Caledonia Air Quality Index (AQI)

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Caledonia, Wisconsin, nestled in Racine County, presents a unique geographic setting influencing its air quality. Located at 42.7986° N, -87.8762° W, the city occupies a gently rolling terrain characteristic of the glacial landscape of southeastern Wisconsin. Its elevation, averaging around 800 feet above sea level, contributes to localized weather patterns. Caledonia’s proximity to Lake Michigan, approximately five miles east, introduces lake-effect phenomena, impacting temperature and humidity, and potentially influencing pollutant dispersion. The surrounding landscape is a mix of agricultural land – primarily corn and soybean fields – and increasingly, suburban development. To the north and west lie more extensive agricultural zones, while to the south, the urban corridor of Racine and Kenosha extends. This urban-rural gradient creates complex air quality dynamics. While rural areas contribute agricultural emissions (ammonia, particulate matter from tilling), the expanding suburban sprawl increases vehicle traffic and associated pollutants. The region historically benefited from manufacturing in Racine, but shifts in industry have altered emission sources. Caledonia itself is largely residential, but its position within the broader Racine-Kenosha metropolitan area means it’s susceptible to regional pollution transport. The prevailing winds, generally from the southwest, can carry pollutants from these more industrialized areas, impacting local air quality.

Caledonia’s air quality follows a distinct seasonal pattern. Spring (March-May) often sees elevated particulate matter from agricultural activities – tilling and planting – combined with pollen. Warm temperatures and increasing sunlight can also promote ground-level ozone formation, particularly on stagnant days. Summer (June-August) typically experiences the best air quality, with prevailing winds dispersing pollutants and rainfall acting as a natural scrubber. However, ozone levels can still peak during heat waves. Autumn (September-November) brings a return of stagnant air masses and potential temperature inversions, trapping pollutants near the ground. Wood burning for heating begins, contributing to particulate matter. November can be particularly challenging. Winter (December-February) is generally characterized by colder temperatures and reduced sunlight, limiting ozone formation. However, increased reliance on heating fuels – wood, oil, and natural gas – elevates particulate matter and carbon monoxide. Snow cover can also enhance temperature inversions. Sensitive groups – children, the elderly, and those with respiratory conditions – should limit strenuous outdoor activity during spring ozone events and winter periods of high particulate matter. Months to favour for outdoor activity are generally June through August, but always check local conditions.