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Lethal and sublethal toxicity of didecyldimethylammonium chloride in early life stages of white sturgeon, Acipenser transmontanus

Identifieur interne : 000286 ( PascalFrancis/Corpus ); précédent : 000285; suivant : 000287

Lethal and sublethal toxicity of didecyldimethylammonium chloride in early life stages of white sturgeon, Acipenser transmontanus

Auteurs : SWEE JOO TEH ; Cecilia Wong ; Vesna Furtula ; Foo-Ching Teh

Source :

RBID : Pascal:03-0528356

Descripteurs français

English descriptors

Abstract

This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

pA  
A01 01  1    @0 0730-7268
A02 01      @0 ETOCDK
A03   1    @0 Environ. toxicol. chem.
A05       @2 22
A06       @2 9
A08 01  1  ENG  @1 Lethal and sublethal toxicity of didecyldimethylammonium chloride in early life stages of white sturgeon, Acipenser transmontanus
A11 01  1    @1 SWEE JOO TEH
A11 02  1    @1 WONG (Cecilia)
A11 03  1    @1 FURTULA (Vesna)
A11 04  1    @1 TEH (Foo-Ching)
A14 01      @1 University of California-Davis, Department of Anatomy, Physiology, and Cell Biology, One Shields Avenue @2 Davis, California 95616 @3 USA @Z 1 aut. @Z 4 aut.
A14 02      @1 Aquatic and Atmospheric Science Division, Environment Canada, 700-1200 West 73rd Avenue @2 Vancouver, British Colombia V6P 6H9 @3 CAN @Z 2 aut.
A14 03      @1 Pacific Environmental Science Centre, Environment Canada, 2645 Dollarton Hwy @2 North Vancouver, British Columbia V7H 1B1 @3 CAN @Z 3 aut.
A20       @1 2152-2158
A21       @1 2003
A23 01      @0 ENG
A43 01      @1 INIST @2 19956 @5 354000112718230270
A44       @0 0000 @1 © 2003 INIST-CNRS. All rights reserved.
A45       @0 17 ref.
A47 01  1    @0 03-0528356
A60       @1 P
A61       @0 A
A64 01  1    @0 Environmental toxicology and chemistry
A66 01      @0 USA
C01 01    ENG  @0 This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.
C02 01  X    @0 002A14D05H1
C03 01  X  FRE  @0 Toxicité @5 01
C03 01  X  ENG  @0 Toxicity @5 01
C03 01  X  SPA  @0 Toxicidad @5 01
C03 02  X  FRE  @0 Animal jeune @5 02
C03 02  X  ENG  @0 Young animal @5 02
C03 02  X  SPA  @0 Animal joven @5 02
C03 03  X  FRE  @0 Survie @5 03
C03 03  X  ENG  @0 Survival @5 03
C03 03  X  SPA  @0 Sobrevivencia @5 03
C03 04  X  FRE  @0 Croissance @5 04
C03 04  X  ENG  @0 Growth @5 04
C03 04  X  SPA  @0 Crecimiento @5 04
C03 05  X  FRE  @0 Cours eau @5 05
C03 05  X  ENG  @0 Stream @5 05
C03 05  X  SPA  @0 Curso agua @5 05
C03 06  X  FRE  @0 Canada @2 NG @5 06
C03 06  X  ENG  @0 Canada @2 NG @5 06
C03 06  X  SPA  @0 Canada @2 NG @5 06
C03 07  X  FRE  @0 Biocide @5 07
C03 07  X  ENG  @0 Biocide @5 07
C03 07  X  SPA  @0 Biocida @5 07
C03 08  X  FRE  @0 Fongicide @5 08
C03 08  X  ENG  @0 Fungicide @5 08
C03 08  X  SPA  @0 Fungicida @5 08
C03 09  X  FRE  @0 Organisme non cible @5 09
C03 09  X  ENG  @0 Non target organism @5 09
C03 09  X  SPA  @0 Organismo no objeto @5 09
C03 10  X  FRE  @0 Acipenser transmontanus @2 NS @5 55
C03 10  X  ENG  @0 Acipenser transmontanus @2 NS @5 55
C03 10  X  SPA  @0 Acipenser transmontanus @2 NS @5 55
C03 11  X  FRE  @0 Ammonium(didécyl diméthyl) chlorure @2 NK @4 INC @5 94
C07 01  X  FRE  @0 Amérique du Nord @2 NG
C07 01  X  ENG  @0 North America @2 NG
C07 01  X  SPA  @0 America del norte @2 NG
C07 02  X  FRE  @0 Amérique @2 NG
C07 02  X  ENG  @0 America @2 NG
C07 02  X  SPA  @0 America @2 NG
C07 03  X  FRE  @0 Pesticide
C07 03  X  ENG  @0 Pesticides
C07 03  X  SPA  @0 Plaguicida
C07 04  X  FRE  @0 Pollution eau @5 19
C07 04  X  ENG  @0 Water pollution @5 19
C07 04  X  SPA  @0 Contaminación agua @5 19
C07 05  X  FRE  @0 Milieu eau douce @5 21
C07 05  X  ENG  @0 Freshwater environment @5 21
C07 05  X  SPA  @0 Medio agua dulce @5 21
C07 06  X  FRE  @0 Pisces @2 NS
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C07 06  X  SPA  @0 Pisces @2 NS
C07 07  X  FRE  @0 Vertebrata @2 NS
C07 07  X  ENG  @0 Vertebrata @2 NS
C07 07  X  SPA  @0 Vertebrata @2 NS
C07 08  X  FRE  @0 Acipenseridae @2 NS @4 INC @5 70
N21       @1 349
N82       @1 PSI

Format Inist (serveur)

NO : PASCAL 03-0528356 INIST
ET : Lethal and sublethal toxicity of didecyldimethylammonium chloride in early life stages of white sturgeon, Acipenser transmontanus
AU : SWEE JOO TEH; WONG (Cecilia); FURTULA (Vesna); TEH (Foo-Ching)
AF : University of California-Davis, Department of Anatomy, Physiology, and Cell Biology, One Shields Avenue/Davis, California 95616/Etats-Unis (1 aut., 4 aut.); Aquatic and Atmospheric Science Division, Environment Canada, 700-1200 West 73rd Avenue/Vancouver, British Colombia V6P 6H9/Canada (2 aut.); Pacific Environmental Science Centre, Environment Canada, 2645 Dollarton Hwy/North Vancouver, British Columbia V7H 1B1/Canada (3 aut.)
DT : Publication en série; Niveau analytique
SO : Environmental toxicology and chemistry; ISSN 0730-7268; Coden ETOCDK; Etats-Unis; Da. 2003; Vol. 22; No. 9; Pp. 2152-2158; Bibl. 17 ref.
LA : Anglais
EA : This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.
CC : 002A14D05H1
FD : Toxicité; Animal jeune; Survie; Croissance; Cours eau; Canada; Biocide; Fongicide; Organisme non cible; Acipenser transmontanus; Ammonium(didécyl diméthyl) chlorure
FG : Amérique du Nord; Amérique; Pesticide; Pollution eau; Milieu eau douce; Pisces; Vertebrata; Acipenseridae
ED : Toxicity; Young animal; Survival; Growth; Stream; Canada; Biocide; Fungicide; Non target organism; Acipenser transmontanus
EG : North America; America; Pesticides; Water pollution; Freshwater environment; Pisces; Vertebrata
SD : Toxicidad; Animal joven; Sobrevivencia; Crecimiento; Curso agua; Canada; Biocida; Fungicida; Organismo no objeto; Acipenser transmontanus
LO : INIST-19956.354000112718230270
ID : 03-0528356

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Pascal:03-0528356

Le document en format XML

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<div type="abstract" xml:lang="en">This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.</div>
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<s0>This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.</s0>
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<s5>05</s5>
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<fC03 i1="05" i2="X" l="SPA">
<s0>Curso agua</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Canada</s0>
<s2>NG</s2>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Canada</s0>
<s2>NG</s2>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Canada</s0>
<s2>NG</s2>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE">
<s0>Biocide</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG">
<s0>Biocide</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA">
<s0>Biocida</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE">
<s0>Fongicide</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG">
<s0>Fungicide</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA">
<s0>Fungicida</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE">
<s0>Organisme non cible</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Non target organism</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Organismo no objeto</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>55</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE">
<s0>Ammonium(didécyl diméthyl) chlorure</s0>
<s2>NK</s2>
<s4>INC</s4>
<s5>94</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Amérique du Nord</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>North America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>America del norte</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Amérique</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA">
<s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE">
<s0>Pesticide</s0>
</fC07>
<fC07 i1="03" i2="X" l="ENG">
<s0>Pesticides</s0>
</fC07>
<fC07 i1="03" i2="X" l="SPA">
<s0>Plaguicida</s0>
</fC07>
<fC07 i1="04" i2="X" l="FRE">
<s0>Pollution eau</s0>
<s5>19</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG">
<s0>Water pollution</s0>
<s5>19</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA">
<s0>Contaminación agua</s0>
<s5>19</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE">
<s0>Milieu eau douce</s0>
<s5>21</s5>
</fC07>
<fC07 i1="05" i2="X" l="ENG">
<s0>Freshwater environment</s0>
<s5>21</s5>
</fC07>
<fC07 i1="05" i2="X" l="SPA">
<s0>Medio agua dulce</s0>
<s5>21</s5>
</fC07>
<fC07 i1="06" i2="X" l="FRE">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="ENG">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="SPA">
<s0>Pisces</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="FRE">
<s0>Acipenseridae</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21>
<s1>349</s1>
</fN21>
<fN82>
<s1>PSI</s1>
</fN82>
</pA>
</standard>
<server>
<NO>PASCAL 03-0528356 INIST</NO>
<ET>Lethal and sublethal toxicity of didecyldimethylammonium chloride in early life stages of white sturgeon, Acipenser transmontanus</ET>
<AU>SWEE JOO TEH; WONG (Cecilia); FURTULA (Vesna); TEH (Foo-Ching)</AU>
<AF>University of California-Davis, Department of Anatomy, Physiology, and Cell Biology, One Shields Avenue/Davis, California 95616/Etats-Unis (1 aut., 4 aut.); Aquatic and Atmospheric Science Division, Environment Canada, 700-1200 West 73rd Avenue/Vancouver, British Colombia V6P 6H9/Canada (2 aut.); Pacific Environmental Science Centre, Environment Canada, 2645 Dollarton Hwy/North Vancouver, British Columbia V7H 1B1/Canada (3 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Environmental toxicology and chemistry; ISSN 0730-7268; Coden ETOCDK; Etats-Unis; Da. 2003; Vol. 22; No. 9; Pp. 2152-2158; Bibl. 17 ref.</SO>
<LA>Anglais</LA>
<EA>This study was conducted to describe the acute lethality and latent toxicity of didecyldimethylammonium chloride (DDAC) on early life stages of white sturgeon (Acipenser transmontanus). Fish responses to 0, 10, 50, 100, 250, 500 μg/L concentrations of DDAC were determined using a 96-h standard static renewal method for acute toxicity testing, with three replicates per concentration. Twenty fish per replicate were tested for 3, 11, and 42-d-old larvae, and 7 fish per replicate were tested for 78-d-old juveniles. Following exposure, survival and growth were evaluated in exposed fish raised in clean water for 2 weeks. The 96-h median lethal concentration (LC50) values for DDAC were 10.0 to 50.0, 58.5, and 99.7 μg/L for 3, 11, and 42-d-old larvae and 100 to 250 μg/L for 78-d-old juveniles. Significant decreases in larval growth and survival were noted at all tested concentrations and in all sturgeon age groups. Results of this study reveal age- and concentration-dependent responses to DDAC. Among the age groups tested, the 3-d-old larvae were the most sensitive group. Results also revealed that 96-h lethality testing alone is not adequate for determining the toxicity of DDAC to white sturgeon.</EA>
<CC>002A14D05H1</CC>
<FD>Toxicité; Animal jeune; Survie; Croissance; Cours eau; Canada; Biocide; Fongicide; Organisme non cible; Acipenser transmontanus; Ammonium(didécyl diméthyl) chlorure</FD>
<FG>Amérique du Nord; Amérique; Pesticide; Pollution eau; Milieu eau douce; Pisces; Vertebrata; Acipenseridae</FG>
<ED>Toxicity; Young animal; Survival; Growth; Stream; Canada; Biocide; Fungicide; Non target organism; Acipenser transmontanus</ED>
<EG>North America; America; Pesticides; Water pollution; Freshwater environment; Pisces; Vertebrata</EG>
<SD>Toxicidad; Animal joven; Sobrevivencia; Crecimiento; Curso agua; Canada; Biocida; Fungicida; Organismo no objeto; Acipenser transmontanus</SD>
<LO>INIST-19956.354000112718230270</LO>
<ID>03-0528356</ID>
</server>
</inist>
</record>

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