Jack Lawson
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Transcript of Jack Lawson
Framework to incorporate & quantify risks of impacts on marine mammal populations from shipping noise, with an Arctic case study … plus role of the CSAS processJack LawsonScience Branch, Department of Fisheries and Oceans, P.O. Box 5667, St. John’s, NL A1C 5X1
(Based partly on “Lawson, J.W. and V. Lesage. 2013. A draft framework to quantify and cumulate risks of impacts from large development projects for marine mammal populations: A case study using shipping associated with the Mary River Iron Mine project. DFO Can. Sci. Advis. Sec. Res. Doc. 2012/154 iv + 22 p. ”)
Presentation Overview
Marine Development Projects (MDP) have increased dramaticallyin Canada, and this trend is expected to continue or be exacerbated
Assessment of MDP impacts made on a case-by-case basis,without a context of effective thresholds relating them to speciesor ecosystem productivity, and without consideration ofcumulative impacts
Growing concern: currently no national approach as to how impacts of industrial projects should be evaluated by DFO Science, which leads to perception of inconsistency
Pressing need: develop a national approach to impact assessment, as well as threshold setting, monitoring standards, and development of guidelines for industry that outline minimum information needs for adequate impact assessment
This framework will include thresholds for assessing impacts against population productivity in the context of population sustainability, and extended to assess cumulative impacts
Case study: Baffinland Iron Mine project as an example of application of a framework to quantify risks of impacts on Arctic mammal populations
Implementing Science advice: Varying roles of Canadian Science Advisory Secretariat (CSAS)
Outstanding Issues For DFO
Should DFO adopt a unified, national framework for marine project reviews to quantify risks of impacts on mammal populations?
– multiple, different international approaches exist if we want to choose an existing method
– how to address context-, species-, and activity-related sources of variation in impact thresholds?
– how to address regional differences in activities, ecosystems, and regulatory regimes?
– is it possible to produce an assessment "tool" to assist the process for proponents and regulators?
Assessing Cumulative ImpactsEnvironmental Impact Assessments often don’t attempt to quantify impact
levels using exposures, but instead employ a posteriori verification to determine whether a given threshold for population decline is exceeded during the life of a project
– usually, thresholds set arbitrarily + not treated as additive by proponents
– for almost all species threshold decline values are so small it is difficult to determine whether they have been exceeded, even using best study designs
– project effects on mammal populations are not easily detected and if such changes are detected, it may be when project activities have resulted in dramatic population declines - not a precautionary approach!
Proposed approach to assess significance of impacts is based on a combination of impacts likelihood and severity if they were to occur
However, more quantitative criteria are used to determine the significance of impacts
1 + 1 + 1 = 1
These descriptors arereflective of the conservationstatus of each species
Can calculate cumulative effects of MDPse.g., consequences from additional ship transits as a result of expansion of an existing MPD or new projects can be assessed quantitatively
Case Study – Baffinland Iron Mine
UnprecedentedYear-round shipping, regardless of icePass through bowhead and other marine mammal aggregations
Case Study – Baffinland Iron MineDistribution data available for bowheads, narwhal, and beluga
indicate that shipping routes for large-scale mining developments such as Baffinland, Hopes Advance, and Raglan mines in the Arctic will overlap areas of core use for these species, especially during winter when open water areas and ice leads provide only habitat
There is a relatively high abundance of ringedseals and walrus along this shipping route
Note: review constrained since more data on marine mammal susceptibility to ship noise
Note: less data on marine mammal susceptibility to ship strike
Modelling Shipping Noise RisksExposure to ship-related noise and movement may lead to mortality or other
negative effects on marine mammal health, behaviour, and habitat use
Key Issue: no field data to assess with certainty the proportion of exposed marine mammals for which effects of shipping noise would detrimentally impact health, reproduction, or survival
So:• one means to estimate significance of impacts is to determine number
of potential individual-exposures relative to total population size
• another is to determine whether specific segments of population are likely to be impacted more than others (e.g., calving females)
Case Study – Baffinland Iron Mine
BUT, extrapolating these exposure estimates to “harm” asit relates to marine mammal populations not clearcut
With rankings of high magnitude, likelihood, and severity, the“Impact” ranking of this shipping noise exposure will be “High”
Case Study – Baffinland Iron Mine
Impacts on reproduction or survivalof even a few whales could lead tonegative impacts on population recovery
Conclusions - BaffinlandCurrently no effectual mitigation measures proposed for Arctic shipping
operations to monitor interactions or avoid/reduce potential impacts of shipping on marine mammals
So, a portion of several already-vulnerable populations would be exposed to ship noise, with potential consequences to population trajectories
Proposed impact assessment framework can help quantify risks of impacts (by bringing in factors such as ship noise) of MDPs on marine mammal populations
Impact assessment framework provides a quantitative approach to begin to address the ever-difficult issue of cumulative impacts
New, large-scale industrial projects have to be assessed in the context of their potential additions to the overall anthropogenic impacts on marine mammal populations + such impacts should be incorporated into precautionary population management by DFO (and include ALL “users”)
Conclusions - A National FrameworkModel to assess impacts of ship strike
could incorporate more factors + informed by better studies in the Arctic
Develop national framework for project impact assessment (e.g., severity, likelihood, impact), threshold setting, and monitoring standards
Model to assess impacts of shipping noise could be made more robust + extended to encompass other types of anthropogenic noise sources + informed by better studies in the Arctic
Develop guidelines for industry that outline the information needed for adequate impact assessment + proposed methodologies for evaluating impacts
Improving the Framework• Include thresholds for assessing impacts against
population productivity, accounting for the conservation status and biology of each species
• Include uncertainty in input parameters!
• Implement more complex impacts from multiple activities and for multiple ecosystem components
• Perhaps allow for ranking/effect scaling for VECs based on socioeconomic or cultural concerns (e.g., lower significant impact threshold?)
Implementing the Approach – there’s an App for that?
• Explicit, quantitative model could ensure that max. number of potentially important considerations are addressed
• Incorporate elements of risk & uncertainty• Could be used by proponents and regulators
to highlight particular issuesor impacts that could warrantbetter baseline study,monitoring, or mitigation
Role of Canadian Science Advisory Secretariat (CSAS) in Activity Reviews
• CSAS coordinates the peer review of scientific issues (such as stock assessments or anthropogenic development proposals) for Fisheries Management in DFO
• Different regions of Canada conduct their resource assessment reviews independently, tailored to regional characteristics and stakeholder needs
• NL, NS, and Nunanvut have establishedprocesses whereby there are federal-provincial co-management agreements
Role of CSAS in Anthropogenic Activity Reviews• Science Advisory Reports (Stock Status Reports, Ecosystem Status
Reports, Habitat Status Reports. Management strategies, frameworks and guidelines on the assessment or evaluation on specific issues, impacts of human activities on ecosystem components as well as recovery assessments on a species or population)
• Research Documents document the scientific basis for the evaluation of fisheries resources by providing progress reports on ongoing investigations (marine mammal population estimates)
• Proceedings Series (record activities at meetings or workshops sponsored by DFO)
• Science Responses document reviews provided by DFO Science, such as when when Science has to respond to urgent and unforeseen requests for scientific information / advice
Role of CSAS in Anthropogenic Activity Reviews
Science Advisory Reports
Science Special Response
Baffinland Iron Mine Environmental Assessment
Proceedings
Research Documents
NIRB
Example: Atlantic Activity Assessments• Federal-Provincial intergovernmental
agreements established oversight boards (C-NLOPB and C-NSOPB)
• Relegate DFO Science and other agency reviews to that of advisory input
• Final decisions on activity approval, and monitoring and mitigation requirements made by the Boards
Example: Nunavut Activity Assessment• Federal-Nunavut intergovernmental
agreements established oversight board (NIRB)
• Relegate DFO Science and other agency reviews to that of advisory input
• Final decisions on activity approval, and monitoring and mitigation requirements made by the Board
Conclusions• Like other countries, Canada is seeking a more
comprehensive and objective means to assess impacts of large marine development projects
• New approach will be better means to achieve these goals, but further international review is planned (international workshop in Nov 2013; post-doc to refine approach by incorporating risk and uncertainty; develop quantitative assessment "tool")
• CSAS role varies across country but new approach and “tool” could increase review consistency
Thank You - Merci
Recommendations For Shipping Impact MitigationShipping operations should undertake the following mitigation measures aimed at reducing the potential for interaction with marine mammals in the Arctic:
– Consider reducing shipping rates during periods when interactions with marine mammals may be the most problematic;
– Consider alternate shipping routes to avoid areas that are identified as having higher marine mammal concentrations;
– Reduce vessel speed as a mitigation measure, which might lower collision risks in open water and to some extent reduce vessel noise output – may be ineffective in reducing or eliminating the risk for whales in polynya or dense pack ice;
– Require proponents to submit clearly-defined monitoring and mitigation plans to collect baseline information necessary to later determine if there have been project-related changes in marine mammal behaviour or residence;
– Ensure that data produced by surveillance monitoring programmes are analysed rigorously by experienced analysts to maximize their effectiveness in providing baseline information and for detecting potential effects of shipping activities on marine mammals; and,
– impact assessment methodology must be more comprehensive by being extended to cumulative effects as there is a critical need to address those in a more formal and systematic way.
Hence the proposed national framework