Figure 3. Experimental Workflow
4. RESULT AND ANALYSIS
4.1 Trail Road Landfill
Figures 4 and 5 show a comparison between the LST and the air
temperature for specific dates in 2007 and 2008. In 2007, the
LST for the Trail Road landfill in April and June is higher than
the air temperature by 10?C. A drop in the temperature
difference is found in July and August, mainly due to relative
low sky visibility and haze effects on the remote sensing
images. The result may be affected even when the atmospheric
correction is applied. The LST for the landfill site is constantly
higher than the air temperature by 6?C during September and
October.
ir Tengrerature
Temperature °C
+
-07 May-23 Tun-15 Tui-17 Aug-02 Aug-27 Sept-19 CcD5
Date
Apmr-21 M
Figure 4. Comparison of LST and the Air Temperature for the
Trail Road Landfill in 2007
In 2008, the difference between the LST and the air temperature
varied due to seasonal changes. On April 14, the LST was 7°C
higher than the air temperature and the difference in the
temperature was more than 10?C during May to August. The
temperature difference drops below 7?C after September except
for the result in October 7th. Based on the results from 2001 to
2009 as well as the results for 2007 and 2008, one can conclude
that the LST for the landfill site is always higher than the air
temperature.
45
40
35
30
25
20
Temperature °C
Apr-14 May-25 Jul-12 Aug-20 Sept-5 Oct-7 Oct-23
Date
Figure 5. Comparison of LST and the Air Temperature for the
Trail Road Landfill for Year 2008
The Trail Road landfill site is monitored by a comprehensive
ground monitoring system, which measures and records the
amount of landfill gas, the quality of surface and groundwater,
and soil contamination. A preliminary analysis was conducted
to determine the correlation between the measurements from
these monitoring wells and the LST derived from the remote
sensing images. Such an analysis has not been performed for the
previous literature which adopted Landsat images for landfill
monitoring. The measurements of two landfill gas monitoring
stations (GM-2 and GM-17) are utilized for this preliminary
analysis. The reasons to select these two stations from the total
of 28 stations are mainly the availability of the measurements
recorded in the annual reports and the well distribution of these
stations among Stages 1 to 4 (see Figure 1).
These monitoring wells measure the percentage of emitting
methane (CHy) and the pressure; the records of CH, are taken to
perform the correlation, as CH, is the main element of landfill
gas. Also, the measurements from the shallow level of the
monitoring wells are taken as it is close to the ground level that
will be close to the land surface for the calculation of LST. Due
to inconsistency between the date of ground measurement and
the date of the remote sensing image acquisition, the ground
data were linearly interpolated so as to align the dates to the
remote sensing image. Correlation analysis is conducted for
both 2007 and 2008 by using the regression analysis.
Figures 6 and 7 show the relationship between the percentages
of emitting methane recorded in station GM-2 (located at the
south of Stage 1) and the LST in 2007 and 2008, respectively.
Figures 8 and 9 show the relationship between the percentages
of emitting methane recorded in station GM-17 (located at the
south of Stage 3) and the LST in 2007 and 2008, respectively.
To remove seasonal effects in the derived LST data, the LST
value is subtracted from the air temperature, so all the
measurements are reduced to the same base. Preliminary
analysis revealed that a mid-correlation was observed for both
of the ground- monitoring wells in 2008 where R? is 0.573 for
GM-2 and R? is 0.914 for GM-17. However, both stations had
low correlation coefficient with the LST measured in 2007
where R was 0.066 in GM-2 and R? was 0.332 in GM-17). In
spite of these results, all the fitted regression lines show that the
amount of emitting methane has direct proportional relationship
to LST.
- 0M RA RA
oO t 4 o «
Percentage of Emitting Methane
Recorded in the Landfill Gas (%)
en + OQ 0
0 2 4 6 8 10 13 14 16
Temperature Difference (*C)
Figure 6. Relationship between the Percentage of Emitting ;
Methane Recorded in GM-2 and the Temperature for 2007 (R
— 0.066)
Percentage of Emitting Methane
Recorded in the Landfill Gas (%)
es
ag
Metha
Percentage of Emtting Methane
Recorded in the Landfill Gas
— 1
ag
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Methai
Percentage of Emitting Methane
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