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Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge, Michael R. Burchell II, François Birgand Site Location North River N Restoration Goals Improve water quality in the North River Restore habitat Provide design guidance for future salt marsh projects in coastal North Carolina

J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

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Page 1: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Continuously monitoring flow, carbon, and nitrogen in a

restored North Carolina salt marsh

J. Randall Etheridge, Michael R. Burchell II, François Birgand

Site Location

Nor

th

Riv

er

N

Restoration Goals

• Improve water quality in the North River

• Restore habitat• Provide design

guidance for future salt marsh projects in coastal North Carolina

Page 2: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

N

300 ft

Construction

Restoration Research Objectives

• Quantify the ability of a restored salt marsh to dissipate excess nutrients

• Quantify the timing and kinetics of nutrient dissipation and/or release

• Correlate the dissipation and/or release of nutrients to the type of organic matter

Page 3: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Method

• Continuous nutrient mass balance between inlet and outlet

• Sediment-water interface process kinetics experiments

• Qualify nature of organic matter using fluorescence measurements

Method

• Continuous nutrient mass balance between inlet and outlet

• Sediment-water interface process kinetics experiments

• Qualify nature of organic matter using fluorescence measurements

Upstream/Downstream Monitoring

P

P

300 ft

N

PNew Flume

New WQ Probe

Flow Control Fence

Flow Monitoring in a Tidal Stream• Cannot use normal

rating curve due to bi-directional flow

• Flumes serve as a constant cross section – cross section area measurement creates the most error in flow monitoring

Downstream flume between tides

Downstream flume at high tide

Page 4: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Flow CalculationsQ = V x A

– Q: flow– V: velocity– A: cross-section area

A

A

Continuous Flow Monitoring

• Doppler velocity meter records velocity and water depth in flume

• Average velocity and water depth recorded every 15 minutes

• Use manual stream gagingto relate Doppler velocity to actual flow in the flume

Doppler velocity meter in the flume bottom

Manual Stream Gaging

Flow Calibration

y = 0.9889xR² = 0.9856

0.000

0.050

0.100

0.150

0.200

0.250

0.300

0.350

0 0.2 0.4

Vmea

n (m

/s)

Vcenter (m/s)

Vi Vc

40% of the depth

Doppler meter

Flow Monitoring in a Tidal Stream• One challenge presented in

the marsh: high tide or water level above the flumes

• Solution: direct flow through the flume using impermeable fence

Page 5: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Downstream Flume

-0.5

-0.4

-0.3

-0.2

-0.1

0

0.1

0.2

0.3

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

Velo

city

(m/s

)

Stag

e (m

)

Stage and VelocityLevelVelocity

Downstream Flume Flow

-0.15

-0.1

-0.05

0

0.05

0.1

0.15

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

Flow

(m3 /s

)

Continuous Water Quality MonitoringParameter Max (mg/L) Resolution

(±mg/L)NO3

-N 70 0.1TOC 150 0.2DOC 90 0.2

• Monitored using UV-visual spectrophotometer placed in the stream

• Absorption spectrum and parameters measured every 15 minutes

Continuous Water Quality Monitoring

0

50

100

150

200

250

300

350

200 300 400 500 600 700Wavelength (nm)

Absorption Spectra

High NO3-NLow NO3-N

Page 6: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Downstream Flume – Daily Sample

0

0.5

1

1.5

2

2.5

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

NO

3-N

(mg/

L)

Nitrate Concentration

Downstream Flume – 15 minute sample interval

0

0.5

1

1.5

2

2.5

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

NO

3-N

(mg/

L)

Nitrate Concentration

Downstream Flume

-0.15

-0.1

-0.05

0

0.05

0.1

0.15

0

0.5

1

1.5

2

2.5

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

Flow

(m3 /s

)

NO

3-N

(mg/

L)

Nitrate Concentration and FlowNO3-NFlow

Downstream Flume

-0.15

-0.1

-0.05

0

0.05

0.1

0.15

5

10

15

20

25

30

35

01/03/2011 02/03/2011 03/03/2011 04/03/2011 05/03/2011 06/03/2011 07/03/2011 08/03/2011 09/03/2011

Flow

(m/s

)

DO

C (m

g/L)

DOC Concentration and FlowDOCFlow

Page 7: J. Randall Etheridge, Michael R. Burchell II, François Birgand · Continuously monitoring flow, carbon, and nitrogen in a restored North Carolina salt marsh J. Randall Etheridge,

Challenges of Continuous Water Quality Monitoring

• Calibration• Preventing/reducing

window fouling• Solar power

Future Research

• Continuously monitor:– pH– Conductivity/Salinity– Dissolved Oxygen– DOM Fluorescence

Future Research

For more information on our future work with organic matter see this poster:Mikan et al., Chromophoric Dissolved and

Particulate Organic Matter Cycling Through a Tidally Influenced Restored Marsh Ecosystem in Eastern North Carolina

Acknowledgements• North Carolina Coastal Federation• United States Environmental Protection Agency• North Carolina Sea Grant/North Carolina Water Resources Research

Institute• North Carolina Ecosystem Enhancement Program• NSF Graduate Research Fellowship Program• Equipment Installation:

– Spencer Davis– Brad Smith– Guillaume Lellouche

• Collaborators:– Dr. Chris Osburn – NCSU Marine, Earth, & Atmospheric Sciences– Molly Mikan

• Others:– Phil Harris (Electronics)– Kris Bass (Installation and site design)– Evan Corbin (Previous research)