The toxic effects of copper on larvae of the barnacle species Chthamalus challengeri

With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive in...

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Published inChinese journal of oceanology and limnology Vol. 33; no. 2; pp. 400 - 409
Main Author 齐磊磊 王影 沙婧婧 王悠 唐学玺
Format Journal Article
LanguageEnglish
Published Heidelberg Springer-Verlag 01.03.2015
Science Press
Springer Nature B.V
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Abstract With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC_50 ranged from 156.07 μg/L (nauplius Ⅱ) to 817.15μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius Ⅱ) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations 〉135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius Ⅱ moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower (P〈0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations _〉45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius Ⅱ could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
AbstractList With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC₅₀ranged from 156.07 μg/L (nauplius II) to 817.15 μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius II) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations ≥135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius II moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower (P <0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations ≥45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius II could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC_50 ranged from 156.07 μg/L (nauplius Ⅱ) to 817.15μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius Ⅱ) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations 〉135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius Ⅱ moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower (P〈0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations _〉45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius Ⅱ could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri . These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC 50 ranged from 156.07 μg/L (nauplius II) to 817.15 μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius II) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations ≥135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius II moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower ( P <0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations ≥45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius II could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC sub(50) ranged from 156.07 mu g/L (nauplius II) to 817.15 mu g/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 mu g/L (nauplius II) to 571.04 mu g/L (cypris). The cypris settlement rate declined significantly when copper concentrations greater than or equal to 135 mu g/L. No cypris was found in the copper concentration of 60 and 75 mu g/L treatment groups stressed for 22 d. Nauplius II moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 mu g/L treatment group was declined to 37.12%, which was significant lower (P <0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations greater than or equal to 45 mu g/L. Despite an initial significant increase at copper concentrations of 30 mu g/L, ammonia excretion rate decreased when copper concentrations greater than or equal to 60 mu g/L. These results suggested that: (1) nauplius II could not develop to the cypris when the copper concentration greater than or equal to 60 mu g/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC50 ranged from 156.07 μg/L (nauplius II) to 817.15 μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius II) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations ≥135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius II moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower (P <0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations ≥45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius II could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
Author Wang, Ying
Wang, You
Sha, Jingjing
Tang, Xuexi
Qi, Leilei
AuthorAffiliation Department of Ecology, College of Marine Life Sciences, Oeean University of China, Qingdao 266003, China
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DocumentTitleAlternate The toxic effects of copper on larvae of the barnacle species Chthamalus challengeri
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Issue 2
Keywords copper
larval stage
sensitivity
pollution monitoring
Language English
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Notes copper; Chthamalus challengeri; larval stage; sensitivity; pollution monitoring
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to investigate the effects of copper on larvae of the barnacle Chthamalus challengeri. These experiments attempted to identify a more sensitive index to monitor copper pollution in marine environments. The 24 h LC_50 ranged from 156.07 μg/L (nauplius Ⅱ) to 817.15μg/L (cypris) and the no observed effect concentration (NOEC) ranged from 81.75 μg/L (nauplius Ⅱ) to 571.04 μg/L (cypris). The cypris settlement rate declined significantly when copper concentrations 〉135 μg/L. No cypris was found in the copper concentration of 60 and 75 μg/L treatment groups stressed for 22 d. Nauplius Ⅱ moulting was not affected by exposure to copper for 24 h; however, when extended to 48 h, the percent moulted in 75 μg/L treatment group was declined to 37.12%, which was significant lower (P〈0.05) than that in the control group. The phototaxis of nauplius II decreased significantly when copper concentrations _〉45 μg/L. Despite an initial significant increase at copper concentrations of 30 μg/L, ammonia excretion rate decreased when copper concentrations ≥60 μg/L. These results suggested that: (1) nauplius Ⅱ could not develop to the cypris when the copper concentration ≥60 μg/L; (2) cypris settlement is more susceptible to copper than cypris mortality rate; (3) nauplius II is the most sensitive larval stage; (4) nauplius II ammonia excretion rate is the most sensitive index to copper and might be as the indicator for copper pollution monitoring.
QI Leilei , WANG Ying , SHA Jingjing , WANG You, TANG Xuexi (1 Department of Ecology, College of Marine Life Sciences, Ocean University of China, Qingdao 266003, China)
37-1150/P
http://dx.doi.org/10.1007/s00343-015-4158-y
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fao_agris_US201500192469
chongqing_primary_664021746
ProviderPackageCode CITATION
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PublicationCentury 2000
PublicationDate 2015-03-01
PublicationDateYYYYMMDD 2015-03-01
PublicationDate_xml – month: 03
  year: 2015
  text: 2015-03-01
  day: 01
PublicationDecade 2010
PublicationPlace Heidelberg
PublicationPlace_xml – name: Heidelberg
– name: Dordrecht
PublicationTitle Chinese journal of oceanology and limnology
PublicationTitleAbbrev Chin. J. Ocean. Limnol
PublicationTitleAlternate Chinese Journal of Oceanology and Limnology
PublicationYear 2015
Publisher Springer-Verlag
Science Press
Springer Nature B.V
Publisher_xml – name: Springer-Verlag
– name: Science Press
– name: Springer Nature B.V
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Snippet With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to...
With the increased use of copper (Cu)-based antifouling (AF) paints, copper has become a potential threat to marine organisms. Experiments were performed to...
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SubjectTerms Abiotic stress
Ammonia
antifouling agents
Antifouling coatings
Antifouling substances
Aquatic life
Biological settlement
Biology
Chthamalus challengeri
Copper
Cypris
Earth and Environmental Science
Earth Sciences
Excretion
Larvae
Larval stage
Marine biology
Marine crustaceans
Marine environment
Marine organisms
Marine pollution
Molting
monitoring
mortality
Mortality causes
Moulting
nauplii
Oceanography
paints
Phototaxis
Pollution
Pollution index
Pollution monitoring
Toxicity
Toxicity tests
幼虫
无节幼体
毒性作用
污染监测
潜在威胁
物种
藤壶
铜浓度
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Title The toxic effects of copper on larvae of the barnacle species Chthamalus challengeri
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Volume 33
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