Difference between revisions of "Salt"
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==Overview== | |||
Each year, Canadians spend over $1 billion on public and private roads, parking lots and sidewalks (Hossain et al., 2015)<ref>Hossain, S.K., Fu, L. and Lake, R., 2015. Field evaluation of the performance of alternative deicers for winter maintenance of transportation facilities. Canadian Journal of Civil Engineering, 42(7), pp.437-448. https://cdnsciencepub.com/doi/abs/10.1139/cjce-2014-0423</ref>. While the use of salt is essential to ensure public safety, there is a growing concern regarding the large quantities of salt (mainly chloride ions), being released to the environment. | |||
In their 2001 assessment under the Canadian Environmental Protection Act, it was found that high releases of road salts from winter maintenance activities were having an adverse effect on freshwater ecosystems, soil, vegetation, and wildlife (Environment Canada, 2001)<ref>Environment Canada. 2001. PRIORITY SUBSTANCES LIST ASSESSMENT REPORT. Road Salts. Canadian Environmental Protection Act, 1999. Environment Canada and Health Canada. https://www.canada.ca/content/dam/hc-sc/migration/hc-sc/ewh-semt/alt_formats/hecs-sesc/pdf/pubs/contaminants/psl2-lsp2/road_salt_sels_voirie/road_salt_sels_voirie-eng.pdf</ref>. Based on this conclusion, Environment Canada developed its “[[https://publications.gc.ca/collections/collection_2012/ec/En49-31-1-5-eng.pdf Code of Practice the Environmental Management of Road Salts]],” which focuses mainly on municipal and provincial road maintenance. This code, which requires the development of Salt Management Plans for those organizations using more than 500 tonnes of road salt annually, was released by Environment Canada in 2004 (Environment Canada, 2004)<ref>Environment Canada. 2004. Code of practice for the Environmental Management of Road Salts. Canadian Environmental Protection Act, 1999 (CEPA 1999). April 2004. EPS 1/CC/5. https://publications.gc.ca/collections/collection_2012/ec/En49-31-1-5-eng.pdf</ref>. While the uptake of these guidelines has been successful, and many agencies have adopted best practices because of it, it is not generally applicable for companies that apply salt to private roads, parking lots, and roadways; and additional measures are needed to realize reductions in these areas. | |||
There are studies and training programs that address these issues, which aim to educate private contractors about best practices, and how these can improve level of service, protect the environment, and reduce costs. However, uptake of these programs has been low. | |||
To address this gap, LSRCA and its partner agencies identified a need for a guideline document that could be used by designers, regulatory agencies, owners, contractors, and others to consider design elements in the design and layout of parking lots and related infrastructure that can help to reduce the requirement for salt application. This effort culminated in the development of the [https://www.lsrca.on.ca/Shared%20Documents/Parking-Lot-Design-Guidelines/Parking-Lot-Guidelines-Salt-Reduction.pdf Parking Lot Guidelines to Promote Salt Reduction]<ref>LSRCA. 2015.Parking Lot Design Guidelines to Promote Salt Reduction. GHD. 11115623 (2). https://www.lsrca.on.ca/Shared%20Documents/Parking-Lot-Design-Guidelines/Parking-Lot-Guidelines-Salt-Reduction.pdf</ref>. | |||
LSRCA commissioned a study into salt management design strategies for parking lots. The entire report can be read here: [[LSRCA salt guide]]. <br> | LSRCA commissioned a study into salt management design strategies for parking lots. The entire report can be read here: [[LSRCA salt guide]]. <br> | ||
The report identified four key design strategies. They may be summarized as: | The report identified four key design strategies. They may be summarized as: |
Revision as of 19:09, 24 March 2022
Overview[edit]
Each year, Canadians spend over $1 billion on public and private roads, parking lots and sidewalks (Hossain et al., 2015)[1]. While the use of salt is essential to ensure public safety, there is a growing concern regarding the large quantities of salt (mainly chloride ions), being released to the environment.
In their 2001 assessment under the Canadian Environmental Protection Act, it was found that high releases of road salts from winter maintenance activities were having an adverse effect on freshwater ecosystems, soil, vegetation, and wildlife (Environment Canada, 2001)[2]. Based on this conclusion, Environment Canada developed its “[Code of Practice the Environmental Management of Road Salts],” which focuses mainly on municipal and provincial road maintenance. This code, which requires the development of Salt Management Plans for those organizations using more than 500 tonnes of road salt annually, was released by Environment Canada in 2004 (Environment Canada, 2004)[3]. While the uptake of these guidelines has been successful, and many agencies have adopted best practices because of it, it is not generally applicable for companies that apply salt to private roads, parking lots, and roadways; and additional measures are needed to realize reductions in these areas.
There are studies and training programs that address these issues, which aim to educate private contractors about best practices, and how these can improve level of service, protect the environment, and reduce costs. However, uptake of these programs has been low.
To address this gap, LSRCA and its partner agencies identified a need for a guideline document that could be used by designers, regulatory agencies, owners, contractors, and others to consider design elements in the design and layout of parking lots and related infrastructure that can help to reduce the requirement for salt application. This effort culminated in the development of the Parking Lot Guidelines to Promote Salt Reduction[4].
LSRCA commissioned a study into salt management design strategies for parking lots. The entire report can be read here: LSRCA salt guide.
The report identified four key design strategies. They may be summarized as:
Effective Grading[edit]
- Areas for vehicular and pedestrian traffic should be graded between 2 - 4 % to reduce the chances of depressions forming over time (maximum permitted 5% for AODA). Small depressions can result in ponded water icing over in the winter.
- Sub bases should be well compacted for the same reason. Preventing ponding and ice formation reduces the salting requirements for those surfaces.
- In winter months efficient salt application should be made along the top of slopes; melting snow will carry the salt solution down-gradient.
Snow Piles[edit]
- Storage locations for snow piles should be in sunny areas with low traffic.
- Consider grading the storage location to distribute the melt-water as sheet flow over a grass filter strip into an adjacent BMP, such as a bioretention cell or infiltration trench. In some cases, with careful vegetation selection and adequate drainage, the BMP itself can serve as a snow storage location.
- Snow storage areas should be clearly marked for seasonal maintenance staff.
Sidewalk Design and Pedestrian Flow[edit]
- Sidewalks that receive infrequent use could be closed for the winter season.
- Maintained sidewalks should be ≥ 1.5 m wide to accommodate plowing and minimize the salting required.
- Using textured pavers can improve grip for pedestrians, again reducing the salt required.
- In busy areas around building entrances, covered walkways and heated mats also reduce salt requirements.
Trees[edit]
- Specifying deciduous trees will maximize winter sunlight penetration. This will naturally enhance the melting of frozen surfaces, limiting the need for winter maintenance.
Other vegetation[edit]
Vegetation varies in its reaction to soils with high salinity:
- Salt in soil water generally makes it more difficult for roots to take up water. This phenomenon mimics drought conditions for the plant.
- If passing traffic sprays salty water onto plants it can reduce cold hardiness in buds and new twigs. These then become more susceptible to freezing, mortality or deformation.
- In high enough concentrations, sodium and chloride can also be directly toxic to plants. In some species the ions are absorbed by the plant and build up in the leaves causing them to die.
Generally, the vegetation growing closest to the source will be most strongly affected by salt. Plants actively growing in late winter (when salt levels are highest) are also more significantly affected. So, warm season grasses offer an advantage over cool season grasses, because they emerge later in the spring when excess salt has been flushed away. Resilient turf grasses are particularly useful in the design of vegetated filter strips, dry ponds and enhanced grass swales. The Ministry of Transportation have standardized a number of grass mixes[5]. The 'Salt Tolerant Mix' is of particular value for low impact development applications alongside asphalt roadways and paved walkways.
Common name | Scientific name | Proportion |
---|---|---|
Tall Fescue | Festuca arundinacea | 25 % |
Fults Alkali Grass | Puccinellia distans | 20 % |
Creeping Red Fescue | Festuca rubra | 25 % |
Perennial ryegrass | Lolium perrenne | 20 % |
Hard Fescue | Festuca trachyphylla | 10 % |
External links[edit]
- ↑ Hossain, S.K., Fu, L. and Lake, R., 2015. Field evaluation of the performance of alternative deicers for winter maintenance of transportation facilities. Canadian Journal of Civil Engineering, 42(7), pp.437-448. https://cdnsciencepub.com/doi/abs/10.1139/cjce-2014-0423
- ↑ Environment Canada. 2001. PRIORITY SUBSTANCES LIST ASSESSMENT REPORT. Road Salts. Canadian Environmental Protection Act, 1999. Environment Canada and Health Canada. https://www.canada.ca/content/dam/hc-sc/migration/hc-sc/ewh-semt/alt_formats/hecs-sesc/pdf/pubs/contaminants/psl2-lsp2/road_salt_sels_voirie/road_salt_sels_voirie-eng.pdf
- ↑ Environment Canada. 2004. Code of practice for the Environmental Management of Road Salts. Canadian Environmental Protection Act, 1999 (CEPA 1999). April 2004. EPS 1/CC/5. https://publications.gc.ca/collections/collection_2012/ec/En49-31-1-5-eng.pdf
- ↑ LSRCA. 2015.Parking Lot Design Guidelines to Promote Salt Reduction. GHD. 11115623 (2). https://www.lsrca.on.ca/Shared%20Documents/Parking-Lot-Design-Guidelines/Parking-Lot-Guidelines-Salt-Reduction.pdf
- ↑ Ontario Provincial Standard Specification. (2014). Construction Specification and for Seed and Cover OPSS.PROV 804. Retrieved from http://www.raqsb.mto.gov.on.ca/techpubs/ops.nsf/0/3a785d2f480f9349852580820062910a/$FILE/OPSS.PROV 804 Nov2014.pdf