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EPA 2003 Blind Audit of Protocol Gases. John Schakenbach, USEPA, CAMD Scott Shanklin, Cadmus Group Bob Wright, USEPA, ORD EPRI CEM User Group Milwaukee, WI May 4-6, 2004. What is the Problem?. Historically, blind audits of calibration gases have shown poor quality initially
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EPA 2003 Blind Audit of Protocol Gases John Schakenbach, USEPA, CAMD Scott Shanklin, Cadmus Group Bob Wright, USEPA, ORD EPRI CEM User Group Milwaukee, WI May 4-6, 2004
What is the Problem? • Historically, blind audits of calibration gases have shown poor quality initially • SO2 RATA using plant’s incorrect cal gas (low by 15%). Source could underreport SO2 by 15% and be undetected for at least 6 months.
Other Reasons Why Accurate Cal Gas is Important • Only daily assurance CEM is really working • Reference Method analyzers need accurate calibration gases to produce accurate RATA results
Purpose of Blind Audits • Help vendors improve gas quality • Help sources identify good vendors
History • 1970’s -1996 EPA audited gases • Posted results • In 1995, one vendor off by -16.3% (CEM would underreport) • Strong utility and vendor support • Auditing strongly correlated with improved gas quality
Current Gas Analysis • First audit in 7 years • Blind audit • 14 national gas vendors • Similar procedures as in past • SRMs and NTRMs used • 42 Protocol tri-blend cylinders • MACTEC (UV and NDIR) and Spectral Insights (FTIR)
Instrumentation • NO - API Model 200AH chemiluminescence • NO - AMETEK Model 922M differential absorption UV • SO2 - Bovar Model 721M differential absorption UV • CO2 - California Analytical Model 3300A NDIR • NO, SO2 and CO2 - Nicolet Nexus Model 760 FTIR • Environics (Graseby-Nutech) Series 3740 gas dilution system
Gas Manifold/Regulator Vent Vent Vacuum Pump Manifold Vent Valve Toggle Valves Selector Valve Check Valves Vent Isolation Valves Transducers P T Cell Computer FTIR Spectrometer Candidate, Zero, SRM or NTRM Gas Standards Spectral Insights Assay Apparatus
Accuracy Criterion • Part 75, Appendix A, sec 5.1.4 requires 2.0% of tag value • Protocol procedures achieve +2% of tag value: 1% Standard Reference Material plus 1% EPA Protocol methodology
Problems • CO2 quenching biased the NO concs from chemiluminescent analyzer low • Chemiluminescent NO concs thrown out • Measurements repeated with a UV analyzer • UV analyzer was set up for 0 - 500 ppm NO, but should have been for 0-1000 ppm • Threw out high level NO concs • Repeated high level NO measurements using FTIR
Problems • SO2 interfered with UV analyzer NO readings • Injected SO2 in N2 to develop a correction • Ran out of high level CO2 SRM for FTIR • Threw out the high level CO2 FTIR results and relied on NDIR
Results • EPA presents the following information without assigning a rating to the gas vendors. • If EPA’s and vendor’s values differ by 2.0% or less, then because of uncertainties in the measurement system, statistically, there is no difference between the two values, e.g., a difference of 2.0% and 0.5% are considered equal. • All vendors that failed are re-analyzing their gas cylinders. When EPA receives the re-analyzed results, they will be posted.
Results • Overall failure rate: 14 of 126 analyses (11%) • 57% of vendors failed • SO2: Worst tag value ~2.5% high • NO: Worst tag value ~8% low • CO2: Worst tag value ~4.9% high • All 42 cylinders met the Protocol Procedure documentation requirements
NO Analyses SO2 Analyses CO2 Analyses UV FTIR Both UV FTIR Both NDIR FTIR Both Low 6/14 4/14 4/14 6/14 1/14 1/14 1/14 1/14 1/14 Mid 2/14 3/14 2/14 0/14 0/14 0/14 0/14 1/14 0/14 High - - - 3/14 - - - 0/14 3/14 0/14 3/14 - - - - - - EPA Protocol Gases not meeting Acceptance Criterion
Lessons Learned • Detailed standard operating procedures for analyzing single and multicomponent mixtures are needed in EPA’s Protocol Procedures, especially for FTIR • First ensure lab can correctly analyze single component cylinders • Then check for interferences by measuring a multicomponent cylinder simultaneously with analyzers for each component gas • Use an SRM or NTRM to get reference spectrum for FTIR measurements
Audits Can Be Effective 1992 1993 1994 1995 1996 2003
Audit Program Issues • Scope • Stringency • Structure
Options - Scope • Part 75 only • All source-level programs, e.g., Part 75, NSPS, SIP, NSR • All source and ambient-level programs
Options - Stringency • Work with vendors to fix problems • Work with vendors and post audit results on web sites • Formal gas vendor certification program
Options - Structure • Spin-off to 3rd party (A2LA, NVLAP, NSF, etc.) to purchase and analyze cylinders (set up fee-based system) with EPA oversight • Through EPA task order, contractor purchases and analyzes cylinders from major suppliers (EPA used to do this) • Other (NELAC, gas vendor-developed mechanism, NIST, EPA lab, etc.)
Initial Recommendations Scope All source and ambient-level programs Stringency Work with vendors; post audit results Structure Set up fee-based system to purchase and analyze cylinders using 3rd party with EPA oversight; or possibly use gas vendor-developed mechanism
Example 3rd Parties for Spin Off • American Association for Laboratory Accreditation (A2LA) • National Voluntary Laboratory Accreditation Program (NVLAP) • National Sanitation Foundation (NSF)
Next Steps • Get more feedback from gas vendors and other interested parties
For a Copy of Presentation www.epa.gov/airmarkets, click on “Recent Additions” near top left corner or John Schakenbach Phone: 202-343-9158 schakenbach.john@epa.gov