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Exchange of ozone and highly reactive nitrogen compounds between the atmosphere and biosphere

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Intensity of segregation. Requires, at least, second-order-closure models. Equation of Continuity: ... Intensity of segregation. Source: Kramm &Meixner (2000) ... – PowerPoint PPT presentation

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Title: Exchange of ozone and highly reactive nitrogen compounds between the atmosphere and biosphere


1
Exchange of ozone and highly reactive nitrogen
compounds between the atmosphere and biosphere
Gerhard Kramm
Atmospheric Science Group Geophysical
Institute University of Alaska Fairbanks Septembe
r 10, 2003
2
Content
  • Motivation
  • Theoretical background
  • Balance equation for reactive trace species
  • Techniques to measure vertical fluxes directly
  • Eddy covariance techniques
  • Eddy accumulation techniques ?
  • Ground chamber techniques (ecological studies)
  • Mass balance method
  • Techniques to determine vertical fluxes
    indirectly
  • Variance method
  • Aerodynamic method
  • Inferential method
  • relaxed eddy accumulation (not preferred)
  • Summary and Outlook

3
  • Motivation

NO, NO2, NH3 VOCs O3, SO2, HNO3
VOCs
NO, N2O, NO2
4
  • Theoretical Background

Balance Equation of Reactive Trace Species
  • Macroscopic system
  • Turbulent system

Hesselbergs averaging calculus (1926)
with
and
5
Segregation effects (Kramm and Meixner, 2000)
6
Intensity of segregation
Requires, at least, second-order-closure models
7
Equation of Continuity
Turbulent system
Macroscopic system
Eulerian form
?
with
Euler operator
8
Simplifications to obtain a tractable equation
set
Steady-state conditions
  • prerequisite to represent an ensemble average by
  • a time average

9
Horizontal homogeneity
?
?
Equation of continuity
Steady-state condition
Horizontal homogeneity
?
10
Extrapolation prescriptions
Highly reactive trace species
Long-lived species (constant flux approximation)
11
Definition of an exchange velocity
deposition velocity
exhalation velocity
?
Horizontal homogeneity (Kramm, Dlugi, Mölders,
2003)
12
Source Kramm Dlugi (1994)
13
Damköhler (1940)
1. HO2 HO2 ? H2O2 7. NO3 Isoprenes ?
P 2. HNO3 NH3 ? NH4NO3 8. OH Isoprenes ?
P 3. O3 NO ? NO2 O2 9. OH Monoterpenes
? P 4. O3 Isoprenes ? Products (P) 10. O3
Olefins ? P 5. O3 Monoterpenes ? P 11. O3
NO2 ? NO3 O2 6. NO3 Monoterpenes ? P
Source Kramm Dlugi (1994)
14
h
Eddy covariance techniques
15
Eddy covariance techniques
Source Nestlen et al. (1993), Kramm and Meixner
(2002)
16
Source Tennekes Lumley (1978)
17
Test to Identify Stationary States
Allan-variance criterion (Allan, 1966)
Allan-Variance sA2
Source Werle et al. (1996)
18
Percival Guttorp (1994)
with Haar (1910) wavelet coefficient
Sample average of k consecutive observations
19
Generated time series data
Source Kramm et al. (1999)
20
Allan variance
Source Kramm et al. (1999)
21
Diurnal variation of mean concentrations
Source Nestlen et al. (1993)
22
Diurnal variation of eddy fluxes
Source Nestlen et al. (1993)
23
Frequency-weighted co-spectra
Source Kramm et al. (2003)
24
Frequency weighted co-spectra
Source Kramm et al. (2003)
25
Intensity of segregation
Source Kramm Meixner (2000)
26
Intensity of segregation
Source Kramm Meixner (2000)
27
Influence of segregation effects
Source Kramm Meixner (2000)
28
Mass balance method
x
x Dx
fertilized soil
Kramm, Dlugi Mölders (2003)
29
?
?
Conclusion Very crude method, but often the only
one
30
Aerodynamic Method
31
NO, NO2, NH3 VOCs O3, SO2, HNO3
VOCs
NO, N2O, NO2
32
NO - NO2 - O3 Cycle
33
Source Kramm et al. (1991)
34
Comparison 1st-order closure vs. 2nd-order
closure
No segregation effects
Source Kramm Dlugi (1994)
35
Source Norbert Beier, University of Munich,
Germany
36
Ground chamber values
Eddy fluxes
Source Meixner et al. (1990), Kramm et al. (1991)
37
NO - NO2 - O3 - NO3 N2O5 - HNO3
Cycle (Nighttime chemistry)
NO O3 ? NO2 O2 NO2 O3 ? NO3 O2 NO3
NO ? 2 NO2 MNO3 NO2 ? N2O5
MN2O5 ? NO2 NO3 N2O5 H2O ? 2 HONO2
38
Source Kramm et al. (1995)
39
Inferential Method (Hicks et al., 1987)
Prerequisite Flux is height-invariant
mi was introduced by Kramm (1989)
40
Resistance network for the vegetation-soil system
CR
rt
rst rint rcu rw,f
1 - sf sf
Cint Ccu Cw,f
foliage
1 - sf sf
rmt Cf rmt,fg
rmt,g rsl rw,sl
1 - sw,sl sw,sl
soil
Csl Cw,st
Source Kramm Dlugi (1994)
41
Possible basis for the inferential method
Source Hicks Matt (1988)
Source Nestlen et al. (1993)
42
Source Hicks Matt (1988)
Source Kramm et al. (2003)
No basis for the inferential method
43
Source Kramm et al. (2003)
Source Hicks Matt (1988)
No basis for the inferential method
44
Source Müller et al. (1993)
45
  • Summary and Outlook
  • Summary
  • It was shown that
  • vertical fluxes of highly reactive trace
    species
  • can be affected by chemical reactions,
  • eddy covariance measurements have to be
    analyzed
  • carefully to identify the influence of
    chemical reactions,
  • the mass balance method is a very crude method,
  • but often the only one,
  • the aerodynamic method can provide reliable
    results,
  • but currently there is only a poor data basis
    for evaluation,
  • the eddy flux of ozone hardly varies with
    height,
  • where ozone is mainly deposited,
  • nitric oxide and nitrogen dioxide can be both
  • emitted and deposited, the vertical eddy
    fluxes are
  • strongly affected by chemical reactions,

46
  • segregation effects must not be ignored,
  • the inferential method should only be applied
  • in the case of long-lived nitrogen trace
    species.
  • Outlook
  • What we need are
  • (further) development of fast-response chemical
    analyzers,
  • sophisticated field experiments carried out
    over low
  • vegetation, where more than one measurement
    level
  • is considered,
  • sophisticated field experiments carried out
    over and
  • within canopies of tall vegetation,
  • sophisticated field experiments performed over
  • heterogeneous terrain,
  • higher-order closure models.
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