucie County. The study included a 5-week aging phase, an 11 month exposure phase, and a 3 month post-treatment (exposure) phase. The aging phase was initiated by flooding agricultural soils with rainwater in 4m3 fiberglass microcosm tanks. Introducing juvenile apple snails ( less than or equal to 7d old) and mosquito fish (2-3cm) into the microcosm tanks initiated the exposure phase. Survival, growth, and reproduction of apple snails and fish, and Cu uptake in apple snails, fish, and periphyton were determined in this study. Water chemistry (e.g., dissolved Cu concentration, dissolved organic carbon and dissolved oxygen concentrations, pH, hardness, alkalinity, etc.) was measured daily or weekly during the study. Initial soil Cu concentrations in Equus, SRB, and AGLR microcosms were 7, 55, and 99mg/kg dw, respectively. Dissolved Cu concentrations in Equus, SRB and AGLR microcosms at the beginning of the study were 3, 82, and 43 mu g/L, respectively and decreased to low saturation levels of about less than or equal to 9kg/L Cu after the first 3 months of the study. The decrease of dissolved Cu concentrations was likely due to the dilution of rainwater. Snail and fish mortality appeared to be higher in SRB microcosms than in Equus and AGLR microcosms. There was no significant difference in growth of the snails between treatments. Snail growth data followed the von Bertalanffy Model. The maximum shell length, shell height, and shell width of the snails calculated by the von Bertalanffy Model (L a] were 2.76, 2.05, and 2.18cm, respectively. The maximum wet weight was 9.38g. Growth rate (k) of the snails increased in order of shell height (0.459), shell length (0.550), and shell weight (0.598). There was no reproduction in the snails in any treatments including the reference during the exposure phase. However, Cu did not affect reproduction of fish during this period. Copper concentrations in periphyton from Equus, SRB, and AGLR microcosms ranged from 2 to 62, 31 to 371, and 13 to 478mg/kg, respectively. Copper concentrations in fish at the beginning, days 30 and 150 of the study ranged from 3.19 to 7.53mg/kg and were not significantly different from the different treatments. Average Cu concentrations in the soft tissue of dead snails from SRB and AGLR microcosms were 4602mg/kg dw (ranged from 2913 to 8370mg/kg dw) and 2824mg/kg dw (ranged from 2118 to 3600mg/kg dw), respectively. The Cu concentrations in the soft tissue of dead snails found in this study were higher than the tissue Cu concentrations in live aquatic organisms reported in the literature. These high Cu concentrations in edible apple snail soft tissue might pose a risk to Florida apple snail predators, including the snail kite. The post-exposure phase, with snails exposed to only water (i.e., no soils) showed depuration of copper from apple snails and reproduction in all treatments. This study characterizes the effects of copper (Cu) on Florida apple snails (Pomacea paludosa) and mosquito fish (Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (AGLR) in St. Lucie County and Sunrise Boys property (SRB) in Palm Beach County) and a reference site (Equus property) in St. Lucie County. The study included a 5-week aging phase, an 11 month exposure phase, and a 3 month post-treatment (exposure) phase. The aging phase was initiated by flooding agricultural soils with rainwater in 4 m(3) fiberglass microcosm tanks. Introducing juvenile apple snails (≤7 d old) and mosquito fish (2-3 cm) into the microcosm tanks initiated the exposure phase. Survival, growth, and reproduction of apple snails and fish, and Cu uptake in apple snails, fish, and periphyton were determined in this study. Water chemistry (e.g., dissolved Cu concentration, dissolved organic carbon and dissolved oxygen concentrations, pH, hardness, alkalinity, etc.) was measured daily or weekly during the study. Initial soil Cu concentrations in Equus, SRB, and AGLR microcosms were 7, 55, and 99 mg/kg dw, respectively. Dissolved Cu concentrations in Equus, SRB and AGLR microcosms at the beginning of the study were 3, 82, and 43 μg/L, respectively and decreased to low saturation levels of about ≤9 μg/L Cu after the first 3 months of the study. The decrease of dissolved Cu concentrations was likely due to the dilution of rainwater. Snail and fish mortality appeared to be higher in SRB microcosms than in Equus and AGLR microcosms. There was no significant difference in growth of the snails between treatments. Snail growth data followed the von Bertalanffy Model. The maximum shell length, shell height, and shell width of the snails calculated by the von Bertalanffy Model (L(∞)) were 2.76, 2.05, and 2.18 cm, respectively. The maximum wet weight was 9.38 g. Growth rate (k) of the snails increased in order of shell height (0.459), shell length (0.550), and shell weight (0.598). There was no reproduction in the snails in any treatments including the reference during the exposure phase. However, Cu did not affect reproduction of fish during this period. Copper concentrations in periphyton from Equus, SRB, and AGLR microcosms ranged from 2 to 62, 31 to 371, and 13 to 478 mg/kg, respectively. Copper concentrations in fish at the beginning, days 30 and 150 of the study ranged from 3.19 to 7.53 mg/kg and were not significantly different from the different treatments. Average Cu concentrations in the soft tissue of dead snails from SRB and AGLR microcosms were 4602 mg/kg dw (ranged from 2913 to 8370 mg/kg dw) and 2824 mg/kg dw (ranged from 2118 to 3600 mg/kg dw), respectively. The Cu concentrations in the soft tissue of dead snails found in this study were higher than the tissue Cu concentrations in live aquatic organisms reported in the literature. These high Cu concentrations in edible apple snail soft tissue might pose a risk to Florida apple snail predators, including the snail kite. The post-exposure phase, with snails exposed to only water (i.e., no soils) showed depuration of copper from apple snails and reproduction in all treatments. This study characterizes the effects of copper (Cu) on Florida apple snails ( Pomacea paludosa) and mosquito fish ( Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (AGLR) in St. Lucie County and Sunrise Boys property (SRB) in Palm Beach County) and a reference site (Equus property) in St. Lucie County. The study included a 5-week aging phase, an 11 month exposure phase, and a 3 month post-treatment (exposure) phase. The aging phase was initiated by flooding agricultural soils with rainwater in 4 m 3 fiberglass microcosm tanks. Introducing juvenile apple snails (≤7 d old) and mosquito fish (2–3 cm) into the microcosm tanks initiated the exposure phase. Survival, growth, and reproduction of apple snails and fish, and Cu uptake in apple snails, fish, and periphyton were determined in this study. Water chemistry (e.g., dissolved Cu concentration, dissolved organic carbon and dissolved oxygen concentrations, pH, hardness, alkalinity, etc.) was measured daily or weekly during the study. Initial soil Cu concentrations in Equus, SRB, and AGLR microcosms were 7, 55, and 99 mg/kg dw, respectively. Dissolved Cu concentrations in Equus, SRB and AGLR microcosms at the beginning of the study were 3, 82, and 43 μg/L, respectively and decreased to low saturation levels of about ≤9 μg/L Cu after the first 3 months of the study. The decrease of dissolved Cu concentrations was likely due to the dilution of rainwater. Snail and fish mortality appeared to be higher in SRB microcosms than in Equus and AGLR microcosms. There was no significant difference in growth of the snails between treatments. Snail growth data followed the von Bertalanffy Model. The maximum shell length, shell height, and shell width of the snails calculated by the von Bertalanffy Model ( L ∞) were 2.76, 2.05, and 2.18 cm, respectively. The maximum wet weight was 9.38 g. Growth rate ( k) of the snails increased in order of shell height (0.459), shell length (0.550), and shell weight (0.598). There was no reproduction in the snails in any treatments including the reference during the exposure phase. However, Cu did not affect reproduction of fish during this period. Copper concentrations in periphyton from Equus, SRB, and AGLR microcosms ranged from 2 to 62, 31 to 371, and 13 to 478 mg/kg, respectively. Copper concentrations in fish at the beginning, days 30 and 150 of the study ranged from 3.19 to 7.53 mg/kg and were not significantly different from the different treatments. Average Cu concentrations in the soft tissue of dead snails from SRB and AGLR microcosms were 4602 mg/kg dw (ranged from 2913 to 8370 mg/kg dw) and 2824 mg/kg dw (ranged from 2118 to 3600 mg/kg dw), respectively. The Cu concentrations in the soft tissue of dead snails found in this study were higher than the tissue Cu concentrations in live aquatic organisms reported in the literature. These high Cu concentrations in edible apple snail soft tissue might pose a risk to Florida apple snail predators, including the snail kite. The post-exposure phase, with snails exposed to only water (i.e., no soils) showed depuration of copper from apple snails and reproduction in all treatments. This study characterizes the effects of copper (Cu) on Florida apple snails (Pomacea paludosa) and mosquito fish (Gambusia affinis) using a replicated outdoor microcosm design. Soils used in this study were collected from two Cu-enriched citrus agricultural sites in South Florida (Agler property (AGLR) in St. Lucie County and Sunrise Boys property (SRB) in Palm Beach County) and a reference site (Equus property) in St. Lucie County. The study included a 5-week aging phase, an 11 month exposure phase, and a 3 month post-treatment (exposure) phase. The aging phase was initiated by flooding agricultural soils with rainwater in 4m³ fiberglass microcosm tanks. Introducing juvenile apple snails (≤7d old) and mosquito fish (2–3cm) into the microcosm tanks initiated the exposure phase. Survival, growth, and reproduction of apple snails and fish, and Cu uptake in apple snails, fish, and periphyton were determined in this study. Water chemistry (e.g., dissolved Cu concentration, dissolved organic carbon and dissolved oxygen concentrations, pH, hardness, alkalinity, etc.) was measured daily or weekly during the study. Initial soil Cu concentrations in Equus, SRB, and AGLR microcosms were 7, 55, and 99mg/kg dw, respectively. Dissolved Cu concentrations in Equus, SRB and AGLR microcosms at the beginning of the study were 3, 82, and 43μg/L, respectively and decreased to low saturation levels of about ≤9μg/L Cu after the first 3 months of the study. The decrease of dissolved Cu concentrations was likely due to the dilution of rainwater. Snail and fish mortality appeared to be higher in SRB microcosms than in Equus and AGLR microcosms. There was no significant difference in growth of the snails between treatments. Snail growth data followed the von Bertalanffy Model. The maximum shell length, shell height, and shell width of the snails calculated by the von Bertalanffy Model (L∞) were 2.76, 2.05, and 2.18cm, respectively. The maximum wet weight was 9.38g. Growth rate (k) of the snails increased in order of shell height (0.459), shell length (0.550), and shell weight (0.598). There was no reproduction in the snails in any treatments including the reference during the exposure phase. However, Cu did not affect reproduction of fish during this period. Copper concentrations in periphyton from Equus, SRB, and AGLR microcosms ranged from 2 to 62, 31 to 371, and 13 to 478mg/kg, respectively. Copper concentrations in fish at the beginning, days 30 and 150 of the study ranged from 3.19 to 7.53mg/kg and were not significantly different from the different treatments. Average Cu concentrations in the soft tissue of dead snails from SRB and AGLR microcosms were 4602mg/kg dw (ranged from 2913 to 8370mg/kg dw) and 2824mg/kg dw (ranged from 2118 to 3600mg/kg dw), respectively. The Cu concentrations in the soft tissue of dead snails found in this study were higher than the tissue Cu concentrations in live aquatic organisms reported in the literature. These high Cu concentrations in edible apple snail soft tissue might pose a risk to Florida apple snail predators, including the snail kite. The post-exposure phase, with snails exposed to only water (i.e., no soils) showed depuration of copper from apple snails and reproduction in all treatments. |
| Author | Hoang, Tham C. Rand, Gary M. Frakes, Robert A. Pryor, Rachel L. |
| Author_xml | – sequence: 1 givenname: Tham C. surname: Hoang fullname: Hoang, Tham C. organization: Ecotoxicology & Risk Assessment Laboratory, Southeast Environmental Research Center, Department of Earth and Environment, Florida International University, 3000 NE 151st Street, North Miami, FL 33181, USA – sequence: 2 givenname: Rachel L. surname: Pryor fullname: Pryor, Rachel L. organization: US Fish and Wildlife Service, Vero Beach, Florida, USA – sequence: 3 givenname: Gary M. surname: Rand fullname: Rand, Gary M. email: randg@fiu.edu organization: Ecotoxicology & Risk Assessment Laboratory, Southeast Environmental Research Center, Department of Earth and Environment, Florida International University, 3000 NE 151st Street, North Miami, FL 33181, USA – sequence: 4 givenname: Robert A. surname: Frakes fullname: Frakes, Robert A. organization: US Fish and Wildlife Service, Vero Beach, Florida, USA |
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| Cites_doi | 10.1007/s10646-008-0236-7 10.1016/j.ecoenv.2003.11.001 10.1006/eesa.1997.1566 10.1016/j.aquatox.2007.02.023 10.1016/S0048-9697(97)05428-4 10.1897/1551-5028(2002)021<0820:MFTAOC>2.0.CO;2 10.1007/s11270-008-9861-2 10.2136/sssaj1993.03615995005700020011x 10.1002/etc.5620190219 10.1097/00010694-195303000-00006 10.2307/1540646 10.1016/S0048-9697(96)05315-6 10.1016/0269-7491(95)00070-4 10.3923/jbs.2004.441.444 10.1002/etc.5620190220 10.1007/s00244-008-9231-5 10.1007/s00244-007-9106-1 10.1016/S0165-7836(96)00537-1 10.1016/S0307-904X(00)00053-6 10.2307/1538217 10.2136/sssaj2005.0255 10.1016/j.fishres.2006.07.002 10.1016/j.envpol.2007.09.024 10.2307/1468190 10.1111/j.1752-1688.2001.tb00968.x 10.1672/07-115.1 10.1016/S0269-7491(02)00333-0 10.1007/s10646-008-0243-8 10.1071/MR04009 10.1016/j.envsoft.2003.03.008 10.1016/S0929-1393(96)00155-2 10.2136/sssaj1995.03615995005900020031x 10.1111/j.1444-2906.2006.01219.x 10.1007/s10646-008-0233-x 10.1002/etc.5620220626 10.1016/j.aquatox.2005.11.009 10.1007/s001289900395 10.1016/0269-7491(92)90099-V |
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| Issue | 4 |
| Keywords | Pomacea paludosa Florida apple snails Copper Freshwater microcosms Ecotoxicology Toxicity Fresh water Microcosm Gastropoda Heavy metal Pollutant Environment Invertebrata Mollusca Biological accumulation |
| Language | English |
| License | CC BY 4.0 Copyright © 2011 Elsevier Inc. All rights reserved. |
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| Snippet | This study characterizes the effects of copper (Cu) on Florida apple snails (
Pomacea paludosa) and mosquito fish (
Gambusia affinis) using a replicated... This study characterizes the effects of copper (Cu) on Florida apple snails (Pomacea paludosa) and mosquito fish (Gambusia affinis) using a replicated outdoor... |
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| SubjectTerms | agricultural soils Agriculture alkalinity Animal, plant and microbial ecology Animals Apples Applied ecology Aquatic Organisms - drug effects Aquatic Organisms - growth & development bioaccumulation Biological and medical sciences boys Citrus Copper Copper - toxicity Culicidae Cyprinodontiformes - growth & development Cyprinodontiformes - metabolism Dissolution dissolved organic carbon dissolved oxygen Ecosystem Ecotoxicology, biological effects of pollution Environmental Monitoring Equus Falconiformes - metabolism fiberglass Fish Floods Florida apple snails Food Chain Fresh Water - chemistry Freshwater Freshwater microcosms Fundamental and applied biological sciences. Psychology Gambusia affinis General aspects hardness Humans hydrochemistry Invertebrates Male Mollusca mortality periphyton Pomacea paludosa predators rain Reproduction Reproduction - drug effects risk Shells Snails Snails - drug effects Snails - growth & development Soil - chemistry Soil Pollutants - toxicity Soils tanks toxicity Water Pollutants, Chemical - metabolism Water Pollutants, Chemical - toxicity |
| Title | Bioaccumulation and toxicity of copper in outdoor freshwater microcosms |
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