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Evaporation from Flux TowersPowerPoint Presentation

Evaporation from Flux Towers

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Evaporation from Flux Towers

S = P – D - ET

drainage

Change in water

content of volume of soil

precipitation

By Dr Marcy Litvak

Dept of Biological Sciences

University of Texas at Austin

(now at the University of New Mexico)

Latent

Heat flux

How do you partition

H and E??

Can directly measure

each of these

variables

Sensible

Heat flux

Eddy Covariance

Directly measure how much CO2

or H2O vapor blows in or out of a

site in wind gusts.

Integrated measure of

ecosystem fluxes

Link changes in [CO2] or [H2O] in the air above a canopy with the upward or downward movement of that air

Flux CO2 = w ’ CO2’

Net Ecosystem Exchange

30 minute timescale

Updraft [CO2] > downdraft [CO2]

Flux >0 carbon source

Updraft [CO2] < downdraft [CO2]

Flux < 0 carbon sink

Sunlight

800

600

Sunlight (Wm-2)

- The net CO2 flux is calculated for each half hour from the measurements of vertical wind and CO2 concentration.
- A positive flux indicates a net loss of CO2 from the surface (respiration) and a negative flux indicates the net uptake of CO2 (photosynthesis)

400

200

0

146.0

146.5

147.0

147.5

148.0

5

0

-5

CO2 Exchange (mmol m-2 s-1)

-10

-15

CO2 Exchange

-20

12 AM

12PM

12AM

12PM

12AM

May 26, 2000

May 27, 2000

CO2 Exchange (mmol m-2 s-1)

- A years worth of half-hour data can be summed to determine how much Carbon the ecosystem gained or lost

5

4

Annual C accumulation

(Tons C ha-1)

3

2

1

0

1999 2000

ET -Eddy covariance method

- Measurement of vertical transfer of water vapor driven by convective motion
- Directly measure flux by sensing properties of eddies as they pass through a measurement level on an instantaneous basis
- Statistical tool

Basic Theory

Instantaneous

Perturbation from

The mean

Instantaneous

signal

Time averaged property

All atmospheric entities show short-period fluctuations about their long term mean value

=

Turbulent mixingPropterties carried by eddies:

Mass, density ρ

Vertical velocity w

Volumetric content

1) Expand

2) Simplify:

a) remove all terms with single primed entity

b) remove terms with fluctuations

c) remove terms containing mean vertical velocity

Eddy covariance

Average vertical flux of entity over

30 minute period

Fluctuation of entity about it’s mean

g kg air-1

Density of air

kg air m-3

ρ

F =

w’

x’

Velocity of air being moved upwards or downwards

m s-1

At any given instant, multiply velocity of air

being moved upwards or downwards at a

speed of m s-1, by the fluctuation of the entitiy

about its mean

mg

s kg

kg

m3

= g m-2 s-1

Result:vertical speed of transfer of entity measured in m s-1

and at a concentration of g per kg of air

g of entity transferred vertically, per square meter of surface area per second

w’

ρv’

J

kg

Latent heat of vaporization

(J kg-1˚C-1)

Mean density of air

QE =

ρ

Lv

Latent Heat

Fluctuation about

the mean of

vertical wind speed

Fluctuation about

the mean of

density of water

vapor in air

mkg

s m2

kg

m3

J

m2s

W

m2

=

=

w’

T’

J

kg ˚C

Specific heat of air at constant pressure

(J kg-1˚C-1)

Mean density of air

QH =

ρ

Cp

Sensible Heat

Fluctuation about

the mean of

vertical wind speed

Fluctuation about

the mean of

air temperature

m◦C

s

kg

m3

J

m2s

W

m2

=

=

Advantages of eddy covariance locations!

- Inherently averages small-scale variability of fluxes over a surface area that increaes with measurement height
- Measurements are continuous and in high temporal resolution
- Fluxes are determined without disturbing the surface being monitored
- Great tool to look at ecosystem physiology

Disadvantages locations!

- Need turbulence!
- Gap filling issues
- Relatively Expensive
- Stationarity issues
- Open-path IRGA issues
- The eddy covariance method is most accurate when the atmospheric conditions (wind, temperature, humidity, CO2) are steady, the underlying vegetation is homogeneous and it is situated on flat terrain for an extended distance upwind.

Stationiarity locations!

Advection

Horizontal concentration gradients may also lead to perturbation calculation errors

Issue of energy balance closure locations!

Impact of encroachment of Ashe juniper and Honey mesquite locations!

on carbon and water cycling in central Texas savannas

Marcy Litvak

Section of Integrative Biology

University of Texas, Austin

Collaboration with:

James Heilman, Kevin McInnes, James Kjelgaard, Texas A&M

Melba Crawford, Roberto Gutierrez, Amy Neuenschwander, UT

Freeman Ranch - Texas State University

Extensive areas of Edwards Plateau historically were dominated by

fairly open live-oak savannas

Honey mesquite dominated by

Ashe juniper

Worst-case scenario:

Due to overgrazing and fire suppression policies….grasslands are

disappearing as woody species increase

Research Objectives dominated by

- Determine sink strength for carbon associated with woody encroachment and analyze the variables that determine gains/losses of carbon from key central Texas ecosystems
- Determine change in ET, energy balance and potential groundwater recharge associated with woody encroachment
- Provide objective data for validation of land surface process models (CLM2 – Liang Yang, UT) related to growth, primary production, water cycling, hydrology
- Aid in regional scale modeling efforts

Carbon/water tradeoff

Experimental design dominated by

- 3 stages of woody encroachment
- Open grassland, transition site, closed canopy woodland
- -NEE carbon, water, energy: open-path eddy covariance
- (net radiation, solar radiation (incoming, upwelling), PAR, air temperature, relative humidity, precipitation)
- -physiological measures of ecosystem component fluxes
- leaf-level gas exchange, sap-flow, bole-respiration rates, herbaceous NEE
- -soil carbon, soil microclimate, soil respiration rates
- Ecosystem structure
- biomass, LAI, species composition

open grassland dominated by

May 2004

(TAMU)

Transition site – July 2004

15-20 year old juniper,mesquite

Live Oak-Ashe juniper

woodland – July 2004

(TAMU)

H/ ( dominated by E)

Bowen Ratio

Energy balance approach to estimating convective fluxes

Seeks to partition energy available into sensible and latent heat terms

Typical values:

0.1- 0.3 tropical rainforests; soil wet year-round

0.4 – 0.8 temperate forests and grasslands

2-6 semi-arid regions; extremely dry soils

> 10 deserts

Bowen Ratio dominated by

Bowen (1926)

B can be approximated as a function of vertical differences of temperature and vapor pressure in the air, or ,

B =g (t2- t1 ) / ( e2 –e1 )

vapor pressures measured

at the same two points

air temperatures measured

at two points at different

heights above the land surface

Psychrometer

Constant

F(T,P)

Bowen Ratio dominated by

Bowen Ratio

Average values of the air-temperature differences (t2 - t1)

and vapor-pressure differences (e2 - e1),

taken every 30 seconds

for a 30-minute period

are used to determine .

Specific heat

capacity

- = QH
QE

Ca

T

=

Lv

ρv

Latent heat

Of vaporization

Bowen Ratio dominated by

The energy budget can then be solved for LE:

LE = ( Rn –G – W) / ( 1+ )

- Uses gradients of heat and water to partition
- available energy into SH and LE
- Assumptions:
- One-dimensional heat and vapor flow, only vertical
- No transfer to/from measurement area from adjacent area
- No significant heat storage in plant canopy
- 2 fluxes originate from same point on land surface
- Atmosphere equally able to transfer heat and water vapor,
- so turbulence need not be considered

Needs large tract of uniform vegetation dominated by

Sensors to measure air

temperature and humidity

Determine average differentials

for 15-minutes, then switch sensors,

and determine average differentials

for another 15 minutes to avoid sensor bias

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