Impacts of noise barriers on near-road air quality

Abstract Numerous health studies conducted worldwide suggest an increase in the occurrence of adverse health effects for populations living, working, or going to school near large roadways. A study was designed to assess traffic emission impacts on air quality near a heavily traveled highway. The portion of highway studied included a section of open field and a section with a noise barrier adjacent to the road. In addition, the section containing the noise barrier included a portion with vegetation in the vicinity of the barrier. Thus, this field study provided an opportunity to evaluate near-road air quality with no barriers, with a noise barrier only, and with a noise barrier and vegetation adjacent to the road. Pollutants measured under these scenarios included carbon monoxide (CO) and particulate matter (PM). Measurements showed the effects of a noise barrier on near-road air quality. The presence of this structure often led to pollutant concentration reductions behind the barrier during meteorological conditions with winds directionally from the road. CO and PM number concentrations generally decreased between 15 and 50% behind the barrier. However, conditions occurred when pollutant concentrations were greater behind the barrier than when no barrier was present. These results imply that the presence of a noise barrier can lead to higher pollutant concentrations on the road during certain wind conditions. In addition, the study results suggested that the presence of mature trees in addition to the barrier further lowered PM number concentrations.

[1]  D. Hall,et al.  Economics of ecosystems management , 1985, Tasks for vegetation science.

[2]  Gail Taylor,et al.  Effective Tree Species for Local Airquality Management , 2000, Arboriculture & Urban Forestry.

[3]  G. H. Heichel,et al.  Roadside Coniferous Windbreaks as Sinks For Vehicular Lead Emissions , 1976 .

[4]  Maughan,et al.  The influence of wooded shelterbelts on the deposition of copper, lead and zinc at Shakerley Mere, Cheshire, England , 1999, The Science of the total environment.

[5]  D. Munch,et al.  Concentration profiles of arsenic, cadmium, chromium, copper, lead, mercury, nickel, zinc, vanadium and polynuclear aromatic hydrocarbons (PAH) in forest soil beside an urban road , 1993 .

[6]  Vlad Isakov,et al.  Traffic and Meteorological Impacts on Near-Road Air Quality: Summary of Methods and Trends from the Raleigh Near-Road Study , 2008, Journal of the Air & Waste Management Association.

[7]  C. Stanier,et al.  An Algorithm for Combining Electrical Mobility and Aerodynamic Size Distributions Data when Measuring Ambient Aerosol Special Issue of Aerosol Science and Technology on Findings from the Fine Particulate Matter Supersites Program , 2004 .

[8]  J Kirby Lidman EFFECT OF A NOISE WALL ON SNOW ACCUMULATION AND AIR QUALITY , 1985 .

[9]  N. Lepp,et al.  ROADSIDE VEGETATION: AN EFFICIENT BARRIER TO THE LATERAL SPREAD OF ATMOSPHERIC LEAD? , 1977 .

[10]  Werner Brilon,et al.  Wind tunnel experiments on micro-scale dispersion of exhausts from motorways , 1993 .

[11]  Yilin Ma,et al.  An on-line instrument for mobile measurements of the spatial variability of hexavalent and trivalent chromium in urban air , 2006 .

[12]  F. Bussotti,et al.  Preliminary studies on the ability of plant barriers to capture lead and cadmium of vehicular origin , 1995 .

[13]  Richard C. Flagan,et al.  Scanning Electrical Mobility Spectrometer , 1989 .

[14]  Vlad Isakov,et al.  The effects of roadside structures on the transport and dispersion of ultrafine particles from highways , 2007 .