figure 1: six tidal marshlands: hutchinson river, ……2016/12/06  · figure 6: average of the...

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From our data, we concluded that vegetative coverage has a positive correlation with erosion along the coast of tidal wetlands. Furthermore, when we compare Figures 4 and 6, the sites that possess a lower percentage of vegetative cover at Pin 1 are also generally losing soil. This means that the abundance of vegetation in the area has an influence on how creek banks are gaining vegetation or eroding away. This is consistent with our hypothesis because we predicted that areas with more vegetation would have less erosion. Fordham University Wildlife Conservation Society New York City Department of Parks and Recreation Christopher Haight, Project Manager Figure 1: Six tidal marshlands: Hutchinson River, Pelham Bay Cove, Udall’s Cove, Spring Creek, Idlewild, and Saw Mill Creek. How does vegetation abundance affect erosion levels? If there is more vegetation abundance, then there is less erosion. New York City (NYC) has roughly 4,000 acres of tidal marshlands that help filter polluted water from the city. 1 We visited six wetlands, where there had been monumental vegetation loss along the riverbanks amounting to a total of 53 acres or 18%. In other words, NYC has lost more than 80% of its historic marsh coverage over the past 40 years. The New York City Department of Parks & Recreation (NYCDPR) conducted an analysis to determine marsh loss from 1974-2012. 2 The data from this research allows the NYCDPR to implement management and support restoration projects. These projects will make NYC’s coastal habitats more resilient to future Sea-Level Rise (SLR) 3 , specifically by restoring the lost marsh edges. This summer we had the opportunity to work alongside the NYCDPR to continue these erosion studies. Hypothesis Introduction Research Question The purpose of this study was to gather more information about how vegetative coverage relates to erosion levels. We worked with the NYCDPR to analyze the erosion facing coastal wetlands today. Specifically, our group wanted to understand how vegetation affects erosion levels, in order to anticipate how the marshes will respond to global change factors. Objective a) We aligned transects (measuring tape) perpendicular to shoreline orientation at 5 sites comparative to Surface Elevation Table (SET) locations. b) 3 Erosion Pins (Rebar) were later positioned along transects. c) Erosion Pins were located: 0m from shore, 3m from shore, and 6m from shore inland towards vegetation. a) Percent cover of various plant species, bare ground, and garbage were monitored in 1 x 1 m quadrats centered over Erosion Pins. b) Each quadrat was assessed using percent cover estimate averages to determine the cover by individual species and non-vegetation. Erosion Pin Protocol Vegetation Coverage Methods Discussion/Conclusion Acknowledgements The Relationship Between Vegetative Coverage and Erosion Levels in NYC Wetlands Fig. 1 Fig. 3 Fig. 2 Fig. 4 Fig. 5 Fig. 6 Pic 1 Pic 2 Pic 3 Ife Adelona, Catherine Lawrence, Chloe Wong, Chris Haight, and Lily Mleczko with Fordham University, the Wildlife Conservation Society and the New York City Department of Parks and Recreation 1 Elmqvist, T., Fragkias, M., Goodness, J., Güneralp, B., Marcotullio, P., McDonald, R. I., . . . Wilkinson, C. (2013). Urbanization, biodiversity and ecosystem services: Challenges and opportunities: A global assessment. New York, NY: Springer Dordrecht Heidelberg. 2 Hartig, E.K., Haight, C., Swadek, R., Larson, M.,& Boger, R. (2016, June). Monitoring and Restoration of New York City’s Receding Salt Marshes. Poster presented at the Society of Wetland Scientists, Corpus Christi, TX. 3 McPhearson, T., D. Maddox, et. al. 2013. Local assessment of New York City: Biodiversity, green space, and ecosystem services. In Cities and biodiversity outlook: Urbanization, biodiversity and ecosystem services: Challenges and opportunities, ed. T. Elmqvist, M. Fragkias, J. Goodness, B. Gu¨neralp, P.J. Marcotullio, R.I. McDonald, S. Parnell, et al., pp. 355–383. Dordrecht: Springer Netherlands. Citation Figure 2: Total Percent cover of vegetation vs. distance vegetative edge has shifted. Figure 3: Distance to vegetative edge vs. percentage coverage of soil. There is more bare ground further from the vegetation line. Figure 4: Percent coverage of total vegetation in each of the sites.. Figure 5: Average distance from the vegetative edge in each of the sites. Figure 6: Average of the total vegetation in the quadrat placed around erosion pin 1 in each of the six sites. Figure 1: Map of 6 tidal marshlands Picture 1: Quadrat set up around erosion pin at Saw Mill Creek Picture 2: Receding shoreline at Saw Mill Creek. Picture 3: Cat, Chloe, and Ife monitoring vegetative coverage in Idlewild. Our research this summer has helped us gain a better understanding of the erosion present in New York City’s salt marshes. Moving forward, we believe that marshes could be restored by supplementing sediment to the water edge and planting native vegetation to increase the stability of the surrounding soil. Future efforts of the NYCDPR should focus on increasing public awareness regarding the function and pivotal importance of salt marshes. Our team noted the vast amount of garbage present in the tidal marshes during our field research. The NYCDPR could implement cleanup events in collaboration with the local communities. Next Steps/Management

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Page 1: Figure 1: Six tidal marshlands: Hutchinson River, ……2016/12/06  · Figure 6: Average of the total vegetation in the quadrat placed around erosion pin 1 in each of the six sites

From our data, we concluded that

vegetative coverage has a positive

correlation with erosion along the coast

of tidal wetlands. Furthermore, when

we compare Figures 4 and 6, the sites

that possess a lower percentage of

vegetative cover at Pin 1 are also

generally losing soil. This means that

the abundance of vegetation in the area

has an influence on how creek banks

are gaining vegetation or eroding away.

This is consistent with our hypothesis

because we predicted that areas with

more vegetation would have less

erosion.

Fordham University

Wildlife Conservation Society

New York City Department of Parks and Recreation

Christopher Haight, Project Manager

Figure 1: Six tidal marshlands: Hutchinson River,

Pelham Bay Cove, Udall’s Cove, Spring Creek, Idlewild,

and Saw Mill Creek.

How does vegetation abundance affect erosion

levels?

If there is more vegetation abundance, then there

is less erosion.

New York City (NYC) has roughly 4,000 acres of

tidal marshlands that help filter polluted water

from the city.1 We visited six wetlands, where there

had been monumental vegetation loss along the

riverbanks amounting to a total of 53 acres or 18%.

In other words, NYC has lost more than 80% of its

historic marsh coverage over the past 40 years. The

New York City Department of Parks & Recreation

(NYCDPR) conducted an analysis to determine

marsh loss from 1974-2012.2 The data from this

research allows the NYCDPR to implement

management and support restoration projects.

These projects will make NYC’s coastal habitats

more resilient to future Sea-Level Rise (SLR)3,

specifically by restoring the lost marsh edges. This

summer we had the opportunity to work alongside

the NYCDPR to continue these erosion studies.

Hypothesis

Introduction

Research Question

The purpose of this study was to gather more

information about how vegetative coverage

relates to erosion levels. We worked with the

NYCDPR to analyze the erosion facing coastal

wetlands today. Specifically, our group wanted

to understand how vegetation affects erosion

levels, in order to anticipate how the marshes

will respond to global change factors.

Objective

a) We aligned transects (measuring tape) perpendicular to shoreline orientation at 5 sites comparative to

Surface Elevation Table (SET) locations.

b) 3 Erosion Pins (Rebar) were later positioned along transects.

c) Erosion Pins were located: 0m from shore, 3m from shore, and 6m from shore inland towards vegetation.

a) Percent cover of various plant species, bare ground, and garbage were monitored in 1 x 1 m quadrats

centered over Erosion Pins.

b) Each quadrat was assessed using percent cover estimate averages to determine the cover by individual

species and non-vegetation.

Erosion Pin Protocol

Vegetation Coverage

Methods Discussion/Conclusion

Acknowledgements

The Relationship Between Vegetative Coverage and Erosion Levels in NYC Wetlands

Fig. 1

Fig. 3 Fig. 2

Fig. 4 Fig. 5 Fig. 6

Pic 1 Pic 2 Pic 3

Ife Adelona, Catherine Lawrence, Chloe Wong, Chris Haight, and Lily Mleczko

with Fordham University, the Wildlife Conservation Society and the New York City Department of Parks and Recreation

1Elmqvist, T., Fragkias, M., Goodness, J., Guneralp, B., Marcotullio, P., McDonald, R. I., . . .

Wilkinson, C. (2013). Urbanization, biodiversity and ecosystem services: Challenges and

opportunities: A global assessment. New York, NY: Springer Dordrecht Heidelberg. 2Hartig, E.K., Haight, C., Swadek, R., Larson, M.,& Boger, R. (2016, June). Monitoring and

Restoration of New York City’s Receding Salt Marshes. Poster presented at the Society of

Wetland Scientists, Corpus Christi, TX. 3McPhearson, T., D. Maddox, et. al. 2013. Local assessment of New York City: Biodiversity,

green space, and ecosystem services. In Cities and biodiversity outlook: Urbanization, biodiversity

and ecosystem services: Challenges and opportunities, ed. T. Elmqvist, M. Fragkias, J. Goodness,

B. Gu¨neralp, P.J. Marcotullio, R.I. McDonald, S. Parnell, et al., pp. 355–383. Dordrecht:

Springer Netherlands.

Citation

Figure 2: Total Percent cover of vegetation vs. distance vegetative edge has shifted. Figure 3: Distance to vegetative edge vs. percentage coverage of soil. There is more bare ground further from the vegetation line.

Figure 4: Percent coverage of total vegetation in each of the sites.. Figure 5: Average distance from the vegetative edge in each of the

sites.

Figure 6: Average of the total vegetation in the quadrat placed around erosion pin 1 in each of the six sites.

Figure 1: Map of 6 tidal marshlands

Picture 1: Quadrat set up around erosion pin at Saw Mill

Creek Picture 2: Receding shoreline at Saw Mill Creek.

Picture 3: Cat, Chloe, and Ife monitoring vegetative coverage in Idlewild.

Our research this summer has helped

us gain a better understanding of the

erosion present in New York City’s salt

marshes. Moving forward, we believe

that marshes could be restored by

supplementing sediment to the water

edge and planting native vegetation to

increase the stability of the

surrounding soil. Future efforts of the

NYCDPR should focus on increasing

public awareness regarding the

function and pivotal importance of salt

marshes. Our team noted the vast

amount of garbage present in the tidal

marshes during our field research. The

NYCDPR could implement cleanup

events in collaboration with the local

communities.

Next Steps/Management