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231224s2017 xx |||||o 00| ||eng c |
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|a 10.1007/s10646-017-1795-2
|2 doi
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|a pubmed24n0902.xml
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|a (DE-627)NLM270703845
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|a (NLM)28382548
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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| 100 |
1 |
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|a Terzopoulou, Evangelia
|e verfasserin
|4 aut
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| 245 |
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|a Study of persistent toxic pollutants in a river basin-ecotoxicological risk assessment
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|c 2017
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| 336 |
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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| 338 |
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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| 500 |
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|a Date Completed 28.07.2017
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|a Date Revised 30.09.2020
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|a published: Print-Electronic
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|a Citation Status MEDLINE
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|a This study presents a complementary approach for the evaluation of water quality in a river basin by employing active and passive sampling. Persistent toxic pollutants representing three classes: organochlorinated pesticides (OCPs), polychlorinated biphenyls (PCBs) and polycyclic aromatic hydrocarbons (PAHs), were studied in grab water samples, in passive samplers/SemiPermeable Membrane Devices (SPMDs) and in fish tissues collected along the Strymonas River, northern Greece at three sampling campaigns during the year 2013. Almost all the target compounds were detected in the study river of Strymonas, northern Greece at the periods of high rainfall intensity and/or low flow-rate. The most frequently detected compounds were 1,2-benzanthracene, benzo(a)pyrene, benzo(b)fluoranthene, endosulfan I, endosulfan II, endosulfan sulfate, endrin aldehyde, fluorene, methoxychlor, polychlorinated biphenyl PCB 28, PCB 180 and pyrene. The family of DDT compounds and aldrin were also occasionally detected. Agricultural run-off and waste effluents are the main sources of hydrophobic organic compounds in the river basin. The use of SPMDs allowed the detection of more micropollutants than active sampling (31 vs. 16, respectively). Results showed relatively low risk however the potential risk associated with micropollutants such as 1,2-benzanthracene, benzo(b)fluoranthene, p,p-dichlorodiphenyldichloroethane (DDD), endosulfan II, methoxychlor, PCB 180 and pyrene should not be neglected. Performing risk assessment based on passive sampling, more information was obtained about temporal and spatial variation. SPMDs could be applied as a pre-evaluation before chemical monitoring in biota
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4 |
|a Journal Article
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|a GC-MS/MS
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|a POPs
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|a Passive sampling
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|a Pesticides
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|a Risk assessment
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|a SPMDs
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|a Benz(a)Anthracenes
|2 NLM
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| 650 |
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7 |
|a Fluorenes
|2 NLM
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| 650 |
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7 |
|a Hydrocarbons, Chlorinated
|2 NLM
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| 650 |
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7 |
|a Organic Chemicals
|2 NLM
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| 650 |
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7 |
|a Pesticides
|2 NLM
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| 650 |
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7 |
|a Polycyclic Aromatic Hydrocarbons
|2 NLM
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| 650 |
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7 |
|a Water Pollutants, Chemical
|2 NLM
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| 650 |
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7 |
|a fluorene
|2 NLM
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| 650 |
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7 |
|a 3Q2UY0968A
|2 NLM
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| 650 |
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7 |
|a PCB 180
|2 NLM
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| 650 |
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7 |
|a 52I0CG8IQX
|2 NLM
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| 650 |
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7 |
|a 2,4,4'-trichlorobiphenyl
|2 NLM
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| 650 |
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7 |
|a 844ODP31Q0
|2 NLM
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| 650 |
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7 |
|a endosulfan sulfate
|2 NLM
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| 650 |
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7 |
|a 8QTV9M19B2
|2 NLM
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| 650 |
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7 |
|a benz(a)anthracene
|2 NLM
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| 650 |
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7 |
|a C5PLF6152K
|2 NLM
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| 650 |
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7 |
|a Polychlorinated Biphenyls
|2 NLM
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| 650 |
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7 |
|a DFC2HB4I0K
|2 NLM
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| 650 |
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7 |
|a Endosulfan
|2 NLM
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| 650 |
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7 |
|a OKA6A6ZD4K
|2 NLM
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| 700 |
1 |
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|a Voutsa, Dimitra
|e verfasserin
|4 aut
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| 773 |
0 |
8 |
|i Enthalten in
|t Ecotoxicology (London, England)
|d 1992
|g 26(2017), 5 vom: 05. Juli, Seite 625-638
|w (DE-627)NLM098212214
|x 1573-3017
|7 nnns
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| 773 |
1 |
8 |
|g volume:26
|g year:2017
|g number:5
|g day:05
|g month:07
|g pages:625-638
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| 856 |
4 |
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|u http://dx.doi.org/10.1007/s10646-017-1795-2
|3 Volltext
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|a AR
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|j 2017
|e 5
|b 05
|c 07
|h 625-638
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