Aerosols and the Environment
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Transcript Aerosols and the Environment
The Characterization of
Atmospheric Particulate Matter
Richard F. Niedziela
DePaul University
16 May 00
The atmosphere
Have you thought about your atmosphere
today?
Physical
dimensions
– matm 5.2 1018 kg 10-6 mearth
– hatm 100 km
– Vatm 1.0 1011 km3 10-1 Vearth
Thermal
profile
– Several different thermal gradients
The atmosphere
The atmosphere
The
atmosphere is made out of...
– 78% N2 (3.9 1018 kg)
– 21% O2 (1.2 1018 kg)
– 1% trace gases and suspended matter, or
aerosols (0.1 1018 kg)
Aerosols
Aerosols
Aerosols are small particles of
condensed matter that are found
throughout the environment, from the
surface of the Earth to the upper
reaches of the atmosphere.
Brilliant red sunsets
Blue hazes in forests
Fog
Aerosol characteristics
An aerosol is characterized by
Composition
Size
Phase
Shape
Aerosol composition
Organic materials
Long-chained
hydrocarbons
Large carboxylic acids
Inorganic materials
Mineral
acids
Metals
Organic/inorganic mixtures
Aerosol size
Particle diameters range from submicron to
tens of microns
10-4
10-3
.01
.1
1
10
100
micron = 1 mm = 10-4 cm = 10-6 m
103
104
Aerosol phase
Liquids
Oil
droplets from vegetation
Sulfuric acid aerosols
Solids
Suspended
crust material
Water ice particles in cirrus clouds
Liquid/solid mixtures
Aerosol shape
Liquids: spherical droplets
Solids: crystals and complex structures
Shape can impact physical, chemical,
and optical properties of aerosols
Some actual aerosols
Sulfate particle
Aluminum particle
T. Reichhardt, Environ. Sci. Tech., 29(8), 360A, (1995).
Aerosol sources
Natural sources
Vegetation
Oceans
Volcanoes
Anthropogenic sources
Vehicle
and industrial emissions
Agricultural practices
Aerosol production
Mechanical action
Abrasion
of plant leaves
Sea spray
Wind
Nucleation and condensation
Cloud
formation
Aerosols and the Environment
Aerosols and the Environment
Ozone depletion
Global climate change
The atmosphere
thermosphere
upper atmosphere
mesopause
altitude (km)
80
mesosphere
60
stratopause
middle atmosphere
40
stratosphere
20
tropopause
troposphere
lower atmosphere
Ozone
O
O
Pungent gas (named after the
Greek word ozein, “to smell”)
“Good” vs. “Bad”
O
– 90% of all ozone
– 10 ppmv peak concentration
– UV screening
O3
Stratosphere
Troposphere
– 10 ppbv peak concentration
– Disinfectant
– Respiratory stress
Ozone
O2 + h
O + O2 + M
O3 + h
O3 + O
O+O
O3 + M
O2 + O
O2 + O2
Chapman mechanism
Proposed in 1930
Qualitative prediction of atmospheric ozone profile
Ozone depletion
There has been a recent overall
decrease in the stratospheric ozone
concentration.
CF2Cl2 + h
Cl + O3
ClO + O
O3 + O
Ozone measured over Payerne, Switzerland
CF2Cl + Cl
ClO + O2
Cl + O2
2 O2
Polar ozone depletion
The loss of ozone over the South Pole is more dramatic
Polar ozone depletion theories
Atmospheric motions
Stratospheric air replaced with
tropospheric air
Discounted due to lack of tropospheric
trace gases in the stratosphere
Polar ozone depletion theories
Reactive nitrogen species chemically
destroy ozone
Discounted due to low concentrations of
nitrogen species during depletion events
Polar ozone depletion theories
Chlorine compounds are responsible for
the ozone depletion
Produced
from CFCs
Persist for up to 100 years
Polar ozone depletion cycle
2ClO + M
Cl2O2 + h
ClOO + M
2Cl + 2O3
2O3 + h
Cl2O2 + M
ClOO + Cl
Cl + O2 + M
2ClO + 2O2
3O2
These reactions are thought to be responsible
for 70% of the observed ozone depletion
Homogeneous reactions
CFCs
h
ClONO2
ClO
h
NO2
Polar stratospheric chemistry
Homogenous chemistry cannot provide
all of the ClO needed to deplete ozone
Ozone depletion occurs in the presence
of polar stratospheric clouds or PSCs
Polar stratospheric clouds
Type I
Formed
near 195 K
Composed of nitric acid and water
Exist in different phases
– Type Ia: Solid nitric acid particles
– Type Ib: Supercooled liquid droplets (sulfuric
acid, nitric acid, water)
Type II
Formed
near 185 K
Water ice particles
Heterogeneous reactions
ClONO2(s) + HCl(s)
PSCs
Cl2(g) + HNO3(s)
ClONO2(s) + H2O(s)
PSCs
HOCl(g) + HNO3(s)
Chlorine is released into the gas phase
Nitrogen is chemically removed
Nitrogen is physically removed
Heterogeneous reactions
h
HCl
HNO3
CFCs
ClONO2
Polar Stratospheric Clouds
PSCs
H2O
Cl2
h
HOCl
h
Cl
Sedimentation
Cl
Polar stratospheric chemistry
h
HCl
CFCs
ClONO2
HNO3
h
ClONO2
h
NO2
H2O
PSCs
HOCl
ClO
Cl2
h
ClO + ClO
h
Cl2O2
h
ClO
Cl
Sedimentation
O3
O2
Polar stratospheric chemistry
Heterogeneous reaction rates are
dependent on PSC phase, composition,
and size
Need to characterize PSCs to fully
investigate depletion process
PSC characterization
Collect infrared spectra of PSCs
Mie scattering theory
Spherical
particles
Complex refractive indices for proposed
PSC components
Complex refractive indices
N n ik
n is the real component of the refractive index
k is the imaginary component of the refractive index
determines how fast light moves through material
n=c/v
determines how light is absorbed by material
k = al / 4p
Optical constants
PSC spectra
Ice
NAD
NAT
O.B.Toon and M.A. Tolbert, Nature, 375, 218, (1995).
Polar stratospheric clouds
Good fits were not obtained using
known optical constants for
Water
ice
Nitric acid monohydrate (NAM): HNO3H2O
Nitric acid dihydrate (NAD): HNO3H2O
Nitric acid trihydrate (NAT): HNO33H2O
Polar stratospheric clouds
PSCs are not pure water or nitric acid
aerosols
Ternary mixtures with sulfuric acid
Determine optical constants for ternary
mixtures
Retrieving optical constants
Retrieve optical constants from infrared
spectra of model PSC aerosols
Frequency
Temperature
Optical constants for NAD
Aerosol flow cell II
Flow
Injection
Port
2
1
3
4
MCT
6
Flow
Exhaust
5
Cooling
Coils
FTIR
Spectrometer
Aerosol flow cell II
Aerosol flow cell II
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Scattering spectra
1.0
Nitric Acid Dihydrate at 180 K
0.8
Extinction
0.6
0.4
0.2
0.0
700
1200
1700
2200
2700
3200
-1
Wavenumber (cm )
3700
4200
4700
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Non-scattering spectrum
0.20
Extinction
0.15
Nitric Acid Dihydrate at 180 K
0.10
0.05
0.00
700
1200
1700
2200
2700
3200
-1
Wavenumber (cm )
3700
4200
4700
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Use Kramers-Kronig
relationship to
calculate n()
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Use Kramers-Kronig
relationship to
calculate n()
Use Mie scattering
theory to calculate
scattering spectrum
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Use Kramers-Kronig
relationship to
calculate n()
Compare calculated and
experimental spectra
Use Mie scattering
theory to calculate
scattering spectrum
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Use Kramers-Kronig
relationship to
calculate n()
Correct k() if necessary
Compare calculated and
experimental spectra
Use Mie scattering
theory to calculate
scattering spectrum
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Use Kramers-Kronig
relationship to
calculate n()
Vary k() scaling factor, K
Correct k() if necessary
Compare calculated and
experimental spectra
Use Mie scattering
theory to calculate
scattering spectrum
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Vary particle size
Use Kramers-Kronig
relationship to
calculate n()
Vary k() scaling factor, K
Correct k() if necessary
Compare calculated and
experimental spectra
Use Mie scattering
theory to calculate
scattering spectrum
Retrieving optical constants
Collect many scattering
spectra representing
different particle sizes
Collect a non-scattering
spectrum to estimate k
k() = Ka()
Select a scattering
spectrum and guess
the particle size
Vary particle size
Use Kramers-Kronig
relationship to
calculate n()
Vary k() scaling factor, K
Correct k() if necessary
Compare calculated and
experimental spectra
Use Mie scattering
theory to calculate
scattering spectrum
Final fit results
1.0
Nitric Acid Dihydrate at 180 K
0.8
Extinction
0.6
0.4
rmed = 0.33 mm
0.2
0.0
700
1200
1700
2200
2700
3200
-1
Wavenumber (cm )
3700
4200
4700
Final optical constants
2.6
2.4
2.2
Nitric Acid Dihydrate at 180 K
2.0
Refractive index
1.8
1.6
n
1.4
1.2
1.0
0.8
0.6
0.4
0.2
k
0.0
700
1200
1700
2200
2700
3200
-1
Wavenumber (cm )
3700
4200
4700
NAD optical constants
Overall good agreement with thin-film
results
Some discrepancies do exist
Comparison of several aerosol and thinfilm spectra suggest substrate
interference
Aerosol vs. thin-film spectra
NAD thin-film spectra
NAD aerosol spectra
Wavenumber (cm-1)
Aerosol optical constants
Optical constants derived from aerosols are
better suited for analyzing atmospheric particles
Aerosol composition
NAD aerosols have a fixed composition
Composition of liquid sulfuric acid
aerosols can vary
Tunable diode laser
Window
to Cell
TDL
Focusing
Objective
Alignment
Pinhole
Beamsplitter
HeNe
Ocular
Bypass
Optics
Slit
Monochromator
To Vacuum
Vacuum Jacket
Tunable diode laser
Tunable diode laser
Diode laser beam samples the same
aerosol stream as the FT-IR
spectrometer
Determines water vapor pressure by
applying Beer’s law to a single water
absorption line
Tunable diode laser
1.0
0.9
Transmission (I/Io)
0.8
0.7
0.6
0.5
0.4
Cell Pressure (Torr)
9.7
49.3
99.5
200.0
300.0
0.3
0.2
1751.39
1751.40
1751.41
1751.42
1751.43
-1
Wavenumber (cm )
1751.44
1751.45
Aerosol flow cell II
Flow
Injection
Port
2
1
3
4
6
5
MCT
Detectors
Flow
Exhaust
TDL and
Optics Box
Cooling
Coils
FTIR
Spectrometer
Sulfuric acid optical constants
One optical constant study by Palmer
and Williams in 1975
Bulk data for a few concentrations at
room temperature
Widely used by atmospheric scientists
Spectra change substantially at low
temperatures
Sulfuric acid optical constants
2.6
2.4
2.2
75 wt% Sulfuric Acid/Water
2.0
Refractive Index
1.8
1.6
n
1.4
1.2
1.0
0.8
0.6
0.4
k
0.2
0.0
800
1300
1800
2300
2800
3300
-1
Wavenumber (cm )
3800
4300
Sulfuric acid optical constants
2.5
38 wt% Sulfuric Acid/Water
Refractive index
2.0
n
1.5
1.0
0.5
k
0.0
800
1300
1800
2300
2800
3300
-1
Wavenumber (cm )
3800
4300
Sulfuric acid optical constants
300
Temperature (K)
280
260
240
220
200
30
40
50
60
Weight % H2SO4
70
80
90
Sulfuric acid optical constants
The Palmer and Williams optical
constants should not be used at low
temperatures
Temperature and composition
dependence indicate interesting ion
equilibrium chemistry
Emphasize the need to perform similar
studies on ternary systems
Aerosols and the Environment
Ozone depletion
Global climate change
The atmosphere
thermosphere
upper atmosphere
mesopause
altitude (km)
80
mesosphere
60
stratopause
middle atmosphere
40
stratosphere
20
tropopause
troposphere
lower atmosphere
Global climate change
Climate depends on the chemical
composition of the atmosphere
Forecasting how the climate will change
Will
our current coastlines disappear?
Will there be another ice age?
Over time, incoming solar energy is
balanced by energy radiated from Earth
Energy balance
Sun
Eath
Earth
Climate Change 1994: Radiative Forcing of Climate Change and An Evaluation of the IS92
Emission Scenarios (Cambridge University Press, Cambridge, 1995).
Energy imbalance
Anything which causes a change in the
energy balance is known as a forcing
Climate responds to forcing by reestablishing energy balance
A forcing example
Doubling CO2 concentration
Forcing of 4 Wm-2
Surface must warm up 1 K to restore
balance
Positive forcing warms the planet,
while negative forcing cools the planet
Forcing sources
Solar output
Surface characteristics of the Earth
Greenhouse gases
H2O,
CO2, O3, CH4, N2O, and halocarbons
Direct interaction with energy radiated from
the Earth
Forcing sources
Aerosols
“Direct”
forcing
– Direct interaction with incoming or outgoing light
“Indirect”
forcing
– Affecting other components of the climate
Forcing contributions
S.E. Schwartz and M.O. Andreae, Science, 272, 1121, (1996).
Aerosol forcing uncertainties
Interaction with light is largely unknown
Lack
of optical constant information
Hygroscopic properties are unknown
Important
gauge of indirect effects
Complex spatial and temporal
distributions throughout the atmosphere
Aerosol forcing effects
Aerosol forcing could offset greenhouse
forcing
Cooling of 2 - 3 K due to “background
aerosols”
Mt. Pinatubo eruption
forcing of -4.5 Wm-2
A temporary, calculated and observed
cooling of 0.5 K
Peak
Tropospheric aerosols
Materials: soil dust, sulfates, sea salt,
soot, and organics
Only sulfates have been “characterized”
Soot and organic aerosols are perhaps
the most important
Present laboratory work
Apply optical constant retrieval method
to organic aerosols
Study hygroscopic properties of organic
aerosols
Characterize multi-component organic
aerosols
Organic aerosols
Primary organic aerosols (POAs)
Emitted
from source as an aerosol
Secondary organic aerosols (SOAs)
Condensation
of gas-phase species on preexisting particles
Composed of terpenes, PAHs, alkanes,
and carboxylic acids
Organic aerosols - terpenes
Organic aerosols - terpenes
Natural sources are nearly ten times
greater than anthropogenic sources
C=C bonds are susceptible to attack by
O3, NO3, and OH
Model organic aerosols
Determine optical constants for singlecomponent organic aerosols
Start with easily obtained materials that
closely represent actual organic
aerosols
Model organic aerosols
2.0
o
Absorbance
1.5
1.0
0.5
0.0
1000
2000
3000
4000
-1
Wavenumber (cm )
5000
Carvone
Aerosol flow cell III
Aerosol flow cell III
Aerosol flow cell III
First spectra
0.40
0.35
0.30
Absorbance
0.25
0.20
0.15
0.10
0.05
0.00
1000
2000
3000
4000
-1
Wavenumber (cm )
5000
Humidity dependence
Add water vapor along with organic
aerosols
Optical constants as a function of
relative humidity
Hygroscopic vs. hygrophilic
Evaluate the indirect effect of organic
aerosols
Multi-component aerosols
Prepare known mixed organic and
mixed organic/inorganic aerosols
Use single-component optical constants
to determine refractive index mixing
rules
Test rules on unknown aerosols
Apply rules to real tropospheric aerosols
Acknowledgments
PSCs (UNC - Chapel Hill)
R.E. Miller, D.R. Worsnop, and M.L. Norman
NASA Upper Atmosphere Research Program
Organic aerosol studies (DePaul University)
Elena Lucchetta
LA&S Summer Research Program (1999)