BAY AREA AIR QUALITY
MANAGEMENT DISTRICT |
Source Category
| Source: | Boiler | Revision: | 3 |
| Document #: | 17.2.1 | ||
| Class: | >33.5 MMBtu/hr to <50 MMBtu/hr Heat Input | Date: | 05/13/98 |
Determination
POLLUTANT |
BACT 1. Technologically Feasible/ Cost Effective 2. Achieved in Practice |
TYPICAL TECHNOLOGY |
| POC | 1. n/d 2. n/s |
1. n/d 2. Good Combustion Practicea |
| NOx | 1. 9 ppmv @ 3% O2
Dry a,b,c 2. 25 ppmv @ 3% O2 Dry a,b,c |
1. Low NOx
Burners + Flue Gas Recirculation + Selective Catalytic Reductiona 2. Low NOx Burners + Flue Gas Recirculationa |
| SO2 | 1. Natural Gas or Treated
Refinery Gas Fuel w/ <.50 ppmv Hydrogen Sulfide and <100 ppmv Total
Reduced Sulfur a,b 2. Natural Gas or Treated Refinery Gas Fuel w/ <100 ppmv Total Reduced Sulfur a,c |
1. Fuel Selection a,b 2. Fuel Selection a,b |
| CO | 1. n/d 2. 100 ppmv @ 3% O2 Dry a,d |
1. n/d 2. Good Combustion Practicea |
| PM10 | 1. n/d 2. Natural Gas or Treated Refinery Gas Fuel a,b |
1. n/d 2. Fuel Section a,b |
| NPOC | 1. n/a 2. n/a |
1. n/a 2. n/a |
References
| a. BAAQMD b. BACT is 20/25 ppmvd NOx @ 3% O2 and 100 ppmvd CO @ 3 % O2 regardless of fuel. However, emergency backup fuel oil w/ < 0.05 wt. % sulfur may be permitted to emit up to 60 NOx ppmvd @ 3% O2 and 100 ppmvd CO @ 3 % O2 during natural gas curtailment. c. NOx determination by BAAQMD Source Test Method ST-13A or B (average of three 30-minute sampling runs); or Continuous Emission Monitor (3-hour average); or BAAQMD approved equivalent. d. CO determination by BAAQMD Source Test Method ST-6 (average of three 30 minute sampling runs); or Continuous Emission Monitor (3-hour average), or BAAQMD approved equivalent. |