Environmental Engineering Reference
In-Depth Information
TABLEĀ 2.1
Ramp Rates for PSCO's Coal-Fired Plants
10-Minute Ramp Rate
Ownedor
IRPResource
Capacity
(MW)
Plant
Fuel
(MW)
%Cap
Arapahoe 3
Coal
Owned
45
6
13
Arapahoe 4
Coal
Owned
111
5
5
Cabin Creek A
HE
Owned
162
95
59
Cabin Creek B
HE
Owned
162
150
93
Cherokee 1
Coal
Owned
107
6
6
Cherokee 2
Coal
Owned
106
6
6
Cherokee 3
Coal
Owned
152
22
14
Cherokee 4
Coal
Owned
352
20
6
Comanche 1
Coal
Owned
325
22
7
Comanche 2
Coal
Owned
335
22
7
Fort. St. Vrain
NG
Owned
690
75
11
Pawnee
Coal
Owned
505
16
3
Valmont 5
Coal
Owned
186
14
8
Valmont 6
Coal
Owned
43
43
100
Arapahoe 5, 6, and 7
NG
IRP
122
20
16
Blue Spruce
NG
IRP
271
81
30
Brush 1 and 3
NG
IRP
76
18
24
Brush 2
NG
IRP
68
19
28
Brush 4
NG
IRP
135
44
33
Fountain Valley
NG
IRP
238
34
14
Manchief
NG
IRP
261
97
37
Rocky Mountain Energy
NG
IRP
587
103
18
Spindle Hill
NG
IRP
269
119
44
Thermo Fort Lupton
NG
IRP
279
147
53
Tristate Brighton
NG
IRP
132
55
42
Tristate Limon
NG
IRP
63
27
43
Valmont 7 and 8
NG
IRP
79
38
48
HE = hydroelectric. NG = natural gas.
generation curve with the event (July 2), then compare the results over the
duration of the event (Method A). TableĀ 2.2 summarizes the calculations. The
measured emission rates for July 29 are presented in the first row. The second
row indicates total emissions for the no-wind scenario; the third row shows
total emissions associated with July 2 generation. Analyzing the emission
impacts in this manner results in the estimate that the wind event reduced
SO 2 by 730 lb, NO X by 1,386 lb, and CO 2 by 392 tons (bottom row). The limita-
tion of Method A is that it replaces the actual emissions that occurred on July
2 with estimated emissions from a stable day; they are lower because of the
inefficiency of the boiler by cycling as described above.
 
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