effects of nutrient nonpoint source pollution on seagrasses in redfish bay
DESCRIPTION
Effects of Nutrient Nonpoint Source Pollution on Seagrasses in Redfish Bay. Kelly Darnell GISWR Fall 2009. Eutrophication. Increase in nutrient concentration Coastal eutrophication increasing Anthropogenic impacts: nutrient nonpoint source (NPS) pollution - PowerPoint PPT PresentationTRANSCRIPT
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Effects of Nutrient Nonpoint Source Pollution on Seagrasses
in Redfish Bay
Kelly DarnellGISWR Fall 2009
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Eutrophication• Increase in nutrient concentration• Coastal eutrophication increasing
– Anthropogenic impacts: nutrient nonpoint source (NPS) pollution
• Negative effects on coastal organisms, systems– Decreased light irradiance, hypoxia, anoxia, decreased
water quality, stress species
www.marietta.edu
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Seagrasses
• Submerged marine plants• Ecosystem services
– Sediment stabilization, particle settlement, food, habitat, nursery proper ecosystem functioning
• High light requirements make seagrasses sensitive to decreased water quality
• Declining worldwide, TX– Anthropogenic impacts
www.dep.state.fl.us
www.unep-wcmc.org
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Seagrass Monitoring in Texas
• Dunton et al. (2005)– Monitoring program for seagrass health indicators
in Redfish Bay– Abiotic: water column nutrients, chlorophyll a,
total suspended solids (TSS), sediment nutrients– Biotic: seagrass cover, biomass, morphology
• Suggest input of nutrient NPS pollution– Water column nutrients
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Objectives
• Obtain a visual representation of suggested nutrient NPS pollution in Redfish Bay– Better understanding of NPS pollution inputs– Cascading effects on seagrasses
• Water column, sediment and seagrass nutrients, seagrass morphology – Dunton et al. (2005)
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Monitoring Sites: Redfish Bay, TX
• 30 sites• 2002-2005
– Summer data
Site 1
Site 30
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Phosphate (PO4): 2002-2005
• No clear trends
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Nitrate (NO3): 2002-2005
• No clear trends
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• Water column nutrients spatially and temporally variable
• Suggested nutrient NPS input in 2002
Phosphate and Nitrate:
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Water Column and Sediment Quality: 2002
1 6 11 16 21 260
5
10
15
20
25
30
f(x) = − 0.406155011278117 x + 14.0241711805539R² = 0.353337877988408
Total Suspended Solids by Site
Site
Tota
l Sus
pend
ed S
olid
Con
cent
ratio
n
1 6 11 16 21 260
0.20.40.60.8
11.21.41.61.8
2
f(x) = − 0.0231794586577679 x + 1.12311494252874R² = 0.220541742418652
Average Porewater Ammonium by Site
Site
Aver
age
Pore
wat
er N
H4 (u
M)
• TSS and average porewater NH4 higher in Northern part of Bay– TSS possibly
detrimental to seagrasses
– NH4 stimulate seagrass growth
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Seagrass Parameters:
2002• Dominant seagrass• Turtlegrass leaf
length and aboveground biomass slightly lower in Northern part of Bay– Seagrass may be
stressed
1 6 11 16 21 2605
101520253035404550
f(x) = 0.328351540088667 x + 24.9238567413289R² = 0.221138839726108
Average Turtlegrass Leaf Length
Site
Leaf
Leng
th (c
m)
1 6 11 16 21 260
50
100
150
200
250
300
350
f(x) = 2.60579688103101 x + 133.345673781427R² = 0.0516306401020048
Average Turtlegrass Aboveground Biomass
Site
Abov
egro
und
Biom
ass (
g DW
m−2
)
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Conclusions So Far
• Results support existence of nutrient NPS pollution in Redfish Bay
• Results suggest seagrass may be negatively affected by indicated NPS pollution
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Future Plans
• Compare nutrient inputs to local precipitation– Obtain an indication of runoff
• Visually represent:– Water column nutrient concentrations by site– Seagrass leaf nutrients by site and year– Seagrass above- and below-ground biomass
by site and year
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Questions?
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Sources
• Dunton KH, Kopecky AL, Maidment D (2005) Monitoring design criteria and biological indicators for seagrass conservation in Texas coastal waters. Final Report for Regional Environmental Monitoring and Assessment Program, EPA
• Texas World Imagery Basemap obtained from ESRI (resources.esri.com)