Anaerobic Inhibition and Biodegradation of Antibiotics in ISO Test Schemes

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Anaerobic Inhibition and Biodegradation of Antibiotics in ISO Test Schemes. / Gartiser, Stefan; Urich, Elke; Alexy, Radka et al.
in: Chemosphere, Jahrgang 66, Nr. 10, 01.01.2007, S. 1839-1848.

Publikation: Beiträge in ZeitschriftenZeitschriftenaufsätzeForschungbegutachtet

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Gartiser S, Urich E, Alexy R, Kümmerer K. Anaerobic Inhibition and Biodegradation of Antibiotics in ISO Test Schemes. Chemosphere. 2007 Jan 1;66(10):1839-1848. doi: 10.1016/j.chemosphere.2006.08.040

Bibtex

@article{617a5714ef3941e89255c60f2183f2e9,
title = "Anaerobic Inhibition and Biodegradation of Antibiotics in ISO Test Schemes",
abstract = "Municipal sewage is the main exposure route for antibiotics that are used in human medical care. Antibiotics that adsorb to the primary sludge and/or sur-plus activated sludge will enter the anaerobic digesters of municipal sewage treatment plants. Here anaerobic biodegradation or inhibition of anaerobic bacteria resulting in a disturbance of the process might occur. ISO standards 13641 (2003) and 11734 (1999) were used for assessing the anaerobic inhibition of 16 and the anaerobic biodegradability of 9 antibiotics respectively. Digestion sludge from a municipal sewage treatment plant (1 g/l d.s.) was used as inoculum in both tests. In ISO 13641 (2003) most antibiotics showed only moderate inhibition effects after a 7 day incubation period, with EC 50 values between 24 mg/l and more than 1000 mg/l (equal to mg/g d.s.). In contrast, metronidazol was decisively toxic to anaerobic bacteria with an EC 50 of 0.7 mg/l. In the anaerobic degradation tests according to ISO standard 11734 (1995), only benzylpenicillin showed certain ultimate biodegradation after 60 days and most antibiotics inhibited the digesting sludge in the respective parallel tested inhibition controls. Thus the inhibition of anaerobic bacteria by antibiotics observed in the degradation tests was higher than expected from the results of the inhibition tests. The possible explanations are that distinct substrates are used (yeast extract versus sodium benzoate), that the digestion sludge loses activity during the washing steps performed for the degradation tests and that the exposure time in the degradation tests was 8 times longer than in the inhibition test.",
keywords = "Anaerobic biodegradability, Anaerobic inhibition, Antibiotics, Effluent",
author = "Stefan Gartiser and Elke Urich and Radka Alexy and Klaus K{\"u}mmerer",
note = "Funding Information: We kindly acknowledge the financial support of the investigations by the German Environmental Protection Agency (UBA, research grant No. 298 63 722).",
year = "2007",
month = jan,
day = "1",
doi = "10.1016/j.chemosphere.2006.08.040",
language = "English",
volume = "66",
pages = "1839--1848",
journal = "Chemosphere",
issn = "0045-6535",
publisher = "Pergamon Press",
number = "10",

}

RIS

TY - JOUR

T1 - Anaerobic Inhibition and Biodegradation of Antibiotics in ISO Test Schemes

AU - Gartiser, Stefan

AU - Urich, Elke

AU - Alexy, Radka

AU - Kümmerer, Klaus

N1 - Funding Information: We kindly acknowledge the financial support of the investigations by the German Environmental Protection Agency (UBA, research grant No. 298 63 722).

PY - 2007/1/1

Y1 - 2007/1/1

N2 - Municipal sewage is the main exposure route for antibiotics that are used in human medical care. Antibiotics that adsorb to the primary sludge and/or sur-plus activated sludge will enter the anaerobic digesters of municipal sewage treatment plants. Here anaerobic biodegradation or inhibition of anaerobic bacteria resulting in a disturbance of the process might occur. ISO standards 13641 (2003) and 11734 (1999) were used for assessing the anaerobic inhibition of 16 and the anaerobic biodegradability of 9 antibiotics respectively. Digestion sludge from a municipal sewage treatment plant (1 g/l d.s.) was used as inoculum in both tests. In ISO 13641 (2003) most antibiotics showed only moderate inhibition effects after a 7 day incubation period, with EC 50 values between 24 mg/l and more than 1000 mg/l (equal to mg/g d.s.). In contrast, metronidazol was decisively toxic to anaerobic bacteria with an EC 50 of 0.7 mg/l. In the anaerobic degradation tests according to ISO standard 11734 (1995), only benzylpenicillin showed certain ultimate biodegradation after 60 days and most antibiotics inhibited the digesting sludge in the respective parallel tested inhibition controls. Thus the inhibition of anaerobic bacteria by antibiotics observed in the degradation tests was higher than expected from the results of the inhibition tests. The possible explanations are that distinct substrates are used (yeast extract versus sodium benzoate), that the digestion sludge loses activity during the washing steps performed for the degradation tests and that the exposure time in the degradation tests was 8 times longer than in the inhibition test.

AB - Municipal sewage is the main exposure route for antibiotics that are used in human medical care. Antibiotics that adsorb to the primary sludge and/or sur-plus activated sludge will enter the anaerobic digesters of municipal sewage treatment plants. Here anaerobic biodegradation or inhibition of anaerobic bacteria resulting in a disturbance of the process might occur. ISO standards 13641 (2003) and 11734 (1999) were used for assessing the anaerobic inhibition of 16 and the anaerobic biodegradability of 9 antibiotics respectively. Digestion sludge from a municipal sewage treatment plant (1 g/l d.s.) was used as inoculum in both tests. In ISO 13641 (2003) most antibiotics showed only moderate inhibition effects after a 7 day incubation period, with EC 50 values between 24 mg/l and more than 1000 mg/l (equal to mg/g d.s.). In contrast, metronidazol was decisively toxic to anaerobic bacteria with an EC 50 of 0.7 mg/l. In the anaerobic degradation tests according to ISO standard 11734 (1995), only benzylpenicillin showed certain ultimate biodegradation after 60 days and most antibiotics inhibited the digesting sludge in the respective parallel tested inhibition controls. Thus the inhibition of anaerobic bacteria by antibiotics observed in the degradation tests was higher than expected from the results of the inhibition tests. The possible explanations are that distinct substrates are used (yeast extract versus sodium benzoate), that the digestion sludge loses activity during the washing steps performed for the degradation tests and that the exposure time in the degradation tests was 8 times longer than in the inhibition test.

KW - Anaerobic biodegradability

KW - Anaerobic inhibition

KW - Antibiotics

KW - Effluent

UR - http://www.scopus.com/inward/record.url?scp=33845225568&partnerID=8YFLogxK

UR - https://www.mendeley.com/catalogue/a010368f-1610-395e-bc77-459755a95689/

U2 - 10.1016/j.chemosphere.2006.08.040

DO - 10.1016/j.chemosphere.2006.08.040

M3 - Journal articles

C2 - 17097129

VL - 66

SP - 1839

EP - 1848

JO - Chemosphere

JF - Chemosphere

SN - 0045-6535

IS - 10

ER -

DOI