The full report is available upon request only.
Please contact Paul Reader at paul.reader@tc.gc.ca using the title of the report, "Evaluation of Environmental and Social Impacts and Benefits of Shortsea Shipping in Canada", to obtain your copy.
The purpose of this study, commissioned by Transport Canada (TC), is to evaluate the environmental and social impacts of shortsea shipping in Canada and to compare the outcome with the rail and road modes. In this context, a model incorporating the best approaches for the assessment of environmental and social impacts was developed so as to compare the three transportation modes on an economic basis. The results of the modal comparison should be used with care, given the general and specific limitations of the model developed for the study.
Environmental and Social Impacts
The environmental impacts considered in this study are fuel consumption efficiency, criteria air contaminants (CAC), greenhouse gases (GHG) and other non-quantifiable environmental impacts, while the social costs considered are accidents, congestion and noise.
The fuel consumption efficiency of the marine, rail and road modes are considered in a context of energy efficiency. The fuel consumption of each mode is measured in litres.
The CAC (SOx, NOx, PM) and GHG (CO2, CH4, N2O) emissions are calculated in grams per tonne of freight per kilometre of freight movement, in order to compare them between the three transportation modes. The economic values of the emissions are then calculated, in the case of CAC, by applying unit costs of air pollution by pollutant emitted by province, and, in the case of greenhouse gases, by applying a unit cost for one tonne of CO2-equivalent.
Other environmental issues, such as operational water pollution, non-indigenous aquatic species, anti-fouling paint and waste management, are not incorporated in the model, given that no methodologies are proposed in the literature for their quantification. Therefore, these impacts are discussed qualitatively in the study.
Moreover, accident cost valuation is based on a methodology that estimates the unit costs of accidents for the three transportation modes. A Statistical Life Value as well as a major injury value are used to calculate the accident unit costs.
Congestion costs are also considered in the model, as time saving and congestion are significant types of social costs. Marginal public costs of highway use by trucks in terms of cents per vehicle - kilometre are used in the model. Given the absence of methodologies in the literature to evaluate congestion costs for the marine and rail modes, the study does not consider congestion costs for those two modes.
Finally, noise costs are considered in the model. Noise costs generally consist of costs for annoyance and health. Marginal costs per province, in terms of dollars per vehicle - kilometre, are used in the model. No noise costs are considered for the marine mode.
The Scenarios
The model used in the study is based on realistic transportation case studies on main Canadian seaways. The four scenarios considered are located on the Great Lakes, the St. Lawrence system, the East Coast and the West Coast.
| Scenario 1 | Scenario 2 | Scenario 3 | Scenario 4 | |
|---|---|---|---|---|
| Great Lakes | St. Lawrence System | East Coast | West Coast | |
| Origin | Superior (WI) | Halifax (NS) | Saint John (NB) | Prince Rupert (BC) |
| Destination | Nanticoke (ON) | Montreal (QC) | Boston (MA) | Richmond (BC) |
| Cargo weight (tonnes) | 25,000 | 10,000 | 35,000 | 25,000 |
| Type of products | Solid bulk | Truck trailers and containers | Petroleum products | Containers |
| Ship type | Seaway (Bulker 25,000) | Ro-Ro's - Lo-Lo's | Product tanker (35,000) | Ro-Ro's |
| Distance (km) | ||||
| Rail | 1,514 | 1,226 | 1,616 | 1,513 |
| Road | 1,466 | 1,251 | 665 | 1,505 |
| Marine | 1,510 | 1,950 | 550 | 704 |
For each scenario, the transportation modes are compared on a 2008-dollar basis. Thus, the model allows for identification of the transportation mode having the lowest environmental and social costs. The results are presented in the following table.
| Total Environmental and Social Costs ($2008) | Scenario 1 | Scenario 2 | Scenario 3 | Scenario 4 |
|---|---|---|---|---|
| Great Lakes | St. Lawrence System | East Coast | West Coast | |
| Rail | $144,391 | $29,665 | $97,285 | $47,305 |
| Road | $350,151 | $97,655 | $175,645 | $174,556 |
| Marine | $29,674 | $30,170 | $4,781 | $10,420 |
Modelling results show that the shortsea shipping transportation mode has the lowest environmental and social costs for three of the four scenarios, while the rail mode has a slightly lower cost compared to the marine mode for the remaining scenarios.
Those results demonstrate that the marine mode seems to gain an advantage in terms of environmental and social costs when the total distance to cover is equal or lower than the distance to cover with the rail or road modes. In the case of the St. Lawrence system scenario, for which the rail mode has lower environmental and social costs, the distance to cover for the marine mode is about 50% higher than those to cover by the two other transportation modes.
Limitations of the Model
The model developed for this study has limitations that limit the scope of the results regarding modal comparison of environmental and social impacts and should be used with care. The following table summarizes the general and specific limitations. They can be considered as suggestions for improving the model.
Shortsea Shipping and Sustainable Development
The results of the study demonstrate the potential that shortsea shipping has in terms of helping the government of Canada reach its sustainable development objectives. The model developed for the study shows that the environmental and social costs of shortsea shipping are generally lower than the rail and road transportation modes, when a port-to-port comparison is considered.
The following recommendations are made regarding the fostering of the development of shortsea shipping activities in a context of sustainable development (SD). Three basic principles are generally applied when developing sustainable development strategies: developing knowledge, promoting responsible action and fostering commitment.
1. Developing knowledge
2. Promoting responsible actions
3. Fostering commitments