hydrological-microbial interactions controlling landscape phosphorus mobility

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Hydrological-Microbial Interactions Controlling Landscape Phosphorus Mobility Jay Regan Environmental Engineering USDA AFRI and NIWQP PD Meeting, October 12, 2016 M. Todd Walter Biological and Environmental Engr. Hunter Carrick Biology Anthony Buda USDA-ARS Pasture Systems & Watershed Mgmt. Research Unit

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Hydrological-Microbial Interactions Controlling

Landscape Phosphorus Mobility

Jay ReganEnvironmental Engineering

USDA AFRI and NIWQP PD Meeting, October 12, 2016

M. Todd WalterBiological and Environmental Engr.

Hunter CarrickBiology

Anthony BudaUSDA-ARS Pasture Systems & Watershed Mgmt. Research Unit

How do microbial activities control P mobility in agroecosystems under fluctuating redox conditions?

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Field sampling:- Stream biofilms (diel

redox fluctuations)

- Soils across soil topographic index gradient (i.e., variable saturation frequencies)

Soil column sampling (controlled conditions)

Primarily focused on:

• Dissimilatory iron-reducing bacteria (DIRB)

• Polyphosphate-accumulating organisms (PAOs)

Dissimilatory iron-reducing bacteria use iron oxides under anaerobic conditions, which liberates P

Hypothesis – DIRB contribute to increased dissolved P under saturated (i.e., anaerobic) conditions

Modified from Weber et al (2006) Nature Reviews Microbiol.

Polyphosphate-accumulating organisms alternate between P release (anaerobic) and P uptake (aerobic)

Anaerobic

Glycogen

ATPPHA

Poly-P

PO43-

Acetic AcidCell Maint.

Aerobic

PO43-

Poly-P

Glycogen

ATPPHA

Cell Growth

H20½O2

PHA - Polyhydroxyalkanoate

Hypothesis – PAOs contribute to increased dissolved P under saturated (i.e., anaerobic) conditions and decreased dissolved P under unsaturated (i.e., aerobic) conditions

Molecular characterization of PAO populations in PA stream biofilms

Field tests on stream biofilm development with variable P loads

Bench tests on stream biofilms under diel redox cycles

5

Emphases of this project report

Bench tests on stream biofilms under diel redox cycles

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• Stream biofilms collected• Cyclic aerobic and anaerobic conditions

imposed to mimic diel conditions in phototroph-dominated biofilms*

• Monitored soluble P, Fe, S, K, Mg, Mn• Measured PAO (DAPI staining and

fluorescence microscopy) in biofilms

*Diel oxygen trends in shallow lake sediments. (Carlton and Wetzel (1988) Limnology and Oceanography)

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Aerobic and anaerobic cycles induced P release during anaerobic periods (not observed in aerobic controls)

Saia et al. (In Review)

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Ca and K (counter ions used in polyphosphate granules) fluctuated with P, but Fe2+ and S (not shown) were stable

Saia et al. (In Review)

P trend not due to iron-reducing bacteria

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At the end of the experiment, more polyP-containing cells were detected in the aerobic biofilm

Saia et al. (In Review)

P trend may be due to PAO… P release from biofilm to water during anaerobic (i.e., night) conditions, uptake in biofilm during aerobic (i.e., light) conditions

Stream biofilms developed with variable P loads

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• Stream biofilms established using in situ enrichment system (vial with P-loaded agar and porous porcelain cap)

• Six different P loadings (incl. ambient)• Collected and analyzed for biomass and various

forms of P

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Increased P loadings did not affect biofilm biomass (Chl-a proxy), but did increase P storage as polyP

Taylor et al. (In Preparation)

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In biofilm P extracts, the polyP fraction increased from 12% at ambient P loading to 45% at max. P loading

Taylor et al. (In Preparation)

PIP – particulate inorganic PPOP – particulate organic P

Stream biofilms accumulate excess P largely as polyP

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Developing a method with lead nitrate staining and NanoSIMS quantification of polyP granules in diatoms

Molecular characterization of PAO in PA stream biofilms

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• Stream biofilms collected from six streams representing a range of geochemical conditions

Molecular characterization of PAO in PA stream biofilms

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• Intracellular polyP stained with DAPI• Biofilms dispersed• Putative PAOs separated with flow

cytometry and cell sorting• 16S rRNA genes of sorted cell fractions

sequenced with MiSeq

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Common Groups:• Ignavibacterium

album• Comamonadaceae• Thauera sp.• Pseudomonas

Sequencing of sorted (yellow) cells showed putative PAO populations

Locke et al. (In Preparation)

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0 100 200 300 400 500 600 700

Chlorophyll-a Measurement (mg/m2)

OligotrophicMesotrophic

Eutrophic

PAO community structures were similar among biofilms from oligotrophic streams (Burkholderiales dominated)

Locke et al. (In Preparation)

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0 100 200 300 400 500 600 700

Chlorophyll-a Measurement (mg/m2)

OligotrophicMesotrophic

Eutrophic

Locke et al. (In Preparation)

Similarly, PAO community structures were similar between biofilms from eutrophic streams

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0 100 200 300 400 500 600 700

Chlorophyll-a Measurement (mg/m2)

OligotrophicMesotrophic

Eutrophic

Locke et al. (In Preparation)

Interestingly, PAO similar to those that predominate many wastewater treatment systems was rare in all biofilm samples

Summary of stream biofilm studies

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• Polyphosphate-accumulating organisms are present in stream biofilm communities

• These PAO contribute to P storage within the biofilm and mobility within the biofilm and overlying waters

• PAO populations in stream biofilms are quite dissimilar from those enriched in enhanced biological phosphorus removal systems… physiology largely uncharacterized

Soil column studies to uncouple DIRB and PAO contributions to P uptake/release under variable saturation conditions

Analysis of P trends and metagenomic analysis of microbial communities

Soil sampling across a range of soil topographic index conditions

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Ongoing research on soil microbial processes

Acknowledgements

Nicholas Locke, Claudia Rojas, Miranda Stockton

USDA AFRI Grant #2014-67019-21636

Sheila Saia

Shayna TaylorKyle Elkin

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Based on flow cytometry data, putative PAOs comprised 13-38% of biofilm-derived particles (cells)

Locke et al. (In Preparation)