Adoption of best practices for the environmental management of road salt in Ontario M. Stone and J. Marsalek ABSTRACT There are increasing concerns regarding the adverse environmental impacts of chloride from road salts. A web-based survey was conducted to determine how the Code of Practice for the environmental management of road salts has inuenced the adoption of best practices in Ontario, Canada. The majority of large Ontario municipalities have salt management plans that adequately address safety and the environment. Most municipalities train a high percentage of permanent staff but only half of seasonal workers and 21% of private contractors are trained. Most training programs cover key learning goals dened by the Code of Practice. There is little improvement in the management of salt-vulnerable areas. Many existing snow disposal sites are poorly designed and do not manage snowmelt quality. The Code has strongly contributed to the adoption and improvement of salt management practices in Ontario by helping to standardize practices and advance the rate of implementation of best practices. Barriers to further implementation of the Code include understanding the Code, institutional will, liability, limited technical/nancial resources and public expectation of high service levels. Further benets can be achieved by aggressively promoting the Code and improving education and training programs for the public, private contractors and staff of road authorities. M. Stone (corresponding author) Department of Geography and Environmental Management, University of Waterloo, Waterloo, ON, Canada N2L 3G5 E-mail: mstone@uwaterloo.ca J. Marsalek Aquatic Ecosystem Management Research Branch, Water Science and Technology Directorate, Environment Canada, Burlington, ON, Canada L7R 4A6 Key words | Code of Practice, road salt management, salt management plans, salt-vulnerable areas INTRODUCTION The necessity to keep highways safe and fully operational in cold regions has led to the development of advanced winter road maintenance plans, which include applications of chemical deicers (mainly road salt, sodium chloride) and trac- tion agents (sand and grit). The release of road salts to the environment has been estimated at 18 million tonnes/year in the USA (Corsi et al. ) and 5 million tonnes/year in Canada (Environment Canada and Health Canada ). In addition to annual use, temporal trends in road salt use are also of interest and indicate a continuing growth, driven by increasing population. Historically, increases in salt appli- cations contributed to environmental effects of deicing salts and the rst reports of these effects were reported in the 1970s (Field et al. ; Hanes et al. ). Similar concerns about road salt effects in Canada (Howard & Hayes ; Marsalek ; Rokosh et al. ; Mayer et al. ; Oberts et al. ; Williams et al. ) led to a comprehensive ve-year scientic assessment of the environmental impacts of road salt to provide a state-of-the-art synthesis of scientic literature regarding the effects of road salt on the environment (Environment Canada and Health Canada ). The assess- ment concluded that, under the road management practices prevalent at that time, signicant discharges of chloride from road salt were having adverse impacts on freshwater ecosystems, groundwater quality, drinking water supplies, soil, vegetation, wildlife and urban infrastructure in many regions of Canada. Furthermore, road salt impacts in urban areas were reported to be exacerbated by modern stormwater management or low impact development (LID) practices, including inltration of chloride-laden runoff, use of storage in ponds, constructed wetlands, and oil and grit separators (Marsalek ). 174 © Environment Canada 2011 Water Quality Research Journal of Canada | 46.2 | 2011 doi: 10.2166/wqrjc.2011.105 Downloaded from http://iwaponline.com/wqrj/article-pdf/46/2/174/379772/174.pdf by guest on 25 June 2022