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How does excessive nitrogen
loading effect the health and
resiliency of Long Island’s
coastal ecosystems?
Christopher J. Gobler
“Nitrogen is the critical limiting factor to
primary producers in Long Island coastal
marine waters”
– Dr. John Ryther, Woods Hole Oceanographic Institute,
Science Magazine, 1971
Population, Suffolk County, NY, USA
0
200,000
400,000
600,000
800,000
1,000,000
1,200,000
1,400,000
1,600,000
1900 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2010
Population
New
York
City
>25,000,000 lbs of nitrogen per year from human waste
Septic tank
Water table
/ aquifer
Nitrogen
In Suffolk County:
• 70% of homes have
septic tanks or
cesspools.
• ~70% of N loads come
from septic tanks and
cesspools.
Loading of wastewater
nitrogen to coastal waters
Nitrogen
Groundwater
flow
0
1
2
3
4
1987 2005
Nitrogencontent(mg/L)
Glacial Magothy
Changes in groundwater nitrogen levels in Suffolk County
40%
increase
200%
increase
Suffolk County Comprehensive Water Resources management plan, 2010
N loads to Great South Bay from watershed
•~70% of N entering Moriches and Shinnecock Bay is from wastewater
(Gobler et al, in progress for NYSDOS).
Kinney and Valiela, 2011
Septic
tanks,
cesspools
Atmosphere
Fertilizer
> 22
18
12
6
< 0.3
4.8
4.8
2.8 2.8
3.1
2.4
3.0
Groundwater nitrogen concentrations,
Eastern Bays
Total N mg L-1
> 22
18
12
6
< 0.3
Groundwater N and buildings
Total N mg L-1
> 22
18
12
6
< 0.3
Groundwater N and agriculture
Total N mg L-1
Pine Barrens
South shore bay nitrogen loads
compared to other water bodies
NYSDEC assessment of Long Island coastal waters
Impaired
Minor impacts
No known impacts
What impairments are brought about by
excessive nitrogen loading?
• Loss of critical habitats: Eelgrass, salt marshes
• Low dissolved oxygen levels, hypoxia
• Acidification, low pH
• Macroalgal blooms: Sea lettuce, Ulva
• Toxic algal blooms: Red, rust, brown tides
• Loss or depletion of shellfisheries and finfisheries
The vital role of salt marshes in coastal
ecosystems and communities
Salt marsh ecosystems
Salt marshes protect coastlines
Chris Bason, Delaware Center for the Inland Bays
Salt marshes protect coastlines
Healthy marsh Nitrogen loaded marsh
“Coastal eutrophication as a driver of salt marsh loss”, Deegan et al 2012, Nature
Dense,
strong
roots
Nutrient
weakened,
roots
0
10
20
30
40
50
60
70
80
90
Manhasset,KingsPoint
Manhasset,PlumPoint
Manhasset,ManorHaven
SouthManhassetBay
NissequogueRiver
StonyBrookHarbor
FlaxPond
MountSinaiHarbor
Peconics,CoreyCreek
Peconics,CedarBeachCreek
SouthOysterBay,GilgoIs.
SouthOysterBay,GooseIs.
WesternBays,MiddleBay
WesternBays,EastBay
Percentlosssince1974
Loss of wetlands on Long Island, since 1974
NYSDEC survey data
Nassau County, North Shore
Suffolk County, North Shore
East end
Suffolk County
South Shore
Nassau County
South Shore
Salt marsh loss, Jamaica Bay
Flooding during
Hurricane Sandy
Flooding in Mastic – Shirley during
Hurricane Sandy
Salt
marsh
Salt
marsh
Each point is a home.
Flooding in Mastic – Shirley, sea level rise
Salt
marsh
Each point is a home.
Flooding scenarios will worsen significantly with weakened
or destroyed salt marshes.
Salt
marsh
Eelgrass:
Critical benthic
habitat
NYS seagrass, 1930 - 2030
NYSDEC Seagrass Taskforce Final Report, 2010; Suffolk County assessment, 2014
0
50,000
100,000
150,000
200,000
1930 2009 2030
Acresofseagrass
90% loss
Extinction in NY
Increasing Nitrogen Loading
Take a deep breath…
Oxygen (O2)
Carbon dioxide (CO2)
Phytoplankton
CH2O + O2 CO2 + H2O
Respiration
Nitrogen loading leads to low oxygen and high CO2
Nitrogen loading
Consumed Produced
Dissolved oxygen (mg L¯¹)
pCO2 (µatm)
Long Island Sound, August 2013
The Forge River, NY, USA
0
1
2
3
4
7
7.1
7.2
7.3
7.4
7.5
7.6
6/30/2012 7/10/2012 7/20/2012 7/30/2012 8/9/2012 8/19/2012
Dissolvedoxygen
(mgL-1)
pH(totalscale)
pH Dissolved oxygen
Effects of high CO2 and low O2 on fish survival
0
10
20
30
40
50
60
70
80
90
Control Low pH Low DO Low pH, Low DO
%Survival
Larval Inland Silversides
High CO2 Low O2 High CO2, low O2
Samples for eelgrass genetic analysesHarmful algal blooms across Long Island
PSP, DSP PSP,
DSP
Cochlodinium
Cochlodinium
Cochlodinium
PSP
Brown tideCochlodinium PSP, red tide DSP, red tide
PSP
PSP
Toxic blue green algae
Toxic blue greens Toxic blue greens
Ulva
Ulva
Ulva
DSP
Samples for eelgrass genetic analyses
Aureococcus
‘Brown tide’
Cochlodinium
‘Rust tide’
Alexandrium
‘Red tide – PSP’
Dinophysis
‘Red tide – DSP’
Enhanced nutrient loading more intense &/or toxic HABs
Gobler et al
2012
Gobler et al
2011;
Gobler and
Sunda 2012
Hattenrath
et al 2010
Hattenrath-
Lehmann 2014
Microcystis
‘Blue green algae’
Harke and
Gobler, 2013
Alexandrium red tides and paralytic shellfish
poisoning (PSP)
Alexandrium
Saxitoxin
Presence of PSP-producing Alexandrium
in NY: 2007-2013
= cells not detected
= < 100 cells L-1
= > 1,000 cells L-1
= 100 - 1,000 cells L-1
**circles represent the highest observed densities at each site**
• Alexandrium found at 47 of 63 sites samples (75%)
Waste
water
N
“Sewage-derived nitrogen loading promotes
intense and toxic Alexandrium blooms.”
Nitrogen impacts on shellfish
• Landings of clams and scallops have declined 99% since 1980.
• Linkages to nitrogen driven HABs, habitat loss, and water quality
degradation.
0
100,000
200,000
300,000
400,000
500,000
600,000
700,000
800,000
1970
1972
1974
1976
1978
1980
1982
1984
1986
1988
1990
1992
1994
1996
1998
2000
2002
2004
2006
Hard clam landings (bushels) in Great South Bay
Conclusion:
Excessive nitrogen loading leads to…
• Loss of critical habitats: Salt marshes, eelgrass
• Low dissolved oxygen levels, hypoxia
• Acidification, low pH
• Macroalgal blooms: Sea lettuce, Ulva
• Toxic algal blooms: Red, rust, brown tides
• Loss or depletion of shellfisheries and finfisheries

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Nitrogen Pollution and The Future of Long Island By Prof. Christopher Gobler

  • 1. How does excessive nitrogen loading effect the health and resiliency of Long Island’s coastal ecosystems? Christopher J. Gobler
  • 2. “Nitrogen is the critical limiting factor to primary producers in Long Island coastal marine waters” – Dr. John Ryther, Woods Hole Oceanographic Institute, Science Magazine, 1971
  • 3. Population, Suffolk County, NY, USA 0 200,000 400,000 600,000 800,000 1,000,000 1,200,000 1,400,000 1,600,000 1900 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2010 Population New York City >25,000,000 lbs of nitrogen per year from human waste
  • 4. Septic tank Water table / aquifer Nitrogen In Suffolk County: • 70% of homes have septic tanks or cesspools. • ~70% of N loads come from septic tanks and cesspools. Loading of wastewater nitrogen to coastal waters Nitrogen Groundwater flow
  • 5. 0 1 2 3 4 1987 2005 Nitrogencontent(mg/L) Glacial Magothy Changes in groundwater nitrogen levels in Suffolk County 40% increase 200% increase Suffolk County Comprehensive Water Resources management plan, 2010
  • 6. N loads to Great South Bay from watershed •~70% of N entering Moriches and Shinnecock Bay is from wastewater (Gobler et al, in progress for NYSDOS). Kinney and Valiela, 2011 Septic tanks, cesspools Atmosphere Fertilizer
  • 7. > 22 18 12 6 < 0.3 4.8 4.8 2.8 2.8 3.1 2.4 3.0 Groundwater nitrogen concentrations, Eastern Bays Total N mg L-1
  • 8. > 22 18 12 6 < 0.3 Groundwater N and buildings Total N mg L-1
  • 9. > 22 18 12 6 < 0.3 Groundwater N and agriculture Total N mg L-1 Pine Barrens
  • 10. South shore bay nitrogen loads compared to other water bodies
  • 11. NYSDEC assessment of Long Island coastal waters Impaired Minor impacts No known impacts
  • 12. What impairments are brought about by excessive nitrogen loading? • Loss of critical habitats: Eelgrass, salt marshes • Low dissolved oxygen levels, hypoxia • Acidification, low pH • Macroalgal blooms: Sea lettuce, Ulva • Toxic algal blooms: Red, rust, brown tides • Loss or depletion of shellfisheries and finfisheries
  • 13. The vital role of salt marshes in coastal ecosystems and communities
  • 15. Salt marshes protect coastlines Chris Bason, Delaware Center for the Inland Bays
  • 16. Salt marshes protect coastlines
  • 17. Healthy marsh Nitrogen loaded marsh “Coastal eutrophication as a driver of salt marsh loss”, Deegan et al 2012, Nature Dense, strong roots Nutrient weakened, roots
  • 19. Salt marsh loss, Jamaica Bay
  • 21. Flooding in Mastic – Shirley during Hurricane Sandy Salt marsh Salt marsh Each point is a home.
  • 22. Flooding in Mastic – Shirley, sea level rise Salt marsh Each point is a home. Flooding scenarios will worsen significantly with weakened or destroyed salt marshes. Salt marsh
  • 24. NYS seagrass, 1930 - 2030 NYSDEC Seagrass Taskforce Final Report, 2010; Suffolk County assessment, 2014 0 50,000 100,000 150,000 200,000 1930 2009 2030 Acresofseagrass 90% loss Extinction in NY Increasing Nitrogen Loading
  • 25. Take a deep breath… Oxygen (O2) Carbon dioxide (CO2)
  • 26. Phytoplankton CH2O + O2 CO2 + H2O Respiration Nitrogen loading leads to low oxygen and high CO2 Nitrogen loading Consumed Produced
  • 27. Dissolved oxygen (mg L¯¹) pCO2 (µatm) Long Island Sound, August 2013
  • 28. The Forge River, NY, USA 0 1 2 3 4 7 7.1 7.2 7.3 7.4 7.5 7.6 6/30/2012 7/10/2012 7/20/2012 7/30/2012 8/9/2012 8/19/2012 Dissolvedoxygen (mgL-1) pH(totalscale) pH Dissolved oxygen
  • 29. Effects of high CO2 and low O2 on fish survival 0 10 20 30 40 50 60 70 80 90 Control Low pH Low DO Low pH, Low DO %Survival Larval Inland Silversides High CO2 Low O2 High CO2, low O2
  • 30. Samples for eelgrass genetic analysesHarmful algal blooms across Long Island PSP, DSP PSP, DSP Cochlodinium Cochlodinium Cochlodinium PSP Brown tideCochlodinium PSP, red tide DSP, red tide PSP PSP Toxic blue green algae Toxic blue greens Toxic blue greens Ulva Ulva Ulva DSP
  • 31. Samples for eelgrass genetic analyses Aureococcus ‘Brown tide’ Cochlodinium ‘Rust tide’ Alexandrium ‘Red tide – PSP’ Dinophysis ‘Red tide – DSP’ Enhanced nutrient loading more intense &/or toxic HABs Gobler et al 2012 Gobler et al 2011; Gobler and Sunda 2012 Hattenrath et al 2010 Hattenrath- Lehmann 2014 Microcystis ‘Blue green algae’ Harke and Gobler, 2013
  • 32. Alexandrium red tides and paralytic shellfish poisoning (PSP) Alexandrium Saxitoxin
  • 33. Presence of PSP-producing Alexandrium in NY: 2007-2013 = cells not detected = < 100 cells L-1 = > 1,000 cells L-1 = 100 - 1,000 cells L-1 **circles represent the highest observed densities at each site** • Alexandrium found at 47 of 63 sites samples (75%)
  • 34. Waste water N “Sewage-derived nitrogen loading promotes intense and toxic Alexandrium blooms.”
  • 35. Nitrogen impacts on shellfish • Landings of clams and scallops have declined 99% since 1980. • Linkages to nitrogen driven HABs, habitat loss, and water quality degradation. 0 100,000 200,000 300,000 400,000 500,000 600,000 700,000 800,000 1970 1972 1974 1976 1978 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 Hard clam landings (bushels) in Great South Bay
  • 36. Conclusion: Excessive nitrogen loading leads to… • Loss of critical habitats: Salt marshes, eelgrass • Low dissolved oxygen levels, hypoxia • Acidification, low pH • Macroalgal blooms: Sea lettuce, Ulva • Toxic algal blooms: Red, rust, brown tides • Loss or depletion of shellfisheries and finfisheries