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Comparison of different microbial bioassays to assess metal contamination in soils.

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Comparison of different microbial bioassays to assess metal contamination in soils. / Tandy, Susan; Barbosa, Vera; Tye, Andy et al.
In: Environmental Toxicology and Chemistry, Vol. 24, No. 3, 03.2005, p. 530-536.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

Tandy, S, Barbosa, V, Tye, A, Preston, S, Paton, G, Zhang, H & McGrath, S 2005, 'Comparison of different microbial bioassays to assess metal contamination in soils.', Environmental Toxicology and Chemistry, vol. 24, no. 3, pp. 530-536. https://doi.org/10.1897/04-197R.1

APA

Tandy, S., Barbosa, V., Tye, A., Preston, S., Paton, G., Zhang, H., & McGrath, S. (2005). Comparison of different microbial bioassays to assess metal contamination in soils. Environmental Toxicology and Chemistry, 24(3), 530-536. https://doi.org/10.1897/04-197R.1

Vancouver

Tandy S, Barbosa V, Tye A, Preston S, Paton G, Zhang H et al. Comparison of different microbial bioassays to assess metal contamination in soils. Environmental Toxicology and Chemistry. 2005 Mar;24(3):530-536. doi: 10.1897/04-197R.1

Author

Tandy, Susan ; Barbosa, Vera ; Tye, Andy et al. / Comparison of different microbial bioassays to assess metal contamination in soils. In: Environmental Toxicology and Chemistry. 2005 ; Vol. 24, No. 3. pp. 530-536.

Bibtex

@article{0ac5bc53335343b0909aeca804423227,
title = "Comparison of different microbial bioassays to assess metal contamination in soils.",
abstract = "These experiments compared the sensitivity of four different types of bioassay over time after five metals were added to a wide range of soils at the maximum concentrations in the European Union Sewage Sludge Directive. Three were chronic assays (most probable number of Rhizobium leguminosarum, soil microbial C and Biolog substrate utilization). The fourth bioassay, an acute biosensor, employed a lux-marked luminescent bacterium (Escherichia coli) in the soil pore water. Five metals were added to 23 different soils as a mixture at Zn = 300, Cd = 3, Pb = 300, Cu = 135, and Ni = 75 mg/kg as nitrate salts and compared with unamended controls. Zinc and Cu were the metals most likely to be toxic at the concentrations used here. In the case of Rhizobium, the number of cells in soil was not affected after 11 d; however, by 818 d the numbers had decreased by four orders of magnitude with increasing concentrations of Zn and Cu in soil solution. Microbial biomass also was not affected after 11 d, but significantly decreased with increased Zn (p < 0.001) and Cu (p < 0.01) in soil solution after 818 d. Toxicity to the soil microbial biomass increased with time, whereas the toxicity to the biosensor remained the same. Biolog substrate utilization profiles were not responsive to the concentrations used here.",
keywords = "Ecotoxicity, Indicators, Monitoring, Risk, Hazard assessment",
author = "Susan Tandy and Vera Barbosa and Andy Tye and Sara Preston and Graeme Paton and Hao Zhang and Steve McGrath",
year = "2005",
month = mar,
doi = "10.1897/04-197R.1",
language = "English",
volume = "24",
pages = "530--536",
journal = "Environmental Toxicology and Chemistry",
issn = "0730-7268",
publisher = "John Wiley and Sons Ltd",
number = "3",

}

RIS

TY - JOUR

T1 - Comparison of different microbial bioassays to assess metal contamination in soils.

AU - Tandy, Susan

AU - Barbosa, Vera

AU - Tye, Andy

AU - Preston, Sara

AU - Paton, Graeme

AU - Zhang, Hao

AU - McGrath, Steve

PY - 2005/3

Y1 - 2005/3

N2 - These experiments compared the sensitivity of four different types of bioassay over time after five metals were added to a wide range of soils at the maximum concentrations in the European Union Sewage Sludge Directive. Three were chronic assays (most probable number of Rhizobium leguminosarum, soil microbial C and Biolog substrate utilization). The fourth bioassay, an acute biosensor, employed a lux-marked luminescent bacterium (Escherichia coli) in the soil pore water. Five metals were added to 23 different soils as a mixture at Zn = 300, Cd = 3, Pb = 300, Cu = 135, and Ni = 75 mg/kg as nitrate salts and compared with unamended controls. Zinc and Cu were the metals most likely to be toxic at the concentrations used here. In the case of Rhizobium, the number of cells in soil was not affected after 11 d; however, by 818 d the numbers had decreased by four orders of magnitude with increasing concentrations of Zn and Cu in soil solution. Microbial biomass also was not affected after 11 d, but significantly decreased with increased Zn (p < 0.001) and Cu (p < 0.01) in soil solution after 818 d. Toxicity to the soil microbial biomass increased with time, whereas the toxicity to the biosensor remained the same. Biolog substrate utilization profiles were not responsive to the concentrations used here.

AB - These experiments compared the sensitivity of four different types of bioassay over time after five metals were added to a wide range of soils at the maximum concentrations in the European Union Sewage Sludge Directive. Three were chronic assays (most probable number of Rhizobium leguminosarum, soil microbial C and Biolog substrate utilization). The fourth bioassay, an acute biosensor, employed a lux-marked luminescent bacterium (Escherichia coli) in the soil pore water. Five metals were added to 23 different soils as a mixture at Zn = 300, Cd = 3, Pb = 300, Cu = 135, and Ni = 75 mg/kg as nitrate salts and compared with unamended controls. Zinc and Cu were the metals most likely to be toxic at the concentrations used here. In the case of Rhizobium, the number of cells in soil was not affected after 11 d; however, by 818 d the numbers had decreased by four orders of magnitude with increasing concentrations of Zn and Cu in soil solution. Microbial biomass also was not affected after 11 d, but significantly decreased with increased Zn (p < 0.001) and Cu (p < 0.01) in soil solution after 818 d. Toxicity to the soil microbial biomass increased with time, whereas the toxicity to the biosensor remained the same. Biolog substrate utilization profiles were not responsive to the concentrations used here.

KW - Ecotoxicity

KW - Indicators

KW - Monitoring

KW - Risk

KW - Hazard assessment

U2 - 10.1897/04-197R.1

DO - 10.1897/04-197R.1

M3 - Journal article

VL - 24

SP - 530

EP - 536

JO - Environmental Toxicology and Chemistry

JF - Environmental Toxicology and Chemistry

SN - 0730-7268

IS - 3

ER -