- Ozone (O3, ground-level)
- Particle Pollution (Particulate Matter, PM)
- Carbon Monoxide (CO)
- Nitrogen Dioxide (NO2)
- Sulfur Dioxide (SO2)
- Lead (Pb)
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Properties Sources Effects Description |
Particle Pollution (Particulate Matter, PM) Properties Sources Effects Description |
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Properties Sources Effects Description Higher levels of CO occur in more urbanized areas, such as Nashua and Manchester, where there are more cars, trucks and other sources and there is a potential for heavy, congested motor vehicle traffic. Areas recording the highest CO levels are ordinarily localized since they are usually associated with roadway intersections. Because carbon monoxide concentrations vary considerably over short distances, areas with relatively higher CO levels are called "hot spots." Hot spot locations include areas with high traffic volumes and congestion, usually caused by traffic signals in an area surrounded or enclosed by buildings. The buildings create a "canyon effect" entrapping carbon monoxide in a confined space. Since carbon monoxide is heavier than air it tends to remain at ground level. The close proximity of buildings does not allow the pollutant to disperse, creating the potential for higher levels of CO in areas occupied by pedestrians and motorists. There is also a significant seasonal variation in CO emissions and ambient air concentrations with peaks occurring during the winter months because cold engines typically run at a lower air to fuel ratio and the catalytic converter must reach firing temperature before it operates efficiently. In addition, during the winter, concentrations of CO often build up to high levels due to more frequent temperature inversions which trap pollutants. The Cities of Manchester and Nashua had been designated nonattainment for CO since the 1970s due to violations of the federal CO standard. Levels of CO have improved significantly since the 1980s in Manchester and Nashua due to federal tailpipe standards for new automobiles and traffic flow improvements in the two cities. In addition, there was a required annual emissions inspection program for most motor vehicles from 1986 to 1994 in the Nashua area (Nashua and 11 surrounding communities). As a result of these efforts, New Hampshire has been in attainment of the National Ambient Air Quality Standard for CO since the mid-1990s and CO trends continue to indicate an improvement in air quality. |
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Properties Sources Effects Description One component of NOX that is considered a direct health risk is NO2, which is the actual NOX related pollutant with an assigned National Ambient Air Quality Standard (NAAQS). It can cause respiratory illness and lung damage. High levels can cause edema, and prolonged high exposure can produce fatal lung damage. NOX is a primary component to ozone (or smog) formation. Ozone forms when NOX and certain volatile organic compounds chemically react in the presence of strong sunlight (ultraviolet wavelengths). An oxygen atom is moved from NO2 to oxygen in the air, creating ozone (O3) – another criteria pollutant. Reducing emissions of NOX is critical to reducing ozone. NOX is also a major contributor to acid rain (or acid deposition). After NOX is released by a source, it travels and chemically reacts in the atmosphere, eventually becoming ammonium nitrate or nitric acid. Ammonium nitrate is a small particle (PM2.5, which is considered to be another criteria pollutant with its own NAAQS), and it also is a visibility-impairing pollutant. Nitric acid is removed from the air through precipitation (rain, snow, etc.), settling of particles, and by condensation from the air onto surfaces, similar to the formation of dew. Acid deposition damages our forests, lakes, and wetlands by robbing them of necessary nutrients and lowering the pH levels, often to levels below what native species can tolerate. The end result of this process is not a void of wildlife, but rather a shifting of species, where a more tolerant species simply populates an area where native species once were dominant. Nitric acid accounts for about one-third of the acidity in precipitation in New Hampshire. Another effect of NOX is the nitrification of lakes, ponds, estuaries, and other wetlands. Nitrogen acts as a fertilizer for plants, and when it is added to water, algae and other aquatic plants may multiply excessively, displacing other inhabitants of the wetland. While NOX emission controls have been added to power plants and automobiles (catalytic converters), growth in energy demand and the amount of vehicle-miles-traveled have offset some of the benefits of the control measures. In New Hampshire, measured NO2 levels have remained relatively stable over the last 20 years, and have shown a slight overall decline. New Hampshire is in attainment of the NO2 NAAQS on a state-wide basis. |
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Properties Sources Effects Description With increasing distance from the source, atmospheric chemistry converts SO2 into various related compounds including ammonium sulfate and sulfuric acid. Ammonium sulfate is a small particle (PM2.5, another criteria pollutant with specific health effects), and it is the leading visibility-impairing pollutant throughout the Northeast. Sulfuric acid, originating from SO2, accounts for about two-thirds of the acidity of the acid deposition (rain, snow, fog) in New Hampshire. Acid deposition strips nutrients from soils, weakening vegetation, and it acidifies water bodies, affecting the wildlife that depends on that water. SO2 reductions are considered critical in programs to reduce acid rain and improve visibility. Following recorded violations of the National Ambient Air Quality Standard in the late 1970s, which were related to the former pulp and paper industry in the Berlin area, sulfur dioxide levels have improved. New Hampshire is currently in attainment for sulfur dioxide and has had no violations of the standard since the early 1980s. |
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Properties Sources Effects Description Unhealthful levels of atmospheric lead are very uncommon since the federal requirement of removing lead as a gasoline additive in the early 1980s. Today’s fuels contain only trace amounts of lead, thus significantly reducing airborne lead. All other sources of lead air pollution are only of local significance and are not a measurable problem in New Hampshire. In 2008, EPA began the process of reviewing and adjusting the National Ambient Air Quality Standard for lead. The result of this process has been a significant reduction to the NAAQS. New Hampshire is still expected to be in attainment of the revised lead standard once designations are completed. |


