11/8/2016 1
RULE 1147 TASK FORCE MEETING
November 8, 2016
Purpose
Discuss third party review and
findings for SCAQMD’s Draft Rule 1147 Technology Assessment For Small and Low Emission Sources
Provide Preliminary Schedule for
Purpose Discuss third party review and findings for SCAQMDs Draft - - PDF document
11/8/2016 RULE 1147 TASK FORCE MEETING November 8, 2016 Purpose Discuss third party review and findings for SCAQMDs Draft Rule 1147 Technology Assessment For Small and Low Emission Sources Provide Preliminary Schedule for Future
Discuss third party review and
Provide Preliminary Schedule for
September 2010 Rule Amendment
EO Commitment to 3rd Party Review
Technical Feasibility
The smallest low NOx burners available for low temperature sources are
400,000 to 500,000 Btu/hour
Retrofitting heated process tanks that do not comply with the NOx limit
requires replacement of the whole system
A 30 ppm emission limit for the primary chamber of multi-chamber
incinerators, burn-off ovens, burn-out furnaces and incinerators is not possible with the available burners Cost Effectiveness
Replacing heating systems on existing in-use spray booths to meet the
NOx emission limit may result in a cost effectiveness higher than SCAQMD criteria used in other programs (e.g., minor source BACT criteria of $27,000/ton)
Retrofitting units with daily emissions of 1 pound/day or less to meet the
NOx limit may result in a cost effectiveness higher than SCAQMD criteria used in other programs
1. Exempt sources with total rated heat input less than 325,000 Btu per hour from the Rule 1147 NOx emission limit. 2. Change the NOx emission limit from 30 ppm to 60 ppm NOx for the primary chamber for all burn-off ovens, burnout furnaces and incinerators. 3. Delay compliance for existing in-use heated process tanks, evaporators and parts washers from the NOx emission limit until the combustion system or tank is modified, replaced or relocated. 4. Delay compliance with the NOx emission limit for existing in-use spray booths until the heating system is modified or replaced or the unit is relocated. 5. Delay compliance with the NOx emission limit for existing in-use units with actual NOx emissions of one pound per day or less until the combustion system is modified or replaced or the unit is relocated.
Will Delay Compliance for up to 4,900 Small & Low Emission Units: Approximately 3,400 units are spray booths and paint prep-stations used
in manufacturing and auto body repair
Approximately 1,500 units are small ovens and dryers, furnaces, kilns and
VOC/PM emission control equipment such as afterburners
The Remaining Units Include: Approximately 750 units from about 20 - 50 years old which were required
to demonstrate compliance with NOx emission limits by 2015
Approximately 750 units with compliant burners permitted since 2000
which must demonstrate compliance over the next 15 years (~ 50/year)
Many units have demonstrated compliance because permit required testing Remaining units will require testing to demonstrate compliance with NOx limits
Draft Technology Assessment Released for Public Review RFP Released For Independent Review of Draft Technology Assessment Draft Technology Assessment Received at Governing Board Meeting ETS Selected by Proposal Review Panel Including SCAQMD, VCAPCD, Furnace Dynamics & S.C. Small Business Alliance ETS Begins Review of Draft Technology Assessment ETS Meets with Stakeholders at Rule 1147 Task Force Meeting ETS Completes Review of Draft Technology Assessment and Stakeholders Comments Rule 1147 Task Force Meeting to Discuss ETS Findings and Suggestions Jan 29, 2016 Feb 5, 2016 Mar 4, 2016 May 31, 2016 June 29, 2016 Aug 3, 2016 Oct 26, 2016 Nov 8, 2016
SCAQMD Draft Technology Assessment: Availability of Technology for Low Temperature Operations Including
Ovens and Dryers
Availability of Technology for High Temperature Operations Including
Furnaces, Kilns and Afterburners
Availability of Technology for Individual Categories of Equipment
Including Heated Spray Booths
Cost Effectiveness Methodology Cost Effectiveness Analysis for Small and Low Emission Sources SCAQMD Recommendations Comments Received at August 3, 2016 Task Force Meeting Comments Received after August 3, 2016 Task Force Meeting
EPA Documents on Emissions, Technology and Assessing Cost Burner Manufacturers SCAQMD Permits Source Test Results Submitted to SCAQMD for Rule 1147 and
Other Programs (summarized in the Draft Technology Assessment)
Discussion at August 3, 2016 Rule 1147 Task Force Meeting with
Stakeholders and SCAQMD Staff
Oral and Written Information Provided to ETS by 1 Stakeholder
at the Conclusion of August Task Force Meeting
Oral and Written Information Provided to ETS by 3 Stakeholders
during August through October 2016
Topics Discussed During and After the August 3, 2016 Task Force Meeting
Rule enforcement, change of ownership, and potential future rule amendment
General comment on applicability of potential to emit (PTE) used for New Source Review
Comments specific to heated tanks and spray washers
4 Written Items at the August 3rd Task Force Meeting from Anthony Endres of FDI
1 discussion of PTE versus of emissions based on operation and 2 examples using smokehouse oven and afterburner previously discussed in Draft Technology Assessment
1 item to SCAQMD dated 2/18/16 on Draft Technology Assessment with questions and comments on rule compliance, PTE, cost effectiveness calculations, and burner types
11 Written Items Received After the August 3rd Task Force Meeting
4 Items received from Anthony Endres of FDI about several retrofits at 1 company, PTE and cost effectiveness and 1 item suggesting BACT and emission limits for furnaces should be individual determinations because each furnace is unique
5 Items received from Jim Waggoner of Industrial Process Equipment on heated tanks, other immersion tube heating applications and burners
1 Item received from Allan Roughton of Wirth Gas Equipment on heated tanks, spray washers and immersion tube heating application burners
Rule Compliance and Issues Outside the Scope of the
Information Supporting the Recommendations of the
Use of Potential to Emit (PTE) for Estimating Emissions,
The Technology Assessment does not use PTE The Technology Assessment uses estimates of average or ranges of
emissions and reductions for the sources evaluated
Average and ranges of emissions are appropriate and necessary
for estimating emission reductions for agency rule development
The Technology Assessment Should Evaluate the Cost to Retrofit Existing Equipment
The Technology Assessment analyzes the cost and cost effectiveness of
retrofitting existing units
The Technology Assessment Should be Consistent With SCAQMD BACT Guidelines
The Technology Assessment is consistent with SCAQMD BACT Guidelines but
Includes equipment useful life in the analysis
Compliance and Maintenance Costs Should be Included In the Cost Effectiveness
It is appropriate to exclude Rule Compliance costs in equipment cost
effectiveness analysis. This is consistent with the SCAQMD BACT Guidelines.
There is insufficient documentation of the maintenance costs proposed by the
commenter
i.e., Burner can replacements may be due to a variety of issues including selection of a
can that is not appropriate for the unit or use of a constant pilot
Examples of Cost Effectiveness Calculations for a Smokehouse and Afterburner
These specific examples were evaluated and addressed in the Technology
Assessment
The Technology Assessment recommendations would exempt those units from
retrofit
An Individual Cost Effectiveness Should be Calculated for Each Unit and a Cost Effectiveness Value That Should Not be Exceeded
This comment concerns SCAQMD policy and not specific to the review, however: The SCAQMD has used a range of cost effectiveness criteria in its programs The Technology Assessment uses average and ranges of emissions The Technology Assessment uses the high end of the range of costs The Technology Assessment uses a screening criteria of $27,000 per ton consistent with
SCAQMD BACT
The SCAQMD Should Use a Cost Effectiveness Criteria of $30,000 per ton
The SCAQMD used a screening criteria of $27,000 per ton
Some Low NOx Burners Have Limited Turndown and are Less Efficient
The burner cited by the commenter is the one of the most used burners The comments on efficiency are not supported by enough information to evaluate
the comment
Information on Units with Large Burners or With Emissions Exceeding 1 Pound/Day
Large units are outside the scope of the Technology Assessment Review
Information Provided on Retrofits at Facilities
Information on some of the units were incomplete or did not have sufficient detail
to evaluate emissions or cost of burner replacement
When sufficient information was available to evaluate the emissions and cost, the
cost effectiveness was in the range used in the Technology Assessment
Comments on Previous Rule Development
Comments on rule development for 2008 and 2011 are noted
Heated Tanks and Spray Washers Cannot
The Technology Assessment has proposed to
Technology is available for new units to comply
Some of the comments and information provided
Availability of Technology to Achieve Rule Emission Limits
Low Temperature Processes – Technology is Available Except for Burners Rated
Less Than 400,000 Btu/hour
High Temperature Processes – Technology is Available for All Sizes of Burners Heated Spray Booths – Technology is Available for Small and Large Booths
Agree with Staff Proposal to Amend Rule to Address the Following Technical Concerns:
The smallest low NOx burners available for low temperature processes are
400,000 to 500,000 Btu/hour
Retrofitting heated process tanks that do not comply with the NOx limit requires
replacement of the whole system
A 30 ppm emission limit for the primary chamber of multi-chamber incinerators,
burn-off ovens, burn-out furnaces and incinerators is not possible with the preferred burners
Additional recommendation to that of staff’s:
Recommend to Change NOx Emission Limit for Afterburner Processes
Operating at Temperatures Less Than 800° F to 60 ppm (Staff Agrees)
Agree with Cost Effectiveness Method Used by SCAQMD Staff Consistent with EPA Method Used by Other Agencies Consistent with Method Used for Rule Development and Other
District Programs
Costs Used for Analysis are Representative of Costs for
Equipment and Installation of Burner Systems
Agree with Staff Proposal to Amend Rule to Address the
Following Concerns
Replacing Heating Systems on Existing in-use Spray Booths May
Result in a Cost Effectiveness Higher Than SCAQMD Criteria Used in Other Programs
Retrofitting Units With Daily Emissions of Less Than 1 pound/day
May Result in a Cost Effectiveness Higher Than SCAQMD Criteria Used in Other Programs
Present ETS Findings to SSC November
Revise Draft Technology Assessment for
Initiate Rule Development – December 2016 Continue Task Force Meetings Rule Amendment – 2nd Quarter 2017