Development of a mechanistic model of Hg in the terrestrial biosphere
description
Transcript of Development of a mechanistic model of Hg in the terrestrial biosphere
Development of a mechanistic model of Hg in the terrestrial
biosphere
Nicole Smith-DowneyHarvard University
GEOS-Chem Users MetingApril 12, 2007
Project Goals• To develop a mechanistic model of mercury in
the biosphere and couple this to the GEOS-Chem Hg simulation
• Specific aims– To model the incorporation, storage and emissions
of Hg from the terrestrial biosphere– Continuum of timescales (annual to century)– Mechanistic nature will allow us to examine
changes in emissions and/or climate – Key is to understand Hg storage in soils
How does Hg enter the soil pool?
Hg0Hg(II)oxidation
reductionwet and dry deposition to
canopy
throughfall
Direct deposition to soil surface
There are four forms of Hg deposition to the biosphere•Hg(II) wet•Hg(II) dry•Hg0 dry•Hg(p)
How does Hg enter the soil pool?
Hg0Hg(II)oxidation
reductionwet and dry deposition to canopy and soil surface
litterfallthroughfall(wet)
Hg0 can be incorporated into leaf tissue (through stomates) then enters the soil pool as litter
• Ecosystem dependent - implies large spatial gradient in deposition• Largest source of Hg to some soils
What happens to Hg in soils
Hg0Hg(II)oxidation
reduction
Binding to organic ligands,
charged soil particles
wet and dry deposition to canopy and soil surface
litterfallthroughfall(wet)
methylation (anaerobic)
Hg0
Hg(II)
The oxidation state of Hg in soils determines the rate of re-emission
Dissolved Hg(II) in soil
waterKorgKorg measured by Lyon et al. 1997 and Khwaja et al. 2006
What happens to Hg in soils
Hg0Hg(II)oxidation
reduction
Binding to organic ligands,
charged soil particles
Immediate re-emission
wet and dry deposition to canopy and soil surface
litterfallthroughfall(wet)
methylation (anaerobic)
Hg0
Hg(II)
Soils that are organic rich will store Hg effectively (Northern peat soils)
Anderson 1979
How does Hg leave soils
Hg0Hg(II)oxidation
reduction
Binding to organic ligands,
charged soil particles
Volatilization to atmosphere
wet and dry deposition to canopy and soil surface
litterfallthroughfall(wet)
methylation (anaerobic)
Hg0
Hg(II)
Biomass Burning (including soils)
Decomposition of organic material leads to the removal of Hg(II) from the system (Heyes et al. 1998)
Evapotranspiration
Implies a method to model Hg
• Tie the lifetime of Hg in soils to the lifetime of different carbon pools
• Base lifetime of Hg(II) against reduction to the lifetime of it’s associated carbon pool
• Use existing biogeochemical model (CASA) as the framework for a mercury model – Combines remote sensing and meteorological observations
to predict ecosystem productivity– Includes plant growth, decomposition and biomass burning– Tracks soil carbon pools of different types (similar to
CENTURY model)
CASA Model
• Global 1x1 degree ecosystem model• NPP is calculated as a function of intercepted
photosynthetically active radiation and light use efficiency
• Using version developed by van der Werf et al. 2001
Potter et al. 1993
CASA Soil Model
At each transfer point, a fraction of the soil pool is respiredDepends on•Litter quality•Temperature•Moisture•Soil Structure
Current Hg Soil Simulation
Hg0 incorporated into leaf tissue proportional to Hg0 dry deposition and LAI
Hg(II) dry deposition is added to surface litter pools
Hg(II) wet deposition is split between the litter pools and the slowpool
Experiment
• Use Pre-industrial deposition estimates from Selin et al. in prep– Hg0 dry = 580 Mg/yr– Hg(II) wet = 780 Mg/yr– Hg(II) dry = 1640 Mg/yr
• Assume uniform deposition over land areas• Spin up soil pools to equilibrium and
examine distribution of Hg storage, emissions and lifetime
Hg storage in soil pools over time
Spatial distribution of Hg storage in soils
Armored pool t=2000 yrs
Slow pool t=2000 yrs
Respiration driven Hg fluxes out of soils
Maximum = 600 g/m2/yr
Hg lifetime in soils against respiration
Maximum = 75 years
Current Work - Layered Soil Model
• Soils are not at equilibrium with current emissions
• Need to track movement of Hg through soil profile
• Use approach of Carrasco et al. 2006 for 14C
• This will allow us to examine the effects of soil burning and decomposition on the Hg budget