Nitrogen cycle
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Transcript Nitrogen cycle
Nitrogen cycle
Biogeochemistry
October 17, 2005
Maria Moskalenko, Gretchen Miles,
Emily Paduano, Jaconette Mirck
Outline
Background Information on N
Papers:
Kaiser, 2001. The Other Global Pollutant
Agriculture: fertilizer & food
Mitsch, 2001. Reducing N loading to Gulf
Mississippi River-hypoxia
Solutions to N-pollution
Driscoll, 2003. N Pollution in Northeast US
Atmospheric Inputs
Estuaries
Models
Discussion
Nitrogen Forms, Phases and
Oxidation States
*
* NOx, greenhouse gases
*
Nitrogen the other global
pollutant (Kaiser, 2001)
Essential element for growth/primary
production
Surplus nitrogen = pollutant
Sources:
Fertilizer
Fossil fuels
Results in various problems:
Algal bloom
Greenhouse gas
Ozone
Solutions
Increase requirements for fossil fuels
Smaller cars
Hybrids
Eat less meat to reduce food of live stock
Less manure
Food control, precise amino acid ratio
Reduce runoff
Increase price of fertilizer
Reducing Nitrogen Loading to the
Gulf of Mexico from the
Mississippi River Basin: Strategies
to Counter a Persistent Ecological
Problem
-Mitsch, et al. 2001
Problems
Anthropogenic Additions of N to aquatic
systems cause
Increased Productivity
Eutrophication
Hypoxia
Fish Kills
Sources
Agriculture
Waste Water
Draining Wetlands
Drained wetlands converted to agricultural land
Solutions: Controlling N in
Miss. River Basin
Modifying Agricultural Practice
- use less fertilizer
- apply fertilizer in spring
- account for N sources present
Riparian and Wetland Buffers
- effective nitrogen sinks due to high
levels of denitrification
Example of Riparian Buffer
Solutions cont.
Urban & Suburban Non-point Source
Control
Point Source Control
Controls on Atmospheric NOx
Mississippi River Diversions
Creation of Wetlands
Benefits of Reducing Nitrogen Levels
in the Mississippi River Basin
Predicted 40% reduction of nitrogen loading
to the Gulf through implementation of these
practices
In addition to reduced hypoxia
-
reduced river pollution
reduced wetland loss
improved river ecosystems
improved control of floods
Northeast U.S. Brief History
Population Changes
Land Use Changes
Capacity of 2nd Growth
Forests for N-retention
N-pollution Sources in
Northeast U.S. (Driscoll et al.
2003)
Atmospheric N Sources
Food Imports
Fertilizer & Farming Practices
Feed Imports
Wastewater Effluent
Mycorrhizae & Legumes
Problems
Acidic Deposition
Ground Level Ozone Formation
Coastal Eutrophication
Acidification & Overfertilization N-enrichment
Forest (N-saturation)
Freshwater
(high flow)
Smog in LA & Chicago
Wet Deposition and Emissions
a: nitrate, sulfate, b: nitrate & ammonium, c: sulfate, nitrate, chloride
Ozone Formation
For Formation: NOx & VOC’s (volitile organic
compounds)
Or NO from soil + Oxygen
VOC’s were thought to be limiting factor
Automobile VOC’s are regulated
VOC’s are also produced naturally (isoprene)
In Northeast U.S. we now believe that NOx
regulates O3 formation
Ground Level O3 in many U.S. cities exceeds
National Ambient Air Quality Standards
Solution: Reductions in N
Management Options:
Coastal Watersheds
Wastewater Treatment Plants
Agriculture
Atmosphere
Fossil fuel electric utilities
Transportation
Agriculture
Purpose of Modeling
Models were run to test proposed
management options and determine
their effectiveness
Atmospheric Model: PnET-BGC
Estuary Loading: WATERSN
Conclusions
Estuary: Major N-source
Wastewater effluent:
Add biotic N-removal to wastewater
treatment practices
Atmosphere:
Source Specific Control
(due to numerous sources)
Discussion Topics
Ecotechnology
Phytoremediation
Willow Project
Theoretical Models vs. Real Life Problems?
Lifestyle Changes
No Meat = No Nitrogen
SUV’s, Hybrids,Public Transportation, Walk, Bike
Other Effects of N
Purely Atmospheric take on N- Aerosols
Willow Applications
Set-aside arable land
Bio-remediation of
contaminated soils, like
brownfields
(phytoremediation)
Nutrient and waste
management systems
Windbreaks/snow
fences
Buffer zones for clean
water
Incorporating willow biomass crops
into riparian buffers produces clean
water and renewable energy (Salix
Maskiner 2000)
Soil Conservation
• Very little soil erosion
•
One year old coppcie growth
once the crop is
established
Negligible N leaching
from established willow
plantings, even with
large applications
nitrogen (Adegbidi
1999, Aronsson et al.
2000).
Nitrogen Movement
Pots with willow
growth
Pots without willow
growth
p-value
NO3-N
(kg/ha)
NH4-N
(kg/ha)
4.3 + 2.6
1.3 + 0.2
140.8 +12.9
1.3 + 0.2
<0.01
0.75
Trial with organic amendments with nitrogen loads ranging from
200 – 1,880 TKN kg/ha (Adeigbidi 1999)
Aerosols
What???
Aerosols absorb
or scatter light
Ecological Effect
Photosynthesis
GCEP 2004 Orientation Presentation by Jeff Gaffney
The End