Acute waterborne nickel toxicity in the rainbow trout ( Oncorhynchus mykiss) occurs by a respiratory rather than ionoregulatory mechanism

The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout ( Oncorhynchus mykiss) in moderately hard (∼140 mg l −1 as CaCO 3) Lake Ontario water, where the 96-h LC 50 for juvenile trout (1.5–3.5 g) was 15.3 mg (12.7–19.0, 95% C.L.) dissolved Ni l −1. No marked im...

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Published inAquatic toxicology Vol. 63; no. 1; pp. 65 - 82
Main Authors Pane, E.F., Richards, J.G., Wood, C.M.
Format Journal Article
LanguageEnglish
Published Amsterdam Elsevier B.V 17.03.2003
Elsevier Science
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Abstract The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout ( Oncorhynchus mykiss) in moderately hard (∼140 mg l −1 as CaCO 3) Lake Ontario water, where the 96-h LC 50 for juvenile trout (1.5–3.5 g) was 15.3 mg (12.7–19.0, 95% C.L.) dissolved Ni l −1. No marked impact of Ni exposure on average unidirectional or net fluxes of Na +, Cl −, or Ca 2+ was observed in juvenile trout exposed for 48–60 h to 15.6 mg Ni l −1 as NiSO 4. Furthermore, when adult rainbow trout (200–340 g) were fitted with indwelling dorsal aortic catheters and exposed for 117 h to 11.6 mg Ni l −1 as NiSO 4, plasma ions (Na +, Cl −, Ca 2+, and Mg 2+) were all well conserved. However, mean arterial oxygen tension dropped gradually to ∼35% of control values. This drop in P aO 2 was accompanied by an acidosis primarily of respiratory origin. P aCO 2 rose to more than double control values with a concomitant drop in arterial pH of 0.15 units. Acute respiratory toxicity was further evidenced by a significant increase in hematocrit (Ht), and plasma lactate, and a significant decrease in spleen hemoglobin (Hb). Following 117 h of exposure to 11.6 mg Ni l −1, the gill, intestine, plasma, kidney, stomach, and heart accumulated Ni significantly, with increases of 60, 34, 28, 11, 8, and 3-fold, respectively. Brain, white muscle, liver, and bile did not significantly accumulate Ni. Plasma Ni exhibited a remarkable linear increase with time to levels approximately 30-fold higher than controls. We conclude that in contrast to most other metals, Ni is primarily a respiratory, rather than an ionoregulatory, toxicant at exposure levels close to the 96-h LC 50. The implications of a waterborne metal as an acute respiratory toxicant (as opposed to ionoregulatory toxicants such as Cu, Ag, Cd, or Zn) with respect to toxicity modeling are discussed.
AbstractList Juvenile rainbow trout were exposed to water from Lake Ontario containing various concentrations of dissolved nickel to determine the 96-hour LC super(50), which was calculated at 15.3 mg/l. Exposure of juveniles for up to 60 hours in water containing 15.6 mg Ni/l did not adversely affect sodium, chloride, or calcium ion flux. Aortic catheterization of adult fish prior to exposure to 11.6 mg Ni for 117 h showed conservation of plasma ions, but a gradual decline in oxygen tension in the arteries, and increasing respiratory acidosis that was confirmed by elevations in plasma lactate levels and hematocrit and a reduction in hemoglobin levels in the spleen. Significant bioaccumulation of Ni was demonstrated in gill, plasma, intestine, heart, stomach, and kidney, without any such increases in Ni content of brain, liver, bile, or muscle. Bioaccumulation increased linearly with duration of exposure.
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard ( approximately 140 mg l(-1) as CaCO(3)) Lake Ontario water, where the 96-h LC(50) for juvenile trout (1.5-3.5 g) was 15.3 mg (12.7-19.0, 95% C.L.) dissolved Ni l(-1). No marked impact of Ni exposure on average unidirectional or net fluxes of Na(+), Cl(-), or Ca(2+) was observed in juvenile trout exposed for 48-60 h to 15.6 mg Ni l(-1) as NiSO(4). Furthermore, when adult rainbow trout (200-340 g) were fitted with indwelling dorsal aortic catheters and exposed for 117 h to 11.6 mg Ni l(-1) as NiSO(4), plasma ions (Na(+), Cl(-), Ca(2+), and Mg(2+)) were all well conserved. However, mean arterial oxygen tension dropped gradually to approximately 35% of control values. This drop in P(aO(2)) was accompanied by an acidosis primarily of respiratory origin. P(aCO(2)) rose to more than double control values with a concomitant drop in arterial pH of 0.15 units. Acute respiratory toxicity was further evidenced by a significant increase in hematocrit (Ht), and plasma lactate, and a significant decrease in spleen hemoglobin (Hb). Following 117 h of exposure to 11.6 mg Ni l(-1), the gill, intestine, plasma, kidney, stomach, and heart accumulated Ni significantly, with increases of 60, 34, 28, 11, 8, and 3-fold, respectively. Brain, white muscle, liver, and bile did not significantly accumulate Ni. Plasma Ni exhibited a remarkable linear increase with time to levels approximately 30-fold higher than controls. We conclude that in contrast to most other metals, Ni is primarily a respiratory, rather than an ionoregulatory, toxicant at exposure levels close to the 96-h LC(50). The implications of a waterborne metal as an acute respiratory toxicant (as opposed to ionoregulatory toxicants such as Cu, Ag, Cd, or Zn) with respect to toxicity modeling are discussed.
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard ( similar to 140 mg l super(-1) as CaCO3) Lake Ontario water, where the 96-h LC50 for juvenile trout (1.5-3.5 g) was 15.3 mg (12.7-19.0, 95% C.L.) dissolved Ni l super(-1). No marked impact of Ni exposure on average unidirectional or net fluxes of Na super(+), Cl super(-), or Ca super(2+) was observed in juvenile trout exposed for 48-60 h to 15.6 mg Ni l super(-1) as NiSO4. Furthermore, when adult rainbow trout (200-340 g) were fitted with indwelling dorsal aortic catheters and exposed for 117 h to 11.6 mg Ni l super(-1) as NiSO4, plasma ions (Na super(+), Cl super(-), Ca super(2+), and Mg super(2+)) were all well conserved. However, mean arterial oxygen tension dropped gradually to similar to 35% of control values. This drop in PaO2 was accompanied by an acidosis primarily of respiratory origin. PaCO2 rose to more than double control values with a concomitant drop in arterial pH of 0.15 units. Acute respiratory toxicity was further evidenced by a significant increase in hematocrit (Ht), and plasma lactate, and a significant decrease in spleen hemoglobin (Hb). Following 117 h of exposure to 11.6 mg Ni l super(-1), the gill, intestine, plasma, kidney, stomach, and heart accumulated Ni significantly, with increases of 60, 34, 28, 11, 8, and 3-fold, respectively. Brain, white muscle, liver, and bile did not significantly accumulate Ni. Plasma Ni exhibited a remarkable linear increase with time to levels approximately 30-fold higher than controls. We conclude that in contrast to most other metals, Ni is primarily a respiratory, rather than an ionoregulatory, toxicant at exposure levels close to the 96-h LC50. The implications of a waterborne metal as an acute respiratory toxicant (as opposed to ionoregulatory toxicants such as Cu, Ag, Cd, or Zn) with respect to toxicity modeling are discussed.
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard (~140 mg l super(-1) as CaCO sub(3)) Lake Ontario water, where the 96-h LC sub(50) for juvenile trout (1.5-3.5 g) was 15.3 mg (12.7-19.0, 95% C.L.) dissolved Ni l super(-1). No marked impact of Ni exposure on average unidirectional or net fluxes of Na super(+), Cl super(-), or Ca super(2+) was observed in juvenile trout exposed for 48-60 h to 15.6 mg Ni l super(-1) as NiSO sub(4). Furthermore, when adult rainbow trout (200-340 g) were fitted with indwelling dorsal aortic catheters and exposed for 117 h to 11.6 mg Ni l super(-1) as NiSO sub(4), plasma ions (Na super(+), Cl super(-), Ca super(2+), and Mg super(2+)) were all well conserved. However, mean arterial oxygen tension dropped gradually to ~35% of control values. This drop in PaO sub(2) was accompanied by an acidosis primarily of respiratory origin. PaCO sub(2) rose to more than double control values with a concomitant drop in arterial pH of 0.15 units. Acute respiratory toxicity was further evidenced by a significant increase in hematocrit (Ht), and plasma lactate, and a significant decrease in spleen hemoglobin (Hb). Following 117 h of exposure to 11.6 mg Ni l super(-1), the gill, intestine, plasma, kidney, stomach, and heart accumulated Ni significantly, with increases of 60, 34, 28, 11, 8, and 3-fold, respectively. Brain, white muscle, liver, and bile did not significantly accumulate Ni. Plasma Ni exhibited a remarkable linear increase with time to levels approximately 30-fold higher than controls. We conclude that in contrast to most other metals, Ni is primarily a respiratory, rather than an ionoregulatory, toxicant at exposure levels close to the 96-h LC sub(50). The implications of a waterborne metal as an acute respiratory toxicant (as opposed to ionoregulatory toxicants such as Cu, Ag, Cd, or Zn) with respect to toxicity modeling are discussed.
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout ( Oncorhynchus mykiss) in moderately hard (∼140 mg l −1 as CaCO 3) Lake Ontario water, where the 96-h LC 50 for juvenile trout (1.5–3.5 g) was 15.3 mg (12.7–19.0, 95% C.L.) dissolved Ni l −1. No marked impact of Ni exposure on average unidirectional or net fluxes of Na +, Cl −, or Ca 2+ was observed in juvenile trout exposed for 48–60 h to 15.6 mg Ni l −1 as NiSO 4. Furthermore, when adult rainbow trout (200–340 g) were fitted with indwelling dorsal aortic catheters and exposed for 117 h to 11.6 mg Ni l −1 as NiSO 4, plasma ions (Na +, Cl −, Ca 2+, and Mg 2+) were all well conserved. However, mean arterial oxygen tension dropped gradually to ∼35% of control values. This drop in P aO 2 was accompanied by an acidosis primarily of respiratory origin. P aCO 2 rose to more than double control values with a concomitant drop in arterial pH of 0.15 units. Acute respiratory toxicity was further evidenced by a significant increase in hematocrit (Ht), and plasma lactate, and a significant decrease in spleen hemoglobin (Hb). Following 117 h of exposure to 11.6 mg Ni l −1, the gill, intestine, plasma, kidney, stomach, and heart accumulated Ni significantly, with increases of 60, 34, 28, 11, 8, and 3-fold, respectively. Brain, white muscle, liver, and bile did not significantly accumulate Ni. Plasma Ni exhibited a remarkable linear increase with time to levels approximately 30-fold higher than controls. We conclude that in contrast to most other metals, Ni is primarily a respiratory, rather than an ionoregulatory, toxicant at exposure levels close to the 96-h LC 50. The implications of a waterborne metal as an acute respiratory toxicant (as opposed to ionoregulatory toxicants such as Cu, Ag, Cd, or Zn) with respect to toxicity modeling are discussed.
Author Pane, E.F.
Richards, J.G.
Wood, C.M.
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  surname: Wood
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Issue 1
Keywords Respiratory toxicity
Nickel
Ionoregulation
Rainbow trout
Waterborne
Salmonidae
Ionic regulation
Toxicity
Exposure
Oncorhynchus mykiss
Heavy metal
Freshwater environment
Vertebrata
Lethal dose 50
Pisces
Water pollution
Biological accumulation
Mechanism of action
Respiration
Language English
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pascalfrancis_primary_14643464
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PublicationCentury 2000
PublicationDate 2003-03-17
PublicationDateYYYYMMDD 2003-03-17
PublicationDate_xml – month: 03
  year: 2003
  text: 2003-03-17
  day: 17
PublicationDecade 2000
PublicationPlace Amsterdam
PublicationPlace_xml – name: Amsterdam
– name: Netherlands
PublicationTitle Aquatic toxicology
PublicationTitleAlternate Aquat Toxicol
PublicationYear 2003
Publisher Elsevier B.V
Elsevier Science
Publisher_xml – name: Elsevier B.V
– name: Elsevier Science
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Snippet The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout ( Oncorhynchus mykiss) in moderately hard (∼140 mg l −1 as CaCO...
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard ( approximately 140 mg...
Juvenile rainbow trout were exposed to water from Lake Ontario containing various concentrations of dissolved nickel to determine the 96-hour LC super(50),...
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard ( similar to 140 mg l...
The acute mechanism of toxicity of waterborne nickel (Ni) was investigated in the rainbow trout (Oncorhynchus mykiss) in moderately hard (~140 mg l super(-1)...
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StartPage 65
SubjectTerms Acid-Base Equilibrium - drug effects
Agnatha. Pisces
Animal, plant and microbial ecology
Animals
Applied ecology
Biological and medical sciences
Calcium - metabolism
Chloride Channels - drug effects
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on protozoa and invertebrates
Effects of pollution and side effects of pesticides on vertebrates
Environmental Exposure - adverse effects
Freshwater
Fundamental and applied biological sciences. Psychology
Ionoregulation
Lethal Dose 50
Nickel
Nickel - toxicity
Oncorhynchus mykiss
Oncorhynchus mykiss - metabolism
Ontario
Rainbow trout
Respiratory System - drug effects
Respiratory toxicity
Sodium - metabolism
Water Pollutants, Chemical - toxicity
Waterborne
Title Acute waterborne nickel toxicity in the rainbow trout ( Oncorhynchus mykiss) occurs by a respiratory rather than ionoregulatory mechanism
URI https://dx.doi.org/10.1016/S0166-445X(02)00131-5
https://www.ncbi.nlm.nih.gov/pubmed/12615421
https://search.proquest.com/docview/14657317
https://search.proquest.com/docview/16159272
https://search.proquest.com/docview/19321772
Volume 63
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