mercury monitoring

Post on 31-Dec-2015

28 Views

Category:

Documents

0 Downloads

Preview:

Click to see full reader

DESCRIPTION

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. - PowerPoint PPT Presentation

TRANSCRIPT

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

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11

ug

/ m

3

RM

Phase I - Initial

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11

ug

/ m

3

RM CEMS #1

Phase I – Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15

ug

/ m

3

RM

Phase I - Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15

ug

/ m

3

RM Wet CEMS CEMS #2

Phase II - Initial

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM

Phase II - Initial

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM Wet CEMS CEMS #2 CEMS #3

Phase II - Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM

Phase II - Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM Wet CEMS CEMS #2

CEMS #3 CEMS #4 CEMS #5

Xray CEMS

Phase III - Pilot Scale

0

5

10

15

20

1 3 5 7 9 11 13 15 17

ug

/ m

3

RM avg

Phase III - Pilot Scale

0

5

10

15

20

1 3 5 7 9 11 13 15 17

ug

/ m

3

RM avg Wet CEMS CEMS #6 CEMS #4

Phase III - Initial

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM

Phase III - Initial

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/ m

3

RM CEMS #2 CEMS #4

CEMS #5 CEMS #6 Xray MS

Selected Phase III – Initial Runs

Run

RM

RM dup

CEMS #6

CEMS #2

CEMS #4

CEMS #5

Xray MS

1 1.36 1.26 1.2 1.6 1.0 1.08

2 5.34 3.05 2.9 2.3 2.4 2.75

4 1.50 1.50 1.5 1.4 1.5 1.38

6 6.91 4.22 4.4 4.7 3.8 4.39

8 14.27 10.1 13.4 11.8 3.4 19.00

11 3.33 3.36 3.2 3.2 3.1 1.1 3.37

Phase III - Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

m3

RM

Phase III - Final

0

5

10

15

20

1 2 3 4 5 6 7 8 9 10 11 12

ug

/m

3

RM CEMS #2 CEMS #4

CEMS #5 CEMS #6 Xray MS

DRAFT Phase IV - Initial

0

5

10

15

20

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg

DRAFT Phase IV – Initial and Proposed MACT Limit

0

5

10

15

20

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg CEMS #4 avg

CEMS #6 avg 10% Limit

DRAFT Phase IV – Initial and Proposed MACT Limit (Rescaled)

0

0.1

0.2

0.3

0.4

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg CEMS #4 avg

CEMS #6 avg 10% Limit

DRAFT Phase IV - Final

0

5

10

15

20

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg

DRAFT Phase IV – Final and Proposed MACT Limit

-1

4

9

14

19

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg CEMS #4 avg

CEMS #6 avg 10% Limit

DRAFT Phase IV – Final and Proposed MACT Limit (Rescaled)

-0.2

-0.1

0

0.1

0.2

0.3

0.4

1 2 3

ug

/ m

3

RM 1 avg RM 2 avg CEMS #4 avg

CEMS #6 avg 10% Limit

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

top related