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Summary of the Horizontal Evaluation of the Canadian Shellfish Sanitation Program

Summary of the Horizontal Evaluation of the Canadian Shellfish Sanitation Program
(PDF, 258 KB)

About the program

The Canadian Shellfish Sanitation Program (CSSP) is a federal food safety program that aims to minimize health risks associated with the consumption of contaminated bivalve molluscan shellfish. Bivalve molluscan shellfish have two hinged shells with a soft-bodied invertebrate contained inside. Many are edible for example oysters, clams, cockles, and mussels.

The CSSP, which dates back to 1925, has a long history of federal organizations working together and many of the activities of the present-day program (see details below) remain the same as those seen throughout its evolution. The CSSP, which is jointly delivered by the Canadian Food Inspection Agency (CFIA), Fisheries and Oceans Canada (DFO) and Environment and Climate Change Canada (ECCC), operates under a Memorandum of Understanding, signed in 2000, which has the stated goal:

To provide reasonable assurance that molluscan shellfish are safe for consumption as food by controlling the harvesting of all molluscs within the tidal waters of Canada.

The CSSP controls shellfish harvest by classifying waters as approved, conditionally approved, restricted, conditionally restricted or prohibited. Water can also be unclassified. Classifications are based on comprehensive water quality monitoring and analysis, and pollution source assessments. Areas are given either an open or closed status according to whether shellfish can be harvested or not.

CFIA is the lead regarding the handling, processing, import and export of shellfish; the marine biotoxin monitoring program; and any other microbiological monitoring program not under the responsibility of ECCC. CFIA tests shellfish for biotoxins, and in response to incidents the agency will also test for micro contaminants such as salmonella.

DFO is the lead department regarding the harvesting of shellfish and notifying stakeholders and partners of the openings and closing of harvest areas. The department is responsible for licensing shellfish harvesting, enacting the opening and closing of shellfish harvest areas, and conducting patrols to enforce compliance of harvest.

ECCC is the lead department regarding recommending the appropriate classification of shellfish harvest waters based on sanitary and bacteriological water quality conditions. The department is responsible for monitoring water quality in shellfish harvest areas and identifying and evaluating sanitary pollution sources that may affect the quality of the waters where shellfish are being harvested for consumption.

About the Evaluation

The objective of the evaluation was to identify challenges and opportunities in the management and delivery of the CSSP to provide senior management from CFIA, DFO and ECCC with evidence-based information to support ongoing discussions about future program direction, decisions and improvements.

The evaluation examined the delivery of the program by all three federal partners and in all three regions where CSSP is implemented i.e., Pacific, Quebec and Atlantic regions over the last five years (2016-17 to 2020-21) and further back where relevant. The program’s relevance, performance and design and delivery were examined through six lines of evidence including: international benchmarking, document/legislative review, data analysis, key informant interviews, financial/cost analysis, and process mapping.

Key Findings

Program Mandate & Evolving Context

Volume and value of Canadian exports of mussel, oyster, clam, geoduck and scallop, compared to imports
Description

This figure is a bar graph. It shows the volume and value in of Canadian exports of mussel, oyster, clam, geoduck and scallop, compared to imports, for the years 2015 to 2021 included.

Volume is in in millions of kilograms; value is in millions of Canadian dollars.

Import volume including scallops

In 2015, import volume including scallops was 19 million kilograms.
In 2016, it was 18 million kilograms.
In 2017, it was 14 million kilograms.
In 2018, it was 12 million kilograms.
In 2019, it was 12 million kilograms.
In 2020, it was 11 million kilograms.
In 2021, it was 9 million kilograms.

Import value including scallops

In 2015, import value including scallops was 166 million dollars.
In 2016, it was 160 million dollars.
In 2017, it was 161 million dollars.
In 2018, it was 146 million dollars.
In 2019, it was 152 million dollars.
In 2020, it was 139 million dollars.
In 2021, it was 109 million dollars.

Export volume including scallops

In 2015, export volume, including scallops was 33 million kilograms.
In 2016, it was 34 million kilograms.
In 2017, it was 36 million kilograms.
In 2018, it was 35 million kilograms.
In 2019, it was 38 million kilograms.
In 2020, it was 29 million kilograms.
In 2021, it was 24 million kilograms.

Export volume excluding scallops

In 2015, export volume, excluding scallops was 25 million kilograms.
In 2016, it was 28 million kilograms.
In 2017, it was 30 million kilograms.
In 2018, it was 29 million kilograms.
In 2019, it was 31 million kilograms.
In 2020, it was 23 million kilograms.
In 2021, it was 20 million kilograms.

Export value including scallops

In 2015, export value including scallops was 411 million dollars.
In 2016, it was 406 million dollars.
In 2017, it was 436 million dollars.
In 2018, it was 426 million dollars.
In 2019, it was 479 million dollars.
In 2020, it was 389 million dollars.
In 2021, it was 304 million dollars.

Export value excluding scallops

In 2015, export value, excluding scallops was 209.3 million dollars.
In 2016, it was 227 million dollars.
In 2017, it was 256 million dollars.
In 2018, it was 263.4 million dollars.
In 2019, it was 293.2 million dollars.
In 2020, it was 220.3 million dollars.
In 2021, it was 181.2 million dollars.

Note: This graph excludes some species due to specificity of data. Further, data is presented both with and without scallops as often scallops are not covered under the CSSP but are not disaggregated from the data.

Source: Canadian trade by species group and species

Program Resources

Comparison of CSSP tracked expenditures and current costs estimates, by partner (in million $)
Description

This figure is a comparison of CSSP tracked expenditures and current cost estimates in millions of dollars. Expenditures tracked in systems total 13.2 million dollars and the current cost estimate for the CSSP program is 21.9 million.

Governance & Leadership

Program Delivery

There are some significant gaps in delivery which present barriers for some stakeholders and partners:

Close to 80% of internal interviewees perceived that the program does not currently provide equitable and inclusive access to shellfish harvesting sites for safe consumption.

Key sources of information are lacking for operational decision-making and risk management, as well as for measuring and reporting on program performance:

41% of interviewees perceived that the necessary information was available in a timely manner to support decision-making for the program.

Recommendations

Recommendation 1

It is recommended that the CSSP ADM Steering committee develop, articulate and communicate to program staff renewed strategic guidance about the program’s priorities, scope and reach to address increasing demands and evolving changes in its operating context.

Recommendation 2

It is recommended that the CSSP ADM steering committee clarify which federal partner is the lead of the CSSP. Further, it is recommended that they review all levels of interdepartmental governance and establish mechanisms to support more effective decision-making, ensure that long-standing issues are resolved, and operational staff are given timely guidance and advice when needed.

Recommendation 3

It is recommended that the CSSP ADM Steering committee seek out opportunities to address resource gaps facing the CSSP to meet existing and increasing demands for program services and delivery. Solutions are required to address current risks related to CSSP resource management in order to ensure that health risks are minimized, the shellfish industry remains strong, and stakeholder and partner needs are served appropriately by the program.

Recommendation 4

It is recommended that the CSSP ADM Steering committee review the CSSP’s performance measures and develop an integrated performance profile with meaningful performance indicators and targets at the program level. Useful and accurate information on the achievement of results is needed to better support the management of the program. Ideally, program level performance indicators could be integrated into the broader results frameworks of the three respective partner organizations. CSSP performance data needs to be tracked, collected and reported consistently and in a timely manner across all three federal partners and all regions. Roles and responsibilities for collecting and storing the data should also be established.

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