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17.Air <br />a. Stationary Source Emissions — Describe the type, sources, quantities, and compositions <br />of any emissions from stationary sources such as boilers or exhaust stacks. Include any <br />hazardous air pollutants and criteria pollutants. Discuss effects to air quality including <br />any sensitive receptors, human health, or applicable regulatory criteria. Include a <br />discussion of any methods used to assess the project's effect on air quality and the <br />results of that assessment. Identify pollution control equipment and other measures <br />that will be taken to avoid, minimize, or mitigate adverse effects from stationary <br />source emissions. <br />No stationary source air emissions are anticipated; therefore, no mitigation is required. <br />b. Vehicle Emissions — Describe the effect of the project's traffic generation on air <br />emissions. Discuss the project's vehicle -related emissions effect on air quality. Identify <br />measures (e.g., traffic operational improvements, diesel idling minimization plan) that <br />will be taken to minimize or mitigate vehicle -related emissions. <br />Motor vehicles emit a variety of air pollutants including carbon monoxide (CO), <br />hydrocarbons, nitrogen oxides, and particulates. The primary pollutant of concern is CO, <br />which is a byproduct of the combustion process of motor vehicles. CO concentrations are <br />highest where vehicles idle for extended periods of time. For this reason, CO concentrations <br />are generally highest in the vicinity of signalized intersections where vehicles are delayed and <br />emitting CO. Generally, concentrations approaching state air quality standards are found <br />within about 100 feet of a roadway source. Further from the road, the CO in the air is <br />dispersed by the wind such that concentrations rapidly decrease. <br />The Minnesota Department of Transportation (MnDOT) has developed a screening method <br />designed to identify intersections that will not cause a carbon monoxide (CO) impact above <br />state standards. MnDOT has demonstrated that even the 10 highest traffic volume <br />intersections in the Twin Cities do not experience CO impacts. Therefore, intersections with <br />traffic volumes lower than these 10 highest intersections will not cause a CO impact above <br />state standards. MnDOT's screening method demonstrates that intersections with total daily <br />approaching traffic volumes below 82,300 vehicles per day will not have the potential for <br />causing CO air pollution problems. None of the intersections impacted by the project exceed <br />the criteria that would lead to a violation of the air quality standards <br />c. Dust and Odors — Describe sources, characteristics, duration, quantities, and intensity <br />of dust and odors generated during project construction and operation. (Fugitive dust <br />may be discussed under Item 17a). Discuss the effect of dust and odors in the vicinity <br />of the project including nearby sensitive receptors and quality of life. Identify <br />measures that will be taken to minimize or mitigate the effects of dust and odors. <br />The project may generate temporary fugitive dust emissions during construction. These <br />emissions would be controlled by sweeping, watering, or sprinkling, as appropriate or as <br />prevailing weather and soil conditions dictate. Dust emissions are not anticipated during <br />operations as all surfaces will either be impervious or vegetated. <br />The construction and operation of the project are not expected to generate objectionable <br />odors. <br />Haviland Fields EAW 23 July 2023 <br />