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  • 标题:Evapotranspiration estimation using energy balance algorithm for pyramid-based spatially enhanced thermal infrared image.
  • 作者:Gowri, V. ; Thirumalaivasan, D.
  • 期刊名称:International Journal of Applied Engineering Research
  • 印刷版ISSN:0973-4562
  • 出版年度:2009
  • 期号:February
  • 语种:English
  • 出版社:Research India Publications
  • 摘要:Evapotranspiration (ET) is the combination of evaporation from the soil surface and transpiration from vegetation. Conventional methods of ET estimation are based on point measurements, which could provide accurate results over the areas surrounding instruments, but the results are not applicable to large heterogeneous areas. With the advent of satellite remote sensing various models concerning the derivation of evapotranspiration using satellite data have been published [1,2,3,4], which provides with spatial estimation of ET. Gowda [5] discusses remote sensing based regional ET prediction algorithms and their limitations, data needs and availability, knowledge gaps, and future opportunities and challenges with respect to agriculture. Remote sensing based Evapotranspiration is presently developed along two types of approach: (a) land surface energy balance and (b) reflectance based crop coefficient.
  • 关键词:Algorithms;Energy (Physics);Evapotranspiration;Infrared imaging;Remote sensing;Temperature measurement

Evapotranspiration estimation using energy balance algorithm for pyramid-based spatially enhanced thermal infrared image.


Gowri, V. ; Thirumalaivasan, D.


Introduction

Evapotranspiration (ET) is the combination of evaporation from the soil surface and transpiration from vegetation. Conventional methods of ET estimation are based on point measurements, which could provide accurate results over the areas surrounding instruments, but the results are not applicable to large heterogeneous areas. With the advent of satellite remote sensing various models concerning the derivation of evapotranspiration using satellite data have been published [1,2,3,4], which provides with spatial estimation of ET. Gowda [5] discusses remote sensing based regional ET prediction algorithms and their limitations, data needs and availability, knowledge gaps, and future opportunities and challenges with respect to agriculture. Remote sensing based Evapotranspiration is presently developed along two types of approach: (a) land surface energy balance and (b) reflectance based crop coefficient.

Remote sensing images exhibit usually either high spectral resolution and low spatial resolution or low spectral resolution and high spatial resolution. The spatial and temporal remote sensing data from the existing set of earth observing satellite platform are not sufficient enough to be used in the estimation of spatially distributed ET. Evaporation is generally estimated by using thermal infrared data acquired by satellite and ground based meteorological data as inputs [1]. The coarse spatial resolution of thermal bands has caused the current ET estimates of little use for analyzing its spatial distribution.

However research opportunities exist to improve the spatial and temporal resolution of ET developing algorithms to increase the spatial resolution of reflectance and surface temperature data derived from Landsat/ASTER/MODIS images using same/other-sensor high resolution multi-spectral images [5]. Due to the tradeoff between spatial and spectral resolution, spatial enhancement of coarser resolution data is desirable [6]. One possible solution comes from the field of data fusion.

Data fusion/merging techniques take advantage of the complementary spatial/spectral resolution characteristics of imaging sensors to spatially enhance the acquired images. Multi resolution techniques are extremely attractive for image understanding since they provide a thorough yet multi fold, description of the imaged scene. Wavelets, subbands and Gaussian/Laplacian Pyramids are most suitable representations to allow spatial analysis to be carried out on multiple scales [7].

Some studies have been published where images acquired in thermal infrared bands have been synthesized with a better spatial resolution with a satisfactory quality by means of images acquired in the visible range [8,9,10,11]. Data fusion based on multi resolution analysis, requires a model to describe about how the spatial details of high resolution image are to be injected into the coarse resolution image.

Goal of this work is to highlight the use of Enhanced Laplacian Pyramids (ELP) as a multi resolution data processing technique for spatial enhancement of thermal infrared image. The spatially enhanced thermal band is subsequently utilized for determining evapotranspiration by means of surface energy balance method.

Materials and Methods

Landsat-7 ETM+ imagery is used for the analysis. There are a total of 8 spectral bands from 15 m (Panchromatic), 30 m (Visible and Short-wave infrared) and 60 m (Thermal). A cloud free Landsat 7 ETM+ data (Path/Row 143/53) for the date 15 May 2001 is obtained from the GLCF University of Maryland website (http://glcfapp.umiacs.umd.edu:8080/esdi/) in GeoTIFF format and are in the UTM Zone 44 N projection and WGS 84 datum. Fig 1 shows the study area selected for this analysis. The image has been analysed for determination of different components of surface energy balance.

[FIGURE 1 OMITTED]

Multiresolution Image Analysis

Data merging techniques have been designed not only to allow integration of different information sources, but also to take advantage of complementary spatial and spectral resolution characteristics [11]. The visible bands exhibit a high spatial resolution compared to the multispectral observations of the same sensor. The goal is to obtain fused bands as similar as possible to what the multispectral sensor would image at the resolution of visible band. Data merging requires the definition of a model describing, how the missing high pass details to be injected into the resampled MS bands, is extracted from visible bands. Since the high-pass filtering technique [12] fusion methods based on injecting high frequency components into resampled versions of MS data have been demonstrated a superior performance. The algorithm proposed in the following work is Enhanced Laplacian Pyramid [13] which is a variant of HPF. Aiazzi [7], reports about the pyramid-based multisensor image data fusion of data from remote sensing images having different ground resolutions. The Enhanced Laplacian Pyramid method is adopted for this study and is described below.

Enhanced Laplacian Pyramids

The basis of the pyramid is the original image. Each level of the pyramid is an approximation of the original image computed from the original image. The Laplacian pyramid (LP) originally proposed in P. J. Burt [14] is a band-pass image decomposition derived from the Gaussian Pyramid (GP), which is a multi resolution image representation obtained through a recursive reduction (low pass filtering and decimation) of the image dataset.

Let [G.sub.o] (i, j) be the original gray-scale image, where i = 0, ..., M-1 and j = 0, ..., N-1, M = u x [2.sup.k], N = v x [2.sup.k]. The GP is defined as [G.sub.k] (i,j) = [reduce.sub.2] [[G.sub.k-1]] (i, j) = [Lr.summation over (m=-Lr)] [Lr.summation over (n=-Lr)] r(m)r(n)[G.sub.k-1] (2i + m, 2j + n)

for k = 1, ..., K, i = 0, 1, ..., M/[2.sup.k]-1 and j = 0, 1, ..., N/[2.sup.k]-1; in which k identifies the level of pyramid, K being the top or base band approximation. Burts parametric kernel {r(m),m = [-L.sub.r], ..., [L.sub.r]} ([L.sub.r] = 2) has been widely used [14, 13]. The 2D reduction low-pass filter stems from a linear symmetric 1-D kernel, generally odd sized.

From the GP, the Enhanced LP (ELP) [13] is determined, for k = 0,.., k-1, as [L.sub.k] (i, j) = [G.sub.k] (i, j)-exp [and.sub.2] [[G.sub.k+1]] (i, j) in which exp [and.sub.2] [[G.sub.k+1]] denotes the (k+1)st GP level expanded by 2 to match the underlying kth level:

exp [and.sub.2] [[G.sub.k+1]] (i, j) = [Le.summation over (m=-Le) (i + m)] [Le.summation over (n=-Le)] e(m)e(n)[G.sub.k+1] (i + m/2, j + n/2)

for i = 0, ..., M/[2.sup.k] - 1, j = 0, ..., N/[2.sup.k] - 1, and k = 0, ... K-1. the 2-D low-pass filter for expansion is given as the outer product of a linear symmetric odd sized kernel {e(m), m = [-L.sub.e], ..., [L.sub.e]}. Summation terms are taken to be null for non-integer values of (i+m)/2 and (j+n)/2, corresponding to interleaving zeros. The base band approximation is added to the band pass ELP ie., [L.sub.K] (m, n) [equivalent to] [G.sub.K] (m, n), to yield a complete image description.

The detail is given as the difference between the original image and an expanded version of the low pass approximation. The detail injection model describes the relationship between the detail observed in high resolution band and the ones that should appear in the enhanced band [11]. The spectral distortion minimisation (SDM) model [15] is adopted here to preserve the spectral information.

Algorithm for Evapotranspiration estimation

Remote sensing has long been recognized as the most feasible means to provide spatially distributed regional ET information on the land surfaces. There are many remote sensing algorithms for estimating the energy balance fluxes on the surface, each algorithm has its own advantages and disadvantages. The surface energy balance for land (SEBAL) is used to estimate the evapotranspiration and other energy balance terms. The processing of the SEBAL model has been done after the standard method described in Bastiaanssen [1] to calculate energy partitioning at the regional scale with an effort to use minimum ground data.

In the SEBAL model, ETa is calculated from satellite images and local weather station data using surface energy balance equation. Since the satellite image provides information for the satellite overpassing time only, the SEBAL computes an instantaneous ET flux for the image time. The instantaneous ET flux is calculated for each pixel of the image as a residual of the surface energy balance equation:

[lambda]E = [R.sub.n] - [G.sub.0] - H (1)

where; [lambda]E is the latent heat flux (measure of evapotranspiration) in [Wm.sup.-2], [R.sub.n] is the net radiation flux at the surface in [Wm.sup.-2], [G.sub.0] is the soil heat flux in [Wm.sup.-2] and H is the sensible heat flux to the air in [Wm.sup.-2].

The net radiation flux at the surface (Rn) is the actual radiant energy available at the surface. It is given by the surface radiation balance equation:

[R.sub.n] = (1 - [alpha])[R.sub.S] [down arrow] + [R.sub.L] [down arrow] - [R.sub.L] [up arrow] - (1 [[epsilon].sub.0])[R.sub.L] [down arrow] (2)

where; [R.sub.S] [down arrow] is the incoming shortwave radiation ([Wm.sup.-2]), [alpha] is the surface albedo (dimensionless), [R.sub.L] [down arrow] is the incoming longwave radiation ([Wm.sup.-2]), [R.sub.L] [up arrow] is the outgoing longwave radiation ([Wm.sup.-2]), and [[epsilon].sub.0] is the surface thermal emissivity (dimensionless).

The next step of the SEBAL is to compute the soil heat flux (G) and the sensible heat flux to air (H). Soil heat flux is the rate of heat storage into the soil and vegetation due to conduction. In the SEBAL, the ratio G/Rn is calculated using the following empirical equation developed by Bastiaanssen:

C/[R.sub.n] = [T.sub.S]/[alpha] (0.0038[alpha] + 0.0074[[alpha].sup.2]) (1 - 0.98[NDVI.sup.4] (3)

where Ts is the surface temperature (in [degrees]C); [alpha] is the surface albedo and NDVI is the Normalized Difference Vegetation Index.

Sensible heat flux is the rate of heat loss to the air by convection and conduction due to temperature difference. The computation of H requires more attention because of the strong dependence upon the type of surface and height of vegetation and local meteorological conditions [16]. It is computed using the following equation for heat transport:

H = ([[rho].sub.a] x [C.sub.p]dT)/[r.sub.ah] (4)

where [[rho].sub.a] is air density (1.15 kgm-3), [C.sub.p] is air specific heat (1004.16 Jkg-1K-1), dT is the temperature difference ([T.sub.S] - [T.sub.a]) and rah is the stability corrected aerodynamic resistance to heat transport (s/m). [r.sub.ah] varies with wind speed, and intensity and direction of the H. Therefore, rah could be determined through several iterations.

[r.sub.ah] = 1n([Z.sub.h] - d/[Z.sub.oh]) - [[psi].sub.h]/u * x k (5)

u * = k x [u.sub.z]/1n([Z.sub.m] - d/[Z.sub.om]) - [[psi].sub.m] (5)

where [Z.sub.m] and [Z.sub.h] are heights in meters above the zero plane displacement (d) of the vegetation, u * is the friction velocity (m/s) which quantifies the turbulent velocity fluctuations in the air and k is von karman's constant (0.41), k is von Karman's constant, [u.sub.z] is the wind speed (m/s) at height [Z.sub.m] and [Z.sub.om] is the momentum roughness length (m). [[psi].sub.m] and [[psi].sub.h] are stability correction factors for momentum and heat transfer, respectively which are functions of Monin-Obukhov stability parameters.

The actual evapotranspiration, [ET.sub.a] (mm/day) is determined as

[ET.sub.a] = 8.64 x [10.sub.7] [LAMBDA](24[integral]0 [R.sub.n])/([[lambda][rho].sub.w]) (7)

where [LAMBDA] = evaporative fraction [[LAMBDA] = [[lambda]E/([lambda]E + H)] on the instantaneous time basis (-); [lambda] are latent heat of vaporization (J/Kg) and [[rho].sub.w] = density of water (Kg/[m.sup.3]).

Approach

In Landsat ETM+ the visible band are acquired at 30m resolution while the thermal band is acquired at a coarser resolution of 60m. The spectral radiances of the visible and thermal infra red band were calculated using the calibration equations for the sensors [17]. The image based atmospheric correction (Dark object subtraction) is carried out for the optical remote sensing data [18]. The atmospheric correction for thermal band is applied as described by Barsi et al., [19]. The atmospherically corrected TIR is resampled to the spatial resolution of the visible band (30m).

Evaporation is generally estimated using the thermal infrared data acquired by satellite data and ground based meteorological data inputs. The SEBAL is carried out as discussed in the section 2.2. The components involved in the ET computation are modeled in a series of steps using ERDAS Imagine 8.6 Model Maker tool. For insight of the practical procedure, Tasumi [20], provide extensive details of step-by-step considerations applied. The actual ET maps derived are at the spatial resolution of the visible bands.

In the next attempt the spatial resolution of the thermal band is enhanced from 60m to 30m by applying the multi resolution approach. Fig 2 reports the scheme for spatial enhancement of the TIR image with spatial details obtained from VNIR image. The ELP was performed, and the spatial detail to be injected into the thermal band was extracted from the visible band (band2). The high-pass details are obtained as the difference between the high resolution image and its low-pass version achieved through low pass filtering. These details are then added to the expanded versions of the low resolution thermal band. The 7 taps kernel is applied to yield a bicubic interpolation for low pass filtering.

The surface temperature images were generated from original TIR band resampled to 30 m and from spatially enhanced TIR image. The values obtained are statistically compared. The SEBAL is applied with the above derived surface temperature maps at 30 m spatial resolution. The flux estimates and evapotranspiration for both the analysis are compared. The Evapotranspiration estimates are also validated using the conventional Penman Monteith method [21].

[FIGURE 2 OMITTED]

Quality Assessment of Spatially Enhanced Image

The ELP has been experimented on Landsat ETM+ image. The similarity of the images to be merged is to be studied before deciding on the selection of VNIR band for obtaining the spatial details. The VNIR band 2 and band 3 are reduced to the resolution of the original TIR image (60m). The correlation analysis is carried out and correlation coefficients are used to quantitatively evaluate the data merging results. The correlation matrix in table 1 reports the similarity which has been computed between original TIR and reduced VNIR bands. The analysis of the table 1 reveals that band 2 is strongly correlated with the TIR band. Since band 2 is most similar to the TIR band, the spatial details to be injected in the expanded TIR band is obtained from band 2. Quality assessment of the data merging is assessed by visual analysis from Fig 3.

[FIGURE 3 OMITTED]

The result of the spatially enhanced TIR image with the band 2 is reported in the table 2. The original 60m TIR has been expanded to the scale of VNIR bands (30m) and are compared with the TIR images merged by means of VNIR band 2 and VNIR band 3. From the correlation matrix reported in table 2 expanded TIR image is similar to the image merged by means of VNIR band 2. Fig 4 shows the expanded original TIR image along with the spatially enhanced image of TIR by means of VNIR band2 and 3.

[FIGURE 4 OMITTED]

The each merged image is reduced to the original resolution (60m) and then compared with the original TIR image. From the results are reported in table 3, the TIR image merged by band 2 is considered for estimating surface temperature image.

Comparison of Surface Temperature Images

The surface temperature images were estimated using the simplified plank function for the resampled TIR image and spatially enhanced TIR image. Table 4 reports the statistical results of surface temperature obtained from resampled TIR image and spatially enhanced TIR image. Table 5 shows the surface temperature of the different landuse/cover. Fig 5 reports the variation in surface temperature for different landuse. The images of the surface temperature for resampled TIR and spatially enhanced TIR image is shown in Fig 6.

[FIGURE 5 OMITTED]

Estimation of Energy Balance and ET.

Surface energy balance algorithm for land (SEBAL) is used to estimate the daily evapotranspiration and the different terms of surface energy balance at the time of satellite overpass. Table 6 depicts the energy balance and daily ET for agricultural landuse type. The table reports the instantaneous values for SEBAL analysis on resampled TIR image and spatially enhanced TIR image.

The spatial variation in the evapotranspiration can be visually read from the Fig 7. The mean values of the different terms calculated from SEBAL analysis are reported in table 8. Prior to the generation of the [ET.sub.a] image, an evaporative fraction image is generated. The statistical analysis indicates the range between 0 and 1 and the mean values are tabulated in table 7. The low evaporative fraction is observed for bareland and high evaporative fraction is observed for water bodies. The agricultural fields closer to the river show high evaporative fraction compared to the nonagricultural land.

The range of [ET.sub.a] for cropped areas is observed between 1.9 and 3.1 mm/day (mean 2.5mm/day) for the image analysed with original 60m TIR image. For the analysis with spatially enhanced TIR image the range of [ET.sub.a] for cropped areas is observed between 3.2 and 4.5 mm/day (mean 3.85 mm/day). In the absence of ground information on energy fluxes the reliability of the estimated [ET.sub.a] by the SEBAL model is checked with conventional evapotranspiration equation using meteorological data. The CROPWAT model is used for the estimation of evapotranspiration from climatic data. The average [ET.sub.a] by using the CROPWAT model (Penman-Monteith equation) is calculated as 2.8 mm/day and satellite based estimation of evapotranspiration show that values are higher than the values computed using CROPWAT.

[FIGURE 7 OMITTED]

Conclusions

The main objective of the paper was to apply multi resolution technique for facilitating the spatial enhancement of the thermal infrared image by exploiting the high spatial resolution visible image as a complementary data. The application of the energy balance equation to satellite remote sensing has matured over the past decades and can bring practical results today. The combination of ground and remotely sensed data is extremely important in areas with insufficient monitoring of meteorological variables. Evapotranspiration at higher spatial resolution is required than coarser resolution for better analysis in various applications. In this study the daily evapotranspiration images was generated from the original TIR image and for the spatially enhanced TIR image. The adopted multi resolution technique of enhanced Laplacian pyramid was working better and the other techniques like wavelet analysis, subband analysis can also be studied.

References

[1] Carlson, T. N., and Buffum, M. J., 1989, "On estimating total daily evapotranspiration from remote sensing temperature measurements," Remote Sens. Environ., 29, pp. 197-207.

[2] Carlson, T.N., Capehart, W. J., and Gillies, R. R., 1995, "A newlook at the simplified method for remote sensing of daily evapotranspiration," Remote Sens. Environ., 49, pp. 264-274.

[3] Bastiaansen, W.G.M., Menenti, M., Feddes, R.A., and Holtslag, A.A.M., 1998, "A remote sensing surface energy balance algorithm for land (SEBAL)-1. Formulation," J. Hydrol., 212-213, pp. 198-212.

[4] Kustas, W.P., and Norman, J.M., 1996, "Use of remote sensing for evapotranspiration monitoring over land surface," Hydrol Sci J., 41(4), pp. 495-516.

[5] Gowda, P.H., and Chavez, J.L., 2008, "ET mapping for agricultural water management: present status and challenges," Irrig Sci., 26, pp. 223-237.

[6] Aiazzi, B., Alparone, L., and Baronti, S., 2002, "Context-driven fusion of high spatial and spectral resolution images based on oversampled multi resolution analysis ," IEEE Trans. Geosci. Remote Sens., 40(10), pp. 2300-2312.

[7] Aiazzi, B., Alparone, L., Baronti, S., and Carla, R., 1998, "An assessment of pyramid-based multisensor image data fusion," Image and signal Processing for Remote Sensing IV, S.B. Serpico, ed., Proc. SPIE 3500, pp. 237-248.

[8] Nishii, R., Kusanobu, S., Tanaka, S., 1996, "Enhancement of low spatial resolution image based on high resolution bands," IEEE Trans. Geosci. Remote Sens., 34(5), pp. 1151-1158.

[9] Liu, J.G., and Moore, J.M., 1998, "Pixel block intensity modulation: adding spatial detail to TM band 6 thermal imagery," Int. J. Remote Sens., 19(13), pp. 2477 - 2491.

[10] Wald, L., and Baleynaud, J.M., 1999, "Observing air quality over the city of Nantes by means of Landsat thermal infrared data," Int. J. Remote Sens., 20(5), pp. 947-959.

[11] Aiazzi, B., Alparone, L., Baronti, S., Santurri, L., and Selva, M., 2005, "Spatial Resolution Enhancement of ASTER Thermal Bands," Image and signal Processing for Remote Sensing XI, S.B. Serpico, ed., Proc. SPIE 5982, pp. 237-248.

[12] Chavez Jr, P.S., Sides, S.C., and Anderson, J.A., 1991, "Comparison of three different methods to merge multiresolution and multispectral data: Landsat TM and SPOT panchoromatic," Photogramm. Eng. Remote Sens., 57(3), pp. 295-303.

[13] Aiazzi, B., Alparone, L., Baronti, S., and Lotti, F., 1997, "Lossless image compression by quantization feedback in a content-driven enhanced Laplacian pyramid," IEEE Trans. Image Processing., 6, pp. 831-843.

[14] Burt, P.J., and Adelson, E.H., 1983, "The Laplacian Pyramid as a compact image code," IEEE Trans.commun., COMM-3, pp. 532-540.

[15] Aiazzi, B., Alparone, L., Baronti, S., Pippi, I., and Selva, M., 2002, "Generalized Laplacian pyramid-based fusion of MS + P image data with spectral distortion minimisation," ISPRS Int. Archives of Photogrammetry and Remote Sensing., 34(3B,W3), pp 3-6.

[16] Ambast, S.K., Keshari, A.K., and Gosain, A.K., 2008, "Estimating regional evapotranspiration using remote sensing: Application to Sone low level canal system, India," J. Irrig. Drain. Eng., 134(1), pp. 13-25.

[17] Landsat 7 Science Data Users Handbook, 2002. Landsat Project Science Office, NASA Goddard Space Flight Center in Greenbelt, Maryland, http://landsathandbook.gsfc.nasa.gov/handbook.html.

[18] Teillet, P.M., and Fedosejevs, G., 1995, "On the dark target approach to atmospheric correction of remotely sensed data," Canadian Journal of remote sensing., 21, pp 374- 387.

[19] Barsi, J.A., Barker, J.L., and Schott, J.R., "An Atmospheric Correction Parameter Calculator for a Single Thermal Band Earth-Sensing Instrument," IGARSS 03, 21-25 July 2003 Centre de Congres Pierre Baudis, Toulouse, France.

[20] Allen, R., Pereira, L., Raes, D., Smith, M., 1998, "Crop evapotranspiration: guidelines for computing crop water requirements," FAO Irrigation and Drainage Paper No. 56. FAO, Rome.

[21] Tasumi, M., and Allen, R.G., 2000, "Application of the SEBAL methodology for estimating consumptive use of water and streamflow depletion in the Bear River Basin of Idaho through Remote Sensing. Appendix A: The theoretical basis of SEBAL," Final Report, The Raytheon Systems Company, EOSDIS Project.

V. Gowri (1) and D. Thirumalaivasan (2)

(1) Visiting Faculty, Institute of Remote Sensing, Anna University, Chennai, India. E-mail: gowrisenthilkumar@gmail.com

(2) Assistant professor Institute of Remote Sensing, Anna University, Chennai, India. E-mail: dtvasan@annauniv.edu
Table 1: Correlation between reduced
VNIR band2 and 3 with original TIR.

Band      2       3        6

2         1      0.9     0.8437
3        0.9      1      0.6845
6      0.8437   0.6645     1

Table 2: Correlation of the merged TIR images (30m) with the Expanded
TIR image.

                           Band 6 enhanced   Band 6 enhanced   Expanded
Band                          by band 2         by band 3      Band 6

Band 6 enhanced by band 2         1              0.8963        0.8263
Band 6 enhanced by band 3      0.8963               1          0.6734
Expanded Band 6                0.8263            0.6734           1

Table 3: Correlation of the original TIR image and the reduced TIR
merged images.

                                    Band 6 enhanced   Band 6 enhanced
Band (60m)                 Band 6      by band 2         by band 3

Band 6                       1          0.8198            0.6053
Band 6 enhanced by band 2  0.8198          1              0.7998
Band 6 enhanced by band 3  0.6053       0.7998               1

Table 4: Statistical result of the surface temperature (Ts).

      Surface Temperature  (Ts in K)

                                 Spatially
                Resampled TIR   Enhanced TIR

Minimum            296.08          265.73
Maximum            318.29          355.26
Mean               306.448         309.368
Std deviation        3.406           6.617

Table 5: Surface temperature values for different
Landuse/cover types.

              Surface Temperatur(Ts in K)

                               Spatially
Land use      Resampled TIR   Enhanced TIR

Agriculture      301.61         309.709
Urban            306.163        314.679
Water            299.018        298.693
Bare land        312.976        329.546

Table 6: Instantaneous parameter over agricultural landuse during
satellite overpass.

                                    SEBAL with    SEBAL with Spatially
                         Units     Resampled TIR      Enhanced TIR

                                   Location: Latitude:10[degrees]
                                   05' 25", Longitude: 77[degrees]
                                   52' 22"
  Surface Albedo          --           0.16               0.161
       NDVI               --           0.688              0.695
Surface Emissivity        --           0.998              0.992
Surface temperature       K          304.076            305.548
 Instantaneous Rn     [Wm.sup.-2]    300.903            290.630
  Instantaneous G     [Wm.sup.-2]     36.147             36.252
  Instantaneous H     [Wm.sup.-2]     59.308              56.24
 Instantaneous LE     [Wm.sup.-2]    205.448            198.138
Evaporative Fraction      --           0.776              0.778
    Rn 24 Hours       [Wm.sup.-2]    345.399            335.394
     Daily ET           mm/day         3.9                3.2

Table 7: Comparison of SEBAL analysis.

                               SEBAL with
Parameters                    resampled TIR

                      Min         Max        Mean

NDVI                 0.092       0.752       0.411
Ts (K)               296.08     318.29      306.448
Rn ([Wm.sup.-2])     137.23     424.91      267.431
G ([Wm.sup.-2])      27.934     58.782      44.064
H ([Wm.sup.-2])      45.083     219.065     83.737
24 hour ET
(mm/day)              0.62        4.5         2.6

                               SEBAL with
Parameters               Spatially Enhanced TIR

                      Min         Max        Mean

NDVI                 0.025       0.798       0.423
Ts (K)               265.73     355.26      309.368
Rn ([Wm.sup.-2])     23.491     431.287     241.878
G ([Wm.sup.-2])      18.55       66.49       42.85
H ([Wm.sup.-2])      16.573     328.268     110.728
24 hour ET
(mm/day)              0.29        6.7        3.45
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