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Geochemical Cycles

THE EARTH: ASSEMBLAGE OF ATOMS OF THE 92 NATURAL ELEMENTS

• Most abundant elements: oxygen (in solid earth!), iron (core),


silicon (mantle), hydrogen (oceans), nitrogen, carbon, sulfur…

• The elemental composition of the Earth has remained


essentially unchanged over its 4.5 Gyr history
– Extraterrestrial inputs (e.g., from meteorites, cometary
material) have been relatively unimportant
– Escape to space has been restricted by gravity

• Biogeochemical cycling of these elements between the different


reservoirs of the Earth system determines the composition of the
Earth’s atmosphere and the evolution of life
BIOGEOCHEMICAL CYCLING OF ELEMENTS:
examples of major processes
Physical exchange, redox chemistry, biochemistry are involved

Surface
reservoirs
Nitrate and sulfate aerosols over the
past 200 years in Greenland
Nitrate (NO3-)
Sulfate (SO42-)

Global anthropogenic
US anthropogenic NOx SO2 emissions
emissions

Year to year variability may be largely dominated by variability in


atmospheric circulation, the trend in background concentrations
reflects source strengths (anthropogenic) in the recent record.
Mayewski et al., 1990
THE NITROGEN CYCLE: MAJOR
PROCESSES
combustion
ATMOSPHERE lightning
N2 NO
oxidation

HNO3
biofixation
denitri-
fication deposition

orgN decay

BIOSPHERE NH3/NH4+ NO3-


assimilation nitrification

burial
weathering

LITHOSPHERE
Oxidation States of Nitrogen

Increasing oxidation number (oxidation reactions)

-3 0 +1 +2 +3 +4 +5

NH3 N2 N2O NO HONO NO2 HNO3


Ammonia Nitrous Nitric Nitrous Nitrogen Nitric acid
NH4+ oxide oxide acid dioxide NO3-
Ammonium NO2- Nitrate
R1N(R2)R3 Nitrite
Organic N

Decreasing oxidation number (reduction reactions)


THE NITROGEN CYCLE: MAJOR
PROCESSES
combustion
ATMOSPHERE lightning
N2 NO
oxidation

HNO3
biofixation
denitri-
fication deposition

orgN decay

BIOSPHERE NH3/NH4+ NO3-


assimilation nitrification

burial
weathering

LITHOSPHERE
BOX MODEL OF THE NITROGEN CYCLE

Inventories in Tg N, 1Tg = 1x1012 g


Flows in Tg N yr-1

What if denitrification shut off while N2 fixation still operated? How long
would it take for the atmosphere to be depleted of N2?
BOX MODEL OF THE NITROGEN CYCLE

Inventories in Tg N, 1Tg = 1x1012 g


Flows in Tg N yr-1

What if denitrification shut off while N2 fixation still operated? How long
would it take for the atmosphere to be depleted of N2?
BOX MODEL OF THE NITROGEN CYCLE

Inventories in Tg N, 1Tg = 1x1012 g


Flows in Tg N yr-1

What if denitrification shut off while N2 fixation still operated? How long
would it take for the atmosphere to be depleted of N2?
NOx emissions (Tg N yr-1) to troposphere

LIGHTNING STRATOSPHERE
5.8 0.2
SOILS
5.1 FOSSIL FUEL
23.1

BIOMASS
BURNING
BIOFUEL
5.2 AIRCRAFT
2.2
0.5
Mapping of tropospheric NO2 from the
GOME satellite instrument (July 1996)

Martin et al. [2002]


Tropospheric Nitrate Formation

Slide courtesy of Shelley Kunasek


Question
1. Together, industrial fertilizer and fossil
fuel combustion contribute double the
natural rate of terrestrial nitrogen
fixation. Industrial fertilizer has
increased the land biofixation rate by
130 Tg N yr-1, and fossil fuel
combustion by 25 Tg N yr-1. Does this
significantly impact the land and ocean
biota reservoirs?
BOX MODEL OF THE NITROGEN CYCLE

Ocean
reservoir
Land reservoir

Inventories in Tg N, 1Tg = 1x1012 g


Flows in Tg N yr-1
Nitrate can lead to eutrophication
Crop N use efficiency typically <40%, so most washes out or is lost to
atmosphere (Canfield et al., 2010).

Diaz and Rosenberg, Science, 2008


Aerosol Indirect Effect
(Biogeochemical Cycles)

Which direction
and why?

Mahowald, Science, 11 November 2011


Aerosol Indirect Effect
(Biogeochemical Cycles)

Mahowald, Science, 11 November 2011


Nitrification and denitrification:
microbial source of N2O in soils and
oceans

Denitrification: NO3- N2 anaerobic conditions

Low yield product of nitrification


N2O
and denitrification

Nitrification: NH4+ NO3-

Oceans: nitrification ~ 4 TgN/yr


Soils: nitrification and denitrification ~7 TgN/yr
Anthropogenic impacts on
atmospheric N2O
Important as
• source of NOx radicals in stratosphere  stratospheric ozone depletion
• greenhouse gas

IPCC
~15% increase since pre-industrial times [2001]
N2O Emissions

Upland crops

Rice fields

Bouwman et al., 2002.


Environmental Impacts of
Anthropogenic Fixed Nitrogen

Pollution
•Photochemical smog (NOx)
•Acid rain (HNO3)
•Eutrophication (HNO3, NH3)
•Nitrogen fertilization and species diversity (HNO3, NH3)
•Stratospheric ozone depletion (N2O)

Climate
•Greenhouse gas (N2O)
•Atmospheric chemistry and the lifetime of greenhouse gases
(such as CH4)
Nitrate and sulfate aerosols over the
past 200 years in Greenland
Nitrate (NO3-)
Sulfate (SO42-)

Global anthropogenic
US anthropogenic NOx SO2 emissions
emissions

Year to year variability may be largely dominated by variability in


atmospheric circulation, the trend in background concentrations
reflects source strengths (anthropogenic) in the recent record.
Mayewski et al., 1990
SULFUR CYCLE
Most sulfur is tied up in sediments and soils. There are large fluxes to the
atmosphere, but with short atmospheric lifetimes, the atmospheric S burden is
small.

SO2: Anthropogenic (fossil fuel combustion) source comparable to natural


sources (soils, sediments, volcanoes)

Sulfur is oxidized in the atmosphere: SO2 ---- > H2SO4


S(+IV) S(+VI)
Sulfate is an important contributor to
acidity of precipitation. Sulfuric acid has
a low Pvap and thus partitions primarily
to aerosol/aqueous phase

Sulfate is a major component of


atmospheric aerosol and contributes to the
formation of new aerosol particles, with
both direct and indirect climate impacts.

Strongly perturbed by human activities!


Major Sulfur Reservoirs on Earth

Sulfur emissions to the Units of Tg S


atmosphere

11% volcanic
11%

29%

60% anthropogenic

60%

29% biogenic

Charlson et al., 1992


Oxidation states of sulfur
Increasing oxidation number (oxidation reactions)

-2 -1 0 +4 +6

H2S(g) CH3SSCH3(g) CH3SOCH3(g) SO2 (g) H2SO4 (aq)


Hydrogen Dimethyl Dimethyl Sulfur dioxide Sulfuric acid
sulfide disulfide sulfoxide HSO3-(aq) HSO4- (aq)
CS2(g) Bisulfite Bisulfate
Carbon SO32-(aq) SO42- (aq)
disulfide Sulfite Sulfate
CH3SCH3 CH3SO3H (aq)
Dimethyl Methane
sulfide (DMS) sulfonic acid
OCS (MSA)
Carbon sulfide

Decreasing oxidation number (reduction reactions)


The Tropospheric Sulfur Cycle: Major
Processes

OH, NO3 OH
CS2 DMS SO2 SO42-
H2S O3, H2O2
OH
MSA

Surface
Sulfate
aerosols:
Natural and
anthropogenic
sources

DMS from phytoplankton


+
SO2 from volcanoes

IPCC, Chapter 5, 2001 kg km-2 hr-1


Environmental Impacts of
Anthropogenic Sulfur

Pollution
•Particulate matter (SO42-)
•Acid rain (H2SO4)

Owen Bricker, USGS

Climate
•Aerosols  CCN
Extra slides
Box model of the sulfur cycle

DMS  3  SO2  22 3  SO42 


OH / NO OH , H O ,O

Dry (16%) and


DMS Anthropogenic Volcanoes Dry deposition wet dep (84%)
(18 Tg S yr-1) (67 Tg S yr-1) (14 Tg S yr-1)
One Box Model Atmospheric “box”;
spatial distribution of X
Chemical Chemical within box is not resolved
production loss
Inflow Fin Outflow Fout
P L
X
D
E

Deposition
Emission
dm
Mass balance equation:   sources - sinks  Fin  E  P  Fout  L  D
dt
m
Atmospheric lifetime:   Fout
Fout  L  D Fraction lost by export: f  F  L  D
out

1 Fout L D 1 1 1
Lifetimes add in parallel:      
 m m m  export  chem  dep
1
Loss rate constants add in series: k  kexport  kchem  kdep

Special Case:
Constant source, 1st order sink
dm S
 S  km  m(t )  m(0)e  (1  e  kt )
 kt

dt k
Steady state
solution
(dm/dt = 0)

Initial condition m(0)

Characteristic time  = 1/k for


• reaching steady state
• decay of initial condition
If S, k are constant over t >> , then dm/dt = 0 and m=S/k: quasi steady state

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