Transcript Slide 1
Mercury Monitoring Barrett Parker, EPA Emissions Measurement Center Basis for Mercury Monitoring • Utility air toxics report to Congress – EPA made determination for MACT rule • Proposed rule 1/30 (69 FR 4652) • New PS included • Comment period closed 3/30 Electric Utility MACT • 12 month rolling average mercury emission limit • Cap and trade system is an alternative EMC Involvement • Collected data on mercury monitors • Made recommendations for proposal • Partnered with CAMD, ORD, NIST, EPRI Test Objectives • Determined – Ability for reliable data over time – Durability, availability, maintenance requirements – Suitability of draft PS-12 for CEMS • Investigated all types of mercury monitors – Sought options for flexibility and accountability Monitoring Types • Periodic Testing (ASTM D 6784-02, M29) – Reference method • Continuous collection, delayed analysis (sorbent tube) • Continuous collection and analysis (CEMS) – Wet conversion, dry conversion, other Monitoring Types (continued) • CEMS and sorbent tube selected – Requested comments on monitoring for sources emitting less than 25 pounds of mercury per year German Experience • Mercury CEMS on Incinerators – No requirements for coal-fired power plants • Visited six incinerators – One co-fired lignite to produce electricity • Sources are well controlled – ESPs, scrubbers, carbon adsorption, and SCR • 3rd party instrument certification Test Phase Description • Phase I (summer 01) – 140 MW firing bituminous coal with cold side ESP – Use 2 German-certified CEMS • Phase II (fall 02) – Same site – Use 6 CEMS and EPRI monitor Test Facility During Phase II • Instruments (left to right) – Envimetrics, Mercury Instruments, Genesis, Opsis, Durag, PS Analytical EPRI’s Carbon Tube Sampler Test Phase Description (continued) • Phase III Pilot (spring 03) – Low level detection and interference checks – Pilot scale facility firing natural gas and lignite, bituminous, and subbituminous coals – Use 3 CEMS and EPRI monitor Test Phase Description (continued) • Phase III (summer 03) – 550 MW firing subbituminous coal with dry FGD, SCR, and baghouse – 5 CEMS and EPRI monitor Test Phase Description (continued) • Phase IV (fall 03) – 440 MW firing bituminous coal with wet FGD and reverse-air baghouse – 2 CEMS and EPRI monitor – 3 three-hour test periods Phase I - Initial 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 RM 8 9 10 11 Phase I - Initial 20 ug / m3 15 10 5 0 1 2 3 4 5 RM 6 7 8 CEMS #1 9 10 11 Phase I – Final 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 RM Phase I - Final 20 ug / m3 15 10 5 0 1 2 3 4 RM 5 6 7 8 9 10 11 12 13 14 15 Wet CEMS CEMS #2 Phase II - Initial 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 RM 8 9 10 11 12 Phase II - Initial 20 ug / m3 15 10 5 0 1 RM 2 3 4 Wet CEMS 5 6 7 8 CEMS #2 9 10 11 12 CEMS #3 Phase II - Final 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 RM 8 9 10 11 12 Phase II - Final 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 8 9 10 11 12 RM Wet CEMS CEMS #2 CEMS #3 CEMS #4 CEMS #5 Xray CEMS Phase III - Pilot Scale 20 ug / m3 15 10 5 0 1 3 5 7 9 11 RM avg 13 15 17 Phase III - Pilot Scale 20 ug / m3 15 10 5 0 1 RM avg 3 5 7 Wet CEMS 9 11 CEMS #6 13 15 17 CEMS #4 Phase III - Initial 20 ug / m3 15 10 5 0 1 2 3 4 5 6 7 RM 8 9 10 11 12 Phase III - Initial 20 ug / m3 15 10 5 0 1 2 3 4 5 RM CEMS #5 6 7 8 CEMS #2 CEMS #6 9 10 11 CEMS #4 Xray MS 12 Selected Phase III – Initial Runs Run RM RM dup 1 2 1.36 5.34 1.26 3.05 1.2 2.9 1.6 2.3 1.0 2.4 1.08 2.75 4 6 8 11 1.50 6.91 14.27 3.33 1.50 4.22 1.5 4.4 10.1 3.2 1.4 4.7 13.4 3.2 1.5 3.8 11.8 3.1 1.38 4.39 19.00 3.37 3.36 CEMS #6 CEMS #2 CEMS #4 CEMS #5 3.4 1.1 Xray MS Phase III - Final 20 ug m3 15 10 5 0 1 2 3 4 5 6 7 RM 8 9 10 11 12 Phase III - Final 20 ug /m3 15 10 5 0 1 2 3 4 5 RM CEMS #5 6 7 8 CEMS #2 CEMS #6 9 10 11 CEMS #4 Xray MS 12 DRAFT Phase IV - Initial 20 ug / m3 15 10 5 0 1 2 RM 1 avg 3 RM 2 avg DRAFT Phase IV – Initial and Proposed MACT Limit 20 ug / m3 15 10 5 0 1 RM 1 avg CEMS #6 avg 2 RM 2 avg 10% Limit 3 CEMS #4 avg DRAFT Phase IV – Initial and Proposed MACT Limit (Rescaled) 0.4 ug / m3 0.3 0.2 0.1 0 1 RM 1 avg CEMS #6 avg 2 RM 2 avg 10% Limit 3 CEMS #4 avg DRAFT Phase IV - Final 20 ug / m3 15 10 5 0 1 2 RM 1 avg 3 RM 2 avg DRAFT Phase IV – Final and Proposed MACT Limit 19 ug / m3 14 9 4 -1 1 RM 1 avg CEMS #6 avg 2 RM 2 avg 10% Limit 3 CEMS #4 avg DRAFT Phase IV – Final and Proposed MACT Limit (Rescaled) 0.4 ug / m3 0.3 0.2 0.1 0 -0.1 1 2 3 -0.2 RM 1 avg CEMS #6 avg RM 2 avg 10% Limit CEMS #4 avg Findings • No sample loss in 200 feet of line • Monitors improving between Phases • Monitors can meet RA requirements of draft PS-12, but low-level correction needed Findings (continued) • Dual train reference method testing is important • Monitors can operate for up to 3 months with routine maintenance Products • Monitoring operational characteristics and costs • Data for GPRA report on Mercury CEMS and coal combustion • Proposed PS 12A – Covers only vapor phase (no particulates) – Designed for fossil fuel fired boiler exhaust – Allows use of existing equipment Products (continued) • Proposed PS 12A (continued) – Requires at least 9 paired sets of 2 hour (minimum) runs – Allows up to 3 sets to be rejected – Specifies results to be within 20% of reference method or 10% of MACT limit – Identifies outliers as • RSD > 10% if mercury > 1 μg / m3 or • RSD > 20% if mercury 1 μg / m3 Products (continued) • Proposed PS 12A (continued) – Requires measurement error test using NIST traceable Hg0 and HgCl2 at zero, mid, and high levels • Calibration standards from NIST – Certified elemental mercury in cylinders • 2, 5, and 20 micrograms per cubic meter – Ionic mercury to follow (1/06) Concurrent Activities • Assist R2 and NJ with PSEG’s NSR settlement • Monitor and assist State rulemakings • Coordinate with ETV mercury CEMS Phase III Next Steps • Respond to proposal comments • Potential additional testing – Longer term subbituminous and bituminous coals with cold side ESP