retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

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Climate change is one of the most important global environmental challenges of this century. Green House Gases (GHGs) are the main culprit for this problem. Though much of research has already been done about the distribution and sources (and sinks) of GHGs , still much more uncertainties are present. Currently, there are only a few satellite instruments in orbit which are able to measure atmospheric GHGs. The High Resolution Infrared Radiation Sounder (HIRS), the Atmospheric InfraRed Sounder (AIRS), and the Infrared Atmospheric Sounding Interferometer (IASI) perform measurements in the thermal infrared (TIR) spectral region. But these are having low sensitivity to lower troposphere. In contrast to this, the sensitivity of instruments measuring reflected solar radiation in the near-infrared (NIR)/shortwave infrared (SWIR) spectral region is much more constant (with height) and shows maximum values near the surface. At present, SCIAMACHY aboard ENVISAT launched in 2002 and TANSO (Thermal And Near infrared Sensor for carbon Observation) aboard GOSAT (Greenhouse gases Observing SATellite) launched in 2009 are the only orbiting instruments measuring in NIR region. Among all the algorithms the WFM-DOAS algorithm (Weighting Function Modified Differential Optical Absorption Spectroscopy) developed at the University of Bremen for the retrieval of trace gases from SCIAMACHY (Buchwitz et al.2005) is mostly used. This is based on the principle of differential detection of radiance in gaseous absorption channels with respect to neighboring atmospheric transparent spectral channels (not influenced by gas) to detect the conc. of desired gas. But scattering at aerosol and/or cloud particles remains a major source of uncertainty for SCIAMACHY XCO2 retrievals(Houweling 2005, Schneising 2008).Of late with the use of new merged fit window approach scientists have come up with less than 0.5 ppm error in the estimation of CO2 in the presence of thin cirrus cloud(Reuter, Buchwitz et. al. 2010). Schneising et. al.,2007,retrieved d three year’s column-averaged CO2 dry air mole fraction from the SCIAMACHY instrument using the retrieval algorithm WFM-DOAS version 1.0, with precision of about 2 ppm. In India a study was undertaken to compare the atmospheric methane concentration pattern from SCIAMACHY with the vegetation dynamics from SPOT, showed fairly good correlation of methane emission with the rice cultivation(Goroshi et. al.).

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Page 1: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing
Page 2: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing
Page 3: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Heavier precipitation,more intense and longer droughts….

Page 4: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

CLIMATE CHANGE

ATMOSPHERIC AEROSOL GREEN HOUSE GASES (GHGs)

GLOBAL WARMINGGLOBAL DIMMING

Page 5: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

GLOBAL AVERAGES OF THE CONCENTRATIONS OF CARBON DIOXIDE, METHANE, NITROUS OXIDE, CFC-12 AND CFC-11

These gases account for about 97% of the direct warming effect of the long-l ived greenhouse gases since 1750. The remaining 3% is contributed by an assortment of 10 minor halogen gases. ( Source NOAA, Annual Greenhouse Gas Index )

CO2N2O

CH4 CFCs

Page 6: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Retrieval & Monitoring of Atmospheric Retrieval & Monitoring of Atmospheric Green House Gases (GHGs) through Green House Gases (GHGs) through remote sensingremote sensing

Debasish Chakraborty Roll No. – 4843Division of Agricultural Physics

Page 7: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

RETRIEVAL: To find or extract stored information.

MONITORING: To watch & check over a period of time in order to see how any phenomena develops/changes so that one can take necessary action. So, monitoring of Green House Gases(GHGs) over the globe is a spatiotemporal property.

GHGs MeasurementConventional

Remote sensing

Page 8: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Standard type of technique to measure GHGs

VIALS

GC analysis

ECD, FID detectors

Gas storage

Gas accumulation over t ime

Closed chamber – Gas Chromatographic analysis, IRGA

Page 9: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Advantage:

Technique is simple

Can be handled with short training

Very accurate

Limitation:

Limited spatial distr ibution

Sampling error

Closed chamber – Gas Chromatographic analysis, IRGA

Page 10: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

SATELLITE MEASUREMENTSADVANTAGE:

Provide Global coverage High temporal resolution Data with sufficient precision is becoming available - Multi-purpose missions-SCIAMACHY,AIRS -Missions dedicated to GHGs-GOSAT/JAXA ; launched on jan,2009

LIMITATION:

Absolute measurement of physical parameters Several disturbances (sensor cal/val, clouds, aerosol etc) Retrieval needs complex algorithms Asks for expertise

Page 11: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Ground Based Project : FLUXNET LIMITATION

DISCONTINUITY OF MEASUREMENTS

COORDINATION BETWEEN STATIONS

UPSCALING METHODS

LIMITED AREA COVERAGE

SATELLITE MONITORING COMBINED WITH THIS GROUND BASED PROJECTS CAN BE A BETTER

OPTION

Page 12: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

ATMOSPHERIC SCIENCE SPACEBORNE INSTRUMENTS

Page 13: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

CURRENTLY WORKING SATELLITES

MID & THERMAL INFRARED REGION(TIR & MIR) HIRS(2002) - NOAA AIRS(2002) - NASA

IASI(2006) - EUMETSAT

DETECTION

Thermal radiation emitted from surface & atmosphere (3.6 to 15µm)

ADVANTAGE:Day & night measurement is possible

DISADVANTAGE:Lack of sensit ivity in lower troposphere

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CURRENTLY WORKING SATELLITES

UV/VIS/NIR/SWIR REGION SCIAMACHY(2002) - ESA TANSO(2009) - JAXA OCO(2009) - NASA

DETECTION

Reflected, backscattered, transmitted & emitted from surface & atmosphere (240 to 2400 nm)

DISADVANTAGE:Restricted to day only

ADVANTAGE:Sensit ivity constant with height & maximum near the surface

Page 15: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

ABSORPTION BANDS OF DIFFERENT CONSTITUENTS

Page 16: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

POSSIBLE ERROR SOURCES

EVALUATED IN ADVANCE: Spectroscopic parameters Solar spectra

CORRECTED BY ADDITIONAL INFORMATION

Cloud covered scene

Aerosol covered scene

Surface elevation

Surface spectra

Water vapor

Temperature

Cirrus effect can be cancelled by 760 nm(O 2 band) and 2000nm (H 2O saturated spectral

region).

Page 17: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

MEASURED DATA FILTERING FOR NOISE REMOVAL

FILTERING ITEMSSolar Zenith Angle

Cloud Estimation

Aerosol at high Altitudes

Filtered spectra

Aerosol Transport Model(ex.SPRINTARS)

Cloud

Input Spectra

Page 18: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

ATMOSPHERE R T MODEL

INITIAL CONSTITUENTS

TEMPERATURE

PRESSURE

ALBEDO

DATA PROCESSING

SYNTHESIZED SPECTRA

FILTERED SPECTRA

Yokota et. al

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VALIDATION

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CASE STUDY-I

STUDY AREA: Boreal forests (Novosibirsk region) & the region of Surgut

SENSOR USED: AIRS AMSU-A

RADIATIVE TRANSFER MODEL: SARTA

RUSSIAN METEOROLOGY AND HYDROLOGY Vol. 34 No. 4 2009

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1. SELECTION OF C02 SENSITIVE CHANNELS

CO2-sensit ive channels at low sensit ivity to interfering factors Nine LW-channels in the spectral range of 699–705 cm –1

Six SW-channels in the spectral range of 1939–2017 cm –1

THE STUDY HAS TWO PARTS:

∆TB(i) = δTB( i) +δqH2O TB(i) + δqO3TB(i) + δqTB(i) + . . . . + ξ i

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2. AIRS DATA INVERSION

Analysis of satell i te data to sample cloud free measurement or measurements reduced to cloud cleared condit ions (http://disc.gsfc.nasa/AIRS/data)

Inverse problem in respect to Xco 2 is solved numerically using the Gauss-Newton iteration algorithm, two independent estimates of Xco2 (LW) & Xco2 (SW) are estimated by AIRS data

Sampling of estimates Xco 2(LW) & Xco2(SW) derived for t ime interval and the sounding area are subject to spatiotemporal f i l tering

The results of aircraft CO 2measurements (spatial ly coincident and quasi- synchronous with satel l i te )at dif ferent alt i tudes are used for comparison

The systematic biases is calculated by -

δ(ᾳ) = [TBobs (ᾳ) - TB

calc (ᾳ)], ᾳ= 1, . . . ., n,

Page 23: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

The standard deviat ions (SD) of Xco 2(sat) from the aircraft observations at alt i tudes 7 and 3 km were calculated to estimate the errors of the results of the satell i te sounding. The SD are 1.5 and 1.2 ppm compared to the aircraft CO2 observations at alt i tudes 7 and 3 km, respectively.

Fig: comparison of satell i te(2) and aircraft data of 7000 m (1) & 3000 m (3)

RESULT COMPARISON

Novosibirsk

Surgut

Page 24: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

CASE STUDY-II

STUDIED GAS: Methane(CH 4)

SENSOR USED: SCIAMACHY (Channel 8 – 2260 to 2385 nm )

RADIATIVE TRANSFER MODEL: SCIATRAN

RADIATIVE TRANSFER ALGORITHM: WFM-DOAS

Atmos. Chem. Phys. Discussion., 4,2004

Page 25: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

THE WFM-DOAS RETRIEVAL ALGORITHM

Based on fitt ing a l inearised radiative transfer model I imod

plus a low order polynomial P i to the algorithm of the ratio of a measured nadir radiance & solar irradiance spectrum,i.e. observed sun-normalised radiance I i

obs . The WFM-DOAS equation can be written as-

|In I iobs (V t ) – [ In I i

mod (V) + ∑δ I imod / δv j /( v j – v j ) + P i (am )]|2 = |RES i|2 →min

The f it parameters are the desired “trace gas vertical column V j” and the polynomial coeff icient a m”.

Fit parameters are determined by LEAST SQUARE method

PRINCIPLE: Differential detection of radiance in gaseous absorption channels with respect to neighbouring atmospheric transparent spectral channels (not influenced by gas) ,to detect the conce. Of desired gas.

Page 26: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Parameters:

Cloud condition- UV PMD(Polarization Measurement Device) SCIAMACHY

Standard atmospheric condition-CH 4, CO2 current concentration

Tropospheric and stratospheric condition- aerosol

Surface albedo and solar zenith angle

Surface elevation

Water vapour column and temperature profi le shift

The reference spectra was generated by-

Radiative transfer model- SCIATRAN

Page 27: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

WFM-DOAS CH 4 VERTICAL COLUMN RETRIEVAL ERROR(A) USING SIMULATED MEASUERMENTS

ERROR B-TEMPERATURE PROFILE SHIFT is included

RESULT DISCUSSION

Page 28: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Tab; Comparison of SCIAMACHY WFM-DOAS v 0.5 with ground based FTS measurement.N= no. of SCIAMACHY measurements compared with FTS.

Result And Discussion

Page 29: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Fig. Methane column averaged mixing ratios as retr ieved from SCIAMACHY WFM-DOAS V 0.5.

RESULT DISCUSSION

Page 30: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

APPLICATION

STUDY AREA: Low and mid lat itudes of Northern Hemisphere

SENSOR USED: SCIAMACHY (1558 to 1594 nm)

ALGORITHM USED : WFM-DOAS version 1.0

Atmos. Chem. Phys. Discuss.,7,2007

Page 31: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

ALGORITHM: WFM-DOAS version 1.0

An improved version (Schneising et al. , 2007). The main problems of the previous version WFMDv0.4 (Buchwitz et al. ,) was solved using spectra with improved calibration Better consideration of surface spectral ref lect ivity variabil i ty I t is no longer required to apply a quite large empirical scal ing factor as was necessary for WFMDv0.4.

QUALITY FILTERING OF SCIAMACHY :

For cloud detection the measured oxygen column(755 to 775 nm) and PMDs is used.

Ground alt i tude(pressure) used in simulation by WFM-DOAS increased above 4.1 km.To reject ground scenes with strong aerosol contamination, addit ional f i l t rat ion of the SCIAMACHY XCO 2 measurements using NASA’s Absorbing Aerosol Index (AAI) data product from TOMS/ Earthprobe was done.

Concentrat ion of CO 2 can only be retr ieved over land , not over sea .

Page 32: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Fig. Atmospheric CO 2 over the northern hemisphere during 2003–2005 as retr ieved from SCIAMACHY

satell i te measurements.

FIRST DIRECT OBSERVATION OF ATMOSPHERIC CO 2 IN YEAR TO YEAR FROM SPACE

Page 33: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Fig; Satell i te retrieved XCO 2 and NOAA ESRL Carbon Tracker global assimilat ion system data

Increase in the amplitude of the CO 2 seasonal cycle with the increase in lat i tude

In the retr ieved XCO 2 seasonal cycle an error of 2ppm is seen.

ERROR & IT’S CORRECTION :

Page 34: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

The correction equation is – DIF=a + b*AMF

Where, DIF=difference between SCIAMACHY & Carbon Tracker

AMF=1/cos(SZA) + 1/cos(LOS) where, AMF=Air mass factor SZA=Solar zenith angle LOS=Line of sight scan angle

Page 35: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

APPLICATION:

STUDY AREA: 50 N to 67.50 S , 54.50 E to 1470 E

SENSOR USED: SCIAMACHY (Channel 8 – 2259 to 2361 nm) with WFM-DOAS V 0.4 SPOT-VEGETATION

ISPRS Archives XXXVIII-8/W3 Workshop Proceedings: Impact of cl imate change on agriculture,2009

Page 36: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

METHODOLOGYGlobal weekly ENVISAT-SCIAMACHY CH4 conce. (ppbv) data of 2004 & 2005

Global 10 days composite of SPOT-NDVI products of 2004 & 2005

Computed mean monthly CH4 (ppbv)

Study area was extracted by overlying the region’s boundary and gridded to 0.50 x 0.50 lat itude/longitude grid

Validation using NOAA-CMDL Global view data

Spatial and temporal variabil i ty over study area

CH4 data covering Kharif season (May-Oct) for

2004 & 2005

NDVI data covering Kharif season(May-Oct) for 2004 &

2005

Correlation between CH 4 conce. & NDVI during Kharif season over study area

Computed mean monthly NDVI

Page 37: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Fig 1. Temporal and Spatial Variat ion of Atmospheric CH4

Concentrat ion Over India During 2004 – 05

RESULTS:

Fig2. Temporal Variat ion of Vegetation Over India

During 2004–05

Page 38: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Fig 3. Two year khari f season averaged CH4 conce .

Fig 4. Two year khari f season averaged NDVI.

Fig 5. Correlat ion between CH 4 Conc. and Vegetation During Kharif Season in 2004-05

Page 39: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

PROBLEM OF THESE STUDIES:

Scattering at aerosol and/or cloud particles remains a major source of uncertainty for SCIAMACHY XCO 2 retr ievals

The XCO2 retr ieval error may amount to 10% in the presence of mineral dust aerosols. Houweling et al. (2005)

The thin scattering layer with an optical thickness of 0.03 in the upper troposphere can introduce XCO 2 uncertainties of up to several percent. Schneising et al. (2008)

Unfortunately, thin clouds with optical thicknesses below 0.1 cannot easily be detected within nadir measurements in the visible and near infrared spectral region. Reuter et al., 2009; Rodriguez et al.(2007).

Page 40: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Recent Advancements

Page 41: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Algorithm: Merged fit windows approach.

Radiative transfer model : SCIATRAN 3.0

Atmos. Meas. Tech., 3, 209–232, 2010

Page 42: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

The measurement vector y consists of SCIAMACHY sun-normalized radiances of two merged fit windows concatenating the measurements in the CO2 and O2 fit window.

= ( , ) + y F x b ԑX = state vectorb = parameter vector&, =ԑ error

The information about these parameters comes mainly from the O2 measurements and is made available in the CO2 band by the merged fit windows approach..

Page 43: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

The accuracy for scenes with optically thin cirrus clouds was drastically enhanced compared to a WFM-DOAS like retrieval.

At solar zenith angles of 400, the presence of ice clouds with optical thicknesses in the range of 0.01 to 1.00 contributed with less than 0.5 ppm to the systematic absolute XCO2 error if a perfect forward model is assumed.

RESULTS:

Page 44: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

Conclusions: Green House Gases (GHGs) can be measured with good accuracy from satellite data if proper algorithms are applied

Through inverse modeling of measured GHGs we can know in detail about their sources and sinks

Further development in understanding about different factors, their interactions influencing the GHG retrieval and improvement in mathematical methods will surely be able to predict GHGs with better accuracy

Monitoring of GHGs emitted from agricultural practices and activities, wetlands over a region can be done with good accuracy

Page 45: Retrieval & monitoring of atmospheric green house gases (gh gs) through remote sensing

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