The Role of Framework Legislation in Implementing Australia's Emission Reduction Commitments under the Paris Agreement
| Author | Michael Bennett |
| Position | PhD candidate, University of Western Australia. The author thanks Professor Alex Gardner and Associate Professor Sarah Murray for their comments on a draft of this article |
| Pages | 240-263 |
240
THE ROLE OF NATIONAL
FRAMEWORK LEGISLATION IN
IMPLEMENTING AUSTRALIA’S
EMISSION REDUCTION
COMMITMENTS UNDER THE
PARIS AGREEMENT
MICHAEL BENNETT*
The Paris Agreement has been widely recognised as a signicant step forward in efforts to address
climate change. However, the success of the agreement in achieving its global goals will depend
critically on the implementation of sufciently ambitious nationally-determined commitments
(‘NDCs’) made under the Agreement. This article explores the potential for national legislation
to support the Paris Agreement by guiding the development of NDCs and establishing political
and legal accountability mechanisms to ensure that they are achieved. It also examines particular
design issues that arise in an Australian context.
INTRODUCTION
Australia on 9 November 2016.2 As at October 2017 it had been ratied by parties
responsible for 87 per cent of global greenhouse gas emissions.3 While President
Trump has threatened to withdraw the United States from the agreement,4 he
would need to win a second Presidential term to do so.5 At least for the time being,
* PhD candidate, University of Western Australia. The author thanks Professor Alex Gardner
and Associate Professor Sarah Murray for their comments on a draft of this article.
yet assigned).
2 United Nations, Status of Agreements: Paris Agreement
ViewDetails.aspx?src=IND&mtdsg_no=XXVII-7-d&chapter=27&clang=_en>.
3 World Resources Institute, Paris Agreement Tracker (2 October 2017)
org/source/ ratication/#?lang=en>.
4 Michael D Shear, ‘Trump Will Withdraw US from Paris Climate Agreement’ New York
Times (online), 1 June 2017
climate-agreement. html>.
5 The United States has indicated that ‘unless the United States identies suitable terms for
reengagement, the United States will submit to the Secretary-General, in accordance with
Article 28, paragraph 1 of the Agreement, formal written notication of its withdrawal
as soon as it is eligible to do so’: Karl Mathiesen ‘Trump Letter to UN on Leaving
Paris Climate Accord – In Full’, Climate Change News (7 August 2017) .
climatechangenews.com/2017/08/07/trump-tells-un-intention-leave-paris-climate-accord-
full/>. Under Article 28.1 the United States is eligible to withdraw ‘[a]t any time after
three years from the date on which this Agreement has entered into force...’. Article 28.2
241
the Paris Agreement remains at the centre of international efforts and the world’s
best hope for limiting anthropogenic climate change.
The Paris Agreement endorses two important global goals: to restrain global
warming to ‘well under’ 2°C relative to pre-industrial levels, and to achieve a
balance between anthropogenic sources and sinks of greenhouse gas emissions
in the second half of this century. Central to achieving these goals is the pledge-
and-review mechanism, under which parties must submit ‘nationally-determined
contributions’ (‘NDCs’) every ve years, following global stocktakes of progress.
The success or failure of the Paris Agreement in achieving its global goals will
turn on the adequacy of successive emission reduction commitments in NDCs,
and on their effective implementation. At the same time, the agreement leaves
a great deal of discretion to parties to determine the nature and scale of their
commitments and contains soft enforcement mechanisms, such as reporting and
expert review, to ensure that parties follow through on their commitments.
This article explores the potentially important role that national framework
legislation can play in supporting the pledge-and-review mechanism
by encouraging nations to submit adequate targets and ensure adequate
implementation. It also examines some of the key design issues that Australia
would need to address in developing framework legislation of this kind. While
framework legislation also has the potential to play an important role with respect
to climate change adaptation, the focus here is on mitigation: that is, reducing
greenhouse gas emissions.6
The article is structured as follows. Part I focuses on the Paris Agreement. It outlines
the goals of the agreement, the central role of the pledge-and-review mechanism,
and the risks that the pledge-and-review mechanism will be undermined by free-
riding behaviour resulting in inadequate national targets and implementation. Part
II considers the potential for national framework legislation to help avoid this
scenario by guiding responsible target-setting and implementation. It examines
the emergence of framework legislation as a signicant regulatory strategy; the
functions it can serve; and the ways in which it can be aligned with, and support,
the goals and processes of the Paris Agreement. Part III turns the focus to Australia,
further provides that any such withdrawal will take effect upon the expiry of one year from
the date of receipt. The combined effect of these provisions is that the earliest date for
withdrawal is 4 November 2020, one day after the next US election: see Fred Pearce, ‘With
the U.S. Out of Paris, What Is the Future for Global Climate Fight?’ Yale Environment
360 (8 June 2017)
future-for-global-climate-ght>. There were other possible options for withdrawing
earlier, namely withdrawing from the United Nations Framework Convention on Climate
Constitutional requirements, but it appears that the Trump Administration has elected not
to pursue these options.
6 For ease of reference, ‘reducing emissions’ is used in this article as shorthand for both
reducing anthropogenic greenhouse gas emissions and increasing greenhouse gas removals
(e.g. through revegetation).
242
with a consideration of three issues that would be especially important in the
development of national framework legislation in this country: the constitutional
basis for the legislation, the role the Australian Parliament should have in target-
setting decisions, and the scope for the legislation to impose duties on public
ofcials to ensure that targets are achieved.
I THE PARIS AGREEMENT
A The Goals of the Paris Agreement
The principal goal of the Paris Agreement is an ambitious one:
[h]olding the increase in the global average temperature to well
below 2 °C above pre-industrial levels and pursuing efforts to limit the
temperature increase to 1.5 °C above pre-industrial levels.7
This long-term temperature goal was informed by the evolving scientic
understanding of the impacts associated with different average global temperatures,
including impacts on water availability, extreme weather events, agricultural
yield, species and ecosystems.8 At a political level, the reference to 1.5°C was
also driven by the demands of island states and least developed countries most
vulnerable to the impacts of climate change.9
Some sense of the scale of the emissions reduction challenge implied by the
long-term temperature goal is provided by estimates of the emissions budget that
humanity must stay within to meet that goal. The concept of an emissions budget
(or carbon budget as it is often called)10 is useful because it is cumulative emissions
to the atmosphere, rather than just emissions in a single year, that result in the
atmospheric greenhouse gas concentrations responsible for climate change.11 In
2014, Australia’s Climate Change Authority considered what global emissions
budget would be consistent with a 2°C goal. Drawing on work by Meinshausen et
al,12 the Authority found that:
7 Paris Agreement art 2.
8 Carl-Friedrich Schleussner et al, ‘Science and Policy Characteristics of the Paris Agreement
Temperature Goal’ (2016) 6 Nature Climate Change 827, 827-8.
9 Ralph Bodle, Lena Donat and Matthias Duwe, ‘The Paris Agreement: Analysis, Assessment
and Outlook’ (2016) 10(1) Carbon and Climate Law Review 5 7; Sara Phillips, ‘Paris
Climate Deal: How a 1.5 Degree Target Overcame the Odds at COP21’, ABC Online, 13
December 2015.
10 A carbon budget is literally ‘a mechanism for accounting for the net sources of carbon
to the atmosphere’: R Quentin Grafton et al, A Dictionary of Climate Change and the
Environment: Economics, Science and Policy (Edward Elgar Publishing, 2012) 49.
However the term is often used to refer to global emissions budgets covering all greenhouse
gases: Climate Change Authority, ‘Reducing Australia’s Greenhouse Gas Emissions -
Targets and Progress Review Final Report’ (2014) 47.
11 For an outline of the scientic basis for carbon budgets and the different methods for
their calculation see Joeri Rogelj et al, ‘Differences Between Carbon Budget Estimates
Unravelled’ (2016) 6(3) Nature Climate Change 245.
12 Malte Meinshausen et al, ‘Greenhouse-gas Emission Targets for Limiting Global Warming
to 2 C’ (2009) 458(7242) Nature 1158, 1161.
243
[a] global emissions budget that provides at least a likely (67 per cent
probability) chance of limiting warming to less than 2 degrees above
pre-industrial levels...equates to a global budget of no more than 1,700
Gt CO2-e emissions of Kyoto gases from 2000 to 2050.13
The Authority further found that approximately 36 per cent of this global budget
had already been used between 2000 and 2012.14 Given that this leaves a little
over 1000 Gt CO2-e, and that annual global emissions currently exceed 50 Gt
CO2-e,15 this implies that very substantial emission reductions would be needed
to live within the remaining budget associated with 2°C of warming, let alone a
goal of closer to 1.5°C.
While the long-term temperature goal is at the heart of the Paris Agreement,
Article 4.1 sets out an important supplementary goal:
In order to achieve the long-term temperature goal as set out in Article
2, Parties aim to reach global peaking of greenhouse gas emissions as
soon as possible, recognizing that peaking will take longer for develop-
ing country Parties, and to undertake rapid reductions thereafter in ac-
cordance with best available science, so as to achieve a balance between
anthropogenic emissions by sources and removals by sinks of green-
house gases in the second half of this century... (italics added).
As with the long-term temperature goal, this net-zero emissions goal is a collective
global goal, rather than one that strictly requires each party to achieve net-zero
emissions.16
B The Pledge and Review Mechanism
specic emissions targets. Instead, each party is required to submit its own
nationally determined contribution.18 Under Article 4.2:
13 Climate Change Authority, above n 10, 50.
14 Ibid.
15 In 2014 global greenhouse gas emissions were approximately 52.7 Gt CO2-e (range 47.9-
57.5 with a 90 per cent condence interval): United Nations Environment Program, ‘The
Emissions Gap Report 2016: A UNEP Synthesis Report’ (2016) 3.
16 Daniel Bodansky, ‘The Legal Character of the Paris Agreement’ (2016) 25(2) Review of
European, Comparative & International Environmental Law 142, 146.
for signature 11 December 1997, 2303 UNTS 162 (entered into force 16 February 2005).
18 The difference with the Kyoto Protocol should not be overstated. While the fact that
emission reduction targets were recorded in an annex to the protocol might on the surface
suggest a ‘top-down’ model of targets being imposed on parties, ‘the reality is that ‘bottom
up’ has always been how diplomacy works in a world that has no central government’:
David G Victor, ‘Copenhagen II or Something New’ (2014) 4(10) Nature Climate Change
853 1.
244
Each Party shall prepare, communicate and maintain successive
nationally determined contributions that it intends to achieve. Parties
shall pursue domestic mitigation measures, with the aim of achieving
the objectives of such contributions.
NDCs are to be prepared by all parties, not just developed countries. However,
the content of NDCs will differ. Developed countries ‘should continue taking
the lead by undertaking economy-wide absolute emission reduction targets’ while
developing country parties are ‘encouraged to move over time towards economy-
wide emission reduction or limitation targets in the light of different national
circumstances’.19
While the long-term, collective goals of the Paris Agreement are clear enough,
the agreement provides little guidance as to how the efforts to achieve these goals
should be divided among nations. The closest it comes to outlining such principles
is Article 4.3, which provides that:
Each Party’s successive nationally determined contribution will represent
a progression beyond the Party’s then current nationally determined
contribution and reect its highest possible ambition, reecting its
common but differentiated responsibilities and respective capabilities, in
the light of different national circumstances.
As at October 2017, 160 nations had submitted NDCs, out of a total of 166 parties
that had ratied the Paris Agreement.20 As discussed below, early estimates
suggest that current NDCs are not adequate to meet the Paris Agreement’s goals.
However, the great hope of the Paris Agreement is that successive NDCs will
progressively strengthen mitigation efforts. The architecture of the agreement
seeks to encourage this in a number of ways. Under Article 4.11 a party ‘may
at any time adjust its existing nationally determined contribution with a view to
enhancing its level of ambition...’.21 Parties are also required to communicate an
NDC every ve years.22 Such communications will be informed, in practice, by
the country’s own reporting on progress in implementing its NDCs,23 technical
expert reviews of those reports24 and global stocktakes of collective progress.25
The Paris Agreement seeks to ratchet up the level of ambition in successive NDCs
through the requirements, already noted, of ‘progression’ and ‘highest possible
ambition’.26
country parties as a recommendation rather than a legally binding obligation see Bodansky,
above n 16, 149-150.
20 UNFCCC Secretariat, NDC Registry (Interim)
Pages/Home.aspx> (accessed 2 October 2017).
21 Paris Agreement art 4.11.
22 Ibid art 4.9.
23 Ibid art 13.7.
24 Ibid art 13.11.
25 Ibid arts 4.9, 14. Art 4.9 explicitly provides that NDCs ‘shall...be informed by the outcomes
of the global stocktake ...’.
26 Ibid art 4(3).
245
The ve-yearly cycle of global stocktakes and successive NDCs is illustrated in
Table 1.
TABLE 1: PARIS AGREEMENT TIMETABLE 2018-2030
Year Event
2018 Facilitative dialogue1
2020 Deadline to communicate NDCs2
2023 Global stocktake
2025 Deadline to communicate NDCs
2028 Global stocktake
2030 Deadline to communicate NDCs
The strength of the Paris Agreement’s ratchet mechanism, and specically
the question of whether a party could downgrade the level of ambition in its
NDC, was the subject of debate following the election of President Trump and
speculation as to whether the United States could downgrade its NDC as an
alternative to withdrawing from the Paris Agreement. On one view, it could do
so because ‘higher ambition is not a legal requirement, and Article 4.11 does not
legally prohibit a party from adjusting its NDC in another direction.’27 A different
view has also been strongly argued: that on its proper interpretation, Article
4.11 ‘only countenances upward adjustment of NDCs’.28 It is argued that this
interpretation is consistent with the object and purpose of the Paris Agreement
because it preserves the effectiveness of the ratchet mechanism that is so central
to its successful operation. The alternative, of allowing parties to downgrade their
emission reduction commitments at any time, would undermine the requirement
that each new NDC represent a progression beyond the then current NDC.29
The Paris Agreement does not specify the timeframe for NDCs. Competing
proposals for ve and 10 year NDCs were put forward in negotiations but no
agreement could be reached on a preferred timeframe.30 This question was
effectively deferred to the rst meeting of the parties,31 which further deferred
27 Susan Biniaz and Daniel Bondansky, Legal Issues Related to the Paris Agreement (Center
for Climate and Energy Solutions, May 2017).
28 Lavanya Rajamani and Jutta Brunnée, ‘The Legality of Downgrading Nationally Determined
Contributions under the Paris Agreement: Lessons from the US Disengagement’ (2017)
Journal of Environmental Law 1, 12.
29 Ibid; Jonathon Church, ‘Guest Post: Can the US Legally Weaken its Paris Agreement
Climate Pledge?’ on Carbon Brief (8 May 2017) g/guest-
post-can-the-us-legally-weaken-its-paris-agreement-climate-pledge>; Lavanya Rajamani,
‘The US and the Paris Agreement: In or Out at What Cost?’ on Blog of the European
Journal of International Law (10 May 2017)
paris-agreement-in-or-out-and-at-what-cost/>.
30 Harald Winkler, ‘Mitigation (Article 4)’ in Daniel Klein et al (eds), The Paris Climate
Agreement: Analysis and Commentary (Oxford University Press, 2017) 157.
31 Paris Agreement art 4(10).
246
the question.32 What is clear is that by 2020 parties using a ve-year timeframe
must have communicated NDCs for 2021-2025 and 2026-2030, and parties (such
as Australia) using a 10 year timeframe will need to communicate or update their
2021-2030 NDCs.33 In other words, all parties must have commitments in place
for the 2021-2030 period by this time.
C Two Risks with the Pledge and Review Mechanism
The tragedy of the commons, as described by ecologist Garrett Hardin in
his famous 1968 article,34 provides a useful conceptual lens through which to
consider the dynamics of the Paris Agreement and associated national actions
to reduce greenhouse gas emissions. The metaphor Hardin employs is that of
cattle being grazed on a commons, ‘a pasture open to all’.35 From the perspective
of each herder it makes sense to graze as many cattle as possible, as individual
herders have the full benet of adding another animal but suffer only a fraction of
the costs of over-grazing. However, the net result of these individual decisions is
the degradation, even the destruction, of the pasture. ‘Therein is the tragedy. Each
man is locked into a system that compels him to increase his herd without limit
– in a world that is limited.36 The dynamic described by Hardin has the potential
to apply to any open access resource that can be depleted by overuse. Obvious
examples are shared sheries37 and water resources,38 but the global atmospheric
commons can be, and often has been, viewed in the same way.39
The tragedy of the commons, with its focus on the often-tragic misalignment
of individual incentives and collective interests, contains a powerful lesson for
the implementation of the Paris Agreement. In a comparable way to Hardin’s
herders, every country has a common collective interest in a sustainable outcome
but an individual incentive to do things that will undermine that outcome. This
position was not fundamentally changed by the Paris Agreement. International
endorsement of the long-term temperature goal was a substantial diplomatic
32 Center for Climate and Energy Solutions, Outcomes of the UN Climate Conference in
marrakech/summary> (accessed 17 July 2017).
33 Paris Agreement art 4.9; 1/CP.21[23]-[25].
34 Garrett Hardin, ‘The Tragedy of the Commons’ (1968) 162(3859) Science 12431.
35 Ibid 1244.
36 Ibid.
37 e.g. Alison Rieser, ‘Prescriptions for the Commons: Environmental Scholarship and the
Fishing Quotas Debate’ (1999) 23 Harvard Environmental Law Review 393.
38 e.g. Shol Bluestein, ‘From the Bottom Up: Redesigning the International Legal Response
to Anthropogenic Climate Change’ (2011) 32 Adelaide Law Review 316, 308.
39 e.g. Peter-Tobias Stoll, ‘The Climate as a Global Common’ in Daniel A Farber and Marjan
Peeters (eds), Climate Change Law: Volume 1 (Elgar, 2016) ; Ottmar Edenhofer et al,
Climate Change 2014: Mitigation of Climate Change. Contribution of Working Group
III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change
(Cambridge University Press, 2014); Barton H Thompson Jr, ‘Tragically Difcult: The
Obstacles to Governing the Commons’ (2000) 30 Environmental Law 241, 253.
247
achievement. However agreement on this goal has not, in itself, changed the
incentives of individual countries. It is still the case that ‘[e]very country has
an incentive to shirk, to free-ride on the efforts of others’40 with respect to their
contribution to the collective goal. These ‘others’ include both other countries and
future generations.
There is a very real risk that this incentive will manifest itself in two ways, in either
case leading to a tragedy of the global atmospheric commons. The rst risk is that
NDCs will not, even if fully implemented, be sufcient to achieve the temperature
goal. While countries have agreed on a global goal, there is still an incentive to
free-ride by making inadequate contributions towards achieving it.41 Given that
there are no clear principles in the Paris Agreement for translating the global goals
to national commitments, there is considerable scope for this to occur. This free-
riding has the potential to manifest itself in a myriad of ways, from the adoption
of convenient assumptions about business-as-usual emissions,42 to the use of
economic modelling that exaggerates the costs of achieving mitigation targets, 43
to the identication of ‘special’ national circumstances to justify modest targets.44
The early evidence suggests that we are heading down a path of inadequate
national commitments. The United Nations Environment Program’s Emissions
Gap Report (2016) found that existing mitigation commitments amount to about
a quarter of what is needed to stay below 2oC and are in fact consistent with
a 3-3.2oC increase in average global temperature above pre-industrial levels by
2100.45 The great hope of the Paris Agreement is that successive NDCs will
represent an ‘upward spiral of ambition’46 to bridge the gap between what has
been committed and what is required, but it remains to be seen whether this can
40 Robert O Keohane and Michael Oppenheimer, ‘Paris: Beyond the Climate Dead End
Through Pledge and Review?’ (2016) 4(3) Politics and Governance 142 2; Richard Cooper
et al, ‘Why Paris Did Not Solve the Climate Dilemma’ in Peter Cramton et al (eds), Global
Carbon Pricing: The Path to Climate Cooperation (The MIT Press, 2016).
41 Keohane and Oppenheimer, above n 42, 2.
42 This is especially important for countries using business-as-usual projections as part
of their baseline – e.g. Korea has set a target to reduce emissions by 27 per cent below
business-as-usual levels by 2030. A generous estimate of business-as-usual levels would
make it easier to achieve that target.
43 Andrew Macintosh, ‘Mitigation Targets, Burden Sharing and the Role of Economic
Modeling in Climate Policy’ (2013) 73 Australian Journal of Public Administration 164.
44 Eckersley, Robyn ‘Climate Leadership Before and After the Paris Agreement’ (Public
Lecture, London School of Economics, 16 November 2016)
GranthamInstitute/ event/public-lecture-climate-leadership-before-and-after-the-paris-
agreement/> (‘there is an ever-present danger of self-differentiation degenerating into a
self-serving apology for a defence of national interests narrowly conceived’).
45 United Nations Environment Program, above n 15, xvi-xvii. See also Joeri Rogelj et al,
‘Paris Agreement Climate Proposals Need a Boost to Keep Warming Well Below 2 C’
(2016) 534(7609) Nature 631 (analysis based on intended NDCs submitted in the lead
up to the Paris Agreement estimating an increase of 2.6–3.1 degrees Celsius above pre-
industrial levels by 2100 if these commitments are fully implemented).
46 Ad Hoc Working Group on the Durban Platform. Parties’ Views and Proposals on the
Elements for a Draft Negotiating Text ADP.2014.6 (UNFCCC, 2014), cited in David
MacKay et al, ‘Price Carbon - I Will if You Will’ (2015) 526 Nature 315, 315.
248
be achieved in the face of strong free-riding incentives.
The second risk is that adequate domestic measures to achieve NDCs will
not be adopted and implemented – a form of free-riding through inadequate
implementation. It is important to note, in this regard, that the Paris Agreement
does not impose hard penalties or sanctions for non-compliance. While the
agreement does create what it calls ‘[a] mechanism to ... promote compliance’,
that mechanism takes the form of a ‘non-punitive’ and ‘facilitative’ expert
committee that reports annually to the Conference of the Parties.47 At most,
there would adverse reputational consequences for parties that are found by this
expert committee to have breached the broad duty to ‘pursue domestic mitigation
measures, with the aim of achieving the objectives [of NDCs]’.48 There is also
limited scope for independent resolution of disputes concerning interpretation or
governments may be tempted to accept the reputational costs of failing to meet
an NDC over the economic and political costs they may face in implementing
effective emission reduction measures.
While there are substantial incentives for free-riding through inadequate targets
and implementation, there are also forces pulling in the other direction. It would
be a mistake to assume countries will always be looking for ways to free-ride
on the efforts of others. Some nations will be driven by electorates that take a
moral stance on the issue, rather than narrowly conceived assessments of national
self-interest.50 Other nations will be motivated hard-headed assessments of the
co-benets of taking action – such as the economic, health and other benets of
replacing fossil fuels with renewable energy.51 While it is true that free-riding by
climate laggards can undermine the Paris Agreement, it is also possible that action
by climate leaders could provide the basis for a ‘virtuous cycle of reciprocation’
between nations.52
47 Paris Agreement art 15.
48 Ibid art 4(2).
49 While the Paris Agreement and UNFCCC allow parties to submit to the jurisdiction of
the International Court of Justice or an arbitral body with respect to settlement of disputes
of this kind, there is no requirement to do so: Paris Agreement art 24; UNFCCC, art 14.
Australia has not done so: Australian Government, National Interest Analysis [2016]
ATNIA 10 (2016) [53].
50 David M. McEvoy and Todd L. Cherry, ‘The prospects for Paris: behavioral insights into
unconditional cooperation on climate change’ (2016) 2 (08/16/online) 16056 1 (presenting
survey evidence from the United States that most Americans support domestic action on
climate change that is not conditional on other countries’ commitments, and that this is
‘driven by notions of responsibility, morality and global leadership’).
51 Fergus Green, Nationally Self-Interested Climate Change Mitigation: A Unied Conceptual
Framework (2015, Grantham Research Institute) 1 (arguing that climate change is mostly
not a tragedy of the commons problem because ‘the majority of emissions reductions
needed to decarbonise the global economy can the achieved in ways that are net-benecial
to countries’ and that ‘the barriers to mitigation action lie, primarily, not in the macro-
incentive structures of states...but rather within the domestic sphere, at the intersection of
domestic interests, institutions and ideas formed in the fossil fuel age’).
52 Stefano Carattini, Simon Levin and Alessandro Tavoni, Cooperation in the Climate
249
In the face of opposing forces for free-riding and climate leadership, will the
pledge-and-review mechanism end in a ‘positive spiral of strengthening trust
and enhanced cooperation’ or ‘a downward spiral of weakening trust and lower
ambition’?53 While only time will tell, one thing is clear: that the more hopeful
scenario will be more likely to be realised if parties’ domestic rules promote
principled target-setting and effective implementation. The next section considers
one regulatory strategy with the potential to achieve these goals and so support the
Paris Agreement’s pledge-and-review mechanism.
II FRAMEWORK LEGISLATION FOR CLIMATE
CHANGE MITIGATION
A The Emergence of Framework Legislation
How can domestic laws guide the setting of responsible national emission
reduction targets and help ensure that these targets are achieved? One way to
do so is to directly address these questions in domestic law through ‘framework
legislation’ for climate change mitigation.54 The value of such legislation has been
highlighted in publications by the Grantham Institute and Inter-Parliamentary
Union,55 but has been largely overlooked in the Australian policy debate.56 For
Commons (Grantham Research Institute on Climate Change and the Environment, 2017)
2. On the need for trust and reciprocity see Elinor Ostrom, ‘A Polycentric Approach for
Coping with Climate Change’ (2014) 15(1) Annals of Economics and Finance; Daniel
H. Cole, ‘Advantages of a Polycentric Approach to Climate Change Policy’ (2015) 5(2)
Nature Climate Change 114.
53 Robert Falkner, ‘The Paris Agreement and the New Logic of International Climate Politics’
(2016) 92(5) International Affairs 1107, 1121.
54 Michal Nachmany et al, ‘The 2015 Globe Climate Legislation Study: A Review of Climate
Change Legislation in 99 Countries’ (Grantham Research Institute on Climate Change
and the Environment, GLOBE and Inter-Parliamentary Union, 2015) 13 (‘Framework
legislation has been dened as a law or regulation with equivalent status, which serves as a
comprehensive, unifying basis for climate change policy, which addresses multiple aspects
or areas of climate change mitigation or adaptation (or both) in a holistic, overarching
manner.’) Legislation sharing some of these features has also been described as ‘emissions
reduction target legislation’ or ‘agship legislation’: see Rob Fowler, ‘Emission Reduction
Targets Legislation’ in Tim Bonyhady and Peter Christoff (eds), Climate Law in Australia
(The Federation Press, 2007) 104 (using the term ‘emissions reduction target legislation’
to describe legislation that incorporates ‘emission reduction targets and timetables’); Terry
Townshend et al, ‘How National Legislation Can Help to Solve Climate Change’ (2013)
3(5) Nature Climate Change 430 (describing a ‘agship law’ as ‘a piece of legislation or
regulation with equivalent status that serves as a comprehensive, unifying basis for climate
change policy’).
55 Alina Averchenkova and Samuela Bassi, ‘Beyond the Targets: Assessing the Political
Credibility of Pledges for the Paris Agreement’ (2016); Alina Averchenkova and Sini
Matikainen, ‘Assessing the Consistency of National Mitigation Actions in the G20 with
the Paris Agreement’ (2016) 6, 17, 22; Nachmany et al, above n 54, 13.
56 An exception is the submission by the Environmental Defender’s Ofces of Australia to the
Commonwealth Government’s review of climate policies: EDOs of Australia, Submission
on Australia’s Climate Change Policy Review, 5 May 2017 .environment.
gov.au/submissions/climate-change/review-climate-change-policies-2017/environmental-
defenders-ofces-of-australia-edoa.pdf>.
250
example, a major report published by Australia’s Climate Change Authority
following the Paris Conference focused exclusively on the ‘toolkit’ of policy and
regulatory measures that should be available to the Australian Government, and
did not consider the higher level question of what overarching framework should
guide successive governments in setting, planning for and achieving its emission
reduction targets.57
The concept of entrenching national or sub-national greenhouse gas emission
reduction targets in legislation (or in instruments made under legislation) pre-dated
the Paris Agreement, but is, nevertheless, a relatively recent policy innovation.
Writing in 2007, Fowler observed that ‘[w]hile the need for targets and timetables
with respect to greenhouse emissions reductions has been recognised for many
years, it is only most recently that the idea of enshrining targets within legislation
has been pursued.’58 Noting a urry of proposals for legislation of this kind being
debated in Europe, the United Kingdom, Canada and South Australia in March
2007, Fowler suggested that these proposals ‘may be part of a wider trend to
develop such legislation in many jurisdictions over the next few years.’59 This
prediction has been borne out by subsequent events. Legislation that contains
national emission reduction targets, or establishes a process for setting such
targets, has now been enacted in the United Kingdom (2008), New Zealand
(2008), South Korea (2010), Austria (2011), Mexico (2012), Switzerland (2013),
Bulgaria (2014), Denmark (2014), Finland (2015), France (2015), Norway (2017)
and Sweden (2017).60 A number of sub-national parliaments have also passed
legislation of this kind, including in Australia, 61 the United States62 and Canada.63
57 Climate Change Authority, ‘Towards a Climate Policy Toolkit: Special Review on
Australia’s Climate Goals and Policies’ (Commonwealth of Australia, 2016).
58 Fowler, above n 54, 120.
59 Ibid.
60 London School for Economics and Grantham Institute, Climate Change Laws of the
World (accessed 29 September 2017) < http://www.lse.ac.uk/GranthamInstitute/climate-
change-laws-of-the-world >; Boot, Pieter Climate Legislation in Europe: Work In Progress
(19 June 2017) http://eeac.eu/wp-content/uploads/2016/04/Presentation-Pieter-Boot-
climate-legislation-June-2017-2.pdf>; Government Ofces of Sweden, ‘Riksdag Passes
Historic Climate Policy Framework’ (15 June 2017)
releases/2017/06/riksdag-passes-historic-climate-policy-framework/>. New Zealand is
listed as having adopted emission reduction target legislation in 2008 because s 224 of the
Climate Change Response Act 2002 (NZ), which provides for the gazettal of targets, was
inserted by legislative amendment in 2008: Climate Change Response (Emissions Trading)
Amendment Act 2008 (NZ) s 50.
61 Climate Change and Greenhouse Emissions Reduction Act 2007 (SA); Climate Change
(State Action) Act 2008 (Tas); Climate Change and Greenhouse Gas Reduction Act 2010
(ACT) s 6; Climate Change Act 2017 (Vic).
62 Center for Climate and Energy Solutions, Greenhouse Gas Emissions Targets (August
2016)targets>
(identifying States with legislated targets as Maine, Connecticut, California, Vermont,
Minnesota, New Jersey, Oregon, Washington, Hawaii and Maryland).
63 e.g. Greenhouse Gas Reductions Targets Act, SBC 2007, c 42; Climate Change and
Emissions Management Act, SA 2003, c 16.7; Climate Change and Emissions Reductions
Act SM 2008 c 17; Environmental Quality Act SQ 2015 c 12; Climate Change Mitigation
and Low-Carbon Economy Act, SO 2016 c 7.
251
B The Functions of Framework Legislation
While the contents of these laws differ, it is possible to identify four main functions
that can be served by framework legislation for climate change mitigation.
First, it can provide a transparent and principled way to set emission reduction
targets. Where targets are directly specied in the legislation, there will at least
be an assurance of parliamentary scrutiny. Where targets are set under delegated
authority, a number of different techniques can be used to ensure transparent and
principled decision-making. These can include a requirement for a decision-maker
to apply, or take into account, specied principles or considerations; requirements
to obtain and publish independent advice; and requirements to engage in public
consultation.
Second, by setting statutory targets rather than just policy-based targets, framework
legislation can signal a greater level of commitment to emission reduction goals.
This is recognised, for example, in the Grantham Institute’s assessment of the
political credibility of intended NDCs submitted prior to the Paris Conference,
which draws a distinction between ‘targets that are formally anchored in laws
passed by parliaments or executive regulation enacted by governments’ and
‘targets that are only included in non-mandatory documents (e.g. white or green
papers), in government announcements (e.g. a speech by a head of state) or
recorded in voluntary international agreements, but not enshrined in national
legislation’.64 Statutory targets are seen to ‘strengthen policy credibility because
they are mandated by law and therefore, in principle, are much more difcult to
breach or revise’.65
Third, framework legislation can facilitate planning for greenhouse gas mitigation,
including through coordination of regulatory mitigation tools. As Peel correctly
identied in 2008, ‘climate change regulations have tended to be adopted in
an ad hoc fashion, rather than as part of a coordinated system or strategic plan
oriented towards the achievement of particular goals’.66 Legislation that requires
governments to plan for how emission reduction targets will be achieved can
address this problem by ensuring a more coordinated and strategic approach.67 In
this way, climate change mitigation laws can catch up with other more established
areas of environmental law – such as the law concerning the management of water
resources, sheries and (to some extent) ambient air quality – where the use of
planning instruments already plays an important role in identifying precise goals
and coordinating the use of measures to achieve them.
64 Averchenkova and Bassi, above n 55, 15.
65 Ibid.
66 Jacqueline Peel, ‘Climate Change Law: The Emergence of a New Legal Discipline’ (2008)
32 Melbourne University Law Review 922; see also Alexander Zahar, Jacqueline Peel and
Lee Godden, Australian Climate Law in a Global Context (Cambridge University Press,
2013) 7.
67 Michael Mehling, ‘Implementing Climate Governance: Instrument Choice and Interaction’
in Climate Change and the Law (Springer, 2013) 23-28.
252
Fourth, emission reduction legislation can create accountability mechanisms that
increase the likelihood of targets being met. As Fowler points out:
There is very little point in incorporating emission reduction targets in
legislation, rather than in a policy instrument, unless the relevant legisla-
tion provides for mechanisms that can hold governments accountable for
the delivery of the relevant targets.68
Mechanisms that provide a measure of political accountability include
requirements for independent advisory bodies or elected ofcials to report
publicly on progress towards achieving targets. The use of statutory targets, with
associated duties and discretions, also opens up the possibility of enabling legal
accountability through the courts.69
C Framework Legislation and the Paris Agreement
The Paris Agreement gives further impetus for the enactment of framework
legislation that performs the functions outlined in the preceding section. Framework
legislation can provide greater credibility to NDC commitments by embedding
them in domestic law, together with planning and accountability requirements.
Such legislation can also promote a principled and transparent approach to setting
the emission reduction targets contained in NDCs. In these ways, the continuing
diffusion of framework legislation among parties to the Paris Agreement has the
potential to help underpin the most positive scenario for the pledge-and-review
mechanism: one of ambitious targets, effective implementation and the realisation
of the Paris Agreement’s goals.
The architecture of the Paris Agreement has some important implications for
the design of future framework legislation. One issue is the alignment between
the target-setting provisions in framework legislation and the Paris Agreement’s
pledge-and-review timetable. The ve-year pledge-and-review cycle suggests
that rather than legislating xed targets well in advance, some exibility
should be retained to set the ambition of targets following global stocktakes.
This would not preclude a long-term legislated emission reduction targets, nor
‘guardrail’ minimum targets along the way. But it would not be consistent with
the pledge-and-review cycle to set a xed target trajectory, with no discretion for
governments to commit to more ambitious targets in the light of information from
global stocktakes. Table 2 provides an example of how the Paris Agreement’s
requirements for communicating NDCs could be aligned with target-setting
requirements in framework legislation.
68 Fowler, above n 54, 118. See also Sarah Waddell, ‘By How Much Will A ‘Price on Carbon’
Actually Lower Australia’s Emissions?: Towards Climate Accountability for Greenhouse
Gas Emissions Abatement’ (2013) 16(1) Australasian Journal of Natural Resources Law
and Policy 1.
69 Fowler, above n 56, 118.
253
TABLE 2: AN EXAMPLE OF TARGET-SETTING ALIGNED WITH THE
PARIS AGREEMENT
Year Paris Agreement requirement National framework legislation
By 2020 Communicate NDCs to 2030 Targets for 2021-2025 and 2026-2030
By 2025 Communicate NDCs to 2035 Target for 2031-2035
By 2030 Communicate NDCs to 2040 Target for 2036-2040
By 2035 Communicate NDCs to 2045 Target for 2041-2045
By 2040 Communicate NDCs to 2050 Target for 2045-2050
Another important question concerns amendments to targets. As we have seen,
the Paris Agreement provides that NDCs may be amended at any time with a view
to increasing their level of ambition, but there are opposing legal arguments as to
whether parties can downgrade the level of ambition in their NDCs. This question
will need to be considered in the drafting of any provision in national framework
legislation concerning amendments to emission reduction targets. A clear statutory
prohibition on amending targets to reduce their level of ambition would help build
state practice that supports the Paris Agreement’s ratchet mechanism.
The Paris Agreement’s long-term temperature and net-zero emissions goals also
need to be considered in the development of national framework legislation. One
difcult issue here is how the long-term temperature goal can help guide national
target-setting. Some ideas can be drawn from existing framework legislation.
One approach is to require the target-setting decision-maker, on advice from
an independent and expert body, to consider whether targets are consistent with
staying within a national emissions budget. This helps to address the issue of
intergenerational equity, as emissions budgets clarify trade-offs: if more of the
budget is used in the next NDC cycle, less will be available for future periods.
Combined with this requirement, decision-makers could be required to confront
the question of what national carbon budget would represent a fair contribution,
relative to the contribution of other nations, to the global temperature goal.
The target-setting provisions of the Climate Change (Scotland) Act 2009 provide
a helpful example of how this can be done. Under that Act, Scottish Ministers
are required, when setting annual targets, to have regard to ‘the objective of
not exceeding the fair and safe Scottish emissions budget’.70 The ‘fair and safe
Scottish emissions budget’ is dened as
the aggregate amount of net Scottish emissions for the period 2010–
2050 recommended by the relevant body as being consistent with
Scotland contributing appropriately to stabilisation of greenhouse gas
concentrations in the atmosphere at a level that would prevent dangerous
70 Climate Change (Scotland) Act 2009 s 4(4)(a).
254
anthropogenic interference with the climate system.71
If the reference to dangerous anthropogenic interference with the climate system
long-term temperature goal, these provisions could provide a good starting point
for a principled approach to translating this goal into national targets.
The task of translating global goals to a national level is simpler for the net zero
emissions goal.72 Legislative action in the short period since the adoption of the
Paris Agreement underlines that this can be done relatively easily. The Australian
Capital Territory and Victoria enacted legislation in 2016 and 2017 respectively
with targets for net-zero emissions by 2050.73 As statements by responsible
Ministers make clear, these legislated targets are intended to align with the net
zero emissions goal in the Paris Agreement.74 Sweden has gone even further,
with a framework law that endorses a goal of net zero emissions by 2045.75
Experience with existing framework legislation shows that long-term national
targets of this kind can assist in guiding the setting of shorter-term emissions
reduction targets. The Climate Change Act 2008 (UK) provides a good example.
Under this Act, ve-year emission reduction targets, in the form of carbon budgets,
must be developed by the Secretary of State ‘with a view to meeting’ legislated
2020 and 2050 targets.76 These carbon budgets must be set having regard to
the recommendations of an independent, expert advisory body, the Committee
on Climate Change.77 In practice, the common thread running through the
Committee’s carbon budget recommendations has been to identify a feasible and
cost-effective path to the 2020 and 2050 targets.78 The Committee has considered
71 Ibid s 4(6).
72 Oliver Geden, ‘An Actionable Climate Target’ (2016) 9(5) Nature Geoscience 340.
73 Renewable Energy Legislation Amendment Act 2016 (ACT) s 4 (amending the Climate
Change and Greenhouse Gas Reduction Act 2010 (ACT) s 6); Climate Change Act 2017
(Vic) s 6.
74 Simon Corbell MLA, ‘ACT Commits to Zero Emissions by 2050’ (Media Release, 3 May
2016); Australian Capital Territory, Parliamentary Debates, Legislative Assembly, 3 May
2016, 1376 (Simon Corbell); Victoria, Parliamentary Debates, Legislative Council, 7
February 2017, 23 (Philip Dalidakis).
75 UN Climate Change Newsroom, ‘Sweden Plans to Be Carbon Neutral by 2045: New
Legislation Sets Goal 5 Years Earlier than Originally Agreed’ (19 June 2017)
newsroom.unfccc.int/unfccc-newsroom/sweden-plans-to-be-carbon-neutral-by-2045/>.
76 Climate Change Act 2008 (UK) s 8.
77 Ibid ss 9, 34(1)(a).
78 Climate Change Committee, The Fifth Carbon Budget: The Next Step Towards a Low-
Carbon Economy (Committee on Climate Change, 2015) 13; Committee on Climate
Change, The Fourth Carbon Budget Review – Part 2: The Cost Effective Path to the 2050
Target (Committee on Climate Change, 2013) 10-11; Committee on Climate Change,
Building a Low-Carbon Economy – The UK’s Contribution to Tackling Climate Change
(Committee on Climate Change, 2008) xviii. On the prominence of the 2050 target in the
Climate Change Act 2008 (UK), and the implications for interpretation of other provisions
of the Act, see Jonathan Church, ‘Enforcing the Climate Change Act’ (2015) 4 UCL
Journal of Law and Jurisprudence 109, 111-12.
255
this question carefully, informed by numerical simulation models that identify
cost-effective paths to meet the targets with given assumptions about technology
cost and availability.79 While a political judgment might favour deferring emission
reductions to later years, the technocratic Committee has recommended ‘a swift
pace of emission reductions in the power sector and an overall abatement path
that is only slightly back-loaded’.80 This advice has been accepted by successive
governments when setting carbon budgets.
The discussion to date suggests that widespread adoption of framework
legislation, aligned with the goals and processes of the Paris Agreement, could
play an important role in overcoming some of the weaknesses with the pledge-
and-review mechanism. This is not, of course, to suggest that a series of cut-and-
paste legal transplants will get the job done. Framework legislation will need
to be designed having regard to each jurisdiction’s particular governmental and
political context.81 In the next section we turn to consider three of the important
design issues in an Australian context.
III DESIGN ISSUES FOR AUSTRALIAN FRAMEWORK
LEGISLATION
A Constitutional Basis for the Legislation
A threshold question for any Commonwealth legislation is whether it is supported
by one or more of the heads of power in section 51 of the Constitution. I consider
below two heads of power with the potential to support national framework
legislation in Australia: the external affairs power (section 51 (xxix)) and the
incidental power (section 51(xxxix)).
Section 51(xxix) of the Constitution empowers the Commonwealth Parliament
‘to make laws ... with respect to ... external affairs’. In order to consider the scope
of the external affairs power in the present context, it is necessary to review the
nature of Australia’s relevant international obligations. The starting point is the
UNFCCC, which is, as its name suggests, a framework convention imposing
broad obligations on parties to the convention. These include obligations to
formulate programmes with measures to address anthropogenic sources and
sinks; to communicate policies and measures it has adopted; to estimate the effect
that these policies and measures will have; and to maintain a national greenhouse
gas inventory.82 The Kyoto Protocol establishes a more precise and detailed
regime for a relatively small number of countries, including Australia. It sets
79 Samuel Fankhauser, ‘A Practitioner’s Guide to a Low-Carbon Economy: Lessons from the
UK’ (2013) 13(3) Climate Policy 345, 347.
80 Ibid 348.
81 Alan Watson, ‘Legal transplants and Law Reform’ (1976) 92 Law Quarterly Review 79,
81-2.
82 UNFCCC arts 4.2, 12
256
binding emission reduction targets, together with a regime to track compliance
and impose sanctions for non-compliance. The Paris Agreement creates a more
inclusive post-2020 regime to succeed the Kyoto Protocol, applying to the vast
majority of nations. However, the obligations imposed by the Paris Agreement
return to the more general language of the UNFCCC, avoiding top-down targets
and detailed implementation obligations in favour of procedural obligations to
submit NDCs and a general obligation for parties to ‘pursue domestic measures,
with the aim of achieving the objectives’ of NDCs.83
On one view, this is a signicant barrier to the enactment of national climate
change legislation relying on the external affairs power. Pillai and Williams’
analysis of the UNFCCC supports this view. They argue that under the external
affairs power ‘the treaty that the statute seeks to implement must embody precise
obligations that are capable of implementation’ and that the UNFCCC, which they
characterise as ‘purely aspirational’, fails this test. 84
Given the expiry of Australia’s emission reduction obligations under the Kyoto
Protocol and strong parallels between the obligations imposed by the UNFCCC and
the Paris Agreement, this analysis, if correct, could have signicant implications
for Commonwealth legislative powers with respect to climate change post-2020.
Indeed, it could have implications for the operation of all Commonwealth climate
change legislation since 1 January 2013. This is because the Doha Amendment
to the Kyoto Protocol,85 which would extend the operation of the Kyoto Protocol
to a second commitment period (2013-2020), has not yet attracted sufcient
ratications to come into effect.86 If the use of the external affairs power does
Administration. It sought to strictly limit substantive obligations going beyond existing
requirements of the UNFCCC, so as to argue that the agreement was not a treaty within the
meaning of that term in the US Constitution, and therefore did not require the concurrence
of two-thirds of the US Senate: Bodansky, above n 16, 149-150; Hari M Osofsky and
Jacqueline Peel, ‘Energy Partisanship’ (2016) 65 Emory Law Journal 695 779; Margaretha
Wewerinke-Singh and Curtis Doebbler, ‘The Paris Agreement: Some Critical Reections
on Process and Substance’ (2016) 39(4) University of New South Wales Law Journal 1486,
1495-6.
84 Sangeetha Pillai and George Williams, ‘Commonwealth Power and Environmental
Management: Constitutional Questions Revisited’ (2015) 32(5) Environmental and
Planning Law Journal 395, 399, citing Victoria v Commonwealth (1996) 187 CLR 416 at
486. Appleby has gone even further, to suggest that the Carbon Credits (Carbon Farming
Initiative) Act 2011 (Cth), as amended in 2014, is not supported by the Kyoto Protocol
because the Kyoto Protocol ‘does not specify the way parties must reach their emissions
target, providing only an indicative list of policies and measures’: Gabrielle Appleby,
‘Explainer: is Direct Action Constitutionally Valid?’, The Conversation (3 November 2014)
(citing Pape v Commissioner of Taxation [2009] HCA 23, [372] (Hayne and Kiefel JJ)).
85 Doha Amendment to the Kyoto Protocol, opened for signature 8 December 2012, [2016]
ATNIF 24 (not yet in force).
86 As at 2 October 2017, 82 countries, including Australia, had ratied or otherwise accepted
the Doha Amendment: United Nations Framework Convention on Climate Change.,
Status of the Doha Amendment (2 October 2017)
257
depend on the existence of binding limits under the Kyoto Protocol, then
Australia’s existing climate laws would have lacked that constitutional support
since the end of the rst commitment period.87
However, I suggest that neither the Paris Agreement, nor for that matter the
UNFCCC, can properly be described as ‘purely aspirational’. Both are treaties,
in the sense of being ‘an international agreement concluded between States in
written form and governed by international law...’.88 Both impose at least some
legally binding obligations on parties. In the case of the Paris Agreement,
these include obligations to prepare and communicate NDCs, pursue associated
domestic mitigation measures, and provide information for the purpose of
tracking NDC implementation. These treaties are, therefore, distinguishable from
other international instruments, such G20 declarations, which might be properly
classied as purely aspirational and insufcient to invoke the external affairs
power.89
While the application of the external affairs power does not fall at this rst
hurdle, there will still be the important question of whether any law that relies
on it is ‘reasonably capable of being considered appropriate and adapted to
implementing’90 the Paris Agreement. I suggest that a Commonwealth law which
guides the development, implementation and monitoring of Australia’s emission
reduction commitments would be likely to be viewed as appropriate and adapted
to the implementation of Australia’s obligations under the Paris Agreement. The
external affairs power extends beyond direct implementation of treaty obligations
to matters reasonably incidental to that implementation.91 These matters are
reasonably incidental to Australia’s obligations to communicate NDCs, take
domestic measures to implement them, and report on progress.
doha_amendment/items/7362.php>. Under articles 20 and 21 of the Kyoto Protocol, three
quarters of the parties to the protocol (144 parties) need to accept the amendment before
it will come into force.
87 On the difculties with relying on the external affairs power between ratication and
entry into force of a treaty see Donald R Rothwell, ‘The High Court and the External
Affairs Power: A Consideration of its Outer and Inner Limits’ (1993) 15 Adelaide Law
Review 209 225-226; Alice De Jonge, ‘Australia’ in Dinah Shelton (ed), International Law
and Domestic Legal Systems: Incorporation, Transformation, and Persuasion (Oxford
University Press, 2011) 33.
88 Vienna Convention on the Law of Treaties, opened for signature 23 May 1969, 1115
UNTS 331 (entered into force 27 January 1980) art 2 (dening a treaty as ‘an international
agreement concluded between States in written form and governed by international law...’;
Bodansky, above n 16, 144-145.
89 Compare Pape v Federal Commissioner of Taxation (2009) 238 CLR 1; [2009] HCA 23,
[476]-[478] (Heydon J) (regarding a G20 declaration); discussed in Pillai and Williams,
above n 84, 399-400.
90 Victoria v Commonwealth (1996) CLR 416, 486; [1996] HCA 56, [34] (joint judgment of
Brennan CJ, Toohey, Gaudron, McHugh and Gummow JJ).
91 Richardson v Forestry Commission (1988) 164 CLR 261; Sarah Joseph and Melissa
Castan, Federal Constitutional Law: A Contemporary View (Lawbook, 2014) 139.
258
The incidental power provides further support for the conclusion that the
Commonwealth Parliament can enact framework legislation. Section 51(xxxix)
of the Constitution relevantly provides that the Parliament shall have power
‘to make laws ... with respect to ... matters incidental to the execution of any
power vested by this Constitution ... in the Government of the Commonwealth.’
The power to make laws incidental to the exercise of executive power extends
beyond facilitation to ‘legislative regulation of the manner and circumstances
of the execution of the executive power of the Commonwealth’.92 It forms part
of a ‘constitutional scheme ... designed to provide mechanisms for control and
accountability of executive action.’93 The incidental power is especially relevant
to framework legislation of the kind discussed in this chapter because this
legislation is specically directed towards control and accountability of executive
action – specically, executive action that has long been undertaken by Ministers
and civil servants to develop emission reduction targets and plans to achieve those
target.94 The use of the incidental power to regulate actions undertaken by the
Commonwealth and Commonwealth agencies is supported by past legislative
practice.95 It provides an alternative constitutional basis, in addition to the external
affairs power, to support framework legislation.
B Parliament’s Role in Setting Emission
Reduction Targets
Australia has long suffered from sharp political divisions over climate change
policy. However, there are some reasons to hope that national framework legislation
could command bipartisan support. Both major political parties support Australia’s
ratication of the Paris Agreement. In this context, legislation that provides a
92 Plaintiff M68/2015 v Minister for Immigration and Border Protection [2016] HCA 1 [122]
(Gageler J).
93 Dan Meagher et al, Hanks’ Australian Constitutional Law: Materials and Cmmentary
(LexisNexis, 2016) 852.
94 An early example is the Hawke and Keating Governments’ endorsement of the Toronto
Targets and the preparation, together with the States and Territories, of the National
Greenhouse Response Strategy (1992).
95 One example is the Gene Technology Act 2000 (Cth), which regulates dealings with
genetically modied organisms – including, for example, release of genetically modied
organisms by the Commonwealth Scientic and Industrial Research Organisation.
The section outlining the constitutional basis of Gene Technology Act 2000 (Cth) cites
the application of a law to ‘the Commonwealth and Commonwealth agencies’ as a
separate basis for the operation of the Act, in addition to its application to constitutional
corporations and constitutional trade and commerce: Gene Technology Act 2000 (Cth) s
13. A second example is the Water Act 2007 (Cth), which provides for the preparation
and implementation of the Basin Plan, a water resource management plan for the Murray-
Darling Basin. The Act imposes an unqualied duty on agencies of the Commonwealth to
perform their functions, and exercise their powers, consistently with that plan. However,
duties on other agencies and persons to act in accordance with the plan are limited by the
scope of relevant heads of power – for example the duty applying to other agencies and
persons ‘imposes an obligation to the extent to which imposing the obligation gives effect
to a relevant international agreement’: Water Act 2007 (Cth) ss 34-36.
259
framework for meeting Australia’s obligations under that agreement, rather than
dictating that particular emission reduction targets or mitigation measures be
adopted, should be able to attract support from both major parties. Among other
things, it should be possible to reach agreement on replacing Australia’s current ad
hoc arrangements for setting emission reduction targets with a more predictable
statutory framework governing the form of targets, when targets are set, target
timeframes, and the consultation and evidence-gathering process leading up to
target-setting decisions. It may even be possible for agreement to be reached on
a long-term net zero emissions goal.
However, there is potential for differences over some of target-related issues,
including one important question we will focus on here: the role of the Australian
Parliament in endorsing emission reduction targets. There is no uniform practice
in existing framework legislation on the question of Parliamentary involvement
in target-setting. For example, while in the United Kingdom both Houses of
Parliament must approve ve-year carbon budgets, in Victoria the parliament
has no decision-making role with respect to ve-year emission reduction targets.
The Victorian legislation requires the responsible Minister to table independent
advice concerning a forthcoming carbon budget,96 thus opening up the possibility
of parliamentary debate on the issue, but this is as far as the Victorian Act goes.
As a matter of law, the likely default position is that a target determination in
Commonwealth framework legislation will be a legislative instrument, within the
meaning of that term in the Legislation Act 2003 (Cth), and therefore subject
to disallowance. Such a determination is an instrument made under a power
delegated by Parliament.97 It clearly applies generally rather than determining the
application of the law in a particular case.98 Assuming that targets are given legal
effect, for example through a duty on the responsible Minister to achieve the target
or to produce plans directed to that end, they would also have ‘the direct or indirect
effect of ... imposing an obligation’.99 All of the elements of the denition of
‘legislative instrument’ would therefore be satised, and the target determination
would be disallowable unless the framework Act specically provided that such
determinations were not legislative instruments,100 or the operation of section
42 of the Legislation Act 2003 (Cth) concerning disallowance were expressly
excluded.101 The classication of emission reduction target determinations as
legislative instruments subject to disallowance would be consistent with the
approach adopted to date for Commonwealth ambient air quality standards,102
96 Climate Change Act 2017 (Vic) s 13(1).
97 Legislation Act 2003 (Cth) s 8(4)(a).
98 Ibid s 8(4)(b).
99 Ibid s 8(4)(c).
100 Ibid s 8(6)(a).
101 Ibid s 44(2).
102 National Environment Protection Council Act 1994 (Cth) s 21; National Environment
Protection (Ambient Air Quality) Measure (Cth).
260
water resource management plans103 and sheries management plans.104
In the partisan Australian political context, the practical implications of granting
the Senate an effective veto over Australian emission reduction targets needs to
be considered. This is, of course, a very real possibility, because the Senate is very
often not under the control of the party in government.105 If target determinations
were disallowable legislative instruments, consideration could be given to setting
a default set of target determinations in the legislation, to avoid a deadlock
situation in which no targets could be made. There is a precedent for this, in the
default national emission caps in the Clean Energy Act 2011 (Cth) (repealed).106
Pursuing a process of Parliamentary involvement raises the interesting question of
whether a target endorsed under national framework legislation could or should
impose a legal constraint on the Australian Government’s communication of
NDCs under Article 4 of the Paris Agreement. As a matter of law, it is likely
that it could. Even if under the Constitution the Commonwealth Executive has
‘an exclusive power to assume international obligations’107 and, for that reason,
the exclusive power to communicate NDCs, framework legislation would not
be usurping this power but conditioning its exercise. It is generally considered
that it would be constitutionally acceptable for the Commonwealth Parliament
to limit or regulate even the executive’s power to enter into treaties, as long as
the Parliament does not itself seek to enter into a treaty.108 Statutory limits on the
communication of NDCs would be likely viewed in the same way. As a matter of
policy and practice, it is less clear that Australian framework legislation should
impose such a constraint. Critics of this approach could argue that it trespasses
unduly on the Commonwealth Government’s traditional role in conducting foreign
affairs.109 They could also point out that it would be inconsistent with Australia’s
treaty-making process, which does not give the Commonwealth Parliament a
103 Water Act 2007 (Cth) s 33; Basin Plan 2012 (Cth).
104 Fisheries Management Act 1991 (Cth) ss 17, 19; e.g. Bass Strait Central Zone Scallop
Fishery Management Plan 2002 (Cth).
105 Features of the Australian system of government leading to this include the fact that the
existing Senate continues until 1 July following a half-Senate election, the election of
Senators for 6 year terms, and the system of proportional representation that makes it
easier to elect minor party candidates: Jospeh and Castan, above n 91, 23; Stephen Barber
and Sue Johnson, Federal Election Results 1901–2014, Research Paper (Parliament of
Australia, 2014) 4 (noting that ‘[s]ince the introduction of proportional representation (PR)
for Senate elections in 1949, the government of the day has only had control (a majority)
in the Senate during 1951–1956, 1959–1962, 1975–1981 and 2005–2007’).
106 Clean Energy Act 2011 (Cth) (repealed) ss 16, 17.
107 Hilary Charlesworth et al, ‘Deep Anxieties : Australia and the International Legal Order’
(2003) 25(4) Sydney Law Review 423, 431, citing R v Burgess; ex parte Henry (1936) 55
CLR 608, 644 (Latham CJ).
108 Legal and Constitutional References Committee, Trick or Treaty? Commonwealth
Power to Make and Implement Treaties (Parliament of the Commonwealth of Australia,
1995) [16.16]-[16.24]; George Winterton, ‘The Relationship Between Commonwealth
Legislative and Executive Power’ (2004) 25 Adelaide Law Review 21, 38-9.
109 Brian R Opeskin, ‘The Role of Government in the Conduct of Australia’s Foreign Affairs’
(1994) 15 Australian Yearbook of International Law 129, 138.
261
decision-making role on whether Australia will ratify a treaty.110 On the other
hand, advocates of this approach could argue that it is desirable to ensure that the
Australian executive acts consistently with legislation directed to implementing
Australia’s international obligations.
C Political and Legal Accountability for Achieving Targets
Framework legislation can promote greater political accountability for achieving
emission reduction targets. The Climate Change Act 1998 (UK) provides a good
example of how this can be done, with techniques that would translate well to
an Australian context. Under that Act, targets take the form of ve-year carbon
budgets expressed as the total quantity of permissible greenhouse gas emissions
over the relevant period. These carbon budgets are made by the Secretary of State
but must rst be approved by both Houses of Parliament.111 Once the carbon
budget has been made, a set of accountability mechanisms come into play. As
soon as practicable after making the carbon budget, the Secretary of State ‘must
lay before Parliament a report setting out proposals and policies’ for meeting
that carbon budget, together with other budgets in force at that time.112 Progress
towards meeting carbon budgets is assessed by the independent Committee on
Climate Change, which must lay reports before Parliament by 30 June each
year.113 The Secretary of State must prepare a response to each report, to be laid
before Parliament by 15 October each year.114 The Secretary of State must also
table statements on the ‘net UK carbon account’ each year and at the end of a
carbon budget period.115 If a carbon budget has been exceeded at the end of a ve-
year carbon budget period, the Secretary of State must ‘lay before Parliament a
report setting out proposals and policies to compensate in future periods for the
excess emissions’.116
Some framework legislation goes beyond traditional political accountability
requirements such as those just described and also imposes duties on public
ofcials to ensure that emission reduction targets are achieved. For example, the
Climate Change Act 2008 (UK) provides that ‘[i]t is the duty of the Secretary of
State to ensure’ that each carbon budget and the Act’s 2050 emissions reduction
target are met.117 How are broad duties of this kind likely to be approached by the
110 Department of Foreign Affairs and Trade, Australia International Treaty Making
Information Kit (Commonwealth of Australia, 2000).
111 Climate Change Act 2008 (UK) s 8.
112 Ibid s 14(1).
113 Ibid s 36.
114 Ibid s 37(1).
115 Ibid ss 16, 18.
116 Ibid s 19(1). The Act does not dene what is meant by ‘compensate’, but it would
presumably mean that an additional quantity of abatement, over and above than already
committed to in future carbon budgets, would need to be achieved – effectively tightening
a future carbon budget or budgets by the excess amount.
117 Ibid ss 1, 4. For other examples, see Climate Change (Scotland) Act 2009 ss 1-3 (duty
of Scottish Ministers to meet 2050 target, an interim 2020 target and annual targets);
Environment (Wales) Act 2016 ss 29-31 (duty of Welsh Ministers to achieve 2050 target,
262
Australian courts, and should they form part of national framework legislation in
Australia?
While the target duties in the Climate Change Act 2008 (UK) are yet to receive any
detailed judicial consideration, they have been the subject of academic analysis
that provides a useful starting point in considering this question. Most commentary
has doubted whether the section duties could be enforced by the courts through
judicial review118 or other means.119 Perhaps the most signicant barrier is that
the courts are likely to refuse to entertain a judicial review application because the
Act provides for an alternative remedy.120 As Macrory puts it, ‘it could be argued
that the legislation explicitly envisages political accountability of government to
Parliament rather than legal accountability to the courts’.121 As we have seen,
this political accountability arises from the statutory reporting requirements,
including a requirement that the Secretary of State report on how any exceedance
of a carbon budget will be compensated for in future carbon budget periods.
While a court may be willing to give a declaration or even order of mandamus
to enforce the Secretary of State’s reporting obligations, it is difcult to see
how a remedy could be granted for breach of the target duty itself. On the face
of it, a simple declaration that a duty has been breached would be a possible
remedy but, as McHarg points out, this ‘might be seen as purely academic, since
a court order would add nothing to the Act’s reporting obligations’.122 What about
the other possibility that has been agged by the UK government: that a court
might order the Secretary of State to purchase offsets to compensate for the
exceedance of the carbon budget?123 There are even more substantial problems
here. To start with, there would be a natural reluctance for a court to intervene
with such an order, given that it would involve ‘complex and polycentric issues
of policy prioritization and resource allocation which are typically regarded as
decadal targets and ve-yearly carbon budgets); Climate Change Act 2017 (Vic) s 8 (duty
on Premier and responsible Minister to ensure that State achieves 2050 target); California
Global Warming Solutions Act, as amended in 2016 by SB32 (duty on State Air Resources
Board to ensure that 2030 target is met).
118 Richard Macrory, ‘The UK Climate Change Act - Towards a Brave New Legal World?’
in Richard Macrory (ed), Regulation, Enforcement and Governance in Environmental
Law (Hart Publishing, 2nd ed, 2014) 255, 265-6; Mark Stallworthy, ‘Legislating Against
Climate Change: A UK Perspective on a Sisyphean Challenge’ (2009) 72(3) The Modern
Law Review 412 423-4; Peter McMaster, ‘Climate Change—Statutory Duty or Pious
Hope?’ (2008) 20(1) Journal of Environmental Law 115; Compare Church, above n 78.
119 McMaster, above n 118, 116-18 (considering and rejecting the possibilities of compensation
for breach of statutory duty and criminal sanctions).
120 Colin Reid, ‘A New Sort of Duty? The Signicance of “Outcome” Duties in the Climate
Change and Child Poverty Acts’ (2012) (4) Public Law 748, 758-9.
121 Richard Macrory, Regulation, Enforcement and Governance in Environmental Law (Hart
Publishing, 2014) 266.
122 Aileen McHarg, ‘Climate Change Constitutionalism? Lessons from the United Kingdom’
(2011) 2(4) Climate Law 469, 478.
123 UK, House of Commons, Public Bill Committee on the Climate Change Bill, 6th session, 1
July 2008 col 236 (Mr P. Woolas).
263
non-justiciable’.124 Moreover, the Act already requires the Secretary of State (not
the courts) to grapple with these issues in preparing a report to Parliament as to
how the excess will be compensated for in future carbon budget periods. It would
not be consistent with the scheme of the Act for a court to intervene before this
report had been prepared, nor to second-guess, in a policy sense, the content of
that report after it has been published.
While apparently sweeping legal duties to achieve targets may give rise to few,
if any, practical remedies, there are two good reasons to consider including
them in Australian framework legislation. The rst is for signal they would send
within the Commonwealth bureaucracy about the importance and priority of
emission reduction goals. As was observed in the debate on the United Kingdom
legislation, legal duties to achieve emission reduction targets are ‘not just about
the punishment in the event of failure’ but about ‘trying to change institutional
behaviour through a change in the law’.125 The second is the signal they would
send to other nations about the seriousness with which Australia is taking its
emission reduction commitments under the Paris Agreement.
CONCLUSION
Growing numbers of countries are enacting framework climate laws that entrench
emission reduction targets, require planning for how targets will be achieved, and
make governments accountable for meeting their targets. This trend pre-dated
Agreement endorses important global goals, but depends critically on nationally-
determined targets and mitigation actions to achieve them. National framework
legislation aligned with the goals and processes of the Paris Agreement can help
by ensuring that emission reduction targets are set in a principled, transparent
and evidence-based manner, and by providing greater credibility that targets,
once set, will be achieved. The climate policy debate in Australia has focused
almost exclusively on the ‘toolkit’ of instruments that should be at the disposal of
governments. In the wake of the Paris Agreement, more attention needs to be given
to the question of how laws should discipline successive Australian Governments
to play their full part in achieving the global goals to which Australia is now
committed.
124 McHarg, above n 122, 477-8.
125 UK, Parliamentary Debates, House of Lords, 27 November 2007 vol 696 col 1209; ibid
472.
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