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De-vegetated marshes may contribute reactive nitrogen to urban estuaries"..pptx
De-vegetated marshes may contribute reactive nitrogen to urban estuaries"..pptx
ecowatchers
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Jun 24, 2024
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About This Presentation
what effect does a de-vegetated marsh have on an urban estuary in terms of nitrogen release
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46.48 MB
Language:
en
Added:
Jun 24, 2024
Slides:
16 pages
Slide Content
Slide 1
De-vegetated Marshes May
Contribute Reactive Nitrogen
to Urban Estuaries
Beryl C.M. Kahn,
Baruch College/The Graduate Center, City University of New York
Jamaica Bay Task Force Meeting
18 June 2024
BaruchcOLEGE
Slide 2
Jamaica Bay Marsh Restoration
Allows for Ecosystem Service
Recovery
Marshes naturally provide:
* Protection against flooding/wave action
* Carbon storage
+ Habitat for birds, fish, invertebrates
* Nitrogen (N) removal through denitrification
+ Over time, restored marshes in Jamaica Bay
perform comparable services to natural marshes
e
Photo by C. Zarnoch
Slide 3
With time, denitrification rates in restored marshes
resemble natural marshes
Jamaica Bay
Hempstead Bay (Zamoch et al, NYSG)
Other studies:
White and Howes 1994 = ~75 umol N m2 hr
(Cape Cod, MA)
Piehler and Smyth 2011 = ~100ymol N m2 h*
(Bogue Sound, NC)
Zarnoch et al. 2016
Slide 4
In restored marshes: denitrification rate corresponds with
belowground biomass
Site
Yellow Bar
Elders West
Elders East
e Joco
Belowground Biomass (g m“)
Zarnoch et al. 2017
Slide 5
Restored marshes act as a sink for dissolved
inorganic nitrogen (DIN)
Yellow Bar (YB) = 3 y/o
Elders East (EE) = 9 y/o
* Negative flux =
DIN uptake
* Marsh sediment
is a DIN sink
e
=
z
3
a y
=
[re
Z
a
Oct 2015
Zarnoch etal. 2016
Slide 6
Jamaica Bay Marshes Experience Rapid Erosion and
Loss
+ Estimates of ~85% of area lost over
the past century
Losses driven by multiple potential factors:
o Sea level rise
o Nloading
o Changes to sediment deposition
* Subsequent changes to N cycling
processes?
Slide 7
How do N cycling processes differ between degraded and intact
(vegetated) marsh sediments?
Eroding Marsh Edge
Nitrification-
Denitrification
Slide 8
Intact (Vegetated) Marsh
(n= 4/site)
Eroded (De-vegetated) Marsh
Peat (n = 4/site)
RSS
Slide 9
Methods: Continuous-Flow
Sediment Core Incubations
and Analysis
Cores fitted with airtight seals
Site water pumped through cores
Compare nutrient content, dissolved
gases between inflow/outflow
Dissolved gases measured on
membrane-inlet mass spectrometer
(MIMS)
+ Dissolved nutrients measured on auto-
analyzer
Slide 10
Results: Denitrification Response to Marsh
Loss
+ Denitrification did not
differ between
vegetated/de-vegetated
marshes
No Flux (umol N m?h-")
Slide 11
Rate (umol N mh-1)
Lenitrinicauon
Keacuve N EMUX
600;
400;
200:
-200
BB
+ De-vegetated marshes:
reactive N efflux ~2x as
high as denitrification
Possible explanations:
+ Lower microbial
assimilation in de-vegetated
sediment
Changes to chemistry
because of decomposition
Slide 12
DIN Flux (umol N m2h-')
2
8
=
300;
>
>
20 30 40
Belowground Biomass (g dry wt)
50
site
88
© swe
MarshType
A Degraded
O intact
Belowground biomass is
significantly lower in
degraded marsh sediments
(p < 0.001)
Reactive N flux negatively
correlates with belowground
biomass (p = 0.015)
Slide 13
Management Takeaways: Marsh Loss and N Release
Net N released: ~250 pmol m?h?
+ 1,400 acres of Jamaica Bay marshes lost over the past century
Daily reactive N contributions from degraded former marsh
areas in summer: 1,100 lbs N day”
+ Continued losses likely to perpetuate eutrophic conditions
« Marsh restoration will likely recover N sink capacity
Slide 14
Appendix
Tags
jamaica bay
nitrogen loading
Categories
Technology
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