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GeoInsighter Summer/Fall 2003 Newsletter

New Hampshire Adjusts Criteria for Calculation of "Air Toxic" Emissions

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New Hampshire (NH) regulates the discharge to air of a substantial number of compounds under rules codified at NH Administrative Rule Env-A 1400, Regulated Toxic Air Pollutants. The list of regulated toxic air pollutants (RTAPs) includes the 189 “hazardous air pollutants” designated by the United States Environmental Protection Agency under the Clean Air Act Amendments of 1990 and some 750 additional compounds for which the American Conference of Governmental Industrial Hygienists has established a threshold limit value (TLV). Collectively, these compounds are those that NH considers to pose a potential health-based risk to the human population and to be in common usage by business and industry. Because of the number and type of compounds regulated under the rule, many businesses will find that they use and emit listed compounds.

Within the context of NH’s statewide permit system for air emissions, business and industry that emit RTAPs above certain thresholds, or in amounts resulting in an exceedance of ambient air limits (AALs) established by the State, are required to obtain a State permit that limits or controls the RTAP emission. Facilities that emit RTAPs, but below applicable thresholds, must maintain and update annual documentation demonstrating compliance with the Env-A 1400 rule. To determine if a permit is required, or to demonstrate compliance, the rule establishes a three tiered test methodology, including a de minimus emission method, an in-stack concentration method, and air dispersion modeling. Generally, the de minimus method, which requires the least data gathering, is evaluated first. For emissions that do not pass the de minimus evaluation, the in-stack method is used to calculate an emission concentration that is compared to AALs to determine compliance. In the last instance, air dispersion modeling, which is more complex and consequently more costly (although the State will perform modeling upon request), may be used to demonstrate compliance with the AALs.

Recent rule changes to the method used in calculating the in-stack concentration have resulted in a relaxation of the applicability of the State permit system to many facilities. In comparison of the calculated in-stack concentration to the AAL, an “adjustment” factor is used, dividing the in stack concentration prior to comparison to the AAL. Prior to April 11, 2003, the adjustment factor was 100. The rule change “adjusts” the “adjustment” factor to 400, effectively increasing the allowable RTAP emission under the in-stack concentration method. Facilities should be aware of the change in their permit evaluation or compliance demonstration efforts.

Christopher M. Rawnsley
cmrawnsley@geoinc.com

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