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Published byMiles Fisher Modified over 9 years ago
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A&WMA Southern Section Annual Meeting Biloxi, MS September 12, 2012 Carla Brown, P.E. MS Dept. of Environmental Quality 601-961-5235 cbrown@deq.ms.gov
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PollutantAveraging Period CurrentPreviousDate of Final Rule* PM-10Annual---50 ug/m 3 July 1, 1987 24-hr150 ug/m 3 July 1, 1987 PM-2.5---July 18, 1997 65 ug/m 3 October 17, 2006 NO 2 Annual53 ppb April 30, 1971 ---February 9, 2010 SO 2 Annual---30 ppbApril 30, 1971 24-hr---140 ppbApril 30, 1971 3-hr500 ppb April 30, 1971 ---August 23, 2010 *Final Rule that established the most current standard, excluding those rules revoking previous standards.
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The background concentrations must be added to modeled concentrations to determine compliance with NAAQS. MS Ambient Air Data: Annual PM-2.5 (2009-2011): 9.5-11.8 ug/m 3 24-hr PM-2.5 (2009-2011): 18-23 ug/m 3 1-hr NO 2 (2011, only one site): 32 ppb 1-hr SO 2 (2011, only one site): 29 ppb Problem – very limited monitor data and background can result in double-counting emissions from stationary sources that are also being included as nearby sources in the model.
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Roxul, a proposed mineral wool facility, was MDEQ’s first PSD processed under these significant NAAQS changes. Proposed emissions from Roxul: PM-10/PM-2.5 = 562/510 TPY SO 2 = 1035 TPY NO x = 403 TPY Modeling initially predicted… 35 violations of 1-hr SO 2 One violation of 24-hr SO 2 61,446 violations of 1-hr NO 2
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Significant NOx contributions from natural gas compressor station engines: Trunkline Compressor Station – 5,500 TPY PTE ANR Sardis Compressor Station – 2,900 TPY PTE Tennessee Gas, New Albany Compressor Station – 1,900 TPY PTE For those receptors showing violations after applying the 0.8 NO 2 :NOx default ratio (still 34,475 instances), the highest contribution from Roxul was determined to be less than 30% of SIL. Per 40 CFR 51.165(b), if less than the SIL, source/project does not cause or contribute to the violation.
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For PSD projects, months added to application preparation. MDEQ has suggested submitting applications piece-meal so as not to delay the permitting process. Time and $$$ due to refining modeling runs to meet the standards or to show no culpability should there be modeled violations.
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How does the State address modeled violations due to existing sources? Based on decisions from the Sixth Circuit Court (1978-80), modeled violations are considered just as valid as measured violations. Require those significant sources to perform air quality analysis? Include limitations in SIP or enforceable operating permit? Install monitor(s) in area of highest predicted impacts (at whose expense?)
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Based upon current modeling protocols, modeled concentrations will generally be much greater than monitored. EPA acknowledged this in March 1, 2011, guidance memo regarding the 1-hr NO 2 standard. Yet EPA had planned to require state-wide modeling to demonstrate compliance with the 1-hr SO 2 standard (generally due to lack of monitors for SO 2 ).
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