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Analysis of Air Pollution Exposure of Individuals in - Clean Air Initiative

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Speed (kph)<br />

Speed (kph)<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

AM Philcoa - Kalaw Runs<br />

0 2 4 6 8 10 12 14<br />

Distance Covered (km)<br />

travel speed mean travel speed mean runn<strong>in</strong>g speed<br />

AM Kalaw to Philcoa Runs<br />

0 2 4 6 8 10 12 14<br />

Distance Covered (km)<br />

travel speed mean travel speed mean runn<strong>in</strong>g speed<br />

PM Philcoa - Kalaw Runs<br />

Philcoa - Kalaw Kalaw - Philcoa<br />

AM PM AM PM<br />

2/8/2001 65 59 45 77<br />

2/9/2001 62 63 56 67<br />

2/12/2001 64 77 50 81<br />

Average 64 66 50 75<br />

Speed (kph)<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

0 2 4 6 8 10 12 14<br />

Distance Covered (km)<br />

travel speed mean travel speed mean runn<strong>in</strong>g speed<br />

Figure 7. Travel Speed-Distance Diagram for AM and PM Runs from<br />

Philcoa to T.M. Kalaw Avenue<br />

Speed (kph)<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

PM Kalaw - Philcoa Runs<br />

0 2 4 6 8 10 12 14<br />

Distance Covered (km)<br />

travel speed mean travel speed mean runn<strong>in</strong>g speed<br />

Figure 8. Travel Speed-Distance Diagram for AM and PM Runs from<br />

T.M. Kalaw Avenue to Philcoa<br />

Table 2. Summary <strong>of</strong> Travel Time to and from Philcoa to T.M. Kalaw Avenue <strong>in</strong> M<strong>in</strong>utes<br />

The authors used different sections along the route with the observed delays to compute the<br />

average travel speed and runn<strong>in</strong>g speed for each section. The sections identified were mostly<br />

between signalized <strong>in</strong>tersections along the route.<br />

Figures 9 to 12 show the variation <strong>in</strong> the measured SPM concentration with respect to the<br />

different sections along the route. There is high variation <strong>in</strong> the observed section<br />

concentrations. A probable reason is that the different sections chosen along the route are<br />

not equidistant from each other, however, as shown <strong>in</strong> the graphs, there are still sections that<br />

have very high disparities among the observed levels for the different runs. This signifies<br />

that the distances between the specified sections do not directly affect SPM concentrations.<br />

The sensitivity <strong>of</strong> the measur<strong>in</strong>g <strong>in</strong>strument to SPM from direct emissions <strong>of</strong> jeepneys along<br />

the route is the reason for these erratic concentrations <strong>of</strong> SPM <strong>in</strong>side the jeepney while <strong>in</strong><br />

transit. Smoke-belch<strong>in</strong>g vehicles near the ridden jeepney or the smoke emitted by the ridden<br />

jeepney itself <strong>in</strong>creases the read<strong>in</strong>gs taken from the measur<strong>in</strong>g <strong>in</strong>strument. Nonetheless, the

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