Eutrophication effects of sulfate reduction in lakes and ...

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Nov 16, 2017 - 4. 2- concentration to NE MN. • < 10 mg/L SO. 4. 2- very sensitive to ... methylmercury accumulation by liquid calcium nitrate amendment: redox.
Eutrophication effects of sulfate reduction in lakes and reservoirs: Case studies and foundations

David Austin, P.E., Senior Ecologist ESA SETAC Minneapolis, Minnesota November 16, 2017

Overview

• Regional sulfate concentrations • Sulfate reduction: mechanism of impacts • Sulfate reduction remediation: case studies • Synopsis and prognosis

MN sulfate in surface waters • Most of Lake Superior Laurentian Shield drainage similar SO42concentration to NE MN • < 10 mg/L SO42- very sensitive to sulfate enrichment

Effect of SO42- reduction on WQ Anoxic positive feedback:

Anoxic negative feedback:

Fe, Mn, PO4, NH4, Hg-CH3

SO4

Mercury methylation efflux to water column starts here Lake Ann, Chanhassen, MN. 8oC, 14 m depth Austin et al. 2016. Suppression of hypolimnetic methylmercury accumulation by liquid calcium nitrate amendment: redox dynamics and fate of nitrate. Lake and Reservoir Management. 32(1):61-73.

6 900 Non-linear sediment efflux induced Lake Ann Data 800 by anoxia Fe-dissolved, mg/L 5

700

NH3-N, mg/L

4

3

Fe-dissolved, mg/L

NH3-N, mg/L

600

• Exponential time scale of nutrient release at 8oC • ~4x faster at 20oC • ~5x at 25oC • ~6x at 30oC

500 400 300

2

200

29-Sep

1-Sep

4-Aug

9-Jul

16-Jun

1

100 5

Temperature dependence of sulfate reduction O2 H2S

COOL/COLD SEDIMENTS

• Deep, cold sediments: O2 depletion rate delays onset of nutrient release • Shallow, cool sediments: o O2 regularly replenished o Nutrient release quenched

O2

H2S WARM SEDIMENTS Ingvorsen et al, 1982

• H2S production at 25oC is 5 times over 10oC • Shallow, warm sediments o H2S flux out of sediments > O2 flux in o Rapid, positive feedback release of nutrients

Sulfate reduction “bottom up” biogeochemical cascade effect on water quality

-

HgCH3+

ALGAE BLOOMS -

CYANOTOXINS

TASTE & ODOR

+

-

SULFATE REDUCTION

+

H2S, Mn, Fe, NH4+

+

Reservoir water quality 101 – The big problems

Poor WQ from any level

High TP, cyanobacteria, Temp, and pH Thermocline Intake Pipe

Anoxia

High Fe, Mn, NH4+ and H2S

Reservoir management 101 – Big solutions

Good WQ from any level

Low TP, lower algae, lower pH, high Temp. Thermocline Intake Pipe

High D.O.

Very low Fe, Mn, NH4+ and H2S, neutral pH

Hypolimnetic oxygenation

Case Study: Saint Paul Regional Water Services, Minnesota Average 50 MGD (189 MLD)  PLEASANT LAKE

Side stream reservoirs, historic poor water quality requiring remediation – Hypolimnetic aeration (HA) + FeCl3:

• Pleasant: 1994 - 2006 • Vadnais: 1987 - 2010 – Hypolimnetic oxygenation (HO) + FeCl3 :

• Pleasant: 2013 - Present • Vadnais: 2011 - Present

Pre-oxygenation

Pre-oxygenation

Hypolimnion Mn, Fe 4

5

3.5

3

2

1

3 Fe, mg/L

Mn, mg/L

4

2.5 2 1.5 1 0.5

0

0

Total phosphorus Hypolimnion 3 2.5

TP, mg/L

2 1.5 1 0.5 0

• TP release from sediments integral part of redox system • Quenching SO42- reduction sharply reduces internal TP loading

Shamrock Reservoir, Georgia

Bottom TP, mg/L

5 4

• Hypereutrophic

3

• Internal TP loading

2

almost entirely a

1

function of SO42-

0 30

reduction 25 20 15 10 5 Bottom sulfate, mg/L

0

Shamrock Reservoir cyanobacteria

SO42- reduction is ecosystem forcing function

8

Cyanobacteria, cells/ml

3.5 10

3 108

• No SO42- reduction →

2.5 108

no blooms

8

2 10

• High SO42- reduction

1.5 108

→ bloom trigger

8

1 10

• Why? Cyanobacteria

7

5 10

0 30

sink into nutrient-rich 25 20 15 10 5 Bottom sulfate, mg/L

0

anoxic water and then float to surface.

Synopsis • Sulfate reduction is a fundamental ecosystem forcing function o Eutrophication o Mercury methylation o Harmful algae blooms / cyanotoxin potential

• Quenching sulfate reduction: engineering design basis for WQ remediation if sediment surface is anoxic o Reversal of eutrophication o Sharp reduction of potential for harmful algae blooms

Outlook for upper Great Lakes • Lake Superior watershed aqueous biogeochemistry is sulfate-limited • Sulfate enrichment consequences: o Non-linear amplification of internal nutrient loading o Accelerated eutrophication o Deterioration of H2S sensitive habitat

• Global warming will amplify effects of sulfate enrichment • Prognosis:

o Unequivocal scientific grounds for concern over sulfate enrichment o Site-specific remediation of sulfate-impacted lakes feasible o Regional impacts require regulatory intervention

Questions?