Appendix IV:AQUATIC
ORGANISM RISK ANALYSIS
Table of Contents
To be Completed by Introductions and Transfers Committees
Unless the authorising jurisdiction requires the Risk Analysis to be prepared
by the proponent
INTRODUCTION
To evaluate risks associated with the introduction or transfer of aquatic
organisms, it is necessary to assess the probability that a species will
become established and the consequences of that establishment. The process
addresses the major environmental components. It provides a standardised
approach for evaluating the risk of genetic, ecological and disease impacts
as well as the potential for introducing a “fellow traveller”
or parasite that might impact the native species of the proposed receiving
waters. It also provides a mechanism for assessment in cases where establishment
of a population in the wild is the intended outcome. This approach has
been adapted from "Final Draft - Report to the Aquatic Nuisance Task
Force - Generic Non-indigenous Aquatic Organisms Risk Analysis Review
Process, Washington, DC, February 9, 1996 by the Risk Assessment and Management
Committee of the U.S. Aquatic Nuisance Species Task Force” (Anon.
1996).
At each of Steps 1, 2 and 3, the element rating and rationale for the
rating should be recorded, based on the following criteria:
A HIGH rating means that the risk is likely or very
likely to occur.
A MEDIUM rating means that there is a probability of
negative impact.
A LOW rating means that the risk is considered to be
insignificant.
Note: For the High and Medium category of risks, application of appropriate
mitigation measures are required to lessen the risk to a Low rating. However,
it is recognized that this may not be possible for all proposals.
The strength of the review process is not in the ratings but in the detailed
biological and other relevant information statements that motivate them.
Part I – Ecological and Genetic Risk Assessment Process
Step 1 Determining the Probability of Establishment (beyond the intended
area of introduction)
Complete the following table and provide a brief rationale with appropriate
references to support the rating given.
Element |
Probability of Establishment
(H, M, L) 1 |
Level of Certainty
(VC to VU) 2 |
Estimate of probability that the introduced species successfully
colonizes and maintains a population in the intended area of introduction3 |
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Estimate the probability of its spreading beyond the intended area
of introduction 4 or,
Estimate the probability of its spreading beyond the intended are
of introduction if it escapes (apply to cases in
which the intended area of introduction is a confined environment)5
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Final Rating 5,6 |
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Explanatory Notes
1.
H High
M Medium
L Low
Element ratings should be supported with data and references, including
a rationale for the rating given.
2.
VC Very certain
RC Reasonably certain
RU Reasonably uncertain
VU Very uncertain
The level of certainty is intended to give an estimate of whether the
element that is being rated is based on scientific knowledge, experience,
or whether it is extremely subjective and based on “best guess”.
Such uncertainties need to be taken into account when making a decision.
3. Characteristics within this element include: the organism coming in
contact with an adequate food resource; suitability of habitat, encountering
appreciable biotic and abiotic environmental resistance; and the ability
to reproduce in the new environment. . If the organism is introduced into
a confined facility (land based, sea cages etc.), the facility itself
is identified as the intended area of introduction.
4. In cases in which the intended area of introduction is a natural habitat
(i.e., the wild) the probability of spreading includes consideration of,
but is not limited to, factors such as the ability to use human intervention/activity
as a means of dispersal
5. In cases in which the intended area of introduction is a confined
environment such as a land facility or cages, the probability of spreading
beyond the area of introduction is dependent on whether the organism escapes
from the area of introduction. For example, a Low probability
of escape from a confined facility will necessarily result in a
Low probability of spreading in the surrounding natural habitat.
If the probability of escape is deemed Medium, the probability
of spreading beyond the area of introduction, if estimated as High,
could still not be rated higher than Medium. Whereas, if the probability
of escape is deemed High, the probability of spreading
beyond the area of introduction will not be limited by its probability
of escape and could be rated as estimated (i.e., High, Medium or Low).
6. The final rating for the Probability of Establishment
is assigned the value of the element with the lowest rating (for example,
High and Low ratings for the above elements
would result in a final Low rating). Again, both events
– probability of the organism successfully colonizing and maintaining
a population in the intended area of introduction (be it a confined environment
such as a facility, or a natural habitat) and the probability of spreading
beyond the intended area of introduction (estimated as explained above)
– need to occur in order to have establishment beyond the intended
area of introduction.
The final rating for the Level of Certainty is assigned
the value of the element with the Lowest level of certainty
(e.g., Very Certain and Reasonably Certain
ratings would result in a final Reasonably Certain rating).
Part 1 – Step 2 Determining the Consequence of Establishment
of an Aquatic Organism
The “Consequence of Establishment” is assigned
a single rating based on environmental impacts.
Element
Estimate of magnitude of environmental impacts, if established. |
Consequences of Establishment(H, M, L) 7 |
Level of Certainty
(VC to VU) 8 |
Ecological impact on native ecosystems both locally and within the
drainage basin.9 |
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Genetic impacts on local self-sustaining stocks or populations.10 |
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Final Rating 11,12 |
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Explanatory Notes
7. See Note 1.
8. See Note 2.
9. Ecological impacts that can affect the distribution or abundance of
native species resulting from alterations in relationships such as predation,
prey availability, and habitat availability. In assessing the ecological
impacts of establishment, the assessors should take into consideration
whether the non-indigenous stock i) enters or alters the habitat of indigenous
species; ii) displaces indigenous species from optimal habitat; iii) affects
the quantity, quality, and availability of food supply of indigenous species;
or, iv) preys on other species of concern.
10. Genetic impacts which can affect the capacity of native species to
maintain and transfer to successive generations its current identity and
diversity. In assessing the genetic impacts, the assessors should take
into consideration whether the non-indigenous stock i) encounters or interacts
with species of concern; ii) affects the survival of local species; iii)
affects the reproductive success of local species; or, iv) affects the
genetic characteristics of native stocks or species.
11. The final rating for the Consequences of Establishment
is assigned the value of the element (individual probability) with the
highest rating (for example: a High probability
of ecological impact and a Medium rating for the probability of genetic
impact would result in an overall High probability of
environmental impact), as both events are independent (i.e., additive
probabilities).
12. See Note 6.
Part 1 – Step 3 Estimating Aquatic Organism Risk Potential
The overall Risk is assigned a single value based on the Probability
of Establishment and the Consequences of Establishment.
Component |
Rating
(H,M,L) |
Level of Certainty
(VC to VU) |
Probability of Establishment estimate13 |
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Consequences of Establishment estimate14 |
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FINAL RISK ESTIMATE 15, 16 |
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Explanatory Notes
13. As estimated in Step 1 - Use the “final rating level”
and “final level of certainty”, respectively.
14. As estimated in Step 2 - Use the “final rating level”
and “final level of certainty”, respectively.
15. Under “element rating ” – Table 1 provides a guide
for categorizing the final risk estimate. See also the explanatory note
number 29 below Table 1.
16. Under “level of certainty” – the final level of
certainty for the Final risk estimate is assigned the value of the element
with the lowest certainty level (e.g. a Very Certain and Reasonably Uncertain
estimate for the probability of establishment and consequences of establishment,
respectively, would result in an overall Reasonably Uncertain level of
certainty).
Definition of Overall Aquatic Organism Risk Potential
HIGH = Organism(s) of major concern (major mitigation
measures are required). It is advised that the proposal be rejected unless
mitigation procedures can be developed to reduce the risk to Low.
MEDIUM = Organism(s) of moderate concern. It is advised
that the proposal be rejected unless mitigation procedures can be developed
to reduce the risk to Low.
LOW = Organism(s) of little concern. It is advised that
the proposal be approved. Mitigation is not needed.
Note: It is advised that the proposal be approved as presented (no mitigating
measures required) only if the overall estimated risk potential is LOW
Note: It is advised that the proposal be approved only if the overall
confidence level for which the overall risk was estimated is VERY CERTAIN
or REASONABLY CERTAIN.
Note: For an overall HIGH or MEDIUM risk, a second risk assessment needs
to be conducted to determine whether the proposed mitigation procedures
are adequate to reduce the overall risk to LOW.
Part 1 – Step 4 Completion of Risk Assessment Documentation
Specific Management Questions (Mitigation Factors or Measures)
Additional Factors and Notes
1. Mitigation measures could reduce risks to a Low rating. Mitigation
measures include but are not limited to the following:
Reducing risk of genetic impact on local stock:
- hold in containment facilities to prevent escape
- use stocks genetically similar to stocks in receiving waters
- sterilize organisms to prevent interbreeding with local populations
Reducing risk of ecological impact on local ecosystems:
- use local stock only
- sterilize organisms to prevent natural reproduction and increase
in population size
- use species that cannot reproduce naturally in receiving waters
- hold in containment facilities to prevent escapes
2 Are there any neighbouring jurisdictions to consult?
If Yes ? Has this been done?
Is the neighbouring jurisdiction concerned?
If Yes ? Has the dispute avoidance mechanism outlined in Appendix II been
applied?
Part 2 – Pathogen, Parasite or Fellow Traveller Risk
Assessment Process
Step 1 Determining the Probability of Establishment
Complete the following table and provide a brief rationale with appropriate
references to support the rating given.
Steps 1 to 3 must be carried out for each hazard identified
in the hazard identification step (Appendix V).
Element |
Probability of Establishment
(H,M,L) 17 |
Level of Certainty
(VC to VU)18 |
Estimate the probability that a pathogen, parasite or fellow traveller
may be introduced along with the species proposed for introduction.
Note that several pathways may exist through which pathogens or accompanying
species can enter fish habitat. Each must be evaluated. |
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Estimate the probability that the pathogen, parasite or fellow traveller
will encounter susceptible organisms or suitable habitat. |
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Final Rating 19, 20 |
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Explanatory notes
17. See Note 1.
18. See Note 2.
19. The final rating for the Probability of Establishment
is assigned the value of the element with the lowest
risk rating (e.g., a Medium and Low
estimate for the above elements would result in an overall Low
rating). Note that the calculation of the final rating follows the multiplication
rule of probabilities (i.e., the probability that a given event will occur
corresponds to the product of the individual probabilities). Thus the
final risk of establishment is assigned the value of the lowest individual
probability estimate. Again, both events – probability of the pathogen,
parasite or fellow traveller successfully colonizing and maintaining a
population in the intended area of introduction (be it in a confined environment
such as a facility, or a natural habitat) and the probability of spreading
beyond the intended area of introduction (estimated as explained above)
– need to occur in order to have establishment beyond the intended
area of introduction.
20. The final rating for the level of certainty for
the Probability of Establishment is assigned the value of the element
with the lowest level of certainty (e.g. a Very
Certain and Reasonably Uncertain ratings for
the above elements would result in a final Reasonably Uncertain
rating).
Part 2 – Step 2 Determining the Consequence of Establishment
of a Pathogen, Parasite or Fellow Traveller
Complete the following table and provide a brief rationale with appropriate
references to support the rating given. The final rating of the Consequences
of Establishment is assigned a single rating based on environmental impacts.
Element
Impacts of establishment of a parasite, pathogen or fellow traveller
on native species and/or aquaculture in the watershed. |
Consequences of Establishment
(H, M, L) 21 |
Level of Certainty
(VC to VU) 22 |
Ecological impacts on native ecosystems both locally and within
the drainage basin including disease outbreak, reduction in reproductive
capacity, habitat changes, etc. |
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Genetic impacts on local self-sustaining stocks or populations (i.e.
whether the pathogen, parasite or fellow traveler affects the genetic
characteristics of native stocks or species). |
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Final Rating 23, 24 |
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Explanatory notes
21. See Note 1.
22. See Note 2.
23. The final rating for the Consequences of Establishment
is assigned the value of the element (individual probability) with highest
risk rating (e.g. High and Medium ratings
for the above elements would result in a final High rating)
as both events are independent (i.e., additive probabilities).
24. See Note 20.
Part 2 – Step 3 Estimating Pathogen, Parasite or Fellow
Traveller Risk Potential
The overall Risk is assigned a single value based on the Probability
of Establishment and the Consequences of Establishment.
Component |
Rating
(H, M, L) |
Level of Certainty
(VC to VU) |
Probability of Establishment estimate 25 |
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Consequence of Establishment estimate 26 |
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FINAL RISK ESTIMATE 27, 28 |
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Explanatory notes
25. As estimated in Step 1 – Use “ final rating for probability
of establishment” and “final rating for the level of certainty”,
respectively.
26. As estimated in Step 2 – Use “final rating for consequences
of establishment” and “final rating for the level of certainty”,
respectively.
27. Under “element rating”, Table 1 below provides a guide
for categorizing the final risk estimate.
28. See Note 20.
Definition of “Pathogen, Parasite, Fellow Traveller Organism
Risk Potential”
HIGH = Organism(s) of major concern (major mitigation
measures are required). It is advised that the proposal be rejected unless
mitigation procedures can be developed to reduce the risk to Low.
MEDIUM = Organism(s) of moderate concern. Mitigation
is justified. It is advised that the proposal be rejected unless mitigation
procedures can be developed to reduce the risk to Low.
LOW = Acceptable risk - organism(s) of little concern.
It is advised that the proposal be approved as presented. Mitigation is
not needed.
Note: It is advised that the proposal be approved as presented only if
the overall risk associated with each identified potential hazard (as
defined in Step 1) was estimated as LOW.
Note: It is advised that the proposal be approved as presented only if
the overall confidence level for which the overall risk is VERY CERTAIN
OR REASONABLY CERTAIN
Note: For an overall HIGH or MEDIUM risk, a second risk assessment needs
to be conducted to determine whether the proposed mitigation procedures
are adequate to reduce the overall risk to LOW
Part 2 – Step 4 Completion of Risk Assessment Documentation
Specific Management Questions (Mitigation Factors or Measures)
Additional Factors and Notes
Mitigation measures could reduce risks to a low rating. Examples of mitigation
measures include the following:
Reducing risk of transferring accompanying pathogens, parasites
and/or fellow travellers
- health inspection and certification
- pre-treatment for pathogens, diseases and parasites
- inspection for fellow travellers
- disinfection prior to discarding water in which the organisms arrived
- vaccination
- disinfection of eggs
- importation as milt or fertilized eggs only
- quarantine incoming organisms and use as broodstock, release F1 progeny
only if no pathogens, parasites or fellow travellers appear.
Table 1. How to Categorize the Final Risk Estimate 29
Probability of Establishment |
Consequences of Establishment |
Final Risk Estimate |
High |
High |
High |
High |
Medium |
High |
High |
Low |
Medium |
Medium |
High |
High |
Medium |
Medium |
Medium |
Medium |
Low |
Medium |
Low |
High |
Medium |
Low |
Medium |
Medium |
Low |
Low |
Low |
Explanatory Note
29. If there is no probability increment between the two estimates, (i.e.,
if the Probability of Establishment is High and the Consequence
of Establishment is Medium) the final risk estimate takes
the value of the highest of the two probabilities to err on the side of
safety (precautionary approach).
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