ArticlePDF Available

Governing by expertise: the contested politics of (accounting for) land-based mitigation in a new climate agreement

Authors:

Abstract

This article analyzes the contested politics of including (and accounting for) land-based mitigation in a post-2020 climate agreement. Emissions from land have been only partially included to date within the United Nations Framework Convention on Climate Change and its Kyoto Protocol. The Paris Agreement, adopted in December 2015 and “applicable to all” for the post-2020 period, raises the possibility of unprecedented reliance on land-based mitigation. This has significant consequences for furthering both ambition and equity in global climate mitigation efforts. Yet, what are these consequences, and how have they manifested themselves in the existing (pre-2020) multilateral climate regime? What role do accounting rules for land-based mitigation play herein? In addressing these questions, we identify key dimensions of what we term the “governance by expertise” approach taken to land-based mitigation to date, which has served to reduce the environmental integrity of existing (developed country) mitigation efforts. Specifically, we analyze land-use accounting rules as a site of politics and highlight the “technicalization of politics” underway in this realm, which obscures the political implications of how land has been included to date. We conclude by considering whether the Paris Agreement institutionalizes similar dynamics, and the environmental integrity and equity implications of doing so.
ORIGINAL PAPER
Governing by expertise: the contested politics
of (accounting for) land-based mitigation in a new
climate agreement
Kate Dooley
1
Aarti Gupta
2
Accepted: 5 July 2016 / Published online: 15 July 2016
The Author(s) 2016. This article is published with open access at Springerlink.com
Abstract This article analyzes the contested politics of including (and accounting for)
land-based mitigation in a post-2020 climate agreement. Emissions from land have been
only partially included to date within the United Nations Framework Convention on Cli-
mate Change and its Kyoto Protocol. The Paris Agreement, adopted in December 2015 and
‘applicable to all’’ for the post-2020 period, raises the possibility of unprecedented reli-
ance on land-based mitigation. This has significant consequences for furthering both
ambition and equity in global climate mitigation efforts. Yet, what are these consequences,
and how have they manifested themselves in the existing (pre-2020) multilateral climate
regime? What role do accounting rules for land-based mitigation play herein? In
addressing these questions, we identify key dimensions of what we term the ‘‘governance
by expertise’’ approach taken to land-based mitigation to date, which has served to reduce
the environmental integrity of existing (developed country) mitigation efforts. Specifically,
we analyze land-use accounting rules as a site of politics and highlight the ‘‘technical-
ization of politics’’ underway in this realm, which obscures the political implications of
how land has been included to date. We conclude by considering whether the Paris
Agreement institutionalizes similar dynamics, and the environmental integrity and equity
implications of doing so.
Keywords Accounting Climate governance Equity Land-based mitigation Land-use,
land-use change and forestry (LULUCF) Negative emissions Paris Agreement United
Nations Framework Convention on Climate Change (UNFCCC)
&Aarti Gupta
aarti.gupta@wur.nl
Kate Dooley
kate.dooley@climate-energy-college.org
1
Australian-German Climate & Energy College, and School of Geography, University of
Melbourne, Parkville, Australia
2
Environmental Policy Group, Department of Social Sciences, Wageningen University,
Hollandseweg 1, 6706 KN Wageningen, The Netherlands
123
Int Environ Agreements (2017) 17:483–500
DOI 10.1007/s10784-016-9331-z
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
1 Introduction
This article analyzes the contested politics of including (and accounting for) land-based
mitigation in a post-2020 climate agreement. Emissions from agriculture and land-use
contribute roughly a quarter of global greenhouse gas (GHG) emissions (IPCC 2014). Yet,
these have been only partially included to date in the multilateral climate regime, which is
centered around the United Nations Framework Convention on Climate Change
(UNFCCC) and its Kyoto Protocol. Under the auspices of these agreements, countries have
sought for the last two decades to agree on guiding principles and binding obligations (for
developed countries) to reduce their GHG emissions.
With the newly concluded Paris Agreement under the UNFCCC, adopted in December
2015 and ‘‘applicable to all’’ for the post-2020 era, the partial inclusion to date of the land
sector looks set to change. Key elements of the Paris Agreement raise the possibility of
unprecedented reliance on land-based mitigation. This includes the temperature goal to
stay ‘‘well below’’ a temperature increase of 2 C and to ‘‘pursue efforts’’ to limit tem-
perature increase to 1.5 C over pre-industrial levels (UNFCCC 2015, Article 2.1). Related
to this is the long-term mitigation goal calling for a peaking of greenhouse gas emissions
‘as soon as possible’’ to be achieved through a ‘‘balance between anthropogenic emissions
by sources and removals by sinks’’ (UNFCCC 2015, Article 4.1). The reference to ‘‘re-
movals by sinks’’ implicates, inter alia, terrestrial sequestration of carbon emissions, i.e.,
the land sector.
1
Much is at stake, given that the land sector is crucial to the pursuit of sustainable
development and poverty eradication, and the most vulnerable populations depend upon
land for food, fuel, and livelihoods. Added to this is the technical and political complexity
inherent in monitoring land-based emissions. A key dilemma is thus how to secure land-
based mitigation so as to enhance collective climate action, without undermining food
security or other essential land-uses.
In this paper, we assess how the challenges of relying on land-based mitigation have
been dealt with in existing (pre-2020) climate governance efforts. Our aim in doing so is to
identify the consequences of pursuing similar approaches in the future. In particular, we
focus on the accounting rules for the land sector developed within the UNFCCC’s Kyoto
Protocol, upon which a post-2020 climate regime is likely to build. We choose to focus on
accounting rules because these rules have shaped the nature and scope of reliance on land-
based mitigation in meeting current developed country emission reduction targets under
the Kyoto Protocol. It is thus crucial and timely to understand the nature of these
accounting rules, how they came to be negotiated, and their implications for ambitious and
equitable pathways to future climate mitigation efforts by all.
In our paper, we view land sector accounting rules as a site of political negotiations,
even as they are technically complex, obscure, and often inscrutable to those lacking
requisite expertise. In analyzing the complex interplay between the technical and political
in this realm, we advance the notion of ‘‘governing by expertise’’ in this article, which we
argue has been the dominant approach to including land-based mitigation in the multi-
lateral climate regime to date. Such an approach has entailed a technicalization of what are
highly contested normative and political questions about who should do what, and how
much, in combating climate change, and what role the land sector should play herein.
1
Land is the only sector where CO
2
is not only emitted (via forest burning and clearing and land-use change
for agriculture, among other activities), but also sequestered (via photosynthesis).
484 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
One caveat is important to note at the outset: A key conflict around land-based miti-
gation in the UNFCCC has centered on the scope and meaning of the term ‘‘land.’’ While
land generally refers to forests, agriculture, and other land-uses, developing countries have
long opposed the inclusion of agriculture within multilateral climate mitigation efforts
under the UNFCCC, given the potential adverse impacts on food security. Our analysis
pertains thus to carbon-related terrestrial emissions, i.e., CO
2
emissions and removals from
forests, soil carbon, and cropping and grazing activities, in line with current Intergov-
ernmental Panel on Climate Change (IPCC) reporting guidelines on so-called LULUCF
(land-use, land-use change and forestry) activities. This excludes consideration of non-CO
2
agricultural activities (such as livestock management and fertilizer use), which are the
dominant sources of emissions from the agricultural sector.
We proceed as follows: We first distill lessons from the manner in which land-use, as
understood above, has been included to date in the existing climate regime. Our discussion
reveals a lack of environmental integrity in the current (accounting) approach to land sector
inclusion.
2
We then review the architecture of target setting in the Paris Agreement and the
envisaged role (and debates around accounting) for the land sector therein. We conclude
with considering the implications for ambition and equity of extending the current
approach to the land sector within the post-2020 regime.
Our analysis relies upon 21 semi-structured interviews conducted during 2015 (in
person during UNFCCC negotiating sessions, or by Skype and telephone) with 14 land-use
negotiators (seven from developing countries and seven from developed countries), three
representatives of non-governmental organizations, and four academics/experts. Intervie-
wees were selected based on their involvement or familiarity with land-use negotiations
and to reflect a range of views. All interviewees were guaranteed anonymity and hence are
only identified here by broad professional affiliation and geographical region. We also
draw upon our own observation of multilateral climate negotiations, from the Lima
meeting in December 2014 to Paris in December 2015, as well as intersessional negoti-
ations, encompassing six sessions. Finally, we rely on an extensive review of primary and
secondary sources, including country submissions to the UNFCCC during 2014-2015
culminating in the Paris Agreement,
3
grey literature, and existing academic analyses.
2 Governing by expertise: accounting as a site of politics
The politics of expertise, i.e., the ‘‘selective use of expert knowledge by political elites to
gain support for their pre-defined policy agendas’’ (Fisher 1990, 28, paraphrased in Lo
¨v-
brand 2009, 404–405), has been a long-standing object of critical science studies scrutiny,
including in the climate domain. Lo
¨vbrand (2009) in particular has explored in detail what
she terms the ‘‘links between knowledge-making and decision-making authority’’ in
multilateral climate negotiations on terrestrial sources and sinks of greenhouse gases. Such
interlinkages are now routinely analyzed within the paradigm of ‘‘co-production,’’ which
refers to a dialectical process whereby knowledge making is constitutive, insofar as it
constructs particular social realities, even as a given social order shapes the nature and
2
By lack of environmental integrity, we mean a discrepancy between what is accounted for, and what the
atmosphere sees.
3
Specifically, we analyzed all country submissions made between January 2014 and June 2015 on ‘‘ele-
ments for a 2015 agreement’’ to Workstream 1 of the Ad Hoc Working Group on the Durban Platform
(ADP) for references to land-use (encompassing 43 submissions).
Governing by expertise: the contested politics of485
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
prospects of such knowledge making and its (selective) legitimation (Jasanoff 2004, see
also Beck 2015; Fogel 2005).
For our purposes here, we view accounting as such a site of co-production. Viewed
through a governance lens, we further conceptualize co-production as the twin processes of
governing (i.e., disciplining)expertise and governing by expertise. These terms build on
two much analyzed phenomena within science and technology studies: the politicization of
science and the scientization of politics (Jasanoff 1998; Weingart 1999; Sarewitz 2004).
The first, politicization of science, refers to the selective evoking of technical knowledge to
further specific political interests and agendas, which we refer to here as governing
expertise. Its mirror process, scientization (or technicalization) of politics, draws attention
to how key morally charged and politically contested questions become translated into, and
debated within, the potentially exclusionary, arcane, and technically impenetrable lan-
guage of science, which may be accessible only to a select elite group of experts (see also
Jasnoff 2003; Gupta 2011; Gupta et al. 2012).
In using ‘‘governing expertise’’ and ‘‘governing by expertise’’ to capture these two
interrelated dynamics, our interest here is not only to show how politics and knowledge
making are intertwined, but also to draw attention to the governance outcomes that flow
from this. We do this through analyzing, inter alia, the Kyoto Protocol’s LULUCF
accounting rules as a site of political conflict, and how these rules have shaped the nature
and scope of land-based mitigation within the UNFCCC.
3 Negotiating land-based mitigation in the current multilateral climate
regime
This section analyzes the twin processes of governing (i.e., disciplining) expertise and
governing by expertise, with regard to land-based mitigation within current multilateral
climate governance. We discuss, first, the political decision taken within the UNFCCC’s
Kyoto Protocol to allow developed countries to include the land sector in meeting their
mandatory emission reduction targets under this agreement and the associated crucial
assumption of fungibility (between terrestrial and industrial emissions) accompanying this
decision. We then turn to an analysis of the LULUCF accounting rules negotiated sub-
sequent to this political decision, which impact upon the scope, scale, and manner in which
land sector mitigation has been relied upon by developed countries to date.
3.1 Governing (disciplining) expertise: agreeing on fungibility
The Kyoto Protocol, adopted in December 1997, introduced legally binding emission
reduction targets for developed countries for the first time. These targets were set for
economy-wide industrial emissions, excluding the land sector.
4
However, the land sector
was subsequently included under the rubric of land-use, land-use change, and forestry
(LULUCF) as a means through which to meet targets on the final day of negotiations in
Kyoto (UNFCCC 1997). The inclusion of LULUCF was contentious from the start, given
that such inclusion had the potential to weaken commitments to reduce GHG emissions
from industrial sources (Fry 2002; Schlamadinger et al. 2007). Tensions arose because of
the potential for some countries to meet their Kyoto targets solely or largely through
claiming significant LULUCF removals, effectively offsetting emissions from the
4
See Annex A to the Kyoto Protocol.
486 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
industrial sector and thus relieving these countries of the need to substantially reduce
industrial emissions (Lo
¨vbrand 2004).
This was evident, for example, from arguments made by some members of the so-called
Umbrella Group of countries, who called for comprehensive inclusion of LULUCF.
5
As
one interviewee involved in the Kyoto negotiations noted, ‘‘the Chair was told by Umbrella
Group countries (US, Canada, Norway, Russia, Iceland), that there is no way we will agree
[to the Kyoto Protocol] unless we can credit some land use activities.’
6
The Alliance of
Small Island States (AOSIS), in particular the Marshall Islands and Barbados, as well as
Costa Rica and Brazil, preferred to limit reliance on terrestrial sinks or exclude them
altogether (Earth Negotiations Bulletin 1997), while the European Union (EU) remained
internally divided over the issue.
7
While the details of these dynamics have been analyzed elsewhere (e.g., Fogel 2005;
Fry 2002,2007), we draw attention to two aspects below: the assumption of fungibility that
underpins use of LULUCF to meet developed country Kyoto targets, which entailed a
disciplining of scientific knowledge, and offset mechanisms negotiated under the UNFCCC
and Kyoto, which also assume fungibility and implicate the land sector in developing
countries as well.
3.1.1 Fungibility between terrestrial and industrial emissions
The conflicts over inclusion of LULUCF in the Kyoto Protocol were due in part to abiding
contestations over the assumption of fungibility, i.e., the assumption that avoided emis-
sions and removals from the land sector were interchangeable with emission reductions
from fossil fuels. This assumption remained singularly contested. Brazil, for example,
‘wanted LULUCF completely out of Kyoto, raising all of the legitimate scientific ques-
tions about this. They didn’t want any kind of cheating which was related to the
accounting. In principle they thought [Kyoto] should be an energy convention, making it
also about forests made it much more complicated.’
8
This was also because, if included in
the Kyoto Protocol, special accounting rules would be needed for LULUCF, given the
unique complexities of the sector that prevented easy comparison between fossil and
terrestrial emissions. As we noted earlier, land is the only sector where CO
2
is not only
emitted (via forest burning and clearing and land-use change for agriculture, among other
activities), but also sequestered (via photosynthesis). As such, there were a wide variety of
political positions articulated at this time on why and how the land sector was different, and
thus how valid the assumption of fungibility was.
9
Fungibility was simultaneously much debated in scientific circles and continues to be.
While some see it as unproblematic (e.g., Estrada et al. 2014; Lee et al. 2015; Parker et al.
2014), others outline key technical barriers to comparability between land and fossil
5
The Umbrella Group is a negotiating bloc of non-EU developed countries. During Kyoto negotiations, it
consisted of Australia, Canada, Iceland, Japan, New Zealand, Norway, the Russian Federation, Ukraine, and
USA. Japan initially opposed inclusion of sinks, but later agreed, when under pressure to take on a higher
emission reduction target (Interview with developing country negotiator, Bonn, Germany, June 9, 2015).
6
Interview with developing country negotiator, Bonn, Germany, June 9, 2015.
7
Ibid.
8
Developing country negotiator, Bonn, June 9, 2015.
9
Interviews with five developed country and seven developing country negotiators, as well as two
LULUCF experts, conducted in person in Bonn, Germany, in June and October; and in Paris, France in
December; and via telephone between July and October, 2015.
Governing by expertise: the contested politics of487
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
emissions, including inter alia, high levels of uncertainty in monitoring land-based emis-
sions; difficulties in distinguishing between anthropogenic and natural causes of land-based
emissions and removals; and non-permanence of removals (Fry 2002; Hansen et al. 2013;
Mackey et al. 2013; Powlson et al. 2011).
For example, with regard to non-permanence of soil carbon sequestration, Powlson et al.
have expressed concern that ‘‘the possibilities for climate change mitigation by this means
may be exaggeratedeven though these limitations have been clearly enunciated in
numerous publications’’ (2011, 43–52). Fry (2002, 162) has observed that the early
LULUCF discussions ‘‘lacked a critical analysis of the efficacy of sinks projects, despite
the fact that, there were a number of scientific articles questioning the efficacy of
LULUCF activities.’’ The sustained scientific critique and persisting debates around the
efficacy and mitigation potential of terrestrial sinks ultimately did not impede the inclusion
of LULUCF in the Kyoto Protocol, indicating that sequestration science (i.e., the science of
removing emissions through terrestrial sinks) was selectively evoked by policy experts in
this realm to align knowledge with a politically desired outcome—the use of sinks in
climate mitigation.
3.1.2 Offsetting
The political decision to assume fungibility between terrestrial and industrial emissions
also laid the basis for including land-based mitigation in developing countries within the
parameters of the Kyoto Protocol. This was achieved through the Clean Development
Mechanism (CDM) of the Kyoto Protocol, which allowed developed countries to partially
meet their Kyoto targets by purchasing credits generated from emission reduction projects
in developing countries (i.e., offsetting ongoing emissions in one place with reductions in
another). Reliance on land-based mitigation was more limited in the CDM than under
LULUCF, largely due to the sheer scale of potential credits the unrestricted inclusion of
land could yield (given higher deforestation rates, and greater land areas in developing
countries). Hence, ‘‘avoided deforestation’’ as an offsetting activity was excluded from the
CDM all together, and reliance on terrestrial sinks was limited to the specific activities of
afforestation and reforestation, and capped at 1 % of Kyoto targets annually (Ho
¨hne et al.
2007). This followed particular opposition to the inclusion of avoided deforestation as a
crediting activity in the CDM, with Brazil, China and AOSIS raising concerns about the
potential for such credits to offset an increase in developed country (industrial) emissions
(Fry 2007).
10
In 2005, a new proposal was made within the UNFCCC to incentivize avoided defor-
estation in developing countries (thus far excluded from the CDM). Established as a
voluntary mechanism, whereby developing countries could receive financial incentives to
reduce emissions from forest loss and enhance sequestration, REDD?
11
has now been
included in the Paris Agreement as a results-based payment mechanism (UNFCCC 2015,
Article 5.2). Furthermore, despite current lack of clarity regarding who (the host or donor
country) can credit any resultant emission reductions, REDD?accounting rules have been
developed to potentially enable REDD?credits to be used as offsets by purchasing
10
This point was also made in an author interview with developing country negotiator, Bonn, Germany,
June 9, 2015.
11
REDD?refers to the agreed eligible activities in developing countries, which are: reducing emissions
from deforestation and forest degradation; conservation of forest carbon stocks; sustainable management of
forests; and enhancement of forest carbon stocks.
488 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
countries or entities. This possibility has led to contentious debates within the UNFCCC
over the stringency of verification required for REDD?results (Dutschke 2013), with
many developing country negotiators noting that REDD?accounting rules are stricter than
those that developed countries adhere to in crediting their own LULUCF activities.
12
Limiting terrestrial sinks in the CDM and developing strict accounting rules for
REDD?can be seen as political compromises in response to concerns expressed by the
EU and AOSIS, among others, over both the environmental integrity and social impacts of
land-based offset projects in developing countries (Fry 2002), even as the scientific debate
over fungibility has remained unchanged.
These political decisions on including land-based mitigation in the climate regime,
accompanied by a selective evoking (or ignoring) of scientific disputes over fungibility,
shaped negotiation of LULUCF accounting rules, to which we turn next.
3.2 Governing by expertise: accounting rules and a technicalization of politics
Once the Kyoto Protocol was agreed, along with the assumption of fungibility between
terrestrial and industrial emissions, negotiations began on developing accounting rules for
the land-use sector within the UNFCCC’s Subsidiary Body for Science and Technological
Advice (SBSTA). This technical negotiating site saw LULUCF negotiators employing
complex scientific arguments about the intricacies of accounting for terrestrial emissions
and removals, yet doing so in a way that suited their specific circumstances, i.e., the
varying potentials in different countries for relying on land-based mitigation in meeting
Kyoto targets.
13
In analyzing these dynamics here, we review below the contested negotiations around,
first, the scope and scale of permitted land-based mitigation and, second, baselines and
reference levels against which to account for land-based mitigation.
14
3.2.1 Scope and scale
Scope (i.e., which land-use activities were to be included) and scale (i.e., limits on land-
based mitigation) quickly became among the most divisive issues in negotiating LULUCF
accounting rules (Ho
¨hne et al. 2007; Schlamadinger et al. 2007). The Umbrella Group (in
particular Canada and the USA) with large forest areas wanted a broad scope and no limits
on using LULUCF to offset industrial emissions. China and the G-77, as well as AOSIS,
opposed this position.
15
The political compromise reached was to develop an accounting innovation: the ac-
tivity-based approach to LULUCF accounting, i.e., accounting for specific land-related
activities, rather than land areas. A widely asserted technical reason for this was to help
distinguish between anthropogenic (i.e., managed) terrestrial emissions and removals from
12
Several interviewees from developing countries made the point that REDD?accounting and safeguard
rules are stricter than LULUCF rules for developed countries. Interviews conducted in Bonn, Germany, June
9 and 11, and via telephone November 21, 2015.
13
Author interviews with several developing country negotiators, in Bonn, Germany, June 9, 11, and
October 21, 2015. See also Fry (2007) and Lo
¨vbrand (2009).
14
An exhaustive account of all land-use accounting rules is beyond the scope of this paper. For compre-
hensive discussion of land-use rules see also, e.g., Estrada et al. (2014), Ho
¨hne et al. (2007), Iversen et al.
(2014), Parker et al. (2014), Schlamadinger et al. (2007).
15
Interview with developing country negotiator, Bonn, Germany, June 9, 2015.
Governing by expertise: the contested politics of489
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
natural carbon fluxes. Once an activity-based approach was selected, however, another key
axis of conflict became whether all land-related activities were to be mandatory or whether
countries could choose which ones (if any) to rely upon in meeting their Kyoto targets.
Countries negotiated extensively on this, with the political implications of these choices
obscured by technically complex discussions of GHG fluxes associated with each desig-
nated activity. Eventually, only the activities of forest clearing and forest planting (since
1990) were declared to be mandatory to account for. Countries could choose whether or not
to account for other land-use activities, including forest management, which is potentially a
large source of both emissions and removals (Ecosystems Climate Alliance 2009).
While some existing analyses of this negotiated division between mandatory and vol-
untary activities for LULUCF accounting emphasize the technical rationales underpinning
them (e.g., Ho
¨hne et al. 2007; Schlamadinger et al. 2007), others point to the political
contestations underlying these decisions (e.g., Fry 2002, and Lo
¨vbrand 2009). In particular,
the decision to characterize forest management as a voluntary activity became one of the
most heavily criticized aspects of LULUCF accounting rules in the Kyoto Protocol’s first
commitment period (2008–2012), given significant under-reporting of forest-related
emissions that became possible as a result (for details, see Daviet and Goers 2009).
In addition to deciding on which activities to include, LULUCF accounting rules also
addressed limits on the use of terrestrial sources and sinks (i.e., the scale of permitted
inclusion). As one developing country negotiator put it, ‘‘If you set the bar too high (i.e.,
with strict limits on inclusion), (countries) will not participate and you get nothing. If the
bar is too low, you do not reduce emissions. It is very hard to balance.’
16
The key concern
was that in the absence of limits, the scale of land sector emissions and removals could
outweigh efforts to reduce industrial emissions (Ho
¨hne et al. 2007). While this was widely
recognized, the withdrawal of the USA from the Kyoto Protocol in 2001 ironically
strengthened the hand of other Umbrella Group countries in securing more widespread
reliance on land-based mitigation within Kyoto, given the need to keep these countries on
board (Fry 2002;Lo
¨vbrand 2009).
With the discussion on scale and limits remaining heated, the EU eventually called for
caps (‘‘allowable limits’’) on LULUCF use by each Kyoto Party, as a compromise. As one
developed country negotiator put it, ‘‘When you’re really uncertain [about your accounting
rules] the political solution is to put a cap.’’
17
While AOSIS countries demanded an in-
depth scientific analysis of proposed caps, given the collective potential of such caps to
meet more than half the Kyoto Protocol’s overall emission reduction target (den Elzen and
Lucas 2003; cited in Ho
¨hne et al. 2007), political expediency saw little such analysis. The
compromise reached was for countries to politically negotiate their own cap on LULUCF,
which had the effect of generating substantial credits that countries could use in meeting
their Kyoto targets.
3.2.2 Baselines and reference levels
How negotiation of LULUCF accounting rules serves as a site of political conflict was also
evident in debates around the baselines against which to assess terrestrial emissions and
removals in a given period. Agreeing on baselines is substantially more complex for the
land sector than it is for industrial emissions, given that land is the only sector with
emissions as well as removals. Industrial emission reductions are straightforwardly
16
Interview with developed country negotiator, Bonn, Germany, June 10, 2015.
17
Interview with developed country negotiator, Bonn, Germany, June 6, 2015.
490 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
assessed through a gross–gross baseline approach, wherein emissions in a base year are
compared with emissions in the reporting period (Rocha et al. 2015). However, inclusion
of emissions and removals in the same accounting framework requires, logically, a net–net
approach.
18
A net–net approach, i.e., comparing emissions minus removals in the base year
against emissions minus removals in the reporting period, would maintain the symmetry of
the gross–gross approach (Rocha et al. 2015; Schlamadinger et al. 2007). While scien-
tifically tenable, the political challenge of using a net–net approach, however, is that any
increase in emissions from the land sector in the reporting period would make targets more
difficult to meet.
19
This possibility is exacerbated by the fact that forest management
decisions of the past determine whether managed forests are a net source or a net sink
during any given period (referred to as legacy effects), leading to most countries with
Kyoto targets refusing to accept a net–net accounting approach.
20
Given this opposition to net–net accounting, a much more complex approach to base-
lines for the land sector was negotiated: the ‘‘gross-net’’ accounting approach. This does
not include emissions and removals from forest-related activities in the baseline, which
reflects only industrial emissions, but does allow for both industrial and (selected) forest-
related activities to be accounted for during the subsequent reporting and commitment
period (Iversen et al. 2014). The gross-net approach is favoured by those countries with an
overall forest sink (i.e., where terrestrial removals are higher than terrestrial emissions in a
commitment period), making overall targets easier to meet. As a result, it has been criti-
cized for permitting unearned or ‘‘windfall’’ credits (Daviet and Goers 2009; Rocha et al.
2015) for such countries.
The gross-net approach was, however, not supported by countries where the forest
sector is an overall source of emissions (i.e., where emissions from deforestation are higher
than removals through forest planting), given that these emissions would then be added to
overall targets, making them harder to meet (Rocha et al. 2015). As one negotiator put it,
‘‘ if you have any kind of rule which is just—deforestation is really bad, you have to
debit it—then straight away any country with high deforestation is going to have very high
emissions under that accounting framework.’
21
However, very few developed countries
have high deforestation rates (Australia being a notable exception
22
), making the decision
to have a gross-net LULUCF accounting approach for Kyoto politically feasible. It proved,
furthermore, to be a boon for those countries (including in the EU) with low deforestation
rates but with intensive forest management, given that forest management was a voluntary
activity that could be excluded from consideration in meeting first commitment period
Kyoto targets.
The contested process of negotiating politically palatable (but also scientifically
defensible) baselines continued for the second commitment period of the Kyoto Protocol
(2013–2019). One key change was that forest management became a mandatory activity
18
This point was made in several interviews, including with a developed country negotiator, Bonn, Ger-
many, June 11, a LULUCF policy expert via telephone June 16, and an NGO representative in Paris, France
December 9, 2015.
19
Interview with developed country negotiator, Bonn, Germany, June 11, 2015.
20
However, a net–net approach is accepted for cropland and grazing lands, where carbon stocks can be
affected in short time periods through management practices (Schlamadinger et al. 2007).
21
Interview with developed country negotiator, Bonn, Germany, June 11, 2015.
22
As a result, Australia negotiated a special clause in the Kyoto Protocol (Article 3.7), allowing it to apply
net–net accounting to deforestation (otherwise only applied to cropland and grazing land management),
resulting in significant windfall credits as deforestation rates dropped from historical highs (Macintosh
2011).
Governing by expertise: the contested politics of491
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
for the Kyoto second commitment period, following intense NGO lobbying to close
‘LULUCF loopholes.’
23
With this, however, the EU, together with some Umbrella Group
countries, insisted on revisiting the gross-net baseline accounting approach for the specific
activity of forest management in the Kyoto second commitment period, once it became
mandatory to include.
With the flexibility to exclude this activity now removed, and the accounting benefits
that this flexibility had earlier conferred now gone, the EU called for forest management
not to be subject to a gross-net baseline, but rather for development of a so-called Forest
Management Reference Level (FMRL) (Iversen et al. 2014
24
). The use of reference levels
is another unique accounting innovation in this context, developed as a political com-
promise between those trying to improve the credibility of accounting rules and those
wanting to maintain flexibility in use of LULUCF to meet targets.
The FMRL means that instead of a baseline against which to judge performance in a
given period, countries can propose a quantified (expected) future level of performance (in
terms of net emissions from forest management) and compare this against actual emissions
at the end of a commitment period (Rocha et al. 2015). Known as a ‘‘projected reference
level,’’ the FMRL was seen by the EU as crucial to avoid the problems of legacy effects
associated with forest management, but was also subject to a cap to avoid excessive credits.
However, any use of reference levels opens up the possibility of inflating future expec-
tations of emissions, in order to make targets easier to meet. As one developed country
negotiator put it, ‘‘The projected reference level is the most politically feasible [accounting
approach] to agree on, there are problems with it, but the alternatives also have problems.
[It is] used for political agreement.’
25
It is also important to note here, in concluding, that the REDD?mechanism also relies
on reference levels (rather than baselines) in assessing performance, allowing countries to
set business-as-usual (BAU) expectations for increases in deforestation and to receive
credits for any improvement against these BAU expectations. The credibility of the ref-
erence level approach is heavily reliant on technical review (Briner and Konrad 2014). Yet
reviews remain fraught with challenges, given extensive scientific uncertainties and
varying political expectations. Analysis has shown that the level of credits from LULUCF
varies widely depending on plausible interpretations of accounting rules (Bo
¨ttcher and
Graichen 2015).
The discussion above shows how the inclusion of land-use to date in the multilateral
climate regime reflects politically negotiated compromises, despite the ostensibly technical
character of LULUCF accounting rules. One dominant response to perceived LULUCF
‘loopholes’’ has been to advocate improved rules and increased ambition through ensuring
that negotiations are ‘‘based on sound science,’’ with greater reliance on data sets to assess
the impact of various options (Ho
¨hne et al. 2007, 354). Yet, the reality that ‘‘LULUCF is a
negotiated system that tries to work around competing national interests’
26
goes against
the notion that ‘‘sound’’ science-based rules, seen as credible by all on the basis of their
23
From interview with NGO representative, Paris, France, December 8, 2015.
24
Iversen et al. point to the mandatory inclusion of forest management as one of the reasons behind the
FMRL; interviews with country negotiations in Bonn, Germany, June 9 and October 21, as well as an NGO
representative in Paris, France, December 9, also raise this issue.
25
Interview with developed country negotiator, Bonn, Germany, June 6, 2015.
26
Interview with developed country negotiator, Bonn, Germany, June 6, 2015.
492 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
technical merits, can be devised. As one negotiator put it, ‘‘there is no perfect rule—what
seems fair to one is an extra burden for another.’
27
As several interviewees have also noted, however, country-specific data on land-use
emissions have improved as a result of requirements for LULUCF accounting, with one
land-use expert adding that ‘‘except in a few countries, fears of LULUCF credits swamping
Kyoto targets did not materialise.’
28
This notwithstanding, our discussion highlights how
LULUCF was introduced into the Kyoto Protocol to make developed country emission
reduction targets easier to meet. Through political negotiations and compromise, complex
accounting rules were designed to both permit and limit the degree to which terrestrial
sinks could be used to offset industrial emissions.
In a post-2020 climate regime, where land is expected to play a more prominent role,
any approach to mitigation that focuses on ‘‘net’’ emissions (i.e., emissions minus
removals), while obscuring the politics hidden in land-use accounting, runs the risk of not
delivering the required ambition and potentially exacerbating inequitable burden sharing.
We turn to these issues next.
4 Negotiating land-based mitigation in the Paris Agreement
The architecture of the post-2020 climate regime differs from that of the Kyoto Protocol. In
contrast to having multilaterally negotiated emission reduction targets for countries, the
overall ambition level is agreed multilaterally in the Paris Agreement through the tem-
perature goal (Article 2.1) and the long-term mitigation goal (Article 4.1) (UNFCCC
2015). In seeking to further these goals, the Paris Agreement institutionalizes two key
elements: a bottom-up process whereby each country develops its own ‘‘nationally
determined contributions’’ (NDCs) to meeting these aggregate goals, which may include
land-based mitigation, and a multilaterally agreed ‘‘transparency framework’
29
through
which to account for, and report on, the progress that countries are making toward
implementing their NDCs.
As in the previous section, we proceed here by first analyzing the dynamics of gov-
erning (i.e., disciplining) expertise that might be discernible in how the land sector is
implicated in the Paris Agreement, with a focus on the long-term mitigation goal. Second,
we consider the current state of debate regarding accounting for land-based mitigation in
the Paris Agreement. Here, we touch briefly upon divergent views over whether a common
accounting framework is required for all countries and associated debates over whether
such a common framework requires countries to take on quantified targets, including for
the land sector. Through doing so, we illustrate the implications of continuing to rely on a
‘governing by expertise’’ approach to land-based mitigation (and its accounting rules) in
the post-2020 era.
27
Interview with developed country negotiator via telephone, October 13, 2015.
28
Interview with LULUCF expert via telephone on June 21, 2015. Other interviews, with a developed
country negotiator in Bonn, Germany, June 10, and a LULUCF expert in Paris, France, December 11, also
made this point.
29
In our discussions below, we focus on accounting issues, rather than on the broader negotiations around a
(common) transparency framework in a new agreement. For an analysis of the contested geopolitics of
transparency in global climate governance, see Gupta and Mason (2016).
Governing by expertise: the contested politics of493
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
4.1 Governing (disciplining) expertise: land-use and the long-term mitigation
goal
Analyzing the prospects for a disciplining of expertise in the manner in which land is
implicated in the Paris Agreement requires consideration of the long-term mitigation goal
articulated within it. Negotiations on language to capture aggregate mitigation ambition
were long and intense, in the lead up to finalization of the agreement in Paris. Terminology
such as ‘‘net-zero emissions,’’ ‘‘near zero,’’ carbon or climate neutrality, and decar-
bonization all appeared in the draft text during the course of the negotiations. A mitigation
goal of ‘‘net-zero’’ emissions was particularly contentious, with some seeing this as a
straightforward scientific statement on an approach to stabilizing atmospheric GHG
emissions,
30
while others viewed it as a political license to ‘‘offset industrial emissions
with land-based sinks.’
31
The net-zero language was introduced to the UNFCCC discussions after the Intergovern-
mental Panel on Climate Change (IPCC) Fifth Assessment Report included long-term miti-
gation pathways that relied heavily on assumptions of ‘‘negative emissions’’ (meaning the
removal of carbon from the atmosphere via terrestrial sinks, often combined with geological
storage) (IPCC 2014). It was first raised during the Lima climate meeting in December 2014,
where New Zealand suggested a mitigation goal of ‘‘net-zero CO
2
emissions by 2100 in line
with the latest science.’
32
Such a positionreceived vocal support from Switzerland,
33
but Brazil
noted that by ascribing ‘‘the latest science’a legal role in the official text ‘we might be creating
some politicization.’
34
Bolivia, Argentina, and Ecuador opposed the use of ‘‘net-zero’’ on the
grounds thatit introduced a new concept that did not appear in the FrameworkConvention, or in
related decisions.
35
Norway and the EU supported the terms carbon or climate neutrality,
36
and
the USA preferred ‘‘decarbonisation of the global economy’ (Ajit 2015a).
With no consensus emerging, the ambiguous language that became the long-term
mitigation goal in the Paris Agreement calls for a ‘‘peaking of greenhouse gas emissions
as soon as possible’’ (i.e., without identifying a specific time frame, or a specific limit on
emissions) to be achieved through ‘‘a balance between anthropogenic emissions by sources
and removals by sinks’’ (UNFCCC 2015, Article 4.1). The term ‘‘removals by sinks’
leaves open the possibility of continuing industrial and terrestrial emissions, as long as
these are (ostensibly) being offset by enhancement of sinks.
It is important to note here that the wording of this long-term mitigation goal is very
close to the contentiously negotiated paragraph on inclusion of land-use in the Kyoto
Protocol, which refers to ‘‘net changes in greenhouse gas emissions by sources and
removals by sinks’ (UNFCCC 1997, Article 3.3, italics added). A key difference is that the
Kyoto Protocol defines the use of sinks as ‘‘limited to afforestation, reforestation and
30
Author interview with LULUCF expert, Paris, France, December 8, 2015.
31
Interview with NGO representative, Bonn, Germany, October 20, 2015.
32
Author personal observation, COP 21 Lima, December 6, 2014.
33
Author personal observation, Geneva, February 8, 2015.
34
Ibid.
35
These points were raised frequently by these countries and were observed during open meetings on the
long-term goal during the September 2015 negotiating session in Bonn, Germany.
36
The position of the EU and Norway on the long-term goal changed throughout the year, from supporting
net-zero in the Bonn September session to calling for carbon and climate neutrality during the Paris
negotiations, as an alternative to the opposition from developing countries on net-zero (author observations;
see also Ajit 2015a).
494 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
deforestation since 1990’’ (UNFCCC 1997, Article 3.3), which circumscribes and limits
the activities that qualify as ‘‘removals by sinks.’’ A second key difference is placement
and context. Article 4.1 in the Paris Agreement is the collective long-term mitigation goal,
while the mitigation goal in the Kyoto Protocol reads, ‘‘Parties shall limit the emissions of
the greenhouse gases listed in Annex A’’ (which refers to energy and industrial emissions,
excluding terrestrial emissions) to ‘‘not exceed their assigned amounts’’ (UNFCCC 1997,
Article 3.1), thus, with a clear focus on reducing emissions from fossil fuel use.
Reliance on land-based mitigation in the Kyoto Protocol was introduced after targets for
industrial emission reductions were set (as discussed in Sect. 3), and was limited from the
start (although the precise nature of these limits remained the subject of political debates).
In the Paris Agreement, on the other hand, land-based sinks have moved from being a
politically contested add-on to occupying center stage in the long-term mitigation goal, as
laid down in Article 4.1.
But why exactly does Article 4.1 of the Paris Agreement implicate land, and to what
extent might this reflect a governing (or disciplining) of expertise, with implications for
environmental integrity and ambition? ‘‘Balancing emissions and removals’’ effectively
means the same as ‘‘net-zero emissions,’’ carbon neutrality, and similar terminology (Levin
et al. 2015), which all imply that terrestrial sinks are both fungible with, and will be used to
offset, ongoing (industrial and terrestrial) emissions (Schaeffer et al. 2013).
So while a goal that essentially puts the world on a pathway toward net-zero global
emissions appears ambitious, Article 4.1 says nothing about the scale of reliance on land-
based mitigation that would be required to meet this global mitigation goal, nor the speed
and timing of a concurrent reduction in fossil fuel use, hence obscuring political questions
around when, how and by whom emissions are reduced. Going beyond this, and of direct
relevance to the governing (disciplining) of expertise, the varied scientific uncertainties and
contestations around the sequestration potential and permanence of terrestrial sinks, as
debated during the Kyoto period, remain salient for the Paris Agreement, leaving open the
prospect that scientific expertise will (continue to be) selectively evoked in justifying
specific efforts at ‘‘balancing emissions and removals’’ in the decades to come.
4.2 Governing by expertise: technicalizing (politics of) land-use accounting?
With the land sector set to play a crucial and open-ended role in future climate mitigation
under the Paris Agreement, a politically charged question is how accounting for this sector
will occur in the post-2020 climate mitigation era, whether a common accounting frame-
work is required for all countries, and if this requires countries to take on quantified targets,
including for the land sector. These debates are linked in turn to overarching conflicts over
differentiation in obligations between developed and developing countries, in an agreement
that is ‘‘applicable to all.’
During negotiation of the Paris Agreement, the EU and the USA took the position that
the purpose of a common accounting framework was to permit comparability, which in
turn required quantified targets (Ajit 2015b). Whether all countries should provide quan-
tified targets thus became, and remains, a particularly contentious issue, tied up with
fundamental conflicts over whether inclusion of the land sector in NDCs is to be voluntary
or mandatory and also whether the land sector can be included in any new market
mechanisms (established via Article 6 of the Paris Agreement).
Throughout the negotiations, countries proposed a variety of approaches to mitigation
commitments, ranging from quantified economy-wide emission reduction targets (e.g.,
Governing by expertise: the contested politics of495
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
EU
37
Switzerland,
38
Norway
39
); a diversity of mitigation actions for developing countries,
including emissions intensity targets (China
40
); and commitments to qualitative policies
and measures (Nepal
41
). This debate has particular relevance for the land sector, due to the
difficulty of quantifying land sector emissions and the complexity of including these in an
accounting framework that includes industrial emissions, as discussed in Sect. 3.
42
The Paris Agreement leaves discussions of a (common) accounting framework and
specific rules for land-use accounting, to future negotiations.
43
We provide here (in
Table 1) a brief overview of a few intended
44
NDCs (INDCs) proposed by countries in the
lead up to the Paris meeting, in order to reveal the diversity of approaches currently being
adopted to land-use (and land-use accounting) in the context of the Paris Agreement, and to
the scope and scale of such inclusion.
45
Table 1provides a glimpse into the political conflicts that are likely to come to the fore
in determining (and accounting for) the contribution of the land sector to countries’ mit-
igation commitments. As a developed country negotiator noted about the politically con-
tested nature of land sector accounting, ‘in the context of a new agreement, capacities of
countries are more diverse, so this adds more complexity to the idea of a common
framework [for land-based mitigation]. It is difficult to find common accounting rules that
suit allsinks have evolved differently in different countries, leading to fighting over
accounting rules to suit national circumstances.’
46
The diversity of country circumstances in the land sector also complicates the idea of
comparability of effort. A recent comprehensive assessment of countries’ INDCs by Grassi
and Dentener (2015) indicates a potential LULUCF mitigation contribution of 20–25 %,
relative to other sectors, by 2030. This implies that the land sector is expected to be a
significant component of mitigation efforts in the future, even as the authors note large
uncertainties in these estimates ‘‘due to countries projections and accounting rules’’
(Grassi and Dentener 2015, 13, italics in original). The INDC Synthesis Report, produced
by the UNFCCC Secretariat, further adds that ‘‘several of the INDCs do not provide
comprehensive information on the assumptions and methods applied in relation to
LULUCF, which presents a major challenge for the quantitative evaluation of the aggre-
gate effect of the INDCs’’ (UNFCCC 2016, 6).
37
The Ad Hoc Working Group on the Durban Platform for Enhanced Action (ADP): the 2015 Agreement.
Submission by Italy and the European Commission on behalf of the European Union and its Member States.
Rome, October 14, 2014.
38
Elements of the 2015 Agreement: Switzerland’s views, March 4, 2014.
39
Norway submission to the ADP, March 6, 2014.
40
Views and proposals on the work of the Ad Hoc Working Group on the Durban Platform for Enhanced
Action. Submission by Nepal on behalf of the Least Developed Countries Group, March 17, 2014.
41
China’s submission on the work of the Ad hoc Working Group on Durban Platform, March 6, 2014.
42
Multiple interviewees emphasized capacity constraints facing developing countries, including three
developed and seven developing country negotiators, one policy advisor, and one NGO representative,
interviews undertaken in Bonn, Germany, June 6-11; by telephone July–October, and in Paris, France,
December 11, 2015.
43
Paragraphs 31, 37, 38 of Decision 1/CP.21 contain mandates for further negotiations to develop
accounting rules (UNFCCC 2015).
44
In 2015, countries submitted intended NDCs, which are expected to become NDCs when the Paris
Agreement enters into force in 2020.
45
It is outside the scope of this paper to analyze all submitted INDCs; our discussion here is illustrative,
rather than comprehensive.
46
Interview with developed country negotiator, Bonn, Germany, June 10, 2015.
496 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
The diversity of country circumstances and approaches, as demonstrated in INDCs,
points to the difficulty of having a common accounting framework for the land sector,
which is highlighted in the politics of deciding upon baselines or reference levels for
terrestrial emissions. Some countries argue that common accounting rules for all would be
feasible, including for the land sector, as long as flexibility exists to set land-based miti-
gation reference levels appropriate to national circumstances.
47
As one developed country
LULUCF negotiator pointed out, ‘‘the key point is having the flexibility to set appropriate
baselines, and I think a lot of developing countries don’t realize that [by doing so] they
could bring their whole land sector in and set baselines that create an expectation of zero
debits, zero credits.’
48
This implies, however, that flexible accounting rules might come to
be seen as a means for countries to report net-zero emissions, rather than as a means by
which to facilitate emission reductions. While flexibility in the setting of reference levels
and/or baselines (to accommodate whether land is a net source or net sink of emissions for
a given country at any given period of time) would be a politically plausible way for
developed and developing countries, with radically different land-use scenarios, to agree to
common accounting rules for the land sector, such an approach would obscure real
emissions from this sector.
Table 1 Overview of land-use inclusion in selected INDCs
Country Mitigation commitment Land-use inclusion Observations
Australia 26–28 % below 2005 by
2030
Included in economy-wide
target. Net–net
accounting based on
inventory reporting
IPCC guidance for natural
disturbance and variation
EU At least 40 % below 1990 by
2030
Included in economy-wide
target, but accounting
rules are yet to be
established
Inclusion of LULUCF may
weaken 40 % target, depending
on accounting rules used
Mexico Unconditional target of
25 % (conditional pledge
of up to 40 %) below BAU
by 2030
0 % deforestation by 2030
included as an adaptation
measure
Conditional pledge will require
market mechanisms; no
reference to accounting rules
New
Zealand
30 % below 2005 by 2030 Included in economy-wide
target and will build on
Kyoto Protocol rules
Provisional target pending
approaches taken to land sector
accounting and access to
carbon markets
Norway 40 % below 1990 by 2030 Included in economy-wide
target, but accounting
rules dependent on EU
decisions
Inclusion of land sector and
subsequent accounting rules
shall not reduce 40 % target
Russia 25–30 % below 1990 by
2030
Included in economy-wide
target
Significant uncertainty around
accounting assumptions for
land-use sink
US 26–28 % below 2005 by
2025
Net–net accounting for land
sector
Notes methodological challenges
to estimating emissions in land
sector
Based on author analysis of selected INDCs submitted in 2015 that included the land sector
47
Interview with developed country negotiator, Bonn, Germany, June 11, 2015.
48
Ibid.
Governing by expertise: the contested politics of497
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
More generally, this highlights the inadequacy of a ‘‘governing by expertise’’ approach
to addressing the social and political questions inherent in the role of land in moving
toward a zero-carbon future. Rather than technicalizing what are fundamentally political
conflicts, future discussions on the scale, scope, and accounting approaches to land-based
mitigation face the challenge of how to reveal and engage with, rather than obscure, the
political choices and trade-offs therein.
5 Conclusion: breaking new ground or allowing history to repeat?
In the recently negotiated Paris Agreement, land-based mitigation has moved from an
earlier marginal and contested role in multilateral climate politics to center stage. This is in
large part due to the assumed reliance on ‘‘negative emissions’’ in the second half of the
century, introduced into the debate through IPCC mitigation scenarios (IPCC 2014) and
now implicated in the long-term mitigation goal. As we have shown here, (over)-reliance
on land-based sinks could have far-reaching political consequences, given the likely dis-
tributional impacts of land-based mitigation, and concerns over fungibility in using ter-
restrial sinks to offset industrial emissions. Furthermore, accounting rules for the land
sector remain a crucial site wherein the level of ambition in the new agreement, and
allocation of responsibility and burden sharing among countries, will be negotiated.
The current state of play on these issues is that the Paris Agreement sets no direct limits
on ‘‘balancing’’ emissions with removals, although it does say that the ‘‘balancing’’ must
be done ‘‘on the basis of equity,’’ and ‘‘in the context of sustainable development and
poverty eradication’’ (UNFCCC 2015, Article 4.1). This notwithstanding, in a context
where removals via terrestrial sinks are expected to make a significant contribution to
achieving the long-term mitigation goal, this implies a need for land to shift, eventually,
from being a net source globally to a net sink. Yet the distributional consequences of this
remain crucial to analyze, with existing models ‘‘universal[ly] projecting that the majority
of agriculture and forestry mitigation, and bioenergy primary energy, will occur in
developing and transitional economies’’ (IPCC 2014, 68). With this in mind, our analysis
reveals the need for a more open political debate over diverse mitigation pathways and
their implications over the course of the century, one which takes into account the social
and environmental limits to land-based mitigation. Negotiating limits to land-based miti-
gation that consider not only the technical, but also the political, socioeconomic and equity
aspects is necessary, in determining how much, where, and what type of land-based
abatement can reasonably be relied upon for climate mitigation.
Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 Inter-
national License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution,
and reproduction in any medium, provided you give appropriate credit to the original author(s) and the
source, provide a link to the Creative Commons license, and indicate if changes were made.
References
Ajit, T. (2015a). Debate behind closed doors on the temperature goal in the Paris agreement, Paris News
Update #19. Penang: Third World Network.
Ajit, T. (2015b). Differentiation under the Paris Agreement—A tough fight, Paris News Update #23. Penang:
Third World Network.
498 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
Beck, S. (2015). Science. In Karen Ba
¨ckstrand & Eva Lo
¨vbrand (Eds.), Research handbook on climate
governance (pp. 286–296). Cheltenham: Edward Elgar.
Bo
¨ttcher, H., & Graichen, J. (2015). Impacts on the EU 2030 climate target of including LULUCF in the
climate and energy policy framework. Berlin: O
¨ko-Institut e.V.
Briner, G., & Konrad, S. (2014). Planting the foundations of a Post-2020 land sector reporting and
accounting framework. Climate Change Expert Group, OECD.
Daviet, F., & Goers, L. (2009). Forests in the balance sheet. Washington, DC: World Resources Institute.
den Elzen, M., & Lucas, P. (2003). FAIR 2.0: A decision-support model to assess the environmental and
economic consequences of future climate regimes. Netherlands Environmental Assessment Agency
(MNP).
Dutschke, M. (2013). Key issues in REDD?verification: Study commissioned by CIFOR. Occasional paper
88. CIFOR: Bogor, Indonesia.
Ecosystems Climate Alliance. (2009). De-constructing LULUCF and its perversities. Global Witness;
Wetlands International; Rainforest Action Network; The Wilderness Society.
Earth Negotiations Bulletin (ENB). (1997). Report of the third conference of the parties to the United
Nations framework convention on climate change: 111 December, 1997. International Institute for
Sustainable Development.
Estrada, M., Lee, D., Murray, B., OSullivan, R., Penman, J., & Streck, C. (2014). Land use in a future
climate agreement. Prepared with support from cooperative agreement #S-LMAQM-13-CA-1128 with
U.S. Department of State.
Fogel, C. (2005). Biotic carbon sequestration and the Kyoto Protocol: The construction of global knowledge
by the intergovernmental panel on climate change. International Environmental Agreements: Politics,
Law and Economics, 5(2), 191–210.
Fry, I. (2002). Twists and turns in the jungle: Exploring the evolution of land use, land-use change and
forestry decisions within the Kyoto Protocol. RECIEL, 11(2), 159–168.
Fry, I. (2007). More twists, turns and stumbles in the jungle: A further exploration of land use, land-use
change and forestry decisions within the Kyoto Protocol. RECIEL, 16(3), 1–15.
Grassi, G., & Dentener, F. (2015). Quantifying the contribution of the land use sector to the Paris climate
agreement, EUR 27561.
Gupta, A. (2011). An evolving science-society contract in India: The search for legitimacy in anticipatory
risk governance. Food Policy, 36(6), 736–741.
Gupta, A., Andresen, S., Siebenhu
¨ner, B., & Biermann, F. (2012). Science networks. In Frank Biermann &
Philipp Pattberg (Eds.), Global environmental governance reconsidered (pp. 69–93). Cambridge, MA:
MIT Press.
Gupta, A., & Mason, M. (2016). Disclosing or obscuring? The politics of transparency in global climate
governance. Current Opinion in Environmental Sustainability, 18, 82–90.
Hansen, J., Karecha, P., Sata, M., et al. (2013). Assessing ‘‘Dangerous climate change’’: Required reduction
of carbon emissions to protect young people, future generations and nature. PLoS ONE, 8(12), 1–26.
Ho
¨hne, N., Wartmann, S., Herold, A., & Freibauer, A. (2007). The rules for land use, land use change and
forestry under the Kyoto Protocol—Lessons learned for the future climate negotiations. Environmental
Science & Policy, 10(4), 353–369.
IPCC (2014). Smith P., et al. Chapter 11: Agriculture, forestry and other land use (AFOLU). In Edenhofer,
O., R. et al. (Eds.), 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.
Iversen, P., Lee, D., & Rocha, M. (2014). Understanding land use in the UNFCCC.
Jasanoff, S. (1998). Fifth Estate: Science advisors as policy makers. Cambridge MA: Harvard University
Press.
Jasanoff, S. (Ed.). (2004). States of knowledge: The coproduction of science and the social order. London:
Routledge.
Jasnoff, S. (2003). (No?) Accounting for expertise. Science and Public Policy, 30(3), 157–162.
Lee, D., Penman, J., & Streck, C. (2015). Land use in a future climate agreement. Washington DC: Climate
Focus.
Levin, K., Morgan, J., & Song, J. (2015). INSIDER: Understanding the Paris agreement’s long-term goal to
limit global warming. Washington, DC: World Resources Institute.
Lo
¨vbrand, E. (2004). Bridging political expectations and scientific limitations in climate risk management—
On the uncertain effects of international carbon sink policies. Climatic Change, 67, 1–12.
Lo
¨vbrand, E. (2009). Revisiting the politics of expertise in light of the Kyoto negotiations on land use
change and forestry. Forest Policy and Economics, 11(5–6), 404–412.
Governing by expertise: the contested politics of499
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
Macintosh, A. (2011). The Australia clause and REDD: A cautionary tale. Climatic Change, 112(2),
169–188.
Mackey, B., Prentice, I. C., Steffen, W., et al. (2013). Untangling the confusion around land carbon science
and climate change mitigation policy. Nature Climate Change, 3(6), 552–557.
Parker, C., Merger, E., Streck, C., et al. (2014). The land-use sector within the post-2020 climate regime.
Copenhagen: Norden.
Powlson, D. S., Whitmore, A. P., & Goulding, C. J. (2011). Soil carbon sequestration to mitigate climate
change: A critical re-examination to identify the true and the false. European Journal of Soil Science,
62(1), 42–55.
Rocha, M., Hare, B., Cantzler, J., et al. (2015). New Zealand deploys creative accounting to allow emissions
to rise. Berlin: Climate Action Tracker.
Sarewitz, D. (2004). How science makes environmental controversies worse. Environmental Science &
Policy, 7(4), 385–403.
Schaeffer, M., Hare, B., Rocha, M., & Rogelj, J. (2013). Adequacy and feasibility of the 1.5C long-term
global limit. Brussels: Climate Action Network Europe.
Schlamadinger, B., Bird, N., Johns, T., et al. (2007). A synopsis of land use, land-use change and forestry
(LULUCF) under the Kyoto Protocol and Marrakech Accords. Environmental Science & Policy, 10(4),
271–282.
UNFCCC. (1997). Adoption of the Kyoto Protocol to the United Nations Framework Convention on Climate
Change, decision 1/CP.3 (FCCC/CP/1997/7/Add.1). Bonn: United Nations Framework Convention on
Climate Change Secretariat.
UNFCCC. (2015). Adoption of the Paris Agreement, decision 1/CP.21 (FCCC/CP/2015/10/Add.1). Bonn:
United Nations Framework Convention on Climate Change Secretariat.
UNFCCC. (2016). Aggregate effect of the intended nationally determined contributions: An update. Syn-
thesis report by the Secretariat.
Weingart, P. (1999). Scientific expertise and political accountability: Paradoxes of science in politics.
Science and Public Policy, 26(3), 151–161.
500 K. Dooley, A. Gupta
123
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
1.
2.
3.
4.
5.
6.
Terms and Conditions
Springer Nature journal content, brought to you courtesy of Springer Nature Customer Service Center
GmbH (“Springer Nature”).
Springer Nature supports a reasonable amount of sharing of research papers by authors, subscribers
and authorised users (“Users”), for small-scale personal, non-commercial use provided that all
copyright, trade and service marks and other proprietary notices are maintained. By accessing,
sharing, receiving or otherwise using the Springer Nature journal content you agree to these terms of
use (“Terms”). For these purposes, Springer Nature considers academic use (by researchers and
students) to be non-commercial.
These Terms are supplementary and will apply in addition to any applicable website terms and
conditions, a relevant site licence or a personal subscription. These Terms will prevail over any
conflict or ambiguity with regards to the relevant terms, a site licence or a personal subscription (to
the extent of the conflict or ambiguity only). For Creative Commons-licensed articles, the terms of
the Creative Commons license used will apply.
We collect and use personal data to provide access to the Springer Nature journal content. We may
also use these personal data internally within ResearchGate and Springer Nature and as agreed share
it, in an anonymised way, for purposes of tracking, analysis and reporting. We will not otherwise
disclose your personal data outside the ResearchGate or the Springer Nature group of companies
unless we have your permission as detailed in the Privacy Policy.
While Users may use the Springer Nature journal content for small scale, personal non-commercial
use, it is important to note that Users may not:
use such content for the purpose of providing other users with access on a regular or large scale
basis or as a means to circumvent access control;
use such content where to do so would be considered a criminal or statutory offence in any
jurisdiction, or gives rise to civil liability, or is otherwise unlawful;
falsely or misleadingly imply or suggest endorsement, approval , sponsorship, or association
unless explicitly agreed to by Springer Nature in writing;
use bots or other automated methods to access the content or redirect messages
override any security feature or exclusionary protocol; or
share the content in order to create substitute for Springer Nature products or services or a
systematic database of Springer Nature journal content.
In line with the restriction against commercial use, Springer Nature does not permit the creation of a
product or service that creates revenue, royalties, rent or income from our content or its inclusion as
part of a paid for service or for other commercial gain. Springer Nature journal content cannot be
used for inter-library loans and librarians may not upload Springer Nature journal content on a large
scale into their, or any other, institutional repository.
These terms of use are reviewed regularly and may be amended at any time. Springer Nature is not
obligated to publish any information or content on this website and may remove it or features or
functionality at our sole discretion, at any time with or without notice. Springer Nature may revoke
this licence to you at any time and remove access to any copies of the Springer Nature journal content
which have been saved.
To the fullest extent permitted by law, Springer Nature makes no warranties, representations or
guarantees to Users, either express or implied with respect to the Springer nature journal content and
all parties disclaim and waive any implied warranties or warranties imposed by law, including
merchantability or fitness for any particular purpose.
Please note that these rights do not automatically extend to content, data or other material published
by Springer Nature that may be licensed from third parties.
If you would like to use or distribute our Springer Nature journal content to a wider audience or on a
regular basis or in any other manner not expressly permitted by these Terms, please contact Springer
Nature at
onlineservice@springernature.com
... Such accounting practices are responding to political rather than scientific considerations and involve a number of risks and complexities (Lövbrand, 2004;Höhne et al., 2007), raising concerns about the weakening of targets (Climate Action Tracker, 2020). While the technical accounting difficulties with making fossil and biotic carbon equivalent have long been recognized, the social, environmental, and climate implications often remain obscured (Fogel, 2005;Dooley and Gupta, 2017). ...
... Rendering biotic and fossil carbon equivalent also conflates the drivers of climate change. It obscures whether mitigation is achieved through reduced fossil emissions or increased biotic sequestration (Dooley and Gupta, 2017), suggesting that full decarbonization of the energy sector can be avoided (or delayed) by sufficient "greening" in the land sector. However, the technological, social, and economic transitions required in these sectors differ significantly, as do their relative contributions to climate change. ...
Article
Full-text available
Concerns are increasingly raised over the centrality of carbon removal in climate policy, particularly in the guise of ‘net-zero’ targets. Most significantly perhaps, treating emissions and removals as equivalent obscures emission reductions, resulting in ‘mitigation deterrence’. Yet the conflation of emission reductions and removals is only one among several implicit equivalences in carbon removal accounting. Here we examine three other forms – carbon, geographical and temporal equivalence - and discuss their implications for climate justice and the environmental risks with carbon removal. We conclude that ‘undoing’ these equivalences would further a just response to the climate crisis and tentatively explore what such undoing might look like in practice.
... For example, the removal by afforestation and reforestation was included in the Kyoto Protocol under the land-use, land-use change and forestry (LULUCF) category. However, there was a huge, political controversy over this decision to include biological carbon sinks as mitigation options (Dooley and Gupta, 2017;Moe and Røttereng, 2018;Carton et al., 2020). The use of terrestrial carbon sinks as carbon offset was-and is still-severely criticised as a way to circumvent necessary mitigation, thereby perpetuating the continued use of fossil fuels. ...
... But this would likely lead to misperceived substitutability that causes harmful consequences and undermines the integrity of mitigation policy. For example, the unrestricted use of landbased CDR might create a perverse incentive to offset industrial carbon emissions from fossil fuels by terrestrial carbon sinks with no considerations of social, ethical and environmental impacts (Dooley and Gupta, 2017;Dooley and Kartha, 2018). Likewise, the prospect of overshoot-i.e., that future large-scale CDR will compensate delayed mitigation today-does not only justify the slow act on mitigation but also risk putting future generations on an unjust gamble (Anderson and Peters, 2016;Lenzi et al., 2018;Asayama and Hulme, 2019). ...
Article
Full-text available
There appears to be a paradox in the debate over carbon dioxide removal (CDR) technologies. On the one hand, CDR is recognised as a crucial technical option to offset residual carbon emissions from fossil fuel use, so that it can help a transition to the net-zero energy system. But on the other hand, a serious concern is raised about CDR as a way to circumvent necessary emissions reduction, hence perpetuating the status quo of fossil fuel use. This apparent paradox of CDR, however, has less to do with technology itself but more with the difficulty to move away from carbon lock-in—the deeply entrenched fossil-fuel-based energy system. The challenge of decarbonisation is indeed about eroding the deep lock-ins that perpetuate the production and consumption of fossil fuels. To understand the role of CDR in overcoming carbon lock-in, looking back the past debate on carbon capture and storage (CCS) is instructive. Although both CCS and CDR are criticised for keeping the fossil status quo, there is a crucial difference between them. Unlike CCS, CDR can possibly avoid the risk of reinforced lock-in, given its physical decoupling from fossil fuel use. And yet CDR has the risk of undue substitution that continues unjustly fossil carbon emissions. A change of the framing question is thus needed to puzzle out the paradox of CDR. To rightly place CDR in the challenge of rapid decarbonisation, we should ask more how CDR technologies can be used in alignment with a managed decline to fossil fuel production.
... To anticipate is to chart the future realms of possibility, thus what is in and out of that frame shapes which 'processes' and what 'practices' are seen to be problematic (Anderson 2010, in Granjou et al. 2017, Esguerra 2019. The assumptions embedded into such models and practices have implications for what decisions are made, and therefore, how costs and benefits are distributed and which injustices are addressed or exacerbated (Dooley & Gupta 2017, Allain et al. 2020. Modelling practices, participatory or otherwise, play out on an existing sociopolitical landscape when they are mobilized to inform decisions. ...
... However, these assumptions have implications for the legitimacy of representations of the future and their utility within decision-making. It matters what and whose knowledge is represented because the socio-political implications of maps and models are in part a product of the assumptions upon which they were founded (Dooley & Gupta 2017). This performative nature has meant that futuring practices themselves have become the focus of political and academic debate and contestation (Esguerra 2019). ...
Article
Future global environmental change will have a significant impact on biodiversity through the intersecting forces of climate change, urbanization, human population growth, overexploitation, and pollution. This presents a fundamental challenge to conservation approaches, which seek to conserve past or current assemblages of species or ecosystems in situ. This review canvases diverse approaches to biodiversity futures, including social science scholarship on the Anthropocene and futures thinking alongside models and scenarios from the biophysical science community. It argues that charting biodiversity futures requires processes that must include broad sections of academia and the conservation community to ask what desirable futures look like, and for whom. These efforts confront political and philosophical questions about levels of acceptable loss, and how trade-offs can be made in ways that address the injustices in the distribution of costs and benefits across and within human and non-human life forms. As such, this review proposes that charting biodiversity futures is inherently normative and political. Drawing on diverse scholarship united under a banner of ‘futures thinking’ this review presents an array of methods, approaches and concepts that provide a foundation from which to consider research and decision-making that enables action in the context of contested and uncertain biodiversity futures.
... Increasing LULUCF emission sinks, in parallel to reducing emissions in the other sectors, is important but outside the scope of this analysis. Additionally, emissions from LULUCF are notably uncertain, and accounting methods vary greatly (Dooley & Gupta 2017;Krug 2018). This increases the uncertainty on emission projections. ...
Article
Full-text available
Many years passed since the adoption of the Paris Agreement, which invites countries to determine their own contributions to climate change mitigation efforts. The Agreement does not offer a standard to measure progress but relies on a process of periodic stocktakes to inform ambition-raising cycles. To contribute to this process, we compare 2021 greenhouse gas emission projections up to 2030 against equivalent projections prepared back in 2015. Both sets of projections were prepared using the same bottom-up modelling approach that accounts for adopted policies at the time. We find that 2021 projections for the G20 as a group are almost 15% lower (approximately 6 GtCO2eq) in 2030 than projected in 2015. Annual emissions grow 1% slower in the coming decade than projected in 2015. This slower growth mostly stems from the adoption of new policies and updated expectations on technology uptake and economic growth. However, around one-quarter of these changes are explained by the effects of the COVID-19 pandemic on short-term emissions and economic forecasts. These factors combined result in substantially lower emission projections for India, the European Union plus the UK (EU27 + UK), the Unites States, Russia, Saudi Arabia, and South Africa. We observe a remarkable change in South African projections that changed from a substantial increase to now a decline, driven in part by the planned phase-out of most of its coal-based power. Emissions in India are projected to grow slower than in 2015 and in Indonesia faster, but emissions per capita in both countries remain below 5 tCO2eq in 2030, while those in the EU27 + UK decline faster than expected in 2015 and probably cross the 5 tCO2eq threshold before 2030. Projected emissions per capita in Australia, Canada, Saudi Arabia, and the United States are now lower than projected in 2015 but remain above 15 tCO2eq in 2030. Although emission projections for the G20 improved since 2015, collectively they still slightly increase until 2030 and remain insufficient to meet the Paris Agreement temperature goals. The G20 must urgently and drastically improve adopted policies and actions to limit the end-of-century warming to 1.5 °C. Supplementary information: The online version contains supplementary material available at 10.1007/s11027-022-10018-5.
... 14 It thus becomes important to ask: who selects the variables that are measured, what assumptions about relevance and representativeness underpin these choices, 37 and what is rendered visible versus what is left obscure? 38,39 This is pivotal because digital technologies always involve a translation of the complexity of the world into computable digits understood against a certain interpretative frame. As a ''critical transparency studies'' perspective has thus long argued, the uptake, institutionalization, and effects of environmental disclosure (including digitally enabled disclosure) need to be scrutinized within the broader normative and political contexts of its generation and use. ...
Article
Full-text available
Digital technologies play an increasingly important role in addressing environmental challenges, such as climate change and resource depletion. Yet, the characteristics and implications of digitalized environmental governance are still under-conceptualized. In this perspective, we distinguish three dimensions of governance: (1) seeing and knowing, (2) participation and engagement, and (3) interventions and actions. For each dimension, we provide a critical perspective on the shifts that digital technologies generate in governance. We argue against the assumption that the use of digital technologies automatically results in improved outcomes or in more democratic decision-making. Instead, attention needs to be paid to the wider political and normative context in which digital technologies are proposed, designed, and used as environmental governance tools. We conclude with key questions for academics and policymakers to broaden the debate on responsible design and use of digital technologies in environmental governance.
... However, decisions are often not based on weighing costs and benefits alone, but on heuristics, culture and values (Aarts and Dijksterhuis, 2000;Kloeckner et al., 2003;Ascher, 2007) within organizations, institutions (Hall et al., 2003;Munck et al., 2014;Dooley, 2017), and communities. ...
Book
Full-text available
Droughts have deep, widespread and underestimated impacts on societies, ecosystems, and economies. They incur costs that are borne disproportionately by the most vulnerable people. The extensive impacts of drought are consistently underreported even though they span large areas, cascade through systems and scales, and linger through time, affecting millions of people and contributing to food insecurity, poverty, and inequality. Climate change is increasing temperatures and disrupting rainfall patterns, increasing the frequency, severity, and duration of droughts in many regions across the globe. As we move towards a 2˚C warmer world, urgent action is required to better understand and more effectively manage drought risk to reduce the devastating toll on human lives and livelihoods, and ecosystems. The GAR Special Report on Drought 2021 explores the systemic nature of drought and its impacts on achievement of the Sendai Framework for Disaster Risk Reduction, the SDGs and human and ecosystems health and wellbeing.
... It is important to note, however, that the land-use sector is often treated as a whole, without clearly separating negative emissions (cf. Dooley and Gupta, 2017;Minx et al., 2018). There is a degree of flexibility in the LT-LEDS with several countries including pathways where enhancement of natural sinks is essential for compensating for residual emissions, while BECCS feature in some pathways providing more time to transform society; without BECCS, emissions need to be reduced faster (e.g., EU, UK, and US). ...
Article
Full-text available
The 2015 Paris Agreement aims to strengthen the global response to climate change, and to maintain an average global temperature well below 2◦C, with aspirations toward 1.5◦C, by means of balancing sources and sinks of greenhouse gas emissions. Following this, the importance of carbon dioxide removal in global emission pathways has been further emphasized, and Negative Emissions Technologies (NETs) that capture carbon from the atmosphere and remove it from the system have been put in the spotlight. NETs range from innovative, engineered technologies, to well-known approaches like afforestation/reforestation. These technologies essentially compensate for a shrinking carbon budget coupled with hard-to-abate future emissions, and a historical lack of action. However, none has been deployed at scales close to what is envisioned in emission pathways in line with the Paris Agreement goals. To understand the potential contribution of NETs to meet global emission goals, we need to better understand opportunities and constraints for deploying NETs on a national level. We examine 17 Long-Term Low Greenhouse Gas Emission Development Strategies (LT-LEDS), and discuss them in the context of available NETs feasibility assessments. Our mapping shows that most countries include NETs in their long-term strategies, and that enhancement of natural sinks is the most dominating type of NET in these strategies. In line with many feasibility assessments, LT-LEDS focus on technical and biophysical considerations, and neglect socio-cultural dimensions. We suggest that feasibility assessments at the national level need to be more holistic; context-specific and comprehensive in terms of aspects assessed.
Chapter
Environmental problems and energy crisis in most nations of the world are traceable to lack of adequate development of processes and products from renewable and nonrenewable resources. This paper examined viable opportunities of developing energy efficient processes and products from renewable and nonrenewable resources. Approach used includes literature review, methodical framework, and theoretical solution for the resolution of the modern-day problems of resource management by finding, optimizing, and recycling processes and products for the betterment of Nigeria. Findings reveal that most researches have not attended to development of energy efficient processes and products. It was concluded that life cycle management of engineering materials is critical to health and wealth of developed and developing countries. Notable interventions and challenges facing public health and sustainable development were highlighted. Detailed knowledge of process engineering and the work of a process engineer both for the benefit of the industry and for the public. Development of energy efficient processes and products from renewable and nonrenewable resources requires adequate and special attention in Nigeria. Recommendations include implementation of effective policy, adequate funding, resource efficiency plan, and involvement of stakeholders at all levels of processes and production. When it comes to products, the materials which they are made of determine what will happen to them after manufacturing and use. Products made of materials like plastic take decades to decompose. Dealing with the sources of energy and disposal of waste is a vital approach to address most environmental issues.
Book
Full-text available
This volume showcases the diversity of climate change politics and practices across Southeast Asia. Through a series of country-level case studies and regional perspectives, the authors in this volume explore the complexities and contested nature of climate governance in what can be considered as one of the most dynamic and multi-faceted regions of the world. They reflect upon the tensions between authoritarian and democratic climate change governance, the multiple roles of civil society and non-state interventions, and the conflicts between state planning and market-driven climate change governance. Shedding light on climate change mitigation and adaptation efforts in Southeast Asia, this book presents the various formal and informal institutions of climate change governance, their relevant actors, procedures, and policies. Empirical findings from a diverse set of environments are merged into a cross-country comparison that allows for elaborating on similar patterns whilst at the same time highlighting the distinct features of climate change governance in Southeast Asia. Drawing on case studies from all Southeast Asian countries, namely Brunei Darussalam, Cambodia, Indonesia, Laos, Malaysia, Myanmar, the Philippines, Singapore, Thailand, Timor-Leste, and Viet Nam, this book will be of great interest to students, scholars, and practitioners dealing with climate change and environmental governance.
Article
Full-text available
Securing accountability of states for their climate actions is a continuing challenge within multilateral climate politics. This article analyses how novel, face-to-face, account-giving processes for developing countries, referred to as ‘Facilitative Sharing of Views’, are functioning within the United Nations Framework Convention on Climate Change (UNFCCC) and what these processes help to shed light on. We analyse the nature and scope of the ‘answerability’ being generated within these novel processes, including what state-to-state questioning and responses focus on, and what ‘performing’ accountability in this manner delivers within multilateral climate politics. We find that a limited number of countries actively question each other within the FSV process, with a primary focus on sharing information about the technical and institutional challenges of establishing domestic ‘measuring, reporting and verification’ systems and, to lesser extent, mitigation actions. Less attention is given to reporting on support. A key aim is to facilitate learning, both from the process and from each other. Much effort is expended on legitimizing the FSV process in anticipation of its continuation in adapted form under the 2015 Paris Agreement. We conclude by considering implications of our analysis. Key policy insights • We analyse developing country engagement in novel face-to-face account-giving processes under the UNFCCC • Analysis of four sessions of the ‘Facilitative Sharing of Views’ reveals a focus on horizontal peer-to-peer learning • States question each other more on GHG emission inventories and domestic MRV systems and less on mitigation and support • We find that limited time and capacity to engage, one-off questioning rather than a dialogue, and lack of recommended follow-up actions risks generating ‘ritualistic’ answerability • Such account-giving also intentionally sidesteps contentious issues such as responsibility for ambitious and fair climate action but may still help to build trust • Much effort is expended on ‘naming and praising’ participant countries and legitimizing the process
Conference Paper
Full-text available
Key Points  Land-use mitigation is essential to meet the goals discussed in the context of avoiding dangerous climate change  The Geneva negotiating text contains all the elements needed to include land use  Work after Paris will be needed on methodological detail and transparency  Existing agreements on LULUCF and REDD-plus are useful and should be recognized and built upon in a new agreement. Overview Land use has a reputation for complexity and has in the past impeded as well as catalyzed international climate negotiations. It seems important therefore, prior to Parties meeting later this year in Paris, to consider what elements from the negotiating text provided by the Geneva meeting in February 2015 should be included in the Paris agreement. This briefing note presents the results of an analysis of the Geneva text with this in mind. It suggests what specific to land-use needs to be included, what can be left to subsequent detailed negotiations, and what will be covered by general provisions of the Paris agreement. The paper also summarizes what explanations should be sought on nationally determined contributions to achieve transparency. Briefing Note
Technical Report
Full-text available
The land-use sector serves key environmental and social functions and supports the livelihoods of around a half of the world’s population. Despite its importance, however, the climate regime fails to formulate a coherent vision or set of incentives for mitigation and adaptation from the sector. The negotiation of a future climate treaty that will take effect in 2020 presents a key opportunity to improve the current system and create an integrated accounting and incentive framework for adaptation and mitigation strategies across all land-uses. This report - conducted by Climate Focus together with UNIQUE forestry and land use - analyses the current status of the land-use sector under the United Nations Framework Convention on Climate Change and its Kyoto Protocol, and formulates options for how various incentives and systems could be harmonized under a future climate treaty.
Article
Full-text available
The complexities inherent in land use, land-use change and forestry (LULUCF) activities have led to contentious and prolonged debates about the merits of their inclusion in the 2008–2012 first commitment period of the Kyoto Protocol. Yet the inclusion of these activities played a key role in agreement on the general framework of the Kyoto Protocol, and LULUCF will likely continue to play a substantial part in negotiations on national commitments post-2012. The Marrakech Accords dictate which LULUCF activities are to be included under the Kyoto Protocol and provide rules on how they are to be accounted in the first commitment period. However, these rules have limitations and drawbacks that may be avoided in the structure of future commitments beyond 2012. Through adherence to the objectives of the United Nations Framework Convention on Climate Change (UNFCCC), and the incorporation of several critical features, a future framework can more effectively address the mitigation challenges and opportunities of this sector.
Article
Full-text available
We assess climate impacts of global warming using ongoing observations and paleoclimate data. We use Earth's measured energy imbalance, paleoclimate data, and simple representations of the global carbon cycle and temperature to define emission reductions needed to stabilize climate and avoid potentially disastrous impacts on today's young people, future generations, and nature. A cumulative industrial-era limit of ∼500 GtC fossil fuel emissions and 100 GtC storage in the biosphere and soil would keep climate close to the Holocene range to which humanity and other species are adapted. Cumulative emissions of ∼1000 GtC, sometimes associated with 2°C global warming, would spur "slow" feedbacks and eventual warming of 3-4°C with disastrous consequences. Rapid emissions reduction is required to restore Earth's energy balance and avoid ocean heat uptake that would practically guarantee irreversible effects. Continuation of high fossil fuel emissions, given current knowledge of the consequences, would be an act of extraordinary witting intergenerational injustice. Responsible policymaking requires a rising price on carbon emissions that would preclude emissions from most remaining coal and unconventional fossil fuels and phase down emissions from conventional fossil fuels.
Article
Full-text available
Depletion of ecosystem carbon stocks is a significant source of atmospheric CO2 and reducing land-based emissions and maintaining land carbon stocks contributes to climate change mitigation. We summarize current understanding about human perturbation of the global carbon cycle, examine three scientific issues and consider implications for the interpretation of international climate change policy decisions, concluding that considering carbon storage on land as a means to 'offset' CO2 emissions from burning fossil fuels (an idea with wide currency) is scientifically flawed. The capacity of terrestrial ecosystems to store carbon is finite and the current sequestration potential primarily reflects depletion due to past land use. Avoiding emissions from land carbon stocks and refilling depleted stocks reduces atmospheric CO2 concentration, but the maximum amount of this reduction is equivalent to only a small fraction of potential fossil fuel emissions.
Chapter
This chapter explores the role of the Intergovernmental Panel on Climate Change (IPCC) in global climate governance. The IPCC represents one of the most ambitious and influential efforts ever undertaken by the international community to provide policy-relevant science. The joint award of the Nobel Peace Prize to the IPCC in 2007 underlined the authoritative status of scientific knowledge in policymaking on climate change. The chapter combines constructivist approaches to explore how and with what effects the IPCC acts as a politically powerful agent in climate politics even if the organization itself claims to be neutral and not policy prescriptive. Based on these empirical findings, it asks whether the IPCC is robust enough to address future challenges in a changing political architecture and outlines some of the questions to be addressed by future research. © Karin Bäckstrand and Eva Lövbrand 2015. All rights reserved.
Article
Transparency is increasingly evoked within public and private climate governance arrangements as a key means to enhance accountability and improve environmental outcomes. We review assumed links between transparency, accountability and environmental sustainability here, by identifying four rationales underpinning uptake of transparency in governance. We label these democratization, technocratization, marketization and privatization, and assess how they shape the scope and practices of climate disclosure, and to what effect. We find that all four are discernible in climate governance, yet the technocratic and privatization rationales tend to overtake the originally intended (more inclusive, and more public-good oriented) democratization and marketization rationales for transparency, particularly during institutionalization of disclosure systems. This reduces transparency's potential to enhance accountability or trigger more environmentally sustainable outcomes.