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Ann M. Brunton 1 , Michael A. Vega 2 , Adam Brady 2 , Jonathan O. Sharp 2 1 University of Arizona 2 Department of Civil and Environmental Engineering, Colorado School of Mines IRONS IMPACT ON NITROGEN CYCLING IN AN OPEN WATER WETLAND TO PROMOTE SUSTAINABLE WATER TREATMENT Re-Invenng the Naons Urban Water Infrastructure (ReNUWIt) Background Microorganisms in constructed wetlands anaerobically remove nitrate from the water. Nitrate removal can take the form of various pathways including denitrificaon, DNRA, anammox, and abioc pathways. Microorganisms can use organic carbon (heterotrophy) or inorganic carbon (autotrophy). The role of ferrous iron in these processes was previously unknown. Methods Anaerobic slurry microcosms with wetland biomat, differing concentraons of ferrous iron given at 15 days Sampling: Aqueous: nitrogen species, sulfide, iron, organic and inorganic carbon, acetate Gas: nitrous oxide and methane Mineral: ferric oxides Microbial: funconal genes for nitrogen cycling processes Hypothesis Heterotrophic denitrificaon will dominate. Secondarily, low iron concentraons will experience autotrophic denitrificaon. High iron concentraons will cause a shiſt towards DNRA (and anammox).

IRON S IMPA T ON NITROGEN YLING IN AN OPEN WATER …

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Page 1: IRON S IMPA T ON NITROGEN YLING IN AN OPEN WATER …

Ann M. Brunton1, Michael A. Vega2, Adam Brady2 , Jonathan O. Sharp2

1University of Arizona 2Department of Civil and Environmental Engineering, Colorado School of Mines

IRON’S IMPACT ON NITROGEN CYCLING IN AN OPEN WATER WETLAND TO

PROMOTE SUSTAINABLE WATER TREATMENT

Re-Inventing the Nation’s Urban Water Infrastructure (ReNUWIt)

Background

• Microorganisms in constructed wetlands anaerobically remove nitrate from the water.

• Nitrate removal can take the form of various pathways including denitrification, DNRA, anammox, and abiotic pathways.

• Microorganisms can use organic carbon (heterotrophy) or inorganic carbon (autotrophy).

• The role of ferrous iron in these processes was previously unknown.

Methods

• Anaerobic slurry microcosms with wetland biomat, differing concentrations of ferrous iron given at 15 days

• Sampling:

• Aqueous: nitrogen species, sulfide, iron, organic and inorganic carbon, acetate

• Gas: nitrous oxide and methane

• Mineral: ferric oxides

• Microbial: functional genes for nitrogen cycling processes

Hypothesis

• Heterotrophic denitrification will dominate.

• Secondarily, low iron concentrations will experience autotrophic denitrification.

• High iron concentrations will cause a shift towards DNRA (and anammox).

Page 2: IRON S IMPA T ON NITROGEN YLING IN AN OPEN WATER …

Conclusions

• Hypothesis: •Heterotrophic denitrification will dominate. Supported. •Secondarily, low concentrations will experience autotrophic denitrification. No Evidence. •High iron concentrations will cause a shift towards DNRA (and anammox). Refuted.

• Likely that abiotic nitrite reduction occurs beyond a threshold iron concentration.

Results

• Reduction in nitrate that corresponds with reduction in organic carbon

• No significant difference in ammonium production among iron concentrations

• More nitrite reduction with high concentration of ferrous iron

• Little difference between control, 5 ppm, and 100 ppm iron microcosms with all species

Control 5uM 100 uM 1000 uM

Unfoiled microcosms at the final time point. The red hue in

the high iron condition indicates iron oxidation