Aarhus Universitets segl

Sulfate biosensor for environmental applications

Publikation: Bidrag til tidsskrift/Konferencebidrag i tidsskrift /Bidrag til avisTidsskriftartikelForskningpeer review

Standard

Sulfate biosensor for environmental applications. / Marzocchi, Ugo; Revsbech, Niels Peter.

I: Limnology and Oceanography: Methods, Bind 20, Nr. 10, 10.2022, s. 674-681.

Publikation: Bidrag til tidsskrift/Konferencebidrag i tidsskrift /Bidrag til avisTidsskriftartikelForskningpeer review

Harvard

Marzocchi, U & Revsbech, NP 2022, 'Sulfate biosensor for environmental applications', Limnology and Oceanography: Methods, bind 20, nr. 10, s. 674-681. https://doi.org/10.1002/lom3.10512

APA

CBE

MLA

Vancouver

Marzocchi U, Revsbech NP. Sulfate biosensor for environmental applications. Limnology and Oceanography: Methods. 2022 okt.;20(10):674-681. doi: 10.1002/lom3.10512

Author

Marzocchi, Ugo ; Revsbech, Niels Peter. / Sulfate biosensor for environmental applications. I: Limnology and Oceanography: Methods. 2022 ; Bind 20, Nr. 10. s. 674-681.

Bibtex

@article{76218d36e85b4c3fbff8fd04ee95574a,
title = "Sulfate biosensor for environmental applications",
abstract = "Sulfate is present in all freshwater and marine environments and is reduced to toxic and corrosive hydrogen sulfide by anaerobic bacteria. By measuring depth profiles of sulfate in sediments, it is possible to obtain estimates of sulfate reduction rates (SRRs). A whole-cell microscale biosensor for sulfate was constructed by placing a mixture of sulfate-reducing and aerobic bacteria in front of a hydrogen sulfide microsensor. The bacteria were supplied with electron donors from a reservoir behind the bacterial biomass. The aerobic bacteria ensured anaerobic conditions in deeper parts of the 150-mu m-thick bacterial layer, so that the sulfate reducers could be active. A typical tip diameter of a sulfate biosensor is 50 mu m. The calibration curve was close to linear in the 0-2 mM range, with a detection limit of about 10 mu M. The 90% response time varied between 90 and 220 s, slowest response at low concentrations. Oxygen and ferrous iron at environmental concentrations gave no interference, but there was a 6% signal difference between stirred and stagnant liquid medium. The sensitivity of the biosensor could be modulated by applying a charge between sensor interior and an external electrode. The lifetime is usually a few weeks. The biosensor was used to measure sulfate profiles in a freshwater sediment.",
keywords = "SENSITIVITY CONTROL, FRESH-WATER, REDUCTION, SEDIMENTS, MICROSENSOR, TRANSPORT, CYCLE, IONS, H2S",
author = "Ugo Marzocchi and Revsbech, {Niels Peter}",
year = "2022",
month = oct,
doi = "10.1002/lom3.10512",
language = "English",
volume = "20",
pages = "674--681",
journal = "Limnology and Oceanography: Methods",
issn = "1541-5856",
publisher = "John Wiley & Sons, Inc.",
number = "10",

}

RIS

TY - JOUR

T1 - Sulfate biosensor for environmental applications

AU - Marzocchi, Ugo

AU - Revsbech, Niels Peter

PY - 2022/10

Y1 - 2022/10

N2 - Sulfate is present in all freshwater and marine environments and is reduced to toxic and corrosive hydrogen sulfide by anaerobic bacteria. By measuring depth profiles of sulfate in sediments, it is possible to obtain estimates of sulfate reduction rates (SRRs). A whole-cell microscale biosensor for sulfate was constructed by placing a mixture of sulfate-reducing and aerobic bacteria in front of a hydrogen sulfide microsensor. The bacteria were supplied with electron donors from a reservoir behind the bacterial biomass. The aerobic bacteria ensured anaerobic conditions in deeper parts of the 150-mu m-thick bacterial layer, so that the sulfate reducers could be active. A typical tip diameter of a sulfate biosensor is 50 mu m. The calibration curve was close to linear in the 0-2 mM range, with a detection limit of about 10 mu M. The 90% response time varied between 90 and 220 s, slowest response at low concentrations. Oxygen and ferrous iron at environmental concentrations gave no interference, but there was a 6% signal difference between stirred and stagnant liquid medium. The sensitivity of the biosensor could be modulated by applying a charge between sensor interior and an external electrode. The lifetime is usually a few weeks. The biosensor was used to measure sulfate profiles in a freshwater sediment.

AB - Sulfate is present in all freshwater and marine environments and is reduced to toxic and corrosive hydrogen sulfide by anaerobic bacteria. By measuring depth profiles of sulfate in sediments, it is possible to obtain estimates of sulfate reduction rates (SRRs). A whole-cell microscale biosensor for sulfate was constructed by placing a mixture of sulfate-reducing and aerobic bacteria in front of a hydrogen sulfide microsensor. The bacteria were supplied with electron donors from a reservoir behind the bacterial biomass. The aerobic bacteria ensured anaerobic conditions in deeper parts of the 150-mu m-thick bacterial layer, so that the sulfate reducers could be active. A typical tip diameter of a sulfate biosensor is 50 mu m. The calibration curve was close to linear in the 0-2 mM range, with a detection limit of about 10 mu M. The 90% response time varied between 90 and 220 s, slowest response at low concentrations. Oxygen and ferrous iron at environmental concentrations gave no interference, but there was a 6% signal difference between stirred and stagnant liquid medium. The sensitivity of the biosensor could be modulated by applying a charge between sensor interior and an external electrode. The lifetime is usually a few weeks. The biosensor was used to measure sulfate profiles in a freshwater sediment.

KW - SENSITIVITY CONTROL

KW - FRESH-WATER

KW - REDUCTION

KW - SEDIMENTS

KW - MICROSENSOR

KW - TRANSPORT

KW - CYCLE

KW - IONS

KW - H2S

U2 - 10.1002/lom3.10512

DO - 10.1002/lom3.10512

M3 - Journal article

VL - 20

SP - 674

EP - 681

JO - Limnology and Oceanography: Methods

JF - Limnology and Oceanography: Methods

SN - 1541-5856

IS - 10

ER -