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Chem. 253

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Title: Chem. 31 9/15 Lecture Author: RDixon Last modified by rd Created Date: 9/14/2005 7:27:31 PM Document presentation format: On-screen Show (4:3) – PowerPoint PPT presentation

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Title: Chem. 253


1
Chem. 253 2/25 Lecture
2
Announcements I
  • Return HW 1.3 Group Assignment
  • Last Weeks Group Assignment
  • most did reasonably well
  • New HW assignment (1.5 posted on website)
  • Next Wednesday
  • Will have HW due
  • No Group Assignment
  • Exam 1
  • Justin will take over (covering water chemistry)

3
Announcements II
  • Exam 1
  • On all topics covered through today
  • Will review topics to know at end of lecture
  • Exam will be mix of short answer questions
    (multiple choice or fill in the blank) work out
    problems
  • I may post an example exam (if I can find a
    relevant copy)
  • Todays Lecture Topics Tropospheric Chemistry
  • Finish up cloud chemistry (Chapter 3 and 4)
  • Atmospheric Effects (Chapter 4)

4
Sulfur, Aerosol, and Cloud ChemistryReview of
Main Concepts I
  • Aerosols
  • suspension of particles in a gas
  • particle size range is related to formation and
    growth
  • three main sizes (ultrafine mode new particles
    from gas phase, accumulation mode processed
    particles, and coarse mode from mechanical
    production)
  • distributions are log normal and can be defined
    based on number, surface area, or mass
  • four main chemical classes (sea-salt, soil dust,
    sulfate, and organic)
  • both primary and secondary sources

5
Sulfur, Aerosol, and Cloud ChemistryReview of
Main Concepts II
  • Sulfur Chemistry
  • both natural and anthropogenic sources
  • mostly emitted as SO2, but reduced S is also
    important
  • predominant pathway is oxidation to H2SO4
  • gas phase oxidation occurs through 2-step OH
    reaction
  • gas phase H2SO4 production can lead to new
    particle formation (although mostly leads to
    growth of existing particles)
  • aqueous phase SO2 oxidation adds mass to
    accumulation mode sized particles

6
Sulfur, Aerosol, and Cloud ChemistryReview of
Main Concepts III
  • Cloud/Precipitation Chemistry
  • Will review add new material

7
Cloud/Precipitation Chemistry- Incorporation of
Pollutants
8
Cloud Chemistry- Incorporation of Pollutants
  • Main mechanisms
  • - Nucleation of cloud droplets on aerosol
    particles
  • - Scavenging of gases
  • - Reactions within the droplet

9
Cloud ChemistryNucleation of Cloud Droplets
  • Cloud droplets can not form in the absence of
    aerosol particles unless RH 300.
  • Cloud droplets nucleate on aerosol particles at
    RH of 100.1 to 101.
  • Cloud droplets should nucleate when RH 100
    except that the vapor pressure over a curved
    surface is less than that over a flat surface
    (due to water surface tension)
  • Smaller particles (d lt 50 nm) have more curved
    surfaces and are harder to nucleate

10
Cloud Chemistry- Nucleation of Cloud Droplets
  • Nucleation more readily occurs with
  • - Larger particles
  • - Particles with more water soluble compounds
    (due to growth according to Raoults law)
  • - Compounds that reduce surface tension
  • - Smaller aerosol number concentrations (less
    competition for water so higher RH values)
  • While larger particles are more efficient at
    nucleation, there are a lot more small particles,
    so number of droplets formed is dominated by the
    accumulation mode (100 nm lt d lt 2.5 mm)

11
Cloud Chemistry- Nucleation of Cloud Droplets
aerosol size distribution (mass based)
0.01
10
1
0.1
log dp (mm)
100
Nucleation efficiency
Soot, soil
hygroscopic aerosol
0
10
1
0.1
0.01
log dp (mm)
12
Cloud Chemistry- Nucleation of Cloud Droplets
  • The concentration of constituents incorporated
    from nucleation depends on the efficiency of
    nucleation and on the liquid water content (or
    LWC).
  • LWC g liquid H2O/m3 of air
  • The higher the LWC, the lower the concentration
    (dilution effect)
  • Cloud nucleation leads to heterogeneous cloud
    droplet composition Ignored here for
    calculations

13
Cloud ChemistryNucleation Example Problems
  • Why is an RH over 100 required for cloud droplet
    nucleation?
  • Why is nucleation efficiency higher in less
    polluted regions (for a given particle size)?
  • An ammonium bisulfate aerosol that has a
    concentration of 5.0 µg m-3 is nucleated with 50
    efficiency (by mass) in a cloud that has a LWC of
    0.40 g m-3. What is the molar concentration?
    What is the cloud pH?

14
Cloud Chemistry- Scavenging of Gases
  • Also Important for covering water chemistry (e.g.
    uptake of CO2 by oceans)
  • For unreactive gases, the transfer of gases to
    cloud droplets depends on the Henrys law
    constant (always)
  • In special cases, transfer can depend on LWC (if
    high), or can be limited by diffusion (if
    reacting very fast in droplets)
  • Henrys Law

where KH constant (at given T) and X molecule
of interest
15
Cloud Chemistry- Scavenging of Gases
unreactive gases
  • When LWC and KH are relatively low, we can assume
    that PX is constant (good assumption for SO2 and
    CO2)
  • Then X KHPX where PX comes from mixing
    ratio
  • When KH is high (gt1000 M/atm), conservation of
    mass must be considered (PX decreases as
    molecules are transferred from gas to liquid)
  • We will only consider 2 cases (low KH case and
    100 gas to water case)

16
Cloud Chemistry- Scavenging of Gases
unreactive gases
  • For compounds with high Henrys law constants, a
    significant fraction of compound will dissolve in
    solution
  • fA 10-6KHRT(LWC) where fA aqueous fraction
    (not used in assigned problems)
  • When fA 1, can use same method as for cloud
    nucleation

From Seinfeld and Pandis (1998)
17
Cloud Chemistry- Scavenging of Gases reactive
gases
  • Many of the gases considered are acidic and react
    further
  • Example Dissolution of SO2 gas
  • Reaction Equation
  • SO2(g) H2O(l) ? H2SO3(aq) KH H2SO3/PSO2
  • H2SO3(aq) ? H HSO3- Ka1 HHSO3-/H2SO3(aq
    )
  • HSO3- ? H SO32- Ka2 HSO32-/HSO3-
  • Note concentration of dissolved SO2 S(IV)
  • H2SO3 HSO3- SO32- H2SO3(1
    Ka1/H Ka1Ka2/H2)
  • Effective Henrys law constant
  • KH KH(1 Ka1/H Ka1Ka2/H2)
    function of pH

18
Cloud ChemistrySome Example Problems
  • Example Problem (low KH case) What is the
    concentration of CH3OH in cloud water if the gas
    phase mixing ratio is 10 ppbv and a LWC of 0.2
    g/m3? The Henrys law constant is 290 M/atm (at
    given temp.). Assume an atmospheric pressure of
    0.9 atm and 20C.
  • Example problem (high KH case) Determine the pH
    and aqueous NO3- concentration (in M) if air
    containing 1 ppbv HNO3 enters a cloud with a
    pressure of 0.90 atm, a T 293K, and a LWC of
    0.50 g/m3. Assume 100 scavenging.

19
Break for Group Activity
20
Cloud Chemistry- Overview of Scavenging
  • Gases scavenged are almost always in Henrys law
    equilibrium
  • We will assume one of two cases occurs
  • so little scavenging that Px(pre-cloud)
    Px(in-cloud)
  • or 100 scavenging (complete transfer from gas
    phase to aqueous phase)
  • Aerosol scavenging depends on size and type of
    particles (with typical lower end of around 100
    nm)

21
Cloud Chemistry- What determines pH?
  • It is complicated
  • Strong acids (HNO3(g) and H2SO4(l)) provide H,
    tempered by NH3 and other bases
  • Both SO2 and CO2 can add acidity through reaction
    of H2XO3 with water
  • In many senarios, including background
    locations, neither SO2 nor CO2 significantly
    contribute to pH

22
Cloud Chemistry- What determines pH?
4 Independent Senerios
Source pH
400 ppmv CO2 5.61
1 ppbv SO2 5.38
1 ppbv HNO3 LWC 0.5 g/m3 4.09
5 mg/m3 NH4HSO4 aerosol LWC 0.5 g/m3 4.06
23
Cloud Chemistry- A Modeled Exampleexample
including ammonium bisulfate, sulfur dioxide and
carbon dioxide
Equilibrium pH where sum of anion charge sum of
cation charge
Calculation method is fairly complex (uses
systematic method)
24
Cloud Chemistry- Reactions in Clouds
  • Cloud reactions are important for water soluble
    species because of higher concentrations in
    clouds
  • Only sulfur chemistry covered here

25
Cloud Chemistry- Reactions in Clouds
  • Reaction of S(IV) and H2O2
  • - HSO3- H2O2 ? HSO4- H2O (acid catalyzed)
  • - Rate kHSO3-HH2O2
  • - Rate kH2O2PSO2
  • - Effectively pH independent

26
Cloud Chemistry- Reactions in Clouds
  • Reaction of S(IV) and Ozone
  • - Two main reactions
  • HSO3- O3 ? HSO4- O2 moderately fast
  • SO32- O3 ? SO42- O2 fast
  • reaction is faster at high pH because more S(IV)
    is present in reactive forms

27
Cloud Chemistry- Reactions in Clouds
28
Cloud Chemistry- Reactions in Clouds
  • Oxidation of S(IV)
  • H2O2 is more important oxidant in acidic clouds
  • O3 can be important in cleaner air
  • Bulk models underestimate O3 reaction
  • Under certain conditions, reactions can be
    diffusion limited

drop 1 pH 4.0
drop 2 pH 6.0
pH of combined drop 4.30
rate ratio (H2O2/O3) at combined pH 1000
rate ratio (H2O2/O3) from independent reactions
in two drops 0.5
29
Cloud/Precipitation Chemistry- Incorporation of
Pollutants
30
Precipitation Chemistry
From Mosimann ETH Dissertation diffusion growth
(top) to high degree of riming (bottom)
  • Precipitation Formation
  • Cloud droplets are collected by collisions with
    rain droplets or snow crystals and transfer their
    contents
  • Snow crystals also can form mainly through
    diffusion from water vapor and are very clean

31
Precipitation Chemistry
  • Precipitation Formation
  • In addition to in-cloud transfer, pollutants can
    be incorporated from below cloud scavenging
  • This tends to be best for aerosols by snow and
    gases by rain
  • Precipitation pollutants are typically somewhat
    lower than low-level cloud concentrations

32
Chapter 4 Consequencesof Polluted Air
  • Effects Covered in Chapter 4 Include Haze, Acid
    Precipitation, and Health Effects
  • We will cover health effects when covering
    toxicology

33
Chapter 4 Consequencesof Polluted Air - Haze
  • How do aerosols affect visibility and what
    factors contribute to reduce visibility?
  • Loss of light transmission (as in spectroscopy)
    can occur due to scattering or absorption
  • usually aerosol scattering is most important
  • NO2 absorption and soot absorption contribute to
    a lesser extent

34
Chapter 4 Consequencesof Polluted Air - Haze
  • Light scattering is most mass efficient (most
    scattered light per g of aerosol) for dp l
  • Thus accumulation or fine aerosol mass is good
    indicator for poor visibility
  • High humidity also makes problem worse due to
    hygroscopic growth of aerosol particles
  • Meteorological conditions trapping pollutants or
    contributing to photo-oxidation also make
    visibility worse

35
Chapter 4 Consequencesof Polluted Air Acid
Rain
  • Main contributors are strong acids HNO3 and H2SO4
  • These species form slowly (e.g. relative to
    ozone), so worst places are downwind of major NOx
    and SO2 sources
  • Besides pollution sources, two other factors are
    important
  • atmospheric neutralization
  • soil chemistry

36
Chapter 4 Consequencesof Polluted Air Acid
Rain
  • Neutralization by Atmospheric Bases
  • NH3 (from fertilizers and animal excretions)
  • CaCO3 (in soil dust)
  • Soil Also Allows Run-off Neutralization
  • Occurs in soils containing carbonates (limestone,
    marble, etc.)
  • Acid Rain More Strongly Affects Soils with Weak
    Buffer Capacity
  • Granite or quartz bedrock regions cant buffer
    acidic precipitation
  • This results in acidic lakes

37
Chapter 4 Consequencesof Polluted Air Acid
Rain
  • Problems with Acidified Water and Soils
  • Plant growth in lakes is reduced, which can
    affect whole ecosystem
  • Additionally, Al and other metals are mobilized
    at lower pH due to shift in
  • Al(OH)3(s) ? Al3 3OH-
  • Many such metals are toxic to fish at higher
    concentrations
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