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" SURFACE COAL MINE MODEL EVALUATION: CORDERO MINE, TSP *** 06/20/95
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-------
APPENDIX E
CORDERO MINE ON-SITE METEOROLOGICAL DATA
This appendix presents the on-site hourly meteorological data that were used in the
Cordero Mine model evaluation study. The listing includes annotations identifying when missing
data occurred and what data substitutions were made.
E-l
-------
-------
Column Description
A Julian Day
B Hour of Day
C Wind Speed (mph)
D Wind Direction (deg)
E Sigma Theta (deg)
F Air Temperature (deg F)
G Precipitation (in)
Note: The following data is for the year 1993.
* Indicates that the information (in the columns
indicated in the parenthesis) came from the
Caballo Rojo met station.
** Indicates that the o, information came from the
Coal Creek Mine's met station.
*** Indicates that the os information came from the
Black Thunder Mine's met station.
139 1
139 2
139 3
139 4
139 5
139 6
139 7
139 8
139 9
139 10
139 11
139 12
139 13
139 14
139 15
139 16
139 17
139 18.
139 19
139 20
139 21
139 22
139 23
139 24
140 1
140 2
140 3
140 4
140 5
140 6
140 7
140 8
140 9
140 10
140 11
140 12
140 13
140 14
140 15
140 16
140 17
140 18
140 19
140 20
140 21
140 22
140 23
140 24
141 1
141 2
141 3
141 4
141 5
141 6
141 7
5.5 297
7.8 304
7.3 311
7.8 331
7.3 323
5.9 295
4.9 325
6.9 347
8.9 353
9.4 16
9.8 356
10.5 339.
9.9 5
10.7 349
12.6 12
11.6 15
10.3 23
11.6 31
11.5 41
8.3 56
5.6 76
5.7 98
7.2 137
7.4 144
10.5 180
10.5 165
10.5 162
10.3 150
11.1 150
14.4 153
14.3 155
15.2 153 .
15.0 158
15.5 159
12.9 159
10.5 146
9.9 147
7.3 138
7.0 228
6.1 125
4.2 163
5.7 141
8.3 133
8.6 147
7.7 156
9.7 159
14.7 193
13.4 174
14.7 162
11.5 165
13.2 158
13.7 158
15.3 169
16.5 164
16.5 164
8
3
3
2
5
5
9
14
18
21
25
17
25
19
20
20
15
10
7
6
8
8
4
4
6
4
3
4
5
4
5
6
8
9
12
15
16
22
, 23
25
24
15
5
3
8
6
7
4
4
5
4
4
4
3
4
45.9
45.9
44.5
41.5
39.3
42.2
48.1
51.6
54.1
55.7
57.2
58.7
59.7
60.8
61.0
60.8
59.2
58.1
55.5
51.6
48.3
45.1
44.0
43.4
42.7
42.0
41.4
42.1
42.4
44.4
46.3
48.9
52.0
55.7
58.8
61.1
.63.6
65.8
67.3
68.3
68.3
67.4
63.5
58.7
56.9
56.7
57.6
56.8
55.5
54.1
51.2
48.6
47.6
49.4
51.8
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0:00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
. 0.00-
0.00
0.00
0.00
0.00
0.00
0.00
Q.OO
E-2
-------
141 8
141 9
141 10
141 11
141 12
141 13
141 14
141 15
141 16
141 17
141 18
141 19
141 20
141 21
141 22
141 23
141 24
142 1
142 2
142 3
142 4
142 5
142 6
142 7
142 8
142 9
142 10
142 11
142 12
142 13
142 14
142 15
142 16
142 17
142 18
142 19
142 20
142 21
142 22
142 23
142 24
143 1
143 2
143 3
143 4
143 5
143 6
143 7
143 8
143 9
143 10
143 11
143 12
143 13
143 14
143 15
143 16
143 17
143 18
143 19
143 20
143 21
143 22
143 23
143 24
144 1
144 2
144 3
144 4
144 5
144 6
144 7
144 8
144 9
144 10
17.7 168
19.2 168
17.9 166
15.6 155
13.7 217
14.0 272
15.5 280
16.1 267
12.8 256
10.4 335
13.1 344
13.5 325
25.6 246
5.0 211
8.1 304
11.6 319
9.2 308
9.2 310
7.3 318
5.7 311
5.5 294
8.6 292
12.1 312
13.7 325
15.0 325
18.6 334
18.5 331
18.3 331
18.6 335
13.0 346
12.3 349
15.5 334
14.9 333
13.0 333
11.1 326
9.5 307
9.0 297
5.8 307
6.1 273
10.0 289
10.0 303
11.0 328
10.2 309
9.4 315
11.2 310
10.4 318
12.6 311
15.9 318
18.2 325
22.7 328
25.9 329
24.4 328
27.3 331
23.5 338
18.0 339
19.2 336
20.7 345
17.0 346
19.2 342
18.3 345
14.7 336
10.1 337
8.8 343
10.2 5
7.2 348
5.4 307
5.2 306
4.7 295
4.9 282
5.5 272
6.1 303
9.1 309
9.9 332
10.3 324
10.1 334
5
5
4
6
17
12
12
10
12
22
11
16
6
27
11
3
4
4
4
5
9
5
3
5
4
4
5 '
6
3
6
11
5
5
5
4
4
6
9
4
3
5
7
5
4
3
. 3
4
3
4
5
5
5
5
6
10
8
12
10
10
10
5
3
1
7
6
12
5
10
5
6
5
7
9
8
11
55.7
58.0
60.3
65.1
74.1
77.0
77.8
77.9
77.6
77.3
73.2
68.4
53.9
55.1
54.6
54.2
52.5
52.9
52.2
52.0
52.5
52.7
52.8
53.8
53.4
56.5
56.4
55.3
53.3
51.8
55.2
55.2
53.7
53.3
52.1
52.2
50.7
46.6
44.4
44.0
42.9
44.7
44.5
44 .3
43.8
43.9
44.4
44 .8
46.5
50.5
51.6
51.3
52.5
53.6
55.4
55.4
54.6
52.7
51.7
50.0
46.5
43.8
42.2
40.8
39.0
36.8
36.5
35.5
37.2
37.8
39.8
42.0
43.6
45.0
46.9
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.54
0.00
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
p. oo
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00.
0.00
'o.oo
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-3
-------
144
144
144
144
144
144
144
144
144
144
144
144
144
144
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
145
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
146
147
141
147
147
147
147
.147
147
147
147
147
147
147
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
. 1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
8
9
10
9
9
8
8
6
4
4
5
5
4
1
3
4
4
3
2
3
4
9
10
9
8
8
7
8
9
9
9
10
9
10
8
8
10
12
10
10
7
10
12
13
9
10
10
14
18
22
19
22
23
19
18
14
10
10
11
15
18
13
12
13
12
9
6
6
9
13
11
10
8
7
7
.8
.1
.3
.8
.4
.2
.1
.0
.7
.0
.6
.2
.5
.9
.8
.8
.2
.2
.7
.0
.5
.4
.2
.6
.6
.7
.2
.7
.2
.0
.6
.2
.9
.4
.4
.5
.6
.2
.0
.6
.9
.3
.2
.8
.9
.1
.8
.1
.7
.6
.7
.9
.5
.7
.0
.9
.6
.8
.6
.8
.2
.8
.0
.2
.9
.2
.9
.3
.5
.5
.3
.8
.9
.2
.3
339
350
340
340
349
337
328
310
319
251
235
183
247
288
228
193
182
174
155
137
174
214
222
214
194
194
174
185
184
175
169
166
149
133
126
136
150
156
169
172
160
154
170
166
199
183
230
266
247
249
257
261
278
262
255
260
261
260
356
337
345
339
337
335
331
321
321
311
329
1
5
5
4
14
11
14
18
20
18
22
18
18
17
19
10
5
17
18
43
29
7
9
16
10
21
13
8
10
17
21
22
28
29
27
18
15
10
4
3
5
4
3
3
3
3'
5
3
5
4
12
9
10
14
10
7
10
9
7
7
5
4
3
2
18
8
8
6
3
2
3
.3
3
5
6
13
17
20
22
25
25
48.
50.
52.
53.
53.
54.
55.
54.
53.
47.
46.
45.
44.
41.
37.
36.
36.
36.
35.
38.
44.
52.
57.
59.
61.
62.
65.
67.
68.
68.
68.
67.
64.
57.
54.
53.
55.
54.
51.
50.
49.
49.
49.
51.
54.
58.
67.
73.
77.
78.
79.
- 80.
80.
79.
78.
77.
72.
66.
65.
62.
61.
58.
55.
53.
52.
47.
46.
50.
54.
56.
58.
60.
62.
64.
66.
6
8
5
0
2
0
0
8
3
9
5
7
6 .
0
8
5
4
1
6
4
1
5
5
8 ,
9
8
3
3
2
3
4
7
3
8
6
9
1
2
5
4
0
5
9
0
4
0
0
4
3
9
6
1
5
4
7
0
9
0
3
9
6
4
0
5
2
6
6
0
1
8
8
8
4
3
3
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
'0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
E-4
-------
147 14
147 15
147 16
147 17
147 18
147 19
147 20
147 21
147 22
147 23
147 24
148 1
148 2
148 3
148 4
148 5
148 6
148 7
148 8
148 9
148 10
148 11
148 12
148 13
148 14
148 15
148 16
148 17
148 18
148 19
148 20
148 21
148 22
148 23
148 24
149 1
149 2
149 3
149 4
149 5
149 6
149 7
149 8
149 9
149 10
149 11
149 12
149 13
149 14
149 15
149 16
149 17
149 18
149 19
149 20
149 21
149 22
149 23
149 24
150 1
150 2
150 3
150 4
150 5
150 6
150 7
150 8
150 9
150 10
150 11
150 12
150 13
150 14
150 15
150 16
5.8 44
5.8 275
6.2 93
9.3 101
11.5 94
9.2 87
7.2 73
9.7 49
16.1 343
14.5 354
15.6 63
13.4 109
10.5 89
9.2 165
8.6 165
3.9 133
3.1 70
8.3 138
9.1 154
7.4 153
6.2 152
5.3 129
5.1 156
6.7 155
9.2 144
11.0 152'
14.6 145
17.3 146
20.4 140
25.1 143
25.5 146
12.4 116
9.1 20
10.0 4
12.8 142
6.6 156
7.1 177
6.6 226
6.5 145
10.5 139
12.1 164
11.5 164
11.8 180
9.9 184
3.8 175
2.9 268
10.4 309
12.8 316
10.4 322
9.6 313
10.6 302
14.1 325
19.7 318
15.5 339
11.8 345
£.7 355
8.7 18
5.0 333
3.7 290
6.6 309
6.3 311
8.4 294
10.6 288
11.5 289
8.5 316
8.3 329
13.5 351
13.7 350
12.3 340
13.3 355
11.0 354
10.1 44
8.8 281
7.5 52
3.3 24
32
29
21
9
7
6
8
8
8
13
13
5
6
7
5
9
13
9
8
8
16
26
28
31
21
15
9
6
5
4
8
12
21
7
4
23
7
13
14
7
6
5
6
7
27
51
15
10
9
14
13
8
8
11
9
8
4
6
14
5
6
5
3
2
6
6
11
15
11
17
21
19
16
15
43
67.1
67.2
66.8
65.9
65.3
63.6
60.7
60.0
55.5
52.2
53.1
53.1
53.0
52.7
52.6
51.8
53.8
55.9
56.9
58.1
60.4
62.8
66.0
68.9
70.1
72.0
72.2
70.0
65.9
62.8
59.7
57.4
56.6
56.3
55.7
54.1
52.5
51.6
50.2
51.2
51.7
53.0
55.8
58.8
62.7
66.9
68.4
70.9
70.3
72.2
71.6
69.8
58.2
61.1
58.0
54.7
53.3
51.0
50.5
49.8
47.9
47.1
47.1
47.7
48.9
52.1
54.8
56.4
59.1
61.4
62.8
62.5
62.7
62.5
63.5
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.12
0.26
0.32
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.22
0.06
0.00
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
•0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-5
-------
150 17
150 18
150 19
150 20
150 21
1.50 22
150 23
150 24
151 1
151 2
151 3
151 4
151 5
151 6
151 7
151 8
151 9
151 10
151 11
151 12
151 13
151 14
151 15
151 16
151 17
151 18
151 19
151 20 .
151 21
151 22
151 23
151 24
152 1
152 2
152 3
152 4
152 5
152 6
152 7
152 8
152 9
152 10
152 11
152 12
152 13
152 14
152 15
152 16
152 17
152 18
152 19
152 20
152 21
152 22
152 23
152 24
153 1
153 2
153 3
153 4
153 5
153 6
153 7
153 8
153 9
153 10
153 11
153 12
153 13
153 14
153 15
153 16
153 17
153 18
153 19
5.8 57
5.9 101
6.7 98
4.4 108
6.2 222
5.1 150
10.4 152
10.2 155
10.0 168
11.4 181
10.4 181
8.2 173
8.3 176
7.9 177
9.5 178
6.8 177
4.1 154
4.7 126
' 5.8 125
7.3 110
8.2 158
7.5 148
9.1 140
10.8 134
12.6 136
11.2 128
10.8 127
12.2 135
17.0 130
20.3 137
19.7 150
15.9 154
15.5 155
13.5 215
5.2 106
7.6 160
9. 9 186
8.0 182
9.8 193
10.9 238*
9.0 270.
13.3 286
15.5 323
11.3 337
13.1 56
11.4 65
12.6 20
8.6 70
7.5 7
14.2 220
20.8 339
13.5 336
9.2 325
6.2 312
7.4 287
11.4. 305
10.2 314
10.1 308
7.8 299
7.3 283
9.6 314
15.0 311
16.8 307
16.2 311
15.9 317
17.9 319
16.4 317
15.4 344
16.8 353
16.7 356
17.5 8
17.0 16
13.9 17
12.4 31
11.8 36
19
15
6
6
10
8
6
5
5
3
3
5
3
6
7
10
22
23
20
21
17
24
19
14
7
4
3
3
5
5
4
5
8
18
22
9 .
5
6
9.
7
12
7
9
15
10
14
11
9
15
29
7,
8
6
5
6
4
4
5
4
5
5
5
5
6
5
6
8
14
19
16
13
10
14
9
7
63.1
63.0
61.5
56.7
54.1
52.2
51.0
49.9
48.7
47.6
46.8
46.2
45.7
47.9
51.6
56.2
60.8
64.9
68.1
70.5
71.4
72.9
72.7
73.0
71.8
69.3
66.8
65.1
63.3
. 60.9
58.9
58.3
58.4
55.0
53.4
51.7
52.4
55.1
56.9
61.5
65.9
.67.7
70.8
66.0
68.6
6 8'. 7
62.6
64.2
61.5
56.4
52.5
52.0
51.7
50.4
48.4
49.9
50.7
50.1
49.5
48.1
47.4
48.4
48.4
49.8
51.2
55.0
56.1
57.8
58.1
59.0
57.6
56.9
55.1
53.4
52.9
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.18
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.08
0.00
o.oi
0.04
,0.00
0.10
0.03
0.02
0.00
0.00-
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-6
-------
153 20
153 21
153 22
153 23
153 24
154 1
154 2
154 3
154 4
154 S
154 6
154 7
154 8
154 9
154 10
154 11
154 12
154 13
154 14
154 15
154 16
154 17
154 18
154 19
154 20
154 21
154 22
154 23
154 24
155 1
155 2
155 3
155 4
155 5
155 6
155 7
155 8
155 9
155 10
155 11
155 12
155 13
155 14
155 15
155 16
155 17
155 18
155 19
155 20
155 21
155 22
155 23
155 24
156 1
156 2
156 3
156 4
156 5
156 6
156 7
156 8
156 9
156 10
156 11
156 12
156 13
156 14
156 15
156 16
156 17
156 18
156 19
156 20
156 21
156 22
12.6 37
11.4 48
8.9 50
8.8 60
10.8 132
8.1 134
11.0 129
11.5 139
14.6 130
12.6 142
9.6 140
14.5 139
16.6 136
19.5 135
22.1 126
21.2 131
20.2 127
20.6 145
19.7 144
17.3 134
16.9 129
12.9 120
9.7 122
9.3 145
11.0 160
9.4 167
11.8 161
11.2 175
10.7 194
9.9 200
8.0 180
9.1 174
11.2 159
11.2 159
14.4 163
15.6 162
16.6 172
20.4 167
22.7 173
22.0 174
22.1 176
21.2 179
20.4 181
19.6 177
21.2 174
22.0 159
23.7 159
22.6 159
22.8 158
21.9 157
20.8 157
19.5 161
18.6 158
17.4 157
14.6 166
14.2 171
12.4 171
13.7 177
12.0 167
11.1 161
10.5 184
8.2 189
5.8 225
5.4 219
6.6 266
7.0 254
10.7 254
8.2 152
9.9 112
6.4 203
5.7 37
6
8
8
11
13
10
8
6
7
5
6
5
6
5
6
5
6
7
7
8
9
8
8
8
7
6
5
5
6
4
4
4
5
4
4
5
7
7
7
8
9
8
10
10
8
5
4
4
4
5
4
3
4
4
5
4
4
3
4
6
8
12
27
41
24
42
44
28
14
37
16
12.9 13 6
13.1 21
12.0 14
5
4
10.8 360 7
49.8
47.4
47.0
46.6
47.4
46.7
46.8
47.1
46.7
46.3
46.5
46.5
45.6
46.1
44.5
43.3
43.5
42.9
44.0
43.7
43.6
43.7
43.0
42.6 '
42.0
41.3
41.3
40.8
39.9
39.2
37.7
38.2
39.9
40.1
40.4
41.1
43.1
45.6
47.4
50.8
54.5
56.4
58.7
60.2
60.5
59.2
57.3
55.9
53.6
51.. 8
51.2
50.0
48.6
47.5
46.1
45.3
44.5
44.5
47.2
49.7
53.7
57.4
62.0
64.6
65.7
65.3
57.8
60.5
62.5
61.4
58.1
56.1
53.8
52.9
52.5
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.08
0.04
0.04
0.03
0.02
0.01
0.04
0.02
0.04
0.02
0.02
0.00
0.01
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
' 0.00
0.00
0.00
0.00
0.04
0.01
0.00
0.01
0.00
0.02
0.00
0.00
0.00
E-7
-------
156 23
156 24
157 1
157 2
157 3
157 4
157 5
157 6
157 7
157 8
157 9
157 10
157 11
157 12
157 13
157 14
157 15
157 16
157 17
157 18
157 19
157 20
157 21
157 22
157 23
157 24
158 1
158 2
158 3
158 4
158 5
158 6
158 7
158 8
158 9
158 10
158 11
158 12
158 13
158 14
158 15
158 16
158 17
158 18
158 19
158 20
158 21
158 22
158 23
158 24
159 1
159 2
159 3
159 4
159 5
159 6
159 7
159 8
159 9
159 10
159 11
159 12
159 13
159 14
159 15
159 16
159 17
159 18
159 19
159 20
159 21
159 22
159 23
159 24
160 1
11.9 352
11.0 18
10.6 28
10.7 25
11.5 359
9.7 13
9.6 21
7.3 40
9.7 40
9.3 63
11.7 83
6.6 83
5.9 63
6.5 89
7.2 94
9.1 117
18.3 224
18.9 152
17.6 151
16.9 143
13.9 146
8.3 179
6.7 181
5.0 213
4.5 59
7.4 97
6.5 214
2.9 157
6.6 245
5.8 285
9.3 226
6.3 200 "
7.3 273
10.8 275
12.6 264
12.0 270
12.9 283
21.7 276
27.2 266
27.5 266
30.5 283
29.1 289 ,
32.8 293
30.8 300
29.5 299
28.6 301
31.3 297
32.8 304
33.1 304
35.0 306
34.0 309
31.1 306
26.6 304
27.3 311
27.6 314
28.6 321
28.9 315
26.9 312
29.4 308
34.3 309
32.3 305
32.8 301
29.1 306
29.7 313
30.4 313
26.7 309
24.3 310
23.6 312
20.6 317
19.4 315
16.0 301
15.0 297
10.3 289
12.3 287
15.3 284
10
7
4
9
9
4
3
7
6
9
6
7
11
13
7
8
6
5
5
6
6
11
14
29
16
6
15
10
30
1.6
10
12
11
6
4
5
7
5
4
-.4
4
4
3
3
3
3
3
3
3
3 .
3
3
3
4
5 .
3
4
4
6
7
7
5
5
6
6
6
4
4
4
3
3
3
3
2
2
51.7
50.9
50.5
49.6
49.6
48.7
48.2
48.7
50.0
52.4
52.5
52.2
54.0
56.5
57.0
58.8
60.0
58.3
55.6
52.6
51.5
51.3
51.0
50.4
50.4
50.8
50.7
50.1,
50.2
49.7
49.1
47.5
47.0
46.5
46.3
46.4
46.3
45.4
43.6
44.2
45.3
45.4
45.8
44.8
43.7
42.8
43.1
43.1
42.6
41.5
41.6
41.8
41.9
42.4
42.7
42.6
43.6
45.6
46.4
47.8
50.1
51.7
53.8
56.3
56.5
56.3
55.5
54.7
53.7
51.7
50.6
49.8
46.8
46.0
46.1
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.18
0.07
,0.16
0.19
0.01
0.00
0.00
0.01
0.01
0.01,
0.00 , .
0.03
0.07
0.09
0.14
0.07
0.11
0.09
0.09
0.11
0.13
0.06
0.09 , ,
0.02
o.oi • •
0.02
0.04
0.01
0.00
0 . 01
0.01
0.00
0.00
0.01
0.01
0.01
0.00
0.00
0.00
0.00 * (C,D,F,G) **
0.00 * (C,D,F,G) **
0.00
0.00
0.00
0.00-
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-8
-------
160 2
160 3
160 4
160 5
160 6
160 7
160 8
160 9
160 10
160 11
160 12
160 13
160 14
160 IS
160 16
160 17
160 18
160 19
160 20
160 21
160 22
160 23
160 24
161 1
161 2
161 3
161 4
161 5
161 6
161 7
161 8
161 9
161 10
161 11
161 12
161 13
161 14
161 15
161 16
161 n
161 18
161 19
161 20
161 21
161 22
161 23
161 24
162 1
162 2
162 3
162 4
162 5
162 6
162 7
162 8
162 9
162 10
162 11
162 12
162 13
162 14
162 15
162 16
162 17
162 18
162 19
162 20
162 21
162 22
162 23
162 24
163 1
163 2
163 3
163 4
14.2 285
12.8 291
12.4 297
11.1 294
13.5 309
17.4 304
15.7 307
14.9 318
14.1 317
13.5 315
12.9 311
11.0 307
8.3 290
6.5 297
4.4 221
3.1 249
3.6 191
4.6 116
6.1 120
6.6 132
8.1 150
5.3 180
7.2 181
7.3 194
6.2 175
5.4 185
4.0 201
5.3 186
5.3 170
4.6 176
4.9 172
4.7 231
6.1 324
3.9 256
3.5 214
4.3 255
5.3 193
5.6 194
6.1 165
8.5 169
9.5 182
5.7 183
6.7 158
9.1 157
8.9 159
8.7 157
7.6 166
10.7 164
10.2 206
6.6 237
5.1 307
3.0 275
7.8 237
4.3 230
5.7 172
8.2 189
14.0 217
18.2 217
22.8 220
21.0 231
19.9 234
19.0 237
15.0 247
7.5 243
10.2 208
14.3 212
13.9 210
11.3 191
11.5 184
12.9 184
13.1 182
13.3 175
12.5 161
9.9 229
6.7 159
2
2
3
3
3
4
6
8
9
11
10
15
13
32
27
53
36
11
3
4
5
9
3
8
9
10
13
6
11
6
9
27
16
35
39
42
30
31
15
15
11
7
3
2
2
2
4
6
12
23
10
21
7
25
14
10
9
8
7
7
10
8
7
6
7
4
4
4
4
4
4
4
7
35
17
46.0
46.7
47.8
47.4
49.5
52.7
54.8
57.2
59.5
61.4
62.6
63.1
63.9
65.3
65.5
67.0
66.7
64.8
59.2
55.3
53.8
51.7
49.7
48.6
47.8
46.7
47.1
44.7
47.1
51.4
56.8
63.5
66.3
68.6
70.4
71.2
71.9
72.1
72.0
73.4
72.5
68.9
63.2
59.2
57.4
56.8
55.9
57.1
55.5
55.4
51.4
51.2
52.8
55.1
58.1
64.0
69.7
72.9
73.5
74.0
75.2
75.8
75.3
72.5
69.6
67.2
64.1
61.3
60.0
58.2
58.1
59.4
58.2
57.6
54.1
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
' 0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-9
-------
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
163
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
164
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
165
166
166
166
166
166
166
166
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
6
6
5
6
11
12
13
15
14
16
16
10
9
9
8
5
2
4
6
6
5
6
7
2
4
6
3
7
13
12
10
9
6
5
6
8
10
13
10
8
7
7
9
3
1
1
2
3
4
3
3
2
3
4
4
3
5
7
7
9
11
11
12
12
12
15
16
19
25
25
24
21
18
15
14
.8
.2
.2
.7
.0
.9
.5
.1
.8
.1
.7
.7
.9
.2
.8
.1
.4
.1
.2
.7
.8
.7
.1
.7
.6
.1
.8
.7
.7
.3
.4
.4
.8
.3
.1
.6
.7
.0
.9
. 9
. 9
.8
.2
.9
.2
.7
.5
.8
.3
.2
.1
.8
.6
.2
.2
.7
.4
.5
.8
.8
.2
.9
.7
.7
.8
.2
.6
.4
.7
.0
.4
.2
.5
.8
.8
183
'195
258
270
267
262
264
259
258
314
9
15
33
62
69
64
109
343
273
273
269
272
268
257
.234
201
259
278
281
281
278
275
249
274
294
326
307
310
314
314
309
294
304
22
344
255
270
274
262
237
216
315
16
25
288
257
99
148
123
136
114
107
104
101
103
110
111
110
109
109
111
116
149
138
157
19
19
17
6
5
5
5
5
5
19
24
29
25
19
6
5
29
17
3
3
3
4
2
4
20
10
12
6
6
7
8
15
31
43
45
39
25
15
14
6
5
3
3
22
24
3
16
5
6
42
59 .
50
24
30
31
63
52
36
30
16
12
8
4
2
3
5
5
5
4
4
5
6
20
11
20
52.
54.
54.
57.
61.
64.
67.
67.
67.
65.
61.
63.
62.
61.
58.
54.
51.
48.
46.
44.
43.
41.
40.
40.
38.
42.
50.
54!
57.
58.
60.
61.
62.
64.
66.
67.
66.
65.
62.
57.
52.
48.
47.
47.
45.
44.
43.
42.
40.
44 .
50.
56.
58.
60.
62.
65.
66.
68.
69.
70.
70.
70.
67.
63.
61.
60.
58.
56.
55.
54.
54.
53.
53.
52.
53.
2
3
9
4
0
4
6
9
8
2
1
1
8
3
7
8
8
0
0
2
4
1
7
1
0
0
8
8
4
8
2
8
8
8
7
0
6
2
8
4
1
4
6
1
7
0
4.
1
5
4
8
6
9
8
8
0
6
2
8
3
5
1
9
8
3
4
2
4
9
8
0
3
2
3
8
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
• o.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
" 0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
* (D) ***
* (D) ***
* (D) **
* (D) ***
* (D) ***
* (D) **
* (D) **
* (D) **
* (D) **
* (D) **
* (D) **
* (D) **
*. (D) **
* (D) **
* (D) **
* (D) **
* (D) **
E-10
-------
166 8
166 9
166 10
166 11
166 12
166 13
166 14
166 15
166 16
166 17
166 18
166 19
166 20
166 21
166 22
166 23
166 24
167 1
167 2
167 3
167 4
167 5
167 6
167 7
167 8
167 9
167 10
167 11
167 12
167 13
167 14
167 15
167 16
167 17
167 18
167 19
167 20
167 21
167 22
167 23
167 24
168 1
168 2
168 3
168 4
168 5
168 6
168 7
168 8
168 9
168 10
168 11
168 12
168 13
168 14
168 15
168 16
168 17
168 18
168 19
168 20
168 21
168 22
168 23
168 24
169 1
169 2
169 3
169 4
169 5
169 6
169 7
169 8
169 9
169 10
12.6 104
10.5 96
9.1 104.
11.1 161
6.6 185
5.1 225
5.9 259
6.9 299
18.9 6
27.1 11
29.1 21
20.9 47
15.3 86
6.70 279
12.6 281
12.8 280
12.8 324
4.5 328
5.3 235
6.4 227
8.3 315
7.4 280
8.6 43
9.1 317
11.2 291
11.6 331
9.6 358
9.6 9
10.9 312
19.6 353
16.2 31
17.6 346
20.1 78
10.6 40
12.7 331
12.6 48
14.4 39
12.3 352
18.4 5
21.5 24
20.4 359
17.9 30
14.3 13
15.9 14
16.9 356
17.2 349
16.7 346
13.9 19
13.0 50
11.9 51
10.7 60
9.0 23
9.7 4
12.6 344
•13.9 19
13.3 47
13.0 52
11.9 62
9.7 53
9.3 58
8.9 52
8.6 67
7.2 46
5.3 15
2.5 79
2.0 96
2.5 112
3.1 338
2.7 234
1.9 257
1.3 231
1.8 157
4.4 199
2.9 188
3.1 149
5
4
9
22
38
44
20
36
25
37
15
7
4
32
4
2
15
33
36
22
21
15
21
26
12
25
29
30
20
17
16
19
6
20
16
12
10
21
16
13
18
11
15
16
16
14
15
13
10
11
12
23
25
20
18
10
9
7
10
6
10
5
9
21
13
8
8
10
14
13
25
21
21
30
33
58.1
63.1
66.6
70.4
73.4
76.7
78.7
79.1
68.8
62.6
58.1
59.0
58.6
57.4
54.8
54.3
55.5
54.5
54.2
54.3
54.9
54.3
54.4
54.2
54.9
57.2
56.9
58.9
59.0
59.5
59.1
55.1
54.1
54.5
53.7
53.2
51.3
50.6
49.9
47.8
47.1
46.5
46.5
46.0
45.5
45.2
45.2
45.5
47.4
48.7
49.4
49.4
49.4
49.1
49.4
50.2
49.3
48.2
47.9
47.6
47.4
46.9
46.8
46.5
46.3
46.2
46.0
46.1
46.4
46.7
47.1
47.6
48.4
49.5
50.2
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.37
0.21 * (C,D,F) ***
0.11 * (C,D,F,G) **
0.00 * (C,D,F,G) **
0.00 * (C,D,F,G) **
0.00 * (C,D,F,G) **
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.04
0.01
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.02
0.01
0.10
0.12
0.01
0.01
0.02
0.01
0.02
0.02
0.00
0.02
0.05
0.03
0.02
0.07
0.05
0.00
0.00
0.00
0.03
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.02
0.00
0.01
0.00
0.00
0.00
0.00
0.03
0.02
0.00
E-ll
-------
169
169
169
169
169
169
169
169
169
169
169
169
169
169
170
170
170
170
170
170
170
170
170
170
no
no
170
no
170
170
170
170
170
170
170
170
170
no
171
171
171
171
171
171
17.1
171
171
171
171
171
171
171
171
171
171
171
171
171
171
171
171
171
172
172
172
172
172
172
172
172
172
172
172
172
172
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11'
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
' 4
5
6
7
8
9
10 -
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
4
2
2
3
4
8
5
6
6
7
6
5
7
7
7
9
8
4
6
4
2
2
5
8
6
6
6
6
7
6
7
5
4
3
4
5
4
6
7
5
5
7
5
4
_4
. 6
4
3
4
4
6
6
6
6
8
7
6
6
7
7
10
13
10
9
12
10
6
10
6
12
15
16
16
19
20
.5
.6
.2
.1
.7
.5
.7
.2
.7
.5
.6
.9
.0
.2
.8
.3
.5
.7
.0
.2
.5
.1
.6
.3
.8
.1
.7
.5
.1
.7
.7
.9
.0
.5
.8
.7
.8
.2
.2
.4
.5
.1
.9
.2
.3
.0
.6
.8
.5
. 9
.0
. 9
.5
.7
.4
.4
.8
.5
.3
. 0
.5
.2
.7
.9
.5
.2
.8
.1
.0
.6
.2
.8
.3
.5
.7
127
201
110
104
130
164
163
159
160
150
152
167
168
174
171
168
175
163
166
166
164
280
292
313
318
313
310
305
290
305
311
304
252
221
195
180
173
174
175
169
170
186
217
128
175
177
156
112
102
98
110
157
151
149
147
140
128
120
132
132
349
259
154
146
154
155
167
151
154
150
140
132
147
151
162
20
43
19
18
14
6
8
6
4
4
4
5
4 .
4
3
3
3
12
10
8
18
39
15
12
15
24
21
21
20
15
12
13
10
5
4
4
9
10
_ 4
4
12
4
23
26
15
7
13
14
14
17
21
18
15
18
11
8
3
5
7
7
5
4
3
5
3
4
10
6
11
6
6
7
8
7
7
51
52
52
52
53
52
52
52
52
52
50
48
47
47
46
45
44
43
44
44
48
56
61
65
67
69
70
72
72
73
74
74
71
68
63
59
56
54
53
52
53
51
51
54
59
65
70
74
76
78
80
80
81
81
81
80
76
70
66
64
64
63
61
60
60
59
58
62
65
69
72
75
75
77
80
.0
.2
.2
.7
.2
.4
.4
.6
.8
.1
.3
.2
.5
.2
.3
.6
.5
.9
.4
.3
.8
.1
.2
.3
.5
.0
.5
.0
.6
.9
.4
.1
.9
.3
. 9
.8
.8
.8
.9
.6
.0
.5
.9
.8
.4
'.3
.6
.6
.7
.5
.0
.3
.3
.9
.3
.4
.7
.8
.6
.7
.1
.5
.5
.7
.2
.2
.2
.4
.8
.0
.0
.3
.6
.9
.4
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
00
00
00
01
00
00
01
02
01
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
E-12
-------
172 14
172 15
172 16
172 17
172 18
172 19
172 20
172 21
172 22
172 23
172 24
173 1
173 2
173 3
173 4
173 5
173 6
173 7
173 8
173 9
173 10
173 11
173 12
173 13
173 14
173 15
173 16
173 17
173 18
173 19
173 20
173 21
173 22
173 23
173 24
174 1
174 2
174 3
174 4
174 5
174 6
174 7
174 8
174 9
174 10
174 11
174 12
174 13
174 14
174 15
174 16
174 17
174 18
174 19
174 20
174 21
174 22
174 23
174 24
175 1
175 2
175 3
175 4
175 5
175 6
175 7
175 8
175 9
175 10
175 11
175 12
175 13
175 14
175 15
175 16
20.1 153
19.3 202
22.7 150
23.6 156
17.8 263
16.6 34
21.0 150
21.5 147
21.8 166
18.1 161
15.5 159
13.1 167
12.3 169
11.1 175
10.4 177
12.9 181
12.1 181
11.3 196
12.4 215
12.9 242
9.2 297
8.2 309
5.9 328
8.2 335
2.9 283
19.0 310
14.0 5
11.6 41
10.5 65
6.8 94
4.2 114
3.2 75
3.9 27
2.5 213
6.1 284
5.1 302
9.3 331
7.1 337
7.0 325
6.1 316
7.9 304
7.9 295
8.0 277
9.2 268
11.2 281
10.9 288
13.1 319
21.2 332
28.7 332
28.0 329
14.5 332
22.1 320
25.1 321
20.3 317
8.9 296
9.8 281
8.6 272
7.0 252
9.5 241
5.9 286
4.9 197
8.6 227
14.2 250
13.5 260
12.4 268
12.7 262
13.1 273
14.3 284
12.6 283
12.1 276
14.9 280
16.6 299
19.4 312
20.4 312
20.4 310
7
9
8
6
7
11
9
4
6
4
4
4
6
6
6
4
4
4
7
9
15
19
29
20
39
20
13
9
9
7
6
12
15
30
15
10
6
9
4
5
5
6
10
9
11
9
11
7
4
4
8
6
5
3
4
3
3
5
3
14
15
6
3
3
3
4
4
5
8
13
11
9
8
7
6
81.8
82.6
75.6
69.0
70.2
68.7
65.2
62.8
61.3
59.6
57.5
56.3
56.1
54.9
53.8
53.5
57.6
62.1
68.1
70.9
72.4
73.1
73.2
68.4
66.6
56.6
61.0
61.1
60.8
59.9
56.6
54.9
53.1
52.2
50.9
49.9 •
50.8
50.4
49.0
48.0
48.9
49.9
51.3
52.8
55.6
57.6
58.6
54.5
48.1
44.3
49.4
52.5
52.3
48.7
44.0
41.7
40.3
39.6
40.6
37.5
35.3
37.9
42.2
43.9
44 .7
46.9
49.8
52.0
55.3
57.9
59.0
58.9
60.0
58.7
57.8
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.07
0.17
0.23
0.06
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
'o.oo
0.00
0.00
0.00
0.00
0.00
E-13
-------
175 17
175 18
175 19
175 20
175 21
175 22
175 23
175 24
176 1
176 2
176 3
176 4
176 5
176 6
176 7
176 8
176 9
176 10
176 11
176 12
176 13
176 14
176 15
176 16
176 17
176 18
176 19
176 20
176 21
176 22
176 23
176 24
177 1
177 2
177 3
177 4
177 5
177 6
177 7
177 8
177 9
177 10
177 11
177 12
177 13
177 14
177 15
177 16
177 17
177 18
177 19
177 20
177 21
177 22
177 23
177 24
178 1
178 2
178 3
178 4
178 5
178 6
178 7
178 8
178 9
178 10
178 11
178 12
178 13
178 14
178 15
178 16
178 17
178 18
178 19
20.0 307
19.4 315
15.7 321
12.4 313
9.7 305
7.1 300
7.6 299
7.3 279
9.3 274
12.2 300
9.4 285
8.9 278
8.2 284
7.4 280
10.5 286
11.9 301
15.4 306
17.2 311
17.0 303
14.1 301
11.7 285
10.4 286
7.7 290
8.2 287
7.4 291
6.6 310
6.0 330
5.1 335
2.6 246
2.7 223
5.7 210
6.7 198
9.5 203
7.5 194
3.9 173
3.6 150
3.1 157
2.2 218
2.9 57
3.2 78
2.3 279
2.5 179
3.8 244
4.6 201
4.6 222
5.0 212
4.5 202
3.5 180
2.9 264
2.9 286
11.5 73
8.1 74
4.6 91
6.1 138
13.6 3
11.7 87
7.7 117
6.7 164
8.2 158
10.4 153
9.6 153
11.1 167
11.5 166
9.3 169
8.1 200
8.9 285
7.4 250
9.1 230
6.9 229
5.3 252
3.5 335
3.7 32
3.5 188
5.6 86
5.4 91
5
5
4
4
4
6
5
6
5
3
4
3
3
3
4
6
9
7
11
13
14
13
21
19
18
14
7
5
19
13
4
'13
7
6
19
12
26
30
16
17
35
35
43
47
41
37
44
37
48
41
6
4
6
. 18
15
8
8
7
3
3
4
4
5
6
12
14
15
13
12
12
17
23
26
10
5
58.1
57.8
55.9
53.0
51.4
50.9
49.9
49.0
49.3
49.8
48.3
46.4
44.4
46.7
50.6
54.0
57.9
59.3
61.2
62.6
63.2
64.8
66.1
67.0
67.5
67.7
66.3
60.8
57.8
55.6
53.8
50.2
49.7
49.8
47.1
44.6
45.2
49.4
54.6
59.3
65.0
69.8
71.9
74.3
76.1
77.5
78.7
79.6
80.5
, 80.4
73.8
68.1
63.8
61.4 .
63.7
60.6
58.3
56.5
55.4
55.9
56.4
59.0
61.8
63.5
69.2
73.4
74.2
76.3
78.2
78.3
79.5
81.7
80.4
78.7
75.0
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00-
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
. 0.00
0.00
0.00
0.00
0.00
0.00-
0.00
0.00
0.00
0.00
0.00
o.oo
0.00
0.00
0.00
0.00
.0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-14
-------
178 20
178 21
178 22
178 23
178 24
179 1
179 2
179 3
179 4
179 5
179 6
179 7
179 8
179 9
179 10
179 11
179 12
179 13
179 14
179 15
179 16
179 17
179 18
179 19
179 20
179 21
179 22
179 23
179 24
180 1
180 2
180 3
180 4
180 5
180 6
180 7
180 8
180 9
180 10
180 11
180 12
180 13
180 14
180 15
180 16
180 17
180 18
180 19
180 20
180 21
180 22
180 23
180 24
181 1
181 2
181 3
181 4
181 5
181 6
181 7
181 8
181 9
181 10
181 11
181 12
181 13
181 14
181 15
181 16
181 17
181 18
181 19
181 20
181 21
181 22
4.7 113
6.3 197
3.6 173
2.8 198
6.6 139
5.9 164
5.7 191
6.6 184
9.0 175
9.7 164
10.5 181
18.1 163
19.0 156
18.8 158
20.7 157
19.8 156
15.3 160
14.2 150
15.3 141
17.9 144
20.1 137
23.8 127
27.2 130
26.6 129
26.1 171
25.4 135
22.8 331
14.9 275
13.3 343
14.1 32
5.7 22
4.4 80
4.2 311
8.8 293
16.3 314
21.4 334
18.9 334
22.8 303
21.4 321
18.4 325
15.3 324
14.6 312
12.5 329
15.3 349
13.1 23
11.4 31
13.4 36
11.7 26
7.4 32
5.0 2
6.6 360
5.7 4
4.6 295
5.1 297
4.2 275
4.9 281
5.0 132
5.9 278
5.3 284
3.0 224
3.4 108
5.7 155
5.2 208
4.6 205
5.0 195
5.0 210
4.9 228
3.5 254
4.2 196
4.8 237
5.8 110
8.1 91
8.3 97
7.2 105
6.6 127
7
13
22
33
16
19
17
10
10
8
9
5
5
6
7
6
9
11
11
9
7
6
5
4
4
4
12
20
22
14
13
14
17
7
5
5
4
18
10
5
8
11
11
15
13
13
10
5
9
25
12
14
16
18
38
38
9
17
6
20
14
16
26
25
29
37
44
46
39
33
20
4
2
4
6
72.0
70.0
67.1
66.4
59.3
59.5
58.5
55.9
55.5
53.5
58.4
59.9
62.2
64.9
68.2
69.7
73.5
77.1
79.4
80.1
81.4
81.2
80.1
77.2
73.0
70.6
70.2
67.9
62.9
63.3
57.6
55.4
52.2
51.2
54.3
55.9
57.3
53.4
49.9
56.5
61.6
63.3
63.6
63.1
63.1
63.3
62.1
60.0
56.8
56.3
55.1
53.2
52.5
53.2
53.1
53.4
53.3
51.8
51.8
53.8
56.7
60.5
62.0
64.5
66.7
68.3
70.5
70.9
70.9
71.9
71.7
67.9
63.0
61.8
61.5
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.20
0.03
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.04
0.01
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
E-15
-------
181
181
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
182
183
183
183
183
183
183
183
183
183
183
183
183
183
183
183
183
183
1,83
183
183
183
183
183
183
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
184
185
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
IS
16
17
18"
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
8
10
18
12
10
7
8
10
11
9
13
11
8
6
4
3
3
4
3
6
9
8
6
6
9
5
2
5
5
5
2
2
10
15
12
18
20
22
21
20
19
21
23
19
19
19
13
17
18
15
8
7
5
3
6
15
18
21
17
12
6
11
24
28
31
29
28
20
13
8
13
18
26
21
24
.4
.9
.1
.9
.2
.6
.5
.9
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.7
.4
.7
.2
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135
146
147
152
209
285
320
324
338
338
336
342
326
335
342 .
259
265
239
217
48
80
71
87
51
118
43
146
143
38
90
113
46
167
164
152
155
148
149
147
255
257
128
124
108-
191
352
213
235
139
349
188
175
160
132
169
313
311
312
313
292
334
232
216
250
260
265
263
297
326
300
297
295
289
289
295
4
5
4
5
12
17
8
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5
10
7
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43
52
45
34
36
27
5
6
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9
9
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6
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6
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14
18
5
4
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8
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50.
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2
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9
7
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0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
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0.
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00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
00
E-16
-------
185 2
185 3
185 4
185 5
185 6
185 7
185 8
185 9
185 10
185 11
185 12
185 13
185 14
185 15
185 16
185 17
185 18
185 19
185 20
185 21
185 22
185 23
185 24
186 1
186 2
186 3
186 4
186 S
186 6
186 7
186 8
186 9
186 10
186 11
186 12
186 13
186 14
186 15
186 16
186 17
186 18
186 19
186 20
186 21
186 22
186 23
186 24
187 1
187 2
187 3
187 4
187 5
187 6
187 7
187 8
187 9
187 10
187 11
187 12
187 13
187 14
187 15
187 16
187 17
187 18
187 19
187 20
187 21
187 22
187 23
187 24
188 1
188 2
188 3
188 4
25.0 295
22.5 292
21.3 299
23.2 295
18.7 291
20.1 289
22.6 292
26.8 295
24.4 289
19.8 282
18.1 288
22.2 307
27.4 309
21.5 296
22.1 312
21.4 313
16.6 309
19.5 319
15.6 305
9.0 295
7.7 280
10.7 289
9.6 275
8.7 274
8.8 276
8.2 276
9.4 282
9.1 276
8.4 282
12.7 292
20.5 308
18.9 305
14.5 307
17.4 296
14.9 303
16.4 308
11.9 289
13.3 301
14.4 310
17.9 336
16.0 330
13.9 331
7.7 309
5.2 276
13.9 282
14.0 305
10.5 289
9.2 286
7.1 283
3.8 264
4.3 277
4.1 285
4.2 266
6.2 291
7.6 284
5.6 309
5.5 320
4.2 323
5.3 331
4.9 34
4.5 258
4.7 14
15.9 359
16.6 323
14.3 317
11.1 323
4.4 16
7.8 283
10.8 299
7.7 292
6.2 284
5.0 276
6.4 246
6.8 271
8.0 258
4
4
4
4
4
4
5
6
6
6
6
9
7
6
7
5
5
5
3
3
5
3
3
3
3
2
2
3
5
8
5
6
8
8
10
10
12
11
9
10
5
5
9
9
5
5
4
4
3
20
14
18
13
1
10
22
27
35
47
31
42
45
24
12
10
8
22
8
3
5
5
7
8
6
4
49.6
49.6
50.3
51.4
52.0
52.5
55.7
58.7
58.4
56.9
59.8
63.0
63.8
60.2
'63.8
63.0
61.0
57.6
55.9
52.8
48.7
47.5
47.9
48.1
46.5
45.4
44.6
44.9
49.8
54.7
58.0
59.9 ,
61. 5'
61.2
63.1
63.1
65.8
66.5
67.3
63.3
62.4
58.8
55.7
52.8
54.0
51.3
50.6
48.4
47.1
46.3
47.2
47.2
47.9
55.0
58.0
60.5
62.4
64.3
65.9
67.1
68.8
69.7
61.4
53.0
51.2
51.0
50.1
49.6
49.6
49.4
50.0
48.9
47.4
46.2
47.1
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.01
0.00
0.00
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.03
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.00
0>. 00
0.00
0.00
0.00
0.01
0.00
0.00
0.00
E-17
-------
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
188
189
189
189
189
189
189.
189
189
189
189
189
189
189
189
189
189
189
189
189
189
189
189
189
189
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
190
191
191
191
191
191
191
191
5
6
7
8
9 '
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
1.9
20
21
22
23
24
1
2
3
4
5
6
7
8
9
10
11 -
12
13
14
15
16
17
18
19
20
21
22
23
24
1
2
3
4
5
6
7
3.
3.
1.
3.
4.
8.
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-------
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E-20
-------
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E-21
-------
APPENDIX F
COPY OF U.S. EPA/A&WMA CONFERENCE PAPER
This appendix includes a copy of a paper presented at the International Symposium on
Measurements of Toxic and Related Air Pollutants, cosponsored by the U.S. EPA and the Air and
Waste Management Association (A&WMA), held in Research Triangle Park, North Carolina in
May 1995. The paper presents an overview of application of the ISC model to surface coal
mining operations, and also presents a comparison of total emissions by source category from the
Cordero Mine data base used in this evaluation.
F-l
-------
-------
Improvements to the Industrial Source Complex Model:
Application to Surface Coal Miming Operations
Jayant A. Hardikar and Roger W. Brode
Pacific Environmental Services, Inc.
5001 South Miami Boulevard
Research Triangle Park, NC 27709-2077
Jawad S. Touma and John S. Irwin
Atmospheric Sciences Modeling Division, Air Resources Laboratoiy
National Oceanographic and Atmospheric Administration
Research Triangle Park, North Carolina 27711
(On Assignment to the Office of Air Quality Planning and Standards,
United States Environmental Protection Agency)
ABSTRACT
As mandated by the Clean Air Act Amendments, the Environmental Protection Agency (EPA) has
been reviewing and improving the accuracy of the Industrial Source Complex (ISC2) model. Three significant
modifications have been incorporated into the recently released beta version of ISCST2 model, called
ISCSTDFT - a new area source algorithm, a new pit retention algorithm and dry and wet deposition
algorithms. EPA has also collected emissions, meteorological and ambient air concentration data from an open
pit surface coal mine. Currently, a study is being carried out to evaluate the performance of the existing and
the new versions of the ISCST2 model for modeling fugitive dust emissions from a surface coal mine
operation.
This paper briefly discusses the new features of the ISCSTDFT model and also describes the
procedures being used for the model evaluation study. A status report along with some preliminary results has
been included as well.
INTRODUCTION
The Clean Air Act Amendments, Section 234(a), require the Environmental Protection Agency (EPA)
to analyze the accuracy of the Industrial Source Complex (ISC2) air quality dispersion model1 and Compilation
of Air Pollutant Emission Factors, AP-422 to determine the effect on the air quality of fugitive dust emissions
from surface coal mines. Fugitive dust emissions from surface coal mine operations include emissions from
bulldozing (coal and overburden), dragline, graders, haul trucks and other vehicles traveling on unpaved haul
roads, loading and unloading of coal and overburden, scraper activity, and wind erosion at various parts of a
coalmine.
The EPA's Office of Air Quality Planning and Standards (OAQPS) has also collected a comprehensive
data base containing the following information: (a) 24-hour ambient air quality data for TSP (particles captured
by the standard high-volume air samples) and PM-10 (particles no greater than 10 micrometers in aerodynamic
diameter) from a nine-station monitoring network distributed in and around the Cordero mine in Wyoming
during the period May-July 1993; (b) on-site meteorological data (including temperature, precipitation, wind
speed, and wind direction) during the monitoring period; (c) time-resolved information about mine operations
(source activity) during the monitoring period; (d) estimation of time-varying emission rates for all significant
sources (i.e., traffic on haul roads and equipment operations associated with topsoil, overburden, and coal
removal) operating during the monitoring period3. In addition, a statistical model evaluation protocol
describing the models and data bases to be used for testing has also been published4.
F-2
-------
The ongoing activities in this arena include:
1. Model implementation: The Industrial Source Complex Short Term (ISCST2) model has been revised to
incorporate a mine pit retention algorithm, an improved area source algorithm, new dry deposition and wet
deposition algorithms. This revised model is referred to as ISCSTDFT. The model has also been modified
to incorporate an hourly emissions file option for the purpose of this model evaluation study. The
ISCSTDFT model is placed on the Technology Transfer Network (TTN) bulletin board for beta testing.
2. Developing improved source characterizations: A method for characterizing the source activity data in the
appropriate formats for the existing and new ISCST2 models is being developed. The models will be run
using those specified source activity methods.
3. Statistical model evaluation protocol: The statistical model evaluation protocol describes the modeling
systems, observational data bases, statistical measures for determining model performance and evaluating
model overprediction. The statistical analysis of model performance will be performed using a model
evaluation software5 that implements the statistical measures for determining model performance and
evaluating model overprediction6. The basic test statistic is a robust estimate of the highest concentration
(RHC), based on the largest concentrations within a data set. The software calculates a composite
performance measure (CPM), based on the absolute fractional bias of the RHC values from the predicted
and observed data sets. Differences in the CPM values between different models provide a measure of the
relative performance of the models on a given data set.
4. Model evaluation: The existing ISCST2 model as well as the ISCSTDFT models will be evaluated as
specified in the model evaluation protocol. The input data to the model evaluation will include the model
predictions based on the source activity methods and the observed concentrations from the ambient
monitoring network.
NEW COMPONENTS OF THE ISCSTDFT MODEL
Dry and Wet Deposition Algorithms
One of the new features in the ISCSTDFT model is the capability to estimate deposition of particles
larger than 0.1 micrometers in diameter. The new deposition algorithm was selected as a result of a study
designed to identify dry deposition models suitable for routine use. Reviews were conducted of methods for
computing dry deposition velocity, plume depletion, and certain micrometeorological parameters from
routinely-available observations. Several observational data bases were identified from the scientific literature
and used in testing and evaluating several particle deposition velocity models. Recommendations for
computing particle deposition velocity, plume depletion, and micrometeorological variables have been
documented by the EPA7.
Improved Area Source Algorithm
Another feature of the ISCSTDFT model is an improved method for estimating ground-level
concentrations from area sources that are characterized by low-level releases with little buoyancy due to either
momentum or temperature. The algorithm selection process included model performance evaluation studies,
wind tunnel data collection and statistical comparisons8. As a result of this effort a numerically efficient area-
source algorithm was selected9. This algorithm, which is based on a numerical integration of the Gaussian
point source plume function over the area, provides improved treatment of source-receptor geometry and
allows placement of receptors within the area source. The user can define the area source as a rotated
rectangle. Another new feature incorporated in ISCSTDFT for this model evaluation study was an option to
specify an initial vertical dispersion parameter (cjzo) for an area source. This was done to study the differences
in modeling roadways as volume sources, as traditional area sources with no initial vertical mixing (Ozo =0) and
as area sources with some initial vertical mixing.
Fit Retention Algorithm
A third feature of the ISCSTDFT model is the ability to account for emissions from large open pits
such as those at surface coal mines. The new algorithm was developed by the EPA10 to properly model
those emissions that remain inside an open surface coal mine (i.e. pit retention). The algorithm was based
F-3
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on a wind tunnel experiment to Study the dispersion of participate matter from surface coal mines. The
wind tunnel experiments demonstated the following:
1. The mass distribution of the particles escaping the top surface of an open pit is different from what is
actually emitted inside the pit. The heavier particles tend to get trapped within the pit, thereby
shifting the mass distribution of the emissions escaping the pit towards the smaller particle sizes.
2. The emissions from a pit show a tendency to be emitted primarily from an upwind sub-area of the pit
opening. Figure 1 depicts this concept graphically. Emissions from a rectangular open pit of length L
and width W will be released out of the pit from an effective sub area of length AL and width AW
which are calculated as a function of the wind direction 6 and the dimensions of the pit. Note that the
user can define the pit source as a rotated rectangle.
3. The high level of turbulence in the pit causes the emitted particles to be initially mixed prior to exiting
the pit. This was found to be particularly important for estimating impacts at receptors close to the
pit.
Perry et. al. ° defined a set of equations to account for these observations. The pit is essentially
modeled as an area source (using the new area source algorithm), whose size is smaller than the actual
size of the pit area. This "effective" pit is always on the upwind side of the actual pit and its size and
shape is a function of the size of the pit, the depth of the pit, the wind speed and wind direction. The
emission rate for each particle size category is adjusted based on an "escape fraction". The escape
fraction reflects the fraction of the particle emissions for a given size category escaping the pit and is a
function of the particle settling velocity and the approach wind speed. A higher settling velocity results in
a lower escape fraction and therefore a lower adjusted emission rate. An initial az proportional to the
effective pit depth is determined. This is later factored into the standard ISCST2 az calculations. The
user can specify an open pit of rectangular shape of arbitrary orientation.
CHARACTERIZING EMISSIONS FROM AN OPEN PIT MINE
As mentioned earlier, particulate emissions from a mine can be caused by many types of activities.
One of the most challenging tasks of modeling a mining operation is the characterization of these
emissions. How does one translate the emission information that is generally collected and reported by
activity type (bulldozing, scraping, shoveling etc.) and by vehicle travel on roads into inputs that can be
input into ISCSTDFT? How should the emissions be distributed if two or more sources overlap spatially
(for example, vehicles traversing on part of a road which is inside the pit)? Moreover, the emissions
might be reported by shifts and the start and end times of the shifts may vary from day to day.
A mine emissions pre-processor has been developed to translate all this information into inputs to
ISCSTDFT. The program, called MINEMISS, reads inputs such as locations and dimensions of pits,
roads and other area and volume source type activities (dumping and loading of trucks). Files listing the
emission rates by shift for the entire modeling period are also read for each activity, type (scraper, dragline
etc.). A file defining the shift tunes is also supplied along with inputs in an options file.
MINEMISS performs two main tasks. First, it creates source input data in an ISC2 format for the
various activities for which the information is provided. The user has the option to characterize roads as
elongated area sources or as equally spaced volume sources. Each road segment is divided into these
areas or volume sources with a unique name assigned to each source. The dimensions, location and
orientation of these sources are calculated automatically from the primitive information provided to the
program. The area sources for roadways are restricted hi their dimensions to a 10:1 aspect ratio due to
the reported limitations of the area source algorithm beyond this ratio. The number of area sources is
determined using the aspect ratio calculated for the segment. If, for example, the ratio exceeds 10:1, but
is less than 21:1, two area sources will be assigned to model this segment. Furthermore, MINEMISS
uses a unique grid methodology for emission sources which move about covering different areas during
different time periods (such as the draglines and the scrapers). A grid of numerous area sources is
created which covers the domain of these moving sources. Each gridded area source is then assigned an
appropriate emission rate for those hours when the sources are active in the particular grid cell.
F-4
-------
Second, after creating the sources, MINEMISS processes emission rates reported by shift and
allocates them to the appropriate pit, area or volume sources. There is a large amount of book-keeping
involved in this process. For example, if a road segment happens to be inside a pit, the emissions from
that segment are added to the pit emissions instead of assigning them to the road area or volume sources.
Emissions may be output either by shift or averaged by shift over the entire modeling period.
The program creates an ISC2-formatted source pathway output file containing all the sources. It
also produces an hourly emissions file corresponding to the source file. These outputs can then be
directly incorporated into an ISC runstream.
For the Cordero model evaluation study, the two active pits were modeled as open pit sources lor
ISCSTDFT and as rectangular area sources for ISCST2. Roads were modeled as area and volume
sources as discussed above. Figure 2 shows the relative locations of the various sources and receptors
for this study. The emission rates were based on three different sets of emission factors. The first set
was based on the emission factors found in Section 8.24 of AP-42 for all sources. This is, currently, the
most commonly used method of estimating emissions from surface coal mines. The other two sets were
enhancements to the Set 1 method. Set 2 was based on a new equation for heavy vehicles, emission
factors contained in Section 8.24 for bulldozing, graders and scrapers and Section 11.2 factors for all
other sources. This new equation for heavy vehicles was based on an emissions testing program at the
Cordero Mine" . Set 3 was similar to Set 2 except that it comprised of hourly emission factors for heavy
and light vehicle traffic. These factors were derived from direct representative on-site emission
measurements. For set 2, an emission control factor was applied based on haul roads silt and soil
moisture content which reflects the effects of road watering. For set 3, the adjustments to emission rates
were made for mitigation due to hourly rainfall or shift-resolved watering activity.
OBSERVATIONS AND CONCLUSIONS
The process of characterizing mine emissions of the Cordero database uncovered several interesting
observations. Most importantly, it was found that the TSP and PMio emissions from vehicle travel on the
unpaved mine roads are much higher than from any other source at this surface coal mine (Figure 3).
Depending on the emission set, the roads can account for as much as 75% of the emissions and the north pit
for about 20%. Even though the emissions from the other sources are small, they are not insignificant because
the ambient air monitors are located quite close to the sources. The emissions from the various sources differ
by shift. In general it was observed that the mid-day shift had more emissions attributed to it than any other
shift Note that in the figures, shift 0 spans hours between midnight to 6 or 7 AM, shift 1 is the entire 10-12
hour day shift and shift 3 spans the hours between 4 or 7 PM through midnight. Figure 4 shows that there are
significant differences between emission rates calculated using the three different sets of emission factors for
the roads. Figure 5 shows similar differences for the north pit. Note that all the emissions have been shown as
annualized emissions in tons per year to give a better perspective on the relative magnitude of paniculate
emissions from the mine. This was based on an assumption that the emissions during the study period are
representative of emissions over the entire year. It is important for the user to note that there was a significant
difference in the number of sources required to model the roads as area sources versus roads as volume
sources. For the Cordero study, 67 area sources were required to model all the roads. On the other hand, 510
volume sources were needed to model the same as volume sources.
Preliminary model comparison results show that the predicted concentrations from roads modeled as
volume sources are quite similar to those from roads modeled as area sources with an initial vertical dispersion
parameter. A test was performed to examine the sensitivity of the predicted concentrations to the width of a
road segment. A150 meter long road segment was modeled as an area source using four different widths -15,
30,45 and 60 meters. A string of receptors were placed perpendicular to the road starting at the median of the
road up to 200 meters from the median. A single stable hour of meteorology was modeled with the wind
blowing toward the receptors. The emission rates for the various road widths were specified such that the total
emission from the entire road segment was always 1.0 grams/second. As seen in Figure 6, it was observed that
the predicted concentrations did not vary significantly for the receptors located beyond the periphery of the
F-5
-------
road. For the receptors that are inside the road segment, the concentrations were higher for the narrower road
segments than the wider road segments due to a higher emission rate per unit area.
The model results are currently being analyzed and compared with observed data following the model
evaluation protocol4. A model evaluation report will be prepared upon completion of the project documenting
the results of the study. :• •
DISCLAIMER
This paper has been reviewed in accordance with the U.S. Environmental Protection Agency's peer and
administrative review policies and approved for presentation and publicatioa Mention of trade names or
commercial products does not constitute endorsement or recommendation for use.
REFERENCES
1. Environmental Protection Agency, 1992: User's Guide for the Industrial Source Complex (ISC2)
Dispersion Models, Volume 1,2, and 3. EPA-450/R-92-008a-c. U.S. Environmental Protection Agency,
Research Triangle Park, NC [NTIS PB92-232461, PB92-232453, and PB92-232479, respectively].
2. Environmental Protection Agency, 1985/1986/1988/1990/1991: Compilation of Pollution Emission
Factors, AP-42, 4th Edition. Supplement A, October 1986. Supplements, September 1988. Supplement
C, September 1990. Supplement D, September 1991. U.S. Environmental Protection Agency, Research
Triangle Park, NC.
3. Environmental Protection Agency, 1994: Modeling Fugitive Dust Impacts from Surface Coal Mining
Operations-Phase I. EPA-454/R-94-024. U. S. Environmental Protection Agency, Research Triangle
Park, NC [NTIS PB95-104980].
Environmental Protection Agency, 1995: Modeling Fugitive Dust Impacts from Surface Coal Mining
Operations-Phase II, Model Evaluation Protocol. EPA-454/R-94-025. U. S. Environmental Protection
Agency, Research Triangle Park, NC [NTIS PB95-146510].
Environmental Protection Agency, 1993: User's Guide for the Model Evaluation Methodology (MEM)
System for Comparing Model Performance, Version 1.0 (Draft). U. S. Environmental Protection Agency,
Research Triangle Park, NC.
Environmental Protection Agency, 1992: Protocol for Determining the Best Performing Model EPA-
454/R-92-025. U. S. Environmental Protection Agency, Research Triangle Park, NC [NTIS PB93-
226082].
Environmental Protection Agency, 1994: Development and Testing of a Dry Deposition Algorithm
(Revised). EPA-454/R-94-015. U. S. Environmental Protection Agency, Research Triangle Park, NC
[NTIS PB94-183100].
Touma, IS., J.S. Irwin, J.A. Tikvart and C.T. Coulter, 1995: A Review of Procedures for Updating Air
Quality Modeling Techniques for Regulatory Programs. Journal of Applied Meteorology, Vol 34 No 3
pp.731-737.
Environmental Protection Agency, 1995: User's Guide for the Industrial Source Complex (ISC2)
Dispersion Models, Volume 2: Revised. U.S. Environmental Protection Agency, Research Triangle Park,
NC.
10. Environmental Protection Agency, 1994: Recommendations on the use of ISC2A for Surface Mining
(Draft). U. S. Environmental Protection Agency, Research Triangle Park, NC.
11. Muleski, G.E., G. Garman, and C. Cowherd, Jr., 1994: Surface Coal Mine Emission Factor Study. Draft
Final Test Report, EPA Contract No. 68-DO-0123, Work Assignment 37 and 55, U.S. Environmental
Protection Agency, Research Triangle Park, NC.
4.
5.
6.
7.
8.
9.
F-6
-------
r—
Wind direction
W
Figure 1: Graphical representation of an open pit source
SCHEMATIC OF THE CORDERO
MODEL EVALUATION STUDY AREA
4000 —i
1
c
1
o
O
•a
I
Q
•3
'O
o
0 —
E2
•§ -4000
-8000
MRI-6
MRI-5
HV-1
MRI-4
MRI-3
HV-2/2A
O
D
Legend
Pitt
PKti>Ara>Soure*>
Road< a« Volume Source!
Road< » ATM Sourcn
ScnptrAdnMy
Monitor Locadont
HV-3
T
-8000
-4000 0
Easting (meters) in Model Domain Coordinates
Figure 2: Sources and receptors for the Cordero model evaluation study
4000
F-7
-------
I
111
SHIFT 2
SHIFT o
I I 1 1 i i I I
I 3 3 I 5
Mine Activity
i
Figure 3: Distribution of emission rates by source type at the Cordero mine
ROADWAY EMISSIONS
SET-1
SET-2
Emission Factor
Figure 4: Variation in the roadway emissions by shift for three different sets of emission factors.
F-8
-------
NORTH PIT EMISSIONS
w
SET-1 SET-2 SET-3
Bnlssion Factor
Figure 5: Variation in the north pit emissions by shift for three different sets of emission factors.
400
Legend Title
' Q RoadWdth = 15m
—0— Road Width = 30m
RoadV\Mth = 45m
Road WWth = 60m
1 10 100
Distance from the Center of the Road (m)
Figure 6: Variation in modeled downwind concentrations for different road widths
F-9
-------
APPENDIX G
GUIDE TO THE EMISSIONS AND MODELING DATA BASE
This appendix is intended to serve as a guide to the data base provided for the surface coal
mine emissions inventory, dispersion modeling, and model evaluation results. The data base
contains all of the data needed to duplicate the analysis, including the inputs to the mine emissions
preprocessor program (MTNEMISS), the inputs to the dispersion models (ISCST3 and ISCST2),
and the inputs to the statistical model evaluation software (EPAMEM and OVERMEN!). Figure
G-l provides a flow chart showing the inputs and outputs for the three stages of the analysis: 1)
emissions preprocessing; 2) dispersion modeling; and 3) statistical evaluation. The inputs to
MINEMISS include the physical source locations and emissions data prepared by MRI for each of
the sets of emission factors and the various source categories. The MINEMISS program
generates the source parameters and hourly emissions file for input to the dispersion model. The
MINEMISS program also generates the source location coordinates for the roadway sources
based on whether volume or area sources are being used. The input files for the ISC models
provided with the data base already include the source parameter data generated by MINEMISS.
These input files, together with the meteorological data and the MINEMISS-generated hourly
emissions files, are sufficient to run the dispersion models. The dispersion models produce
POSTFELE outputs of predicted concentrations that are used as input to the model evaluation
software (EPAMEM), along with the observed concentration data and the EPAMEM input
options file. The daily average meteorology file (CORDERO. AVG) is needed for the diagnostic
evaluation component of EPAMEM to work properly, even though the diagnostic evaluation
component is given a weight of zero in this analysis. A separate program called OVERMEM (not
shown in Figure G-l) is used to perform the analysis of model overprediction. The OVERMEM
program uses the basic inputs as the EPAMEM program.
All of the data indentified on this flow chart are contained in compressed files on two 3.5"
diskettes, except for the hourly emission files (*.EMI) produced by MINEMISS. The hourly
emission files are not included due to their size, however, they can be easily generated from the
data provided. When uncompressed, the sixteen hourly emission files (one for each model and
pollutant combination) would occupy almost 250 Mb of disk storage. The contents of each of the
files is described below.
G-l
-------
Source
Emission
Files
Shift
Definitions
(SHIFTS.DBF)
Source
Locations
(SOURCES.LOG)
Road
Locations
(ROADS.LOC)
MINEMISS
Input Files
(*.MIN)
MINEMISS
Emissions
Preprocessor
Program
Meteorology
File
(CORDERO.MET)
Hourly
Emission
Files
(*.EMI)
ISC Model
Input Files
(*.IHP)
ISCST3/ISCST2
Dispersion
Model
Observed
^Concentrations
C.OBS)
Daily Average
Meteorology
(CORDERO.AVG)
ISC Model
POSTFILE
Outputs
(*.PST)
EPAMEM Input
Files
(*.INP)
EPAMEM
Statistical
Evaluation
Software
I
EPAMEM
Statistical
Evaluation
Results
(*.OUT)
Figure G-l. Flow Chart of the Emissions Preprocessing, Modeling and Evaluation Analysis
G-2
-------
Disk#l:
MINEMISS.ZIP-
Code and EXE files fop the MINEHISS Emissions Preprocessor
Length Name Description
412970 MINEMISS.EXE LAHEY EXE for the Emissions Preprocessor
341343 MINEAREA.EXE LAHEY EXE for the ISCST2 Version of the Emissions Preprocessor
40471 EMIAREA.FOR FORTRAN Code for the Emissions Preprocessor
36869 EHIPROC.FOR Modified Version of EMIAREA.FOR for ISCST2 Output
69260 MINEMISS.FOR FORTRAN Code for the Emissions Preprocessor
62929 SETUP.FOR FORTRAN Code for the Emissions Preprocessor
11080 HINEHISS.INC FORTRAN Code for the Emissions Preprocessor
974922
EMIS1NP.ZIP- Input Files
Length
5016
5016
5016
5016
1952
2352
2352
2297
2207
90312
5016
2195
2299
2299
2586
2586
2586
2586
2586
2586
5016
5016
5016
5016
2044
2352
2352
2297
2207
90314
5016
2195
2483
2299
2586
2586
2586
2586
2586
2586
Name
DCOAL-N.EH1
DCOAL-S.EH1
DOVER-N.EM1
DOVER-S.EM1
DRAGLINE. EM1
LCOAL-N.EM1
LCOAL-S.EM1
LOVER-N.EM1
LOVER-S.EH1
ROADS. EM1
SCRAPER. EH1
UCOAL.EH1
UOVER-N.EM1
UOVER-S.EH1
WCOAL-N.EM1
WCOAL-S.EM1
ULOVER-N.EM1
WLOVER-S.EM1
WUOVER-N.EM1
WUOVER-S.EM1
DCOAL-N.EM2
DCOAL-S.EM2
DOVER-N.EH2
DOVER -S.EH2
DRAGLINE.EH2
LCOAL-N.EM2
LCOAL-S.EM2
LOVER-N.EM2
LOVER -S.EM2
ROADS. EM2
SCRAPER. EH2
UCOAL.EM2
UOVER-N.EH2
UOVER-S.EM2
WCOAL-N.EH2
WCOAL-S.EM2
WLOVER-N.EM2
WLOVER-S.EM2
UUOVER-N.EM2
WUOVER-S.EH2
for MINEMISS, the Emissions Preprocessor
Description
SET
SET
SET
SET
SET
SET
SET
SET
. SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
SET
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
2
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
Emissions
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
Coal Bulldozing/Northpit
Coal Bulldozing/Southpit
Overburden Bulldozing/Northpit
Overburden Bulldozing/Southpit
Dragline Activity
Coal Loading/Northpit
Coal Loading/Southpit
Overburden Loading/Northpit
Overburden Loading/Southpit
Vehicle Travel Over Roads
Scraper Activity
Coal Unloading
Overburden Unloading/Northpit
Overburden Unoading/Southpit
Wind Erosionacoal Loading/Northpit
Wind Erosionacoal Loading/Southpit
Wind ErosionaOverburden Loading/Northpit
Wind ErosionSlOverburden Loading/Southpit
Wind ErosionSOverburden Unloading/Northpit
Wind Erosion30verburden Unloading/Southpit
Coal Bulldozing/Northpit
Coal Bulldozing/Southpit
Overburden Bulldozing/Northpit
Overburden Bulldozing/Southpit
Dragline Activity
Coal Loading/Northpit
Coal Loading/Southpit
Overburden Loading/Northpit
Overburden Loading/Southpit
Vehicle Travel Over Roads
Scraper Activity
Coal Unloading
Overburden Unloading/Northpit
Overburden Unoading/Southpit
Wind Erosionacoal Loading/Northpit
Wind Erosionacoal Loading/Southpit
Wind ErosionaOverburden Loading/Northpit
Wind ErosionaOverburden Loading/Southpit
Wind ErosionaOverburden Unloading/Northpit
Wind ErosionaOverburden Unloading/Southpit
G-3
-------
5016
5016
5016
5016
2044
2352
2352
2297
2207
90312
5016
2195
2483
2299
2586
2586
2586
2586
2586
2586
1620
3266
7388
1223
1220
1171
1167
1168
1167
1163
1164
1223
1220
1171
1167
1168
1167
1163
1164
DCOAL-N.EM3
DCOAL-S.EM3
DOVER-N.EH3
DOVER- S.EH3
DRAGLINE.EH3
LCOAL-N.EH3
LCOAL-S.EH3
LOVER-N.EH3
LOVER-S.EM3
ROADS. EH3
SCRAPER. EH3
UCOAL.EM3
UOVER-N.EM3
UOVER-S.EH3
WCOAL-N.EH3
WCOAL-S.EH3
WLOVER-N.EM3
WLOVER-S.EH3
WUOVER-N.EH3
UUOVER-S.EM3
SHIFTS.DEF
ROADS. LOC
SOURCES. LOC
PSET1PV2.HIN
PSET3SV2.MIN
PSET2PV.HIN
PSET2SV.MIN
PSET3SV.HIN
PSET2PA.HIN
PSET2SA.MIN
PSET3SA.HIN
TSET1PV2.HIN
TSET3SV2.H1N
TSET2PV.MIN
TSET2SV.MIN
TSET3SV.MIN
TSET2PA.HIN
TSET2SA.MIN
TSET3SA.MIN
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
SET 3 Emissions
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
from
Definition of Shift
Locat i on/Coordi nates
Locat i on/Coordi nates
MINEMISS Input
MINEHISS Input
HINEMISS Input
HINEHISS Input
HINEMISS Input
MINEHISS Input
HINEMISS Input
HINEHISS Input
HINEHISS Input
MINEHISS Input
HINEMISS Input
MINEMISS Input
HINEMISS Input
MINEMISS Input
MINEMISS Input
MINEHISS Input
File
File
File
File
File
File
File
File
File
File
File
File
File
File
File
File
Coal Bulldozing/Northpit
Coal Bulldozing/Southpit
Overburden Bui Idozi ng/Northpi t
Overburden Bulldozing/Southpit
Dragline Activity
Coal Loading/Northpit
Coal Loading/Southpit
Overburden Loading/Northpit
Overburden Loading/Southpit
Vehicle Travel Over Roads
Scraper Activity
Coal Unloading
Overburden Unloading/Northpit
Overburden Unoading/Southpit
Wind Erosionacoal Loading/Northpit
Wind ErosiorflCoal Loading/Southpit
Wind Erosionaoverburden Loading/Northpit
Wind Erosionaoverburden Loading/Southpit
Wind Erosionaoverburden Unloading/Northpit
Wind Erosionaoverburden Unloading/Southpit
Start and End Times
of Road Segments
of Area/Volume Sources
for HODEL-1
for MODEL-2
for HODEL-3
for MODEL-4
for HODEL-5
for MODEL-6
for MODEL-7
for MODEL-8
for HODEL-1
for MODEL-2
for MODEL-3
for MODEL-4
for MODEL-5
for MODEL-6
for MODEL-7
for HODEL-8
- PH10
* See NOTES Below
- TSP
* See NOTES Below
479810
ISCST3 FORTRAN Code
ISCST3SR.ZIP-
Length Name Description
625 F77LISCS.BAT Batch File for Compiling with LAHEY
93249 CALC1.FOR ISCST3 Routine
18584 CALC2.FOR 1SCST3 Routine
14791 CALC3.FOR ISCST3 Routine
24802 CALC4.FOR ISCST3 Routine
55014 COSET.FOR ISCST3 Routine
54310 DEPFLUX.FOR ISCST3 Routine
56794 INPSUM.FOR ISCST3 Routine
58876 ISCST3.FOR ISCST3 Routine
45477 HESET.FOR ISCST3 Routine
33909 METEXT.FOR ISCST3 Routine
65310 OUSET.FOR ISCST3 Routine
69066 OUTPUT.FOR ISCST3 Routine
9025 PCCODE.FOR ISCST3 Routine
46538 PITAREA.FOR ISCST3 Routine
14573 PRISE.FOR ISCST3 Routine
67008 RESET.FOR ISCST3 Routine
32926 SETUP.FOR ISCST3 Routine
26966 SIGHAS.FOR ISCST3 Routine
101448 SOSET.FOR ISCST3 Routine
G-4
-------
20819
5098
20934
439
2194
166
938941
TGSET.FOR
DEPVAR.INC
MAIN1.INC
MAINZ.INC
HAIN3.INC
F77LISCS.LRF
ISCST3 Routine
ISCST3 Routine
ISCST3 Routine
ISCST3 Routine
ISCST3 Routine
ISCST3 Link Response File
ISCINPUT.ZIP- ISCST2/ISCST3 Input Files
Length Name
55490
74692
74710
79053
79048
79048
24417
24412
24412
7491 1
74929
79133
79128
79128
24497
24492
24492
CORDERO.
MET
PSET1PV2.INP
PSET3SV2
PSET2PV.
PSET2SV.
PSET3SV.
PSET2PA.
PSET2SA.
PSET3SA.
TSET1PV2
TSET3SV2
TSET2PV.
TSET2SV.
TSET3SV.
TSET2PA.
TSET2SA.
TSET3SA.
.INP
1NP
INP
INP
INP
INP
INP
.INP
.INP
INP
INP
INP
INP
INP
INP
Cordero Hourly Meteorology (A!
ISCST2
ISCST2
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
ISCST2
ISCST2
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
Input
File
File
File
File
File
File
File
File
File
File
File
File
File
File
File
File
for
for
for
for
for
for
for
for
for
for
for
for
for
for
for
for
MODEL- 1
MODEL-2
HODEL-3
MODEL-4
MODEL -5
MODEL-6
MODEL-7
MODEL-8
MODEL -1
MODEL-2
MODEL-3
MODEL-4
MODEL-5
MODEL-6
MODEL-7
MODEL-8
975992
17
PM10
* See NOTES Below
TSP
* See NOTES Below
ISCOUTPT.ZIP- ISCST2/ISCST3 Output Files
Length Name
653991
654237
756950
756950
756950
336264
336264
336264
719659
719823
836414
836414
836414
357252
357252
357252
24300
24300
24300
24300
24300
24300
24300
24300
PSET1PV2.0UT
PSET3SV2.0UT
PSET2PV.OUT •
PSET2SV.OUT
PSET3SV.OUT
PSET2PA.OUT
PSET2SA.OUT
PSET3SA.OUT
TSET1PV2.0UT
TSET3SV2.0UT
TSET2PV.OUT
TSET2SV.OUT
TSET3SV.OUT
TSET2PA.OUT
TSET2SA.OUT
TSET3SA.OUT
PSET1PV2.PST
PSET3SV2.PST
PSET2PV.PST
PSET2SV.PST
PSET3SV.PST
PSET2PA.PST
PSET2SA.PST
PSET3SA.PST
ISCST2 Output File for MODEL-1
ISCST2 Output File for MODEL-2
ISCST3 Output File for MODEL-2
ISCST3 Output File for MODEL-4
ISCST3 Output File for MODEL-5
ISCST3 Output File for MODEL-d
ISCST3 Output File for MODEL-7
ISCST3 Output File for MODEL-8
ISCST2 Output File for MODEL-1
ISCST2 Output File for MODEL-2
I SCST3 Output File for MODEL-3
ISCST3 Output File for MODEL-4
ISCST3 Output File for MODEL-5
ISCST3 Output File for MODEL-6
ISCST3 Output File for MODEL-7
ISCST3 Output File for MODEL-S
ISCST2 POST File for MODEL-1
ISCST2 POST File for MODEL-2
ISCST3 POST File for MODEL-3
ISCST3 POST File for MODEL-4
ISCST3 POST File for MODEL-5
ISCST3 POST File for MODEL-6
ISCST3 POST File for MODEL-7
ISCST3 POST File for MODEL-8
PM10
* See NOTES Below
TSP
* See NOTES Below
- PM-10
* See NOTES Below
G-5
-------
24300
24300
24300
24300
24300
24300
24300
24300
TSET1PV2
TSET3SV2
.PST
.PST
TSET2PV.PST
TSET2SV.
' TSET3SV.
TSET2PA.
TSET2SA.
TSET3SA.
PST
PST
PST
PST
PST
ISCST2
ISCST2
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
ISCST3
POST
POST
POST
POST
POST
POST
POST
POST
File
File
File
File
File
File
File
File
for
for
for
for
for
for
for
for
MODEL- 1
MODEL-2
HODEL-3
MODEL -4
MODEL-5
MOOEL-6
MODEL-7
MODEL-8
- TSP
* See NOTES Below
9997150
32
* NOTES:
HOOEL-1 Through MODEL-8 are in the Same Order as the models listed in Table 8 (p 32)
from Surface Coal Mining Operations - Phase II
(Model Evaluation Protocol)"
Following is the file naming convention for the various models:
Character 1
: P - PM10
T - TSP
Characters 2-5: SET1 - Emission Set 1
SETH - Emission Set 2
SET3 - Emission Set 3
Character 6 : P - 30-day Period Average
S - Shift Average
Character 7 : V - Roads as Volume Sources
A - Roads as Area Sources
(Character 8) : (null) - ISCST3
2 - ISCST2
Disk #2:
====s============================================
EPAHEM.ZIP- Code and EXE files for EPAHEM
Length Name
2474182 EPAMEM.EXE
219343 EPAMEM.FOR
9982 MAIN1.INC
439 MAINZ.INC
Description
LAHEY EXE for EPAMEM
FORTRAN code for EPAMEM
FORTRAN code for EPAMEM
FORTRAN code for EPAMEM
2703946
OVERMEM.ZIP - Code and EXE files for Overprediction Version of EPAMEM
Length Name
Description
2907670 OVERMEM.EXE LAHEY EXE for the "Overprediction" version of
221674 OVERMEN.FOR FORTRAN code for the "Overprediction vers on of EPAMEM
9982 HAIN1.INC FORTRAN code for the "Overprediction version of EPAMEM
439 MAIN2.INC FORTRAN code for the "Overprediction" version of EPAMEM
3139765 4
G-6
-------
MEMFILES.ZIP-
Length Name
EPAHEH / OVERMEM Inputs and Outputs
2550
3270
3270
4030
4030
4027
4027
31891
36127
31891
36127
355640
CORDERO.AVG
24H-PM10.0BS
24H-TSP.OBS
PMSTAT.INP
PMOVER.INP
TSPSTAT.INP
TSPOVER.INP
PMSTAT.OUT
PHOVER.OUT
TSPSTAT.OUT
TSPOVER.OUT
19
Description
Daily Average Meteorology
24-Hr Average Monitored Concentrations / PM-10
24-Hr Average Monitored Concentrations / TSP
EPAMEM Input File for PM-10 Best-Model Analysis
OVERMEM Input File for PM-10 Overprediction Analysis
EPAMEM Input File for TSP Best-Model Analysis
OVERMEN Input File for TSP Overprediction Analysis
EPAMEM Output File for PM-10 Best-Model Analysis
OVERMEM Output File for PM-10 Overprediction Analysis
EPAMEM Output File for TSP Best-Model Analysis
OVERMEM Output File for TSP Overprediction Analysis
APPNDXC.ZIP- Modeled and Observed Concentrations (from Appendix C)
Length Name Description
96820 APPNDXC.TXT
96820
Modeled and Observed Concentrations in space delimited text
file, based on the tables in Appendix C
1
G-7
-------
-------
TECHNICAL REPORT DATA
(Please read Instructions on reverse before completing.)
1. REPORT NO.
EPA-454/R-96-002
3. RECIPIENT'S ACCESSION NO.
4 . TITLE AND SUBTITLE
Modeling Fugitive Dust Impacts from Surface Coal
Mining Operations-Phase III. Evaluating Model
Performance
5. REPOBT DATE
December 1995
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
8 . PERFORMING ORGANIZATION REPORT NO.
9. PERFORMING ORGANIZATION NAME AND ADDRESS
10. PROGRAM ELEMENT NO.
Pacific Environmental Services, Inc.
5001 S. Miami Blvd.
Research Triangle Park, NC 27709
11. CONTRACT/GRANT NO.
EPA Contract No. 68D30001
12 . SPONSORING AGENCY NAME AND ADDRESS
U.S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Emissions, Monitoring & Analysis Division
Research Triangle Park, NC 27711
13. TYPE OF REPORT AND PERIOD COVERED
Final Report
14. SPONSORING AGENCY CODE
15. SUPPLEMENTARY NOTES
EPA Work Assignment Manager:
Jawad S. Touma
16. ABSTRACT
This report -is the third part of a study under Section 234 of the amended Clean Air Act
which requires that EPA analyze the accuracy of the Industrial Source Complex (ISC)
model and AP-42 Compilation .of Air Pollutant Emission Factors to determine the effect
on air quality of fugitive particulate emissions from surface coal mines. The first
report, titled "Modeling Fugitive Dust Impacts from Surface Coal Mining Operations-
Phase I", 454/R-94-024 described the field monitoring program to collect data on
ambient air quality, meteorology and source activity at a surface coal mine in the
Powder River Basin in Wyoming. The second report titled "Modeling Fugitive Dust
Impacts from Surface Coal Mining Operations-Phase II, Model Evaluation Protocol" EPA-
454/R-94-025 defined the procedures that were used to identify the best performing
model. This third report presents the results of the performance evaluation of several
models which include the recent improvements to the ISC model applicable to fugitive
particulate emissions, and improvements to the emission factors used to estimate
emissions from surface coal mine activity.
AND DOCUMENT ANALYSIS
DESCRIPTORS
b. IDENTIFIERS/OPEN ENDED TERMS
Air Pollution
Air Quality Dispersion Models
Meteorology
Surface Coal Mines
Fugitive Dust
18. DISTRIBUTION STATEMENT
Release Unlimited
19. SECURITY CLASS (Report]
Unclassified
21. NO..OF PAGES
156
20. SECURITY CLASS IPage)
Unclassified
XPA Torn 2220-1 (Rev. 4-77)
PREVIOUS EDITION IS OBSOLETE
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