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Assessing Adaptive Management in Alberta’s Energy Resource Sector

By: Martin Olszynski

PDF Version: Assessing Adaptive Management in Alberta’s Energy Resource Sector

Research Commented On: “Failed Experiments: An Empirical Assessment of Adaptive Management in Alberta’s Energy Resources Sector” (UBC L Rev) (Forthcoming)

It was three years and six months ago – almost to the day – that I published my first ABlawg post. The Joint Review Panel (JRP) assigned to conduct the environmental assessment of Shell’s then-proposed Jackpine oil sands mine expansion project had just released its report. That report was notable for several reasons, including that it was the first to conclude that an oil sands mine was likely to result in “significant adverse environmental effects” pursuant to the Canadian Environmental Assessment Act 2012, SC 2012, c 19 (CEAA, 2012). In Shell Jackpine JRP Report: Would the Real “Adaptive Management” Please Stand Up?, however, I focused on the role that adaptive management had played in the Joint Review Panel’s determination of the project’s environmental effects. Briefly, adaptive management is defined by the Canadian Environmental Assessment Agency as “a planned and systematic process for continuously improving environmental management practices by learning about their outcomes.” The concern that I have expressed over the past few years is that, as practiced in Canada, adaptive management appears to be seldom planned or systematic. The problem was that I couldn’t show this to be the case – until now.

In a recent paper, I examine the implementation and effectiveness of adaptive management in Alberta’s energy resources sector. Using freedom of information processes, publicly available documents, and communication with the relevant regulator, I collected the environmental impact statements, environmental assessment reports (e.g. the Shell Jackpine JRP Report), statutory approvals and required follow-up reports for thirteen energy projects in Alberta: two coal mines, three oil sands mines, and eight in situ oil sands operations. In each case, the proponent proposed adaptive management for at least one environmental issue or problem. I then analyzed these various documents to determine the conception, implementation, and, to the extent possible, effectiveness of adaptive management with respect to each project throughout the regulatory cycle (i.e. from the proposal stage through to approval and reporting). Simply put, I set out to determine how adaptive management was actually being applied in this context.

Unfortunately, the results confirm longstanding concerns about the implementation of adaptive management in natural resources development.

The Efficiency Plank in Alberta’s Climate Leadership Plan

By: Nigel Bankes

PDF Version: The Efficiency Plank in Alberta’s Climate Leadership Plan

Report Commented On: Getting it Right: A More Energy Efficient Alberta, Final Report of the Alberta Energy Efficiency Advisory Panel, released 23 January 2017 and related press release

As reported in previous posts, Alberta’s Climate Leadership Plan (CLP) released in November 2015 following receipt of the Leach Report has four key planks: (1) phasing out emissions from coal-generated electricity and developing more renewable energy, (2) implementing a new carbon price on greenhouse gas emissions, (3) a legislated oil sands emission limit, and (4) employing a new methane emission reduction plan.

The government introduced legislation to implement an economy-wide carbon price in June 2016 (the Climate Leadership Implementation Act) with the results of that in the form of the carbon levy coming into force on January 1 of this year (2017). The fall session of the legislature (2016) saw the introduction and passage of Bill 25, The Oil Sands Emission Limit Act to implement the third objective, a legislated oil sands emission limit (I commented on Bill 25 here) and followed this up with Bill 27, the Renewable Electricity Act to implement the second half of the first plank – developing more renewable energy. I commented on Bill 27 here. Then there were subsequent developments with respect to transforming Alberta’s “energy only” market which I commented on here. This last post also commented on the first half of the first plank of the CLP, i.e. the agreement between the province and the owners on the phase-out of coal generating facilities and the level of compensation payable.

As part of the plan to replace coal generation the province has also been looking at energy efficiency policies and micro or distributed generation. Although energy efficiency measures do not result in more generation they do suppress load and avoid (or at least postpone) the need to build or run new generation. While energy efficiency has a lower public profile than new generation, most commentators suggest that energy efficiency and demand side management policies are usually among the most cost effective measures for meeting load and for reducing greenhouse gas emissions – especially where the current energy mix, as in Alberta, is carbon intensive.

Legal Designation of the New Castle Wilderness Protected Areas

By: Shaun Fluker

PDF Version: Legal Designation of the New Castle Wilderness Protected Areas

Orders in Council commented on:

Order in Council 020/2017 (amendments to South Saskatchewan Regional Plan under Alberta Land Stewardship Act)

Order in Council 021/2017 (amendments to Forest Provincial Recreation Areas Order)

Order in Council 022/2017 (designation of the Castle Provincial Park under Provincial Parks Act)

Order in Council 023/2017 (designation of the Castle Wildland Provincial Park under Provincial Parks Act)

Order in Council 024/2017 (amendments to the Public Lands Administration Regulation)

On January 20, 2017 the Lieutenant Governor in Council issued 5 Orders in Council and thereby followed thru on Alberta’s commitment announced back in September 2015 to legally protect the area in southwestern Alberta known as the Castle wilderness with a new wildland provincial park and a new provincial park. What remained to be seen back in September 2015 was what this legal protection would exactly amount to, and these Orders in Council provide us with the important details. At the time of the announcement back in September 2015 I provided some context for these new designations in At Long Last – Legal Protection for the Castle Wilderness. Collectively these Orders in Council create the Castle Wildland Provincial Park and the Castle Provincial Park effective February 16, 2017, and implement consequential amendments to existing regulations to accommodate these new designations.

Co-Owners and Adverse Possession – The Uniqueness of Alberta?

By: Nickie Nikolaou

PDF Version: Co-Owners and Adverse Possession – The Uniqueness of Alberta?

Case Commented On: Verhulst Estate v Denesik, 2016 ABQB 668 (CanLII)

In an earlier post, I concluded that Master Schlosser was correct in finding that a co-owner will typically not be able to claim their co-owner’s interest in the property through the doctrine of adverse possession. In this appeal upholding that decision, Justice D.L. Shelley queries whether a co-owner in Alberta can ever make a claim for adverse possession against a co-owner. This leads her on an interesting journey across Canada which suggests, but does not conclude, that Alberta might be unique in its treatment of co-owners and adverse possession.

Recent Analysis Shows Canada was Losing Fish Habitat Before 2012 Budget Bills

By: Martin Olszynski and Brett Favaro

PDF Version: Recent Analysis Shows Canada was Losing Fish Habitat Before 2012 Budget Bills

Matter commented on: Standing Committee on Fisheries and Oceans’ Review of the Fisheries Act RSC 1985, c F-14

Back in October of last year, we appeared before the Standing Committee on Fisheries and Oceans (FOPO) in the context of its review of the 2012 changes to the habitat protection provisions of the Fisheries Act. Shortly after our appearance it occurred to us that it would be useful, using the best evidence available in the short time that was left, to provide FOPO – indeed all Canadians – with some quantifiable estimate of the state of fish habitat protection in Canada (the deadline for public submissions was November 30th, 2016).

Consequently, we returned to Professor Olszynski’s original access to information request from 2015 that provided the evidentiary basis for his article “From ‘Badly Wrong’ to Worse: An Empirical Analysis of Canada’s New Approach to Fish Habitat Protection Laws” (2015) 28(1) J Env L & Prac 1). Briefly, Professor Olszynski obtained all of the subsection 35(2) authorizations issued by DFO’s two largest regions (Pacific, Central and Arctic) over a six-month period (May 1 to October 1) for the years 2012, 2013, 2014. Generally speaking, each authorization contains information about the project proponent, project type (e.g. a bridge, a mine, a dam), project location, the size and kind of impacts to habitat, and the amount of compensation or offsetting habitat required – if any. We recorded the total area that each project was authorized to impact (in m2), as well as the total amount of compensation habitat required. Of the 86 authorizations in 2012, eight authorized impacts that were not described in terms of area (e.g. the proponent was authorized to destroy 1,500 eelgrass plants, or to dewater a stream killing all its fish); these were excluded from our analysis, leaving us with 78 authorizations.

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