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Chemical analysis of estrogens, organochlorine and organonitrogen pesticides as possible endocrine disruptors Scheldt-estuary [Chemische analyse van oestrogenen, organochloor en organostikstof pesticiden als mogelijke endocriene verstoorders in het Schelde-estuarium]
Citation
Noppe, H.; De Brabander, H.; De Wasch, K.; Laboratory for Chemical Analysis - Ugent, Belgium; (2006): Chemical analysis of estrogens, organochlorine and organonitrogen pesticides as possible endocrine disruptors Scheldt-estuary. https://marineinfo.org/id/dataset/19
Contact:
Vakgroep Veterinaire Volksgezondheid & Voedselveiligheid (UGent-VVV)
Availability: Unrestricted after moratorium period
Data are initially restricted, but the access condition relaxes to academic or unrestricted once a specified period of time after an event (such as collection, publication, completion of QC procedures or project cessation) has elapsed
Data are initially restricted, but the access condition relaxes to academic or unrestricted once a specified period of time after an event (such as collection, publication, completion of QC procedures or project cessation) has elapsed
Description
Water, sediment, suspended matter and biota were sampled along the Western Scheldt from 2002 to 2006. All matrices were analysed for estrogens, organochlorine and organonitrogen pesticides using SPE, HPLC, GC-MS/MS and LC-MS/MS. more
In order to evaluate the potential risk of endocrine disruptors, the occurrence of these compounds needs to be documented. Water, sediment, suspended matter and biota were sampled along the Western Scheldt from 2002 to 2006. All matrices were analysed for estrogens, organochlorine and organonitrogen pesticides using SPE, HPLC, GC-MS/MS and LC-MS/MS. The aim this part of the ENDIS-RISKS project is to give an overview of the occurrence and the concentration of the selected endocrine disruptors in the Scheldt estuary.
In order to evaluate the potential risk of endocrine disruptors, the occurrence of these compounds needs to be documented. Water, sediment, suspended matter and biota were sampled along the Western Scheldt from 2002 to 2006. All matrices were analysed for estrogens, organochlorine and organonitrogen pesticides using SPE, HPLC, GC-MS/MS and LC-MS/MS. The aim this part of the ENDIS-RISKS project is to give an overview of the occurrence and the concentration of the selected endocrine disruptors in the Scheldt estuary.
Scope
Themes:
Coastal studies (e.g. shores, estuaries), Environmental quality/pollution
Keywords:
Ecotoxicology, Estrogens, Fungicides, Herbicides, Hormones, Insecticides, Pesticides, Steroids, Water quality, ANE, Scheldt Estuary, ANE, Netherlands, Westerschelde, Bath, ANE, Netherlands, Westerschelde, Hansweert, ANE, Netherlands, Westerschelde, Terneuzen, ANE, Netherlands, Westerschelde, Verdronken Land van Saeftinge, ANE, Netherlands, Westerschelde, Vlissingen, Belgium, Zeeschelde, Antwerp, Belgium, Zeeschelde, Doel, Crangon crangon (Linnaeus, 1758), Neomysis integer (Leach, 1814)
Geographical coverage
ANE, Scheldt Estuary [Marine Regions]
ANE, Netherlands, Westerschelde, Bath Stations
[Marine Regions]
S12
Coordinates: Long: 4,225; Lat: 51,365 [WGS84]
Coordinates: Long: 4,225; Lat: 51,365 [WGS84]
ANE, Netherlands, Westerschelde, Hansweert Stations
[Marine Regions]
S07
Coordinates: Long: 4; Lat: 51,4367 [WGS84]
Coordinates: Long: 4; Lat: 51,4367 [WGS84]
ANE, Netherlands, Westerschelde, Terneuzen Stations
[Marine Regions]
S04
Coordinates: Long: 3,825; Lat: 51,345 [WGS84]
Coordinates: Long: 3,825; Lat: 51,345 [WGS84]
ANE, Netherlands, Westerschelde, Verdronken Land van Saeftinge Stations
[Marine Regions]
S09
Coordinates: Long: 4,0783; Lat: 51,37 [WGS84]
Coordinates: Long: 4,0783; Lat: 51,37 [WGS84]
ANE, Netherlands, Westerschelde, Vlissingen Stations
[Marine Regions]
S01
Coordinates: Long: 3,57; Lat: 51,4167 [WGS84]
Coordinates: Long: 3,57; Lat: 51,4167 [WGS84]
Belgium, Zeeschelde, Antwerp Stations
[Marine Regions]
S22
Coordinates: Long: 4,3917; Lat: 51,2188 [WGS84]
Coordinates: Long: 4,3917; Lat: 51,2188 [WGS84]
Belgium, Zeeschelde, Doel Stations
[Marine Regions]
S15
Coordinates: Long: 4,2733; Lat: 51,3133 [WGS84]
Coordinates: Long: 4,2733; Lat: 51,3133 [WGS84]
Temporal coverage
2002 - 2006
Unknown
Unknown
Parameters
Alpha-Estradiol Methodology
Atrazine Methodology
Beta-Estradiol Methodology
Chlordane
Endosulfan
Estrone Methodology
Ethinylestradiol Methodology
Kepone
Toxaphene
Vinclozolin
Atrazine Methodology
Beta-Estradiol Methodology
Chlordane
Endosulfan
Estrone Methodology
Ethinylestradiol Methodology
Kepone
Toxaphene
Vinclozolin
Alpha-Estradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Alpha-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Atrazine: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Atrazine: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Atrazine: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Atrazine: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Atrazine: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Atrazine: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Atrazine: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Beta-Estradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Beta-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Beta-Estradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Beta-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Beta-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Beta-Estradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Beta-Estradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Estrone: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Estrone: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Estrone: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Estrone: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Estrone: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Estrone: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Estrone: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Ethinylestradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Ethinylestradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Ethinylestradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Ethinylestradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Ethinylestradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Ethinylestradiol: SPE GCMS/MS
(1) Description protocol for the detection of organonitrogen pesticides (atrazine, simazine, terbutylazine) in water samples: After pH adjustment, the samples are filtered and extracted using SDB solid phase extraction cartridges. The extracts are analysed by GC-MS/MS (EI). The data processing is performed by Xcalibur 1.3. and MSOffice Excel. The identification of the organonitrogen pesticides is based on the relative retention time and a specific mass spectrum. Quantification is performe
Ethinylestradiol: GC-EI-MS-MS
Description protocol for pesticides and estrogenes in biota, SPM and sediment: Extraction is performed using accelerated solvent extraction (ASE). After HPLC fractionation or clean-up using the SPE from water analysis samples are analysed bij GC-EI-MS-MS
Contributors
Universiteit Gent; Faculteit Diergeneeskunde; Vakgroep Veterinaire Volksgezondheid & Voedselveiligheid; Laboratorium voor Chemische Analyse (LCA), data creator, data owner
De Wasch, Katia
Noppe, Herlinde
De Brabander, Hubert
Noppe, Herlinde
De Brabander, Hubert
Belgian Science Policy (BELSPO), data owner
Universiteit Gent; Faculteit Diergeneeskunde; Vakgroep Veterinaire Volksgezondheid & Voedselveiligheid (VVV)
Related datasets
Parent dataset:
ENDIS-RISKS fysico-chemical measurements and hyperbenthos in the Scheldt river, 2002-2006.
Project
ENDIS-RISKS: Endocrine disruption in the Scheldt Estuary: distribution, exposure and effects
Publication
Based on this dataset
Noppe, H. (2007). Occurrence of hormones in the Scheldt estuary: an analytical challenge!, in: Mees, J. et al. (Ed.) (2007). VLIZ Young Scientists' Day, Brugge, Belgium 2 March 2007: book of abstracts. VLIZ Special Publication, 39: pp. 14
Noppe, H. et al. (2007). Multi-analyte approach for the determination of ng.l-1 amounts of steroid hormones in unidentified aqueous samples. Anal. Chim. Acta 586(1-2): 22-29. https://dx.doi.org/10.1016/j.aca.2006.08.048
Noppe, H. (2006). Analytiek van hormoon verstorende stoffen in milieumatrices = Analytics of endocrine disrupting chemicals in environmental matrices. PhD Thesis. Universiteit Gent. Faculteit Diergeneeskunde: Gent. ISBN 978-90-5864-100-7. 153 pp.
Noppe, H. et al. (2006). Development and validation of an analytical method for detection of estrogens in water, in: Noppe, H. Analytiek van hormoon verstorende stoffen in milieumatrices = Analytics of endocrine disrupting chemicals in environmental matrices. pp. 21-41
Noppe, H. et al. (2005). Development and validation of an analytical method for detection of estrogens in water. Anal. Bioanal. Chem. 382(1): 91-98. dx.doi.org/10.1007/s00216-005-3174-8
Noppe, H. et al. (2005). Endocriene verstoringen in het Schelde estuarium (1) = Endocrine disruptors in the Scheldt estuary (1), in: Mees, J. et al. (Ed.) (2005). VLIZ Young Scientists' Day, Brugge, Belgium 25 February 2005: book of abstracts. VLIZ Special Publication, 20: pp. 50
Dataset status: Completed
Data type: Data
Data origin: Research
Metadatarecord created: 2004-05-10
Information last updated: 2017-11-17