incorporation of tritium transport processes into

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Haruyasu Nagai, Masakazu Ota Research Group for Environmental Science, Japan Atomic Energy Agency System for Prediction of Environmental Emergency Dose Information Multi-model Package Incorporation of Tritium Transport Processes into Atmosphere-soil-vegetation Model: SOLVEG ~OBT dynamics in plants using the SOLVEG code after an accidental tritium release~ 1/18

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Page 1: Incorporation of Tritium Transport Processes into

Haruyasu Nagai, Masakazu OtaResearch Group for Environmental Science,

Japan Atomic Energy Agency

System for Prediction of Environmental Emergency Dose Information Multi-model Package

Incorporation of Tritium Transport Processes into Atmosphere-soil-vegetation Model: SOLVEG

~OBT dynamics in plants using the SOLVEG code after an accidental tritium release~

1/18

Page 2: Incorporation of Tritium Transport Processes into

Land surface model SOLVEG2Outline of Study

ObjectivesDevelopment of sophisticated land surface model

including radionuclide (Tritium) transport processesUnderstand and predict behavior of radionuclide at land-surface

by numerical experiment

Model developmentStep 1: Heat and water exchange processesStep 2: Canopy radiation and stomatal resistance SOLVEGStep 3: CO2 exchange processes SOLVEG2

EMRAS-II: Radionuclide transport processes (THO, OBT)

2/18

Page 3: Incorporation of Tritium Transport Processes into

Diffusion

Fog water Water vaporPhase change

Latent heat

Temperature

Wind, Turbulence

CO2 concentration

Surface exchange: Momentum, Heat, Water, CO2

Rain

CO2 assimilation,Transpiration

Heat exchange,Evaporation/condensation

Absorption, Emission

Temperature, waterHeat/water budget

Drip

InterceptionPhotosynthesis

Short waveLong wave

Scattering

Surface water

Advection& Diffusion

Surface budget: Heat, Water, CO2

Uptake: Water & CO2 Water vaporLiquid waterPhase change

Latent heatTemperature

CO2 conc.

Root/soil respiration

Soil

Vegetation

Atmosphere

Physical processes are calculated at each layer of vertical multi-layer modelBold: main var., Underlined: processes, Red: heat/rad., Blue: water, Green: CO2

Land surface model SOLVEG2Physical processes

3/18

Page 4: Incorporation of Tritium Transport Processes into

Atmosphere Diffusion:

Soil Heat:

Liquid water:

Water vapor:

Vegetation Heat budget:Leaf water:Water flux:

Radiation Short wave: Downward and upward transfer(Next slide) Direct (visible + near-infrared) + Diffuse (visible + near-infrared)

Long wave: Downward and upward transfer

φ∂∂φ

∂∂

∂∂φ F

zK

zt z +=

zT

CEC

CH

zTK

ztT s

ss

ww

ss

bsT

s

∂∂

ρρ∂∂

∂∂

∂∂

−+=

⎟⎟⎠

⎞⎜⎜⎝

⎛++−= bt

w

w

w EEz

Et ∂

∂ρ∂

η∂ 1

[ ]ρ∂

∂η∂∂

∂ηη∂ bs

wawswws E

zqfD

ztq

+=− )()(

pccc HlEHR ++=

dcapdd PEEE

dtdw

−+−= int

( ) colprdr EEPEa

dzdP

−+−= int

bb lEH −=

fa weeqvu ,,,,,, λθφ =

sdc EEE +=

Transpiration

Evaporation/condensation

Boundary conditionSource term

Net radiation

Land surface model SOLVEG2Basic equations (1): heat, water, momentum

4/18

Page 5: Incorporation of Tritium Transport Processes into

Radiation scheme (coefficients based on Verstraete 1987, 1988)

Short: (direct)

(diffuse)(visible)(near-IR)

Long wave:

( ) ,↓↓

′+′+= dwwrdd SAaaF

dzdS

( )[ ] ( ) ,1 ↓↑↓↓

−′+−′+′+−= ddfrdswsbrsswwsfrss SfaFSAfaFSAafaF

dzdS

( )[ ] ( ) .1 ↓↓↑↑

+′++′+′+−−= ddbrdswsbrsswwsfrss SfaFSAfaFSAafaF

dzdS

( )[ ] ( ),1 44allccsbsfrs TLwkTLfLfaF

dzdL σσε −+−−−= ↓↑↓

( )[ ] ( ).1 44allccsbsfrs TLwkTLfLfaF

dzdL σσε −−−−−−= ↑↓↑

ScatteringLeaf projection cf.: Frd

Scattering cf.:fdf (forward),fdb (backward)

Depend on solar angleand leaf surface angle

Forward scattering cf.: fsf Back scattering cf.: fsb

└Depend on leaf surface angle┘Leaf projection cf.: Frs

Depend on leaf area density

Land surface model SOLVEG2Basic equations (2): radiation

5/18

Page 6: Incorporation of Tritium Transport Processes into

Stomatal resistance (Jarvis scheme): BATS (Dickinson et al. 1993)

rs,min ⇒ measured parameter

fr, fs, fm, ft : Functions of PAR, soil water, humidity, temperature

CO2 assimilation (An): Farquhar et al. (1980)

wc, we, ws, Rd : Depend on PAR, leaf CO2 conc., temperature

Stomatal resistance (rs): Collatz et al. (1991, 1992)

m (constant), b (minimum conductance) ⇒ measured parametercs CO2 partial pressure at leaf surfacees/esat(Tv) Relative humidity at leaf surfacepa Atmospheric pressure

( ) dsecn RwwwA −= ,,min

( ) bpTe

ecAmg

r avsat

s

s

ns

s

+==1

111min,

−−−= tmsrss ffffrr

Land surface model SOLVEG2Basic equations (3): CO2, stomata resistance

2 options

6/18

Page 7: Incorporation of Tritium Transport Processes into

Soil CO2 conservation: Simunek and Suarez (1993)

Volume:Diffusion:Advection:⇒ Treatment of CO2 in gas and aqueous phase together by

Henry’s Law: cw = KHRTca

ca CO2 conc. in soil airηw Volumetric water contentEt

* Root uptake (transpiration)S CO2 source term (= soil: Ss + root: Sr)

SRTcKEcEzz

cDz

cVt aHtaE

aEaE +−

∂∂

−∂∂

∂∂

=∂∂ **

( ) ,wHwwsE RTKV ηηη +−=( ) ,wwHawwsE DRTKDD ηηη +−=

,***wHaE RTEKEE +=

( ) ( ) ( ) ( ) ( )tfcfTffzfSS sasswssss η0=( ) ( ) ( ) ( ) ( )tfcfTffzfSS rarrwrrrr η0=

Land surface model SOLVEG2Basic equations (4): soil CO2

7/18

Page 8: Incorporation of Tritium Transport Processes into

- 2 0 0

0

2 0 0

4 0 0

6 0 0

9 7 1 2 7 1 5 7 1 8 7 2 1 7 2 4 7 2 7 7 3 0 7

J u lia n d a y s ( L S T )

LH

(W

m-2)

- 4 0

- 2 0

0

2 0

9 7 1 2 7 1 5 7 1 8 7 2 1 7 2 4 7 2 7 7 3 0 7

J u lia n d a y s ( L S T )

FC

mol m

-2 s

-1)

APR MAY JUN JUL AUG SEP OCT NOV

Observation○: daily mean◇: daily max+: daily min

Calculation―: daily mean―: daily max―: daily min

Upward positive

Latent heat (water vapor) flux

CO2 flux

Good performance for water and CO2 exchanges at grassland (AmeriFlux data)Diurnal variation and seasonal change are well reproduced.

It can be applied for detailed simulation of 3H and 14C transport.

Land surface model SOLVEG2Water and CO2 fluxes at grassland

8/18

プレゼンター
プレゼンテーションのノート
3行目:「大気部分をWSPEEDI最新版として実運用へ」が正確
Page 9: Incorporation of Tritium Transport Processes into

Land surface model SOLVEG2Incorporation of HTO transport processes

ConceptProcess based HTO transport model to simulate dynamic behavior of HTO in air-soil-plant systemExplicit calculation of HTO transport in a similar way as water and vapor transport

Model developmentStep 1: transport in the atmosphere and bare soil (no decay)

• In-soil transport by Yamazawa (2001) applied for BIOMASS Theme 3-F (rise of HTO from contaminated groundwater)

• Atmospheric transport for HTO vapor (1-D diffusion eq.)• Test calculation using met. data of AmeriFlux (previous slide)

Step 2: inclusion of plant uptake processesStep 3: OBT formation and translocation

9/18

Page 10: Incorporation of Tritium Transport Processes into

external input: precipitation

stomata

Fog water

Diffusion equation

Precipitation

Conservation equationof vertical flux

Water vapor in air

Diffusion equation

Ground surface water budget eq.

Water vapor in soil

Diffusion eq.

Liquid water in soil

Transport equation

Leaf surface waterWater budget eq.

accretion

accretioncondensationevaporation

interception

drip

evaporation/condensationtranspi-

ration

evaporation/condensation

evaporation/condensation

evaporation/condensation

drip

run-off

uptake by root

Land surface model SOLVEG2Incorporation of HTO transport processes

Water and vapor exchange processes

Step 1

HTO transport processCalculate HTO conc. foreach variable of water

Step 2

New variable:Plant water

Water budget eq.(root uptake - transpiration)

Step 3OBT formation and

translocation

10/18

Page 11: Incorporation of Tritium Transport Processes into

Soil HTO transport: Yamazawa (2001) applied for BIOMASS theme 3

Liquid phase:

Gas phase:

Surface B.C.:

χw, χsa , χr HTO conc. in soil water (Bq/m3-water), soil air and air (Bq/m3-air)ηw, ηsw Volumetric soil water content and saturated value (m3/m3)ρw Density of soil water (kg/m3)Ew Vertical liquid water flux (kg/m2/s)DTw, Dta Effective diffusivities of HTO in water and HTO vapor in air (m2/s)fsa(ηw) Tortuosity for diffusion in soil aireb HTO conc. in soil air (Bq/m3-air)cE0, |ur| Bulk transfer coefficient for evaporation, wind speed (m/s)

bw

Twwww

ww ez

Dz

Ezt

−⎟⎠⎞

⎜⎝⎛

∂∂

∂∂

+∂∂

−=∂∂ χχ

ρχη 1

Land surface model SOLVEG2In-soil HTO transport processes

( )[ ] ( ) bsa

wsaTasawws ez

fDzt

+⎥⎦⎤

⎢⎣⎡

∂∂

∂∂

=−∂∂ χηχηη

+: evaporation-: Condensation

( ) ( )rsarEbz

sawsaTa ce

zfD χχχη −=+

∂∂

−=

0000

0 u Atmosphere-land exchange

11/18

Page 12: Incorporation of Tritium Transport Processes into

HTO budget:

Stomata uptake:

Root uptake:

OBT formation: (proportional to CO2 assimilation rate)

OBT decomposition: (proportional to respiration rate)

χv , χa HTO conc. in leaf water (Bq/m3-water) and air (Bq/m3-air)ηv Leaf water content in unit leaf area (m3/m2)ra , rs Resistances (s/m) of leaf boundary layer and stomataqsat(Tc) Saturated specific humidity (kg/kg) at leaf temperature (Tc)ρa, ρw Density of air and water (kg/m3)Er Root uptake rate of HTO (Bq/m3/s)froot(zs,z) Distribution function of root uptake watermw , mglu Weight of 1 mol water and glucose (kg/mol)Ag , Rd Gross CO2 assimilation rate and respiration rate (mol-CO2/m2/s)Sint OBT amount in intermediate pool (Bq/kg)

resphotrootstomvv EEEEt

+−+=∂∂ χη

Land surface model SOLVEG2HTO budget in leaf

( )⎭⎬⎫

⎩⎨⎧

−+

= vw

acsata

sastom Tq

rrE χ

ρρχ1

( ) ( ) ssroot

z

srroot dzzzfzEE btm ,0∫=

gww

vphot AmE

ρχ

=

dglures RmSE61

int=

12/18

Page 13: Incorporation of Tritium Transport Processes into

Carbohydrate formation and translocation processes based on experimental result (Fondy & Geiger 1982)

Land surface model SOLVEG2OBT formation and translocation

Daytime Nighttime

0.19EAn0.48EAn

0.26EAn1.00EAn

starch

0.46EAn

1.00ERd

4.58ERd

5.23ERd

7.07ERd

intermediatesintermediates

sucrosesucrose starch

structuralstructural

Translocation Translocation

CO2 assimilation rate An Respiration rate Rd

OBT formation: EAn OBT decomposition: ERd

13/18

Page 14: Incorporation of Tritium Transport Processes into

Land surface model SOLVEG2Test calculation

[Calculation setting]Experiment: HTO exposure to blooming vine at Cadarache (Guenot and Belot 1984)Comparison with measurement of TWFT concentration and OBT amount in leaf

Chamber

HTO generator

0.10.30.50.71.0

Crown

5.08.0

1.53.0

1500 m3 h-1

12.0Vertical coordinate (m)Meteorological data

Atmosphere

Vinyl film

Input data

–2.0

Stem

–1.0–0.50–0.10 –0.05–0.02

–0.20

Blower

Soil

Rooting zone

ExperimentHTO exposure from 09 to 13 LST

Calculation

14/18

Page 15: Incorporation of Tritium Transport Processes into

TFWT concentration Cal. & Obs.

Local time on 1 Jul. 1982

TFW

T co

nc.

2000

4000

0

Come to equilibrium several hours after start/end of exposure

(3) TFWT conc.

(1) Air HTO conc. (input)

(2) HTO flux

(Bq

m-3

)

600

1x106

0

-600

1x103

1x100

(Bq

m-2

s-1)

(MB

q m

-3)

HTO

con

c.H

TO fl

ux

TFWT conc.: Cal. / Obs.

9–13 h period 1.3 (n = 8)

0.5 (n = 30)13–120 h period

Stomatal conductance: almost constant

Exposure start: Exposure end:

Air→LeafLeaf→Air

Exposure(1)

(2)

(3)1000

3000

105 Bq m-3

101 Bq m-3

z = 0.6 m

z = 0.6 m

8 10 12 14 16 18 20

ObsCal. z = 0.6 m

15/18

Page 16: Incorporation of Tritium Transport Processes into

0 12 24 36 48 60 72 84 96 108 120

Obsz = 0.85 mz = 0.6 mz = 0.4 m

OBT amount in leaf Cal. & Obs.

Time from 1982 7/1 0:00 (h)

OB

T am

ount

0.5

1.0

0

(MB

q kg

-1)

OB

T In

vent

ory

50(M

Bq

m-2

)

1015 Intermediate

Structuralstarch

sucrose

OBT : Cal. / Obs.9–13 h period 0.6 (n = 8)

1.4 (n = 30)13–120 h period

(1) OBT inventory in each pool(MBq m-2)

(2) OBT amount(MBq kg-1)

Exposure

daynight top

middlelow

day night

16/18

Page 17: Incorporation of Tritium Transport Processes into

Total OBT fixed during exposure1%

2%

2%

t = 48 h

t = 120 h

t = 24 h

Residual

35%

28%

63%

42%57%

Respired

70%

Translocated

15% OBT fixed to structural carbohydrates

Fate of OBT generated in leaf 17/18

Page 18: Incorporation of Tritium Transport Processes into

Land surface model SOLVEG2Summary

Incorporation of HTO transport into SOLVEGProcess based HTO transport model to simulate dynamic behavior of HTO in air-soil-plant systemExplicit calculation of HTO transport in a similar way as water and vapor transport Step 1: transport in the atmosphere and bare soil (no decay)Step 2: inclusion of plant uptake processesStep 3: OBT formation and translocationTest using experimental data at Cadarache (Guenot and Belot 1984)Calculated results seem to be reasonable.Submitted to JER:Masakazu Ota and Haruyasu Nagai, “Development and validation of a dynamical atmosphere–vegetation–soil HTO transport and OBT formation model”

18/18