EsturgeonV1, PascalFrancis, Curation, bibRecord, 000321

Non-dioxin-like PCBs in ten different fish species from the Danube river in Serbia

Identifieur interne : 000321 ( PascalFrancis/Curation ); précédent : 000320; suivant : 000322

Non-dioxin-like PCBs in ten different fish species from the Danube river in Serbia

Auteurs : Sasa Jankovic [Serbie] ; Marijana Curcie [Serbie] ; Tatjana Radicevic [Serbie] ; Srdan Stefanovic [Serbie] ; Mirjana Lenhardt [Serbie] ; Ksenija Durgo [Croatie] ; Biljana Antonijevic [Serbie]

Source :

Environmental monitoring and assessment [ 0167-6369 ] ; 2011.

RBID : Pascal:12-0428422

Descripteurs français

Pascal (Inist)
- Dérivé de la dioxine, Dibenzo-p-dioxine(2,3,7,8-tétrachloro), Polychlorobiphényles, Pisces, Rivière, Cours eau, Surveillance écologique, Hydrocarbure chloré, Composé aromatique, Hydrocarbure halogéné, Serbie, Chlore composé organique, Halogène composé organique.
Wicri :
- geographic : Serbie.

English descriptors

KwdEn :
- Aromatic compound, Chlorocarbon, Dioxin derivatives, Environmental monitoring, Halogenated hydrocarbon, Pisces, Polychlorobiphenyls, Rivers, Serbia, Stream.

Abstract

This work has been developed to examine the level of non-dioxin-like (ndl) PCBs (28, 52, 101, 138, 153 and 180) in (a) ten different freshwater fish species from the Danube river, (b) two sampling points: up and downstream of the industrial zone of the city of Pancevo (ecological hot spot in Serbia) and (c) two time points i.e., in 2001 and 2006. Obtained results would serve to analyse spatial, temporal and congener profile characteristics of ndl PCBs cumulated in fish tissues due to environmental pollution. Sixty-four samples of the following species were collected: wels (Silirus glanus), pike (Esox lucius), bream (Abramis brama), crucian carp (Carassius carassius), pike pearch (Stizostedion lucioperca), barbel (Barbus barbus), tench (Tinca tinca), sterlet (Acipenser ruthenus L.), common carp (Cyprinus carpio) and bighead carp (Hypophthalmichthys nobilis). Gas chromatography coupled with electron capture detector was used for analysis of ndl PCBs. Total ndl PCBs content in upstream samples ranged from 2.7 to 98.1 ng/g and from 4.9 to 68.3 ng/g in 2001 and 2006, respectively. During the 5 years, ndl PCBs content increased significantly in downstream samples i.e., ndl PCBs varied from 13.7 to 46.1 ng/g and from 14.4 to 107.2 ng/g in 2001 and 2006, respectively. PCBs 138 and 180 were predominant congeners in 2001, while in 2006 the most abundant PCB congeners were 138 and 153. In 2006, the presence of PCB 28 and PCB 52 has indicated a recent contamination event. Data on continual monitoring of PCBs in all relevant environmental compartments together with appropriate biomonitoring data are expected to give comprehensive insight into the fate and behaviour profile of these contaminants.

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C01	`01`		`ENG`	@0 This work has been developed to examine the level of non-dioxin-like (ndl) PCBs (28, 52, 101, 138, 153 and 180) in (a) ten different freshwater fish species from the Danube river, (b) two sampling points: up and downstream of the industrial zone of the city of Pancevo (ecological hot spot in Serbia) and (c) two time points i.e., in 2001 and 2006. Obtained results would serve to analyse spatial, temporal and congener profile characteristics of ndl PCBs cumulated in fish tissues due to environmental pollution. Sixty-four samples of the following species were collected: wels (Silirus glanus), pike (Esox lucius), bream (Abramis brama), crucian carp (Carassius carassius), pike pearch (Stizostedion lucioperca), barbel (Barbus barbus), tench (Tinca tinca), sterlet (Acipenser ruthenus L.), common carp (Cyprinus carpio) and bighead carp (Hypophthalmichthys nobilis). Gas chromatography coupled with electron capture detector was used for analysis of ndl PCBs. Total ndl PCBs content in upstream samples ranged from 2.7 to 98.1 ng/g and from 4.9 to 68.3 ng/g in 2001 and 2006, respectively. During the 5 years, ndl PCBs content increased significantly in downstream samples i.e., ndl PCBs varied from 13.7 to 46.1 ng/g and from 14.4 to 107.2 ng/g in 2001 and 2006, respectively. PCBs 138 and 180 were predominant congeners in 2001, while in 2006 the most abundant PCB congeners were 138 and 153. In 2006, the presence of PCB 28 and PCB 52 has indicated a recent contamination event. Data on continual monitoring of PCBs in all relevant environmental compartments together with appropriate biomonitoring data are expected to give comprehensive insight into the fate and behaviour profile of these contaminants.
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Pascal:12-0428422

Le document en format XML

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<front><div type="abstract" xml:lang="en">This work has been developed to examine the level of non-dioxin-like (ndl) PCBs (28, 52, 101, 138, 153 and 180) in (a) ten different freshwater fish species from the Danube river, (b) two sampling points: up and downstream of the industrial zone of the city of Pancevo (ecological hot spot in Serbia) and (c) two time points i.e., in 2001 and 2006. Obtained results would serve to analyse spatial, temporal and congener profile characteristics of ndl PCBs cumulated in fish tissues due to environmental pollution. Sixty-four samples of the following species were collected: wels (Silirus glanus), pike (Esox lucius), bream (Abramis brama), crucian carp (Carassius carassius), pike pearch (Stizostedion lucioperca), barbel (Barbus barbus), tench (Tinca tinca), sterlet (Acipenser ruthenus L.), common carp (Cyprinus carpio) and bighead carp (Hypophthalmichthys nobilis). Gas chromatography coupled with electron capture detector was used for analysis of ndl PCBs. Total ndl PCBs content in upstream samples ranged from 2.7 to 98.1 ng/g and from 4.9 to 68.3 ng/g in 2001 and 2006, respectively. During the 5 years, ndl PCBs content increased significantly in downstream samples i.e., ndl PCBs varied from 13.7 to 46.1 ng/g and from 14.4 to 107.2 ng/g in 2001 and 2006, respectively. PCBs 138 and 180 were predominant congeners in 2001, while in 2006 the most abundant PCB congeners were 138 and 153. In 2006, the presence of PCB 28 and PCB 52 has indicated a recent contamination event. Data on continual monitoring of PCBs in all relevant environmental compartments together with appropriate biomonitoring data are expected to give comprehensive insight into the fate and behaviour profile of these contaminants.</div>
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<fA11 i1="01" i2="1"><s1>JANKOVIC (Sasa)</s1>
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<fA14 i1="01"><s1>Institute of Meat Hygiene and Technology, Kacanskog 13</s1>
<s2>11000 Belgrade</s2>
<s3>SRB</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>4 aut.</sZ>
</fA14>
<fA14 i1="02"><s1>Department of Toxicology "Akademik Danilo Soldatović", Faculty of Pharmacy, University of Belgrade, Vojvode Stepe 450</s1>
<s2>11221 Belgrade</s2>
<s3>SRB</s3>
<sZ>2 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="03"><s1>Institute for Multidisciplinary Research, University of Belgrade, Kneza Višeslava 1a</s1>
<s2>11030 Belgrade</s2>
<s3>SRB</s3>
<sZ>5 aut.</sZ>
</fA14>
<fA14 i1="04"><s1>Department for Biochemical Engineering, Faculty of Food Technology and Biotechnology, Zagreb University, Krsnjavoga 25</s1>
<s2>1000 Zagreb</s2>
<s3>HRV</s3>
<sZ>6 aut.</sZ>
</fA14>
<fA20><s1>153-163</s1>
</fA20>
<fA21><s1>2011</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>19359</s2>
<s5>354000500178060130</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2012 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>1 p.1/4</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>12-0428422</s0>
</fA47>
<fA60><s1>P</s1>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Environmental monitoring and assessment</s0>
</fA64>
<fA66 i1="01"><s0>NLD</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>This work has been developed to examine the level of non-dioxin-like (ndl) PCBs (28, 52, 101, 138, 153 and 180) in (a) ten different freshwater fish species from the Danube river, (b) two sampling points: up and downstream of the industrial zone of the city of Pancevo (ecological hot spot in Serbia) and (c) two time points i.e., in 2001 and 2006. Obtained results would serve to analyse spatial, temporal and congener profile characteristics of ndl PCBs cumulated in fish tissues due to environmental pollution. Sixty-four samples of the following species were collected: wels (Silirus glanus), pike (Esox lucius), bream (Abramis brama), crucian carp (Carassius carassius), pike pearch (Stizostedion lucioperca), barbel (Barbus barbus), tench (Tinca tinca), sterlet (Acipenser ruthenus L.), common carp (Cyprinus carpio) and bighead carp (Hypophthalmichthys nobilis). Gas chromatography coupled with electron capture detector was used for analysis of ndl PCBs. Total ndl PCBs content in upstream samples ranged from 2.7 to 98.1 ng/g and from 4.9 to 68.3 ng/g in 2001 and 2006, respectively. During the 5 years, ndl PCBs content increased significantly in downstream samples i.e., ndl PCBs varied from 13.7 to 46.1 ng/g and from 14.4 to 107.2 ng/g in 2001 and 2006, respectively. PCBs 138 and 180 were predominant congeners in 2001, while in 2006 the most abundant PCB congeners were 138 and 153. In 2006, the presence of PCB 28 and PCB 52 has indicated a recent contamination event. Data on continual monitoring of PCBs in all relevant environmental compartments together with appropriate biomonitoring data are expected to give comprehensive insight into the fate and behaviour profile of these contaminants.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14D05A</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>002A15B</s0>
</fC02>
<fC02 i1="03" i2="X"><s0>002A14B04C</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Dérivé de la dioxine</s0>
<s2>FR</s2>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Dioxin derivatives</s0>
<s2>FR</s2>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Dibenzo-p-dioxine(2,3,7,8-tétrachloro)</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Polychlorobiphényles</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Polychlorobiphenyls</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Polichlorobifenilos</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Pisces</s0>
<s2>NS</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Pisces</s0>
<s2>NS</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Pisces</s0>
<s2>NS</s2>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Rivière</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Rivers</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Río</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Cours eau</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Stream</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Curso agua</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Surveillance écologique</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Environmental monitoring</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Vigilancia ecológica</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Hydrocarbure chloré</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Chlorocarbon</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Hidrocarburo clorado</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Composé aromatique</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Aromatic compound</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Compuesto aromático</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Hydrocarbure halogéné</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Halogenated hydrocarbon</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Hidrocarburo halogenado</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Serbie</s0>
<s2>NG</s2>
<s5>19</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Serbia</s0>
<s2>NG</s2>
<s5>19</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Serbia</s0>
<s2>NG</s2>
<s5>19</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Chlore composé organique</s0>
<s4>INC</s4>
<s5>87</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Halogène composé organique</s0>
<s4>INC</s4>
<s5>88</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Europa</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Composé organique</s0>
<s2>NA</s2>
<s5>26</s5>
</fC07>
<fC07 i1="03" i2="X" l="ENG"><s0>Organic compounds</s0>
<s2>NA</s2>
<s5>26</s5>
</fC07>
<fC07 i1="03" i2="X" l="SPA"><s0>Compuesto orgánico</s0>
<s2>NA</s2>
<s5>26</s5>
</fC07>
<fC07 i1="04" i2="X" l="FRE"><s0>Polluant organique persistant</s0>
<s5>27</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG"><s0>Persistent organic pollutant</s0>
<s5>27</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA"><s0>Contaminante organico persistente</s0>
<s5>27</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE"><s0>Milieu eau douce</s0>
<s5>28</s5>
</fC07>
<fC07 i1="05" i2="X" l="ENG"><s0>Freshwater environment</s0>
<s5>28</s5>
</fC07>
<fC07 i1="05" i2="X" l="SPA"><s0>Medio agua dulce</s0>
<s5>28</s5>
</fC07>
<fN21><s1>331</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
</record>

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Non-dioxin-like PCBs in ten different fish species from the Danube river in Serbia

Non-dioxin-like PCBs in ten different fish species from the Danube river in Serbia

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