a very real and practical contribution? lessons from the kalimantan
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A very real and practical contribution? Lessons from
the Kalimantan Forests and Climate Partnership
Erik Olbrei and Stephen Howes
Abstract
On 9 September 2007, Australian Ministers and the Indonesian President announced a $100 million Kalimantan Forests and Climate Partnership (KFCP). This would involve protecting 70,000 hectares of peat forests, re-flooding 200,000 hectares of dried peatland, and planting 100 million trees in Central Kalimantan, Indonesia. Since then, the ambitions of KFCP have been quietly but drastically scaled back. The area expected to be re-flooded by the project is now just over 10 per cent of the original target. And little progress has been made on the ground. Four years on, blocking of the large canals required for re-flooding has yet to commence, and only 50,000 trees have been planted against the initial target of 100 million. What has happened to what was labelled at its launch as “a very real and very practical contribution”, one which would yield “immediate and tangible results”? We analyse KFCP both as an aid “announceable” and as a REDD (Reducing Emissions from Deforestation and Degradation) demonstration project, and reach two main conclusions. First, KFCP illustrates the damage that an emphasis on announcing new projects and a lack of attention to reporting on project progress can cause aid. Not enough has been done to publicly reposition KFCP as a much smaller, demonstration project. Second, slow progress made in implementing KFCP (and other REDD projects), when juxtaposed against the continued rapid rate of land conversion in Indonesia, suggests that the current approach is not working. There is no easy solution. Reducing deforestation in Indonesia is a difficult task because the drivers of deforestation – which range from weak governance to a strong industry lobby and the attractive economics of palm oil – are strong and difficult to tackle. If it is worth continuing, then the focus on pilots and processes which has characterised Australia’s engagement in Indonesia’s forestry sector in recent years should be re-oriented towards a more ambitious engagement. This should be supported by a vigorous high-level policy dialogue and at least the realistic prospect of a large amount of public funds.
Discussion Paper 16
MARCH 2012
A very real and practical contribution? Lessons from the
Kalimantan Forests and Climate Partnership
Erik Olbrei
Stephen Howes
Erik Olbrei (erik.olbrei@anu.edu.au) is a Research Associate of
the Development Policy Centre. He completed a Master of
Climate Change qualification by research at the ANU in 2011.
Stephen Howes (stephen.howes@anu.edu.au) is Professor of
Economics and Director, Development Policy Centre, Crawford
School of Public Policy, Australian National University.
Olbrei, E & Howes, S 2012, ‘A very real and practical contribution? Lessons
from the Kalimantan Forests and Climate Partnership’, Development
Policy Centre Discussion Paper #16, Crawford School of Public Policy,
The Australian National University, Canberra.
The Development Policy Centre is a research unit at the
Crawford School of Public Policy, The Australian National
University. The discussion paper series is intended to facilitate
academic and policy discussion. Use and dissemination of this
discussion paper is encouraged; however, reproduced copies
may not be used for commercial purposes.
The views expressed in discussion papers are those of the
authors and should not be attributed to any organisation with
which the authors might be affiliated.
For more information on the Development Policy Centre, visit
http://devpolicy.anu.edu.au
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A very real and practical contribution? Lessons from the Kalimantan
Forests and Climate Partnership
Acknowledgements
A large number of people provided their time and insights, upon which we have
drawn extensively in the development of this paper. For the first part of the
research, undertaken in late 2010 and early 2011, we are indebted to Tim Jessup,
Grahame Applegate, George Collett and Neil Scotland at the Indonesia Australia
Forest Carbon Partnership office in Jakarta; Dan Heldon at AusAID, Nick
Mawdsley, former team leader of the Ex-Mega Rice Project Master Plan; Pak Eko
Pranadhita, Pak Al Zaqie, Pak Herwasono, Ben Tular, and KFCP Coordinator
Erwinsyah of the KFCP project team in Palangkaraya. We are particularly
indebted to project personnel in the field, including Ibu Natalia at Mantangai
Hulu, Ibu Endang at Katunjung, Pak Suhada and Pak Josef from the KFCP / CARE
field staff, as well as Pak Jhanson Regalino. In Canberra, John Raison and Pep
Canadell were very helpful.
During the second visit to Indonesia we benefited greatly from discussions with
Dr Suwido and Dr Yusurum at UNPAR, Arie Rompas of WALHI, Pak Budi, Saribi,
Angi Rohan, and Nurhadi in Kapuas, while in Jakarta, Pak Yuyu at the Ministry of
Forestry, Elfian Effendi at Greenomics, Rogier Klavier at UN-REDD, and Bill
Hellier were of great assistance. In Bogor we met with the team at Telapak
including Pak Hapsoro and Pak Abu, as well as the team at Forest Watch
Indonesia.
Particular thanks to Jacqui DeLacy (Senior Representative, AusAID Jakarta) as
well as Tim Jessup, Brendan Mackey, Pak Medrilzam, Peter McCawley, Frank
Jotzo, Julia Newton-Howes, Robin Davies and Luca Tacconi for valuable
comments on various drafts of this paper.
Finally, we hasten to add that responsibility for the conclusions and
perspectives set out in this paper rests with the authors alone.
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1. Introduction
On 9 September 2007, then Australian Minister for Foreign Affairs, Alexander
Downer, then Minister for Environment and Water Resources, Malcolm Turnbull,
and the Indonesian President, Susilo Bambang Yudhoyono, announced the $100
million Kalimantan Forests and Climate Partnership (KFCP). KFCP, they
announced, would protect 70,000 hectares (ha) of peat forests, re-flood 200,000
ha of dried peatland, and plant 100 million trees in Central Kalimantan,
Indonesia. It would lead to a reduction of 700 million tonnes of greenhouse gas
emissions over a period of 30 years (Antara 2007; Downer 2007). It would, as
Minister Downer put it, make “a very real and very practical contribution to
improving our environment” (Downer 2007a).
Four years on, the emissions-reduction ambitions of KFCP have been quietly but
drastically scaled back, and little progress has been made on the ground. KFCP is
now described as a demonstration project, and the area to be re-flooded is now
just over 10 percent of the original total. The blocking of large canals required
for re-flooding of deforested peatland has not yet commenced, development of
reference emission levels is incomplete, and only a modest start has been made
with re-planting of peatland species.
What has happened to a project which promised, according to Minister Downer
in September 2007, “immediate and tangible results”? This is an important
question. Foreign aid is particularly subject an emphasis on “announceables”
(Easterly 2002). The recent Australian Independent Review of Aid Effectiveness
noted that “The aid program has always been prone to a strong focus on
announcements by ministers”, and recommended that an “effectiveness culture
focused on results, rather than an announcement culture leading to
fragmentation, should drive the aid program” (Hollway et al. 2011:256). There is
little in the public domain to suggest that the KFCP objectives have been
changed, and little indication that it is not on track to meet its new, much more
modest objectives. Case-study analyses such as this are important to promote
accountability for aid spending.
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An analysis of KFCP also promises to throw light on both the Indonesian and the
international effort to reduce emissions from deforestation and degradation
(REDD)1 in tropical developing countries. Land-use, land-use change and
forestry (LULUCF) is estimated to contribute 12–15% of all global anthropogenic
greenhouse gases (GHGs), about the same as transport and agriculture.2 And
most emissions from deforestation and forest degradation are in developing
countries. Indonesia is both one of the highest emitters as a result of
deforestation and a leading REDD supporter.
The Bali Action Plan, agreed at the 2007 United Nations Framework Convention
on Climate Change Conference (UNFCCC 2008), hosted by the Indonesian
Government, generated a wave of optimism in relation to efforts to reduce
forestry-related emissions. Much effort has subsequently gone into developing
the processes and practical approaches needed to implement REDD. A large
number of “preparatory” and “readiness” activities, involving development of
national plans, methodologies, policies, and pilot or demonstration projects, are
under way. These are intended to lead to an implementation phase with
payments through an international carbon market for quantified forestry-related
emission reductions against agreed reference levels (Angelsen et al. 2009;
Ministry of Forestry 2010; RECOFTC 2010). One survey counted over 100
readiness activities and around 80 demonstration projects aimed at trialling
REDD institutions, mechanisms and implementation strategies as at October
2009 (Cerbu 2010). Indonesia is the most prominent among REDD host
countries, with around half of all global REDD activities (Wertz-Kanounnikoff
and Kongphan-Apirak 2009).
1. REDD is now often referred to as ‘REDD+’ to indicate that sustainable forestry has been added to the agenda (in addition to reducing emissions by avoiding deforestation and forest degradation). However, for simplicity, we continue to use the acronym ‘REDD’ throughout this paper, except where ‘REDD+’ appears in quotes. 2. LULUCF emissions have long been thought to be around 18% of all emissions, but this has recently been revised. A re-calculation for 2008 using IPCC methods but using updated (lower) estimates for deforestation and degradation from FAO resulted in lower CO2 emission estimates for the sector. At the same time, emissions from fossil fuel have increased more than predicted, again reducing the LULUCF share. This study estimated the LULUCF share to be 15% of all emissions (Van Der Werf, 2009). Against that, the World Resources Institute’s Climate Analysis Indicators Tool (CAIT) data for 2005 (its most recent data which includes land-use change) estimates total global emissions of 44 Gt, of which electricity and heating comprise 28%, agriculture 13.8%, transportation 12.2% and LULUCF 12.2% (WRI 2011).
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Although a number of broad international surveys of REDD project experiences
have been written to date (Wertz-Kanounnikoff and Kongphan-Apirak 2009;
Westholm et al 2009; Corbera 2010), we have been unable to find any in-depth
studies of individual REDD projects, as opposed to broad studies across groups
of projects. A common theme across various surveys is that progress has been
slower than expected (Creed and Nakhooda 2011). Another study notes
confusion as to how lessons learnt from pilot activities will feed into national
REDD development (REDD-net 2010).
A small but valuable literature is also emerging which draws on lessons from
related fields. The Centre for International Forestry Research (CIFOR) in Bogor
has produced reports on the lessons for REDD from Indonesia’s $8 billion
Reforestation Fund (Barr et al. 2010), and from efforts to control illegal logging
in Indonesia (Luttrell 2011). Country studies of PNG (Howes 2009) and of Ghana
(Hansen CP et al. 2009), as well as international surveys (McCarthy and Cramb
2009: 41, 44; Li 2011; World Bank 2011a), studies of earlier forestry reform
efforts (Chomitz et al. 2007, Hansen, CP et al 2009; Goers-Williams et al. 2011),
and studies of Indonesia (Verchot et al. 2010) all point to systemic issues which
will need to be addressed if rates of deforestation are to be brought down. These
include corruption, illegal logging, land tenure uncertainty, the power of forestry
industry lobbies, weak enforcement of laws, and the economics of oil palm. One
clear conclusion is that “fundamental governance issues must be addressed if
REDD+ is to be effective” (Luttrell et al. 2011:52-56). In general, the literature
casts doubts on the view that REDD is “a significant, cheap, quick and win-win
way to reduce greenhouse emissions” (Angelsen 2008: 15-16).3
Given the importance of these systemic forces, whether focusing on
demonstration projects and readiness activities makes sense depends on both
the success of the initial activities, and the broader context. A demonstration
project which is quick to show success, and which is undertaken in a static
context, makes more sense than a project which is slow to show results in a
deteriorating context. The relevant context is both Indonesian (what is
3. The Australian Government itself has claimed that REDD is “one of the most cost-effective means to reduce emissions in the short term” (Australian Government 2008).
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happening to the forestry sector?) and international (what are the prospects for
a REDD market?). An assessment of KFCP therefore requires an analysis not
only of the progress of KFCP itself but also of contemporaneous developments in
Indonesia’s forestry sector and in REDD negotiations.
The structure of this paper reflects such an approach. Section 2 builds on this
introduction by setting the context for the study with an overview of Indonesia’s
deforestation challenge. Section 3 then begins the analysis with an examination
of the origins of KFCP and explains the downsizing of objectives from the original
announcement to the documented project design. Section 4 documents and
explains the slow progress KFCP is making. Section 5 analyses recent trends and
developments in international REDD negotiations, efforts to address
deforestation in Indonesia, as well as developments in Central Kalimantan.
Section 6 concludes.
The research reported in this paper is based on two visits by the first author to
Indonesia, in November-December 2010 and September 2011. The research
involved meetings in Jakarta with KFCP project personnel, the AusAID Jakarta
office, Indonesian Government personnel from various agencies, NGOs, and
research personnel from the Centre for International Forestry Research in
Bogor. It also involved visits to Palangkaraya, the capital of Central Kalimantan,
for discussions with KFCP personnel and provincial government officials,
discussions with district officials at Kuala Kapuas, and a field visit to two KFCP
project locations, Mantangai Hulu and Katunjung, where discussions were held
with project personnel and representatives from the local communities. A list of
interviewees is at Annex 1.
2. Indonesia’s Deforestation Challenge
This section describes the relevant context in Indonesia prior to the KFCP
project, up to 2008. More recent contextual developments are covered in Section
5, after discussion of KFCP.
Although Java has long been deforested, Indonesia’s less populated Outer Islands
retained most of their forest cover until the 1960s. Large-scale exploitation of
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outer island forests began in 1967, when Suharto’s New Order regime effectively
nationalised Indonesia’s forests through the introduction of a concession system
under the Basic Forestry Law (Barr 2001; Neilson 2010: 29; see also Arnold
2008). Logging was the first of the forest industries to take off. By the mid-
1970s Indonesia supplied 44 per cent of the world hardwood log market. Some
585 concessions covering 62 million ha (mha) were issued over a 30-year
period. In the 1980s the pulp and paper industries began a dramatic expansion,
with production capacity increasing by 600% between 1987 and 1997 (Barr
2001, pp. 22-37). Also in the 1980s, Indonesia’s palm oil industry embarked on
the growth path that led to Indonesia becoming the world’s largest oil palm
producer. The area under oil palm increased from just 250,000 ha in 1978 to 3
mha by 1997, and 6.3 mha by 2007 (FPP /Sawit Watch 2006, World Bank 2010).
These industries impacted heavily on Indonesia’s forests. In the 1960s, the
national forest estate comprised 130 mha, but by the time the Asian Financial
Crisis brought about the end of the Suharto era in 1998, some 40 mha had been
deforested (Barr 2001). In addition, vast areas of existing forest had been
severely degraded.4
Indonesian deforestation rates are notoriously difficult to measure, but Hansen
MC et al (2009) have recently developed some useful estimates. According to
them, in the 1990s, the deforestation rate averaged 1.8 mha a year. In 2000,
when poor economic conditions reduced demand for oil palm (Casson 2000) and
with an oversupply of cleared land, the deforestation rate dropped sharply to
below 0.5 mha. Annual deforestation rates climbed steadily thereafter, rising
once again above 1 mha by 2005 (Hansen MC et al, 2009).5
Some 21 mha of forest was lost between 1990 and 2005. Around 75% of this
took place in the lowland forests of Sumatra and Kalimantan (Hansen MC et al,
2009: 9). With much of Indonesia’s 22.5 mha of carbon-rich peat forest located
4. Deforestation is often defined as a reduction of canopy cover below 10 per cent. By definition, then, almost 90 per cent of the forest cover can be removed and an area is still classified as forest, although degraded. (Kanninen 2007:15). 5. While Hansen estimates that deforestation rates averaged 0.71 mha/yr over the period 2000-2005, the FAO estimates Indonesia’s forest loss as averaging 1.87 mha/yr over the same period (FAO 2009).
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in these areas, large areas of peatland were deforested. Forested peatland
declined from 18 mha in 1985 to just 12 mha in 2006 (Hooijer et al. 2006).
The greenhouse significance of peatland deforestation lies in the fact that
Indonesian peat swamp forests store 20 times more carbon than tropical
rainforests on mineral soils (Jaenicke et al. 2010). And unlike forests on mineral
soils, where most carbon is released upon deforestation, deforested and drained
peatland releases high levels of carbon over many years after deforestation, as
the peat decomposes or is burnt.6 Deep peat – where the peat extends to depths
of 3-12 metres (Hooijer et al 2006) – poses particular environmental risks.
Indonesia is the world’s fifth largest source of greenhouse emissions, at over 2
billion tonnes (Gt) in 2005.7 Three quarters of these emissions (1459 Mt CO2e)
were from the land-use change and forestry sector and from deforested
peatland. Just 398 Mt CO2e were sourced from energy and transport. While
estimates vary, Indonesia’s peatland emissions (from deforestation,
decomposition and fires) are likely to be at least 1 Gt a year.8 This is nearly twice
Australia’s emissions from all sources, and roughly equal to those of Germany
(DNPI 2010, pp. 10-11; WRI 2011, p. ix).
One peatland swamp area of particular concern is the Ex-Mega Rice Project
(EMRP) area in Central Kalimantan. In what is now described even in Indonesian
government documents as “a phenomenal failure” (GOI 2010, p. 43), President
Suharto in 1995 ordered that over one mha of Kalimantan peat swamp be
drained for conversion to rice growing. The peatland was drained, but was
6. Peat is an accumulation of large amounts of carbon-rich decayed vegetation matter. Geologically, it is a precursor to brown coal. Typically peat forms in wetland or marshy conditions where plant material is inhibited from decaying fully by acidic and anaerobic conditions. Up to 90% of peatland carbon is stored below ground. In peatland forests, peat builds up into domes over thousands of years. 7. The World Resources Institute’s CAIT database estimated Indonesia’s emissions at 2.042 Gt in 2005, thus fifth globally after China, USA, the EU and Brazil. Indonesia’s National Council on Climate Change provides a figure of 2.1 Gt in 2005 (DNPI 2010: 10; WRI 2011). 8. The DNPI provides estimates of emissions from peatland decomposition in 2005 at 300 Mt CO2e, from fires at 472 Mt CO2e, and from deforestation at another 250 Mt CO2e (DNPI 2010). However, estimates of decomposition emissions alone range from 355 – 855 Mt CO2e a year, with a mean of 632 Mt CO2e, and some researchers now consider it more likely that these emissions are at the higher end of the range (Hooijer, pers. comm., 2/02/2011). See also Lutrell et al 2011: 14, citing discussion in Indonesia’s Second National Communication to the UNFCCC and World Bank 2008.
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unsuitable for rice growing. The canals created to drain the swamp are now
used for transport, and much of the peatland lies abandoned. Some is used for
smallholder agriculture by the indigenous Dayak people who inhabit the area.
The land continues to burn frequently, leading to transboundary haze and high
levels of greenhouse gas emissions. During the 1997 El Nino, 474,000 ha of
peatland burned, contributing to massive transboundary hazes with major
health impacts across Southeast Asia (Page et al 2002). An increasing amount is
being turned over to palm oil plantations. The EMRP area has been the subject of
a number of projects and initiatives to revert it to its original condition, and was
the location chosen for the KFCP.
By the mid-2000s, when global climate change discussions turned to
mechanisms for reducing deforestation, the Indonesian Government took an
active interest, and in 2007 emerged as a leading advocate of REDD. It
established the Indonesia Forest Carbon Alliance (IFCA), a team of local and
overseas experts which produced the IFCA Consolidation Report, a detailed
blueprint for REDD in Indonesia (Ministry of Forestry 2008). The Ministry of
Forestry also passed a number of regulations setting out procedures for REDD
demonstration activities and for implementation of REDD (summarised in
Luttrell et al. 2011: 17).
The IFCA study reflected an expectation that a carbon market would emerge and
deliver revenues to Indonesia between US$650 million and $5 billion a year.9 It
also devoted close attention to the problem of peatland emissions, noting that
restoration of water tables, fire prevention, various governance challenges, and
gaps in greenhouse accounting science would all need to be addressed before
peatland could be taken up in a REDD scheme.
In line with the Bali Action Plan, the IFCA report proposed that a number of
demonstration projects be undertaken, and that these should test how reference
emission limits (RELs) might be established, how reductions in baseline
emissions might be achieved, how monitoring and carbon accounting could be
developed, and how payments could be made to those who achieved the
9. The IFCA report presents a range of calculations (Ministry of Forestry 2008: 4, 54).
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emission reductions (Ministry of Forestry 2008). The Kalimantan Forests and
Climate Partnership became the first project in Indonesia of this type.
3. The fate of an announceable: KFCP’s origin and downsizing
In March 2007, in a press statement entitled “Australia to lead the world”, then
Australian Prime Minister John Howard announced a $200 million Global
Initiative on Forests and Climate (GIFC), heralding it as “a material advance in
the global effort to tackle climate change” (Howard 2007). Australia’s overall
forest carbon commitment grew after 2007 to $273 million, and was re-badged
as the International Forest Carbon Initiative (IFCI) in 2008.
In September 2007, six months after the initial GIFC announcement, the KFCP
project was announced as a $100 million partnership with the ambitious targets
mentioned in the introduction. Funding would be contributed by Australia ($30
million) and by various other sources, unspecified except for BHP Billiton. It
would be “the largest greenhouse abatement project to flow so far” from the
GIFC (Downer 2007). In the following year, various Indonesia-related initiatives
within IFCI (including KFCP) were gathered together and launched by Prime
Minister Rudd and President Yudhoyono in June 2008 as the Indonesia Australia
Forest Carbon Partnership (IAFCP 2008). The IAFCP initiatives totalled $70
million, increasing to $100 million with Australian government announcements
at Cancun (Combet 2010). KFCP is the largest and clearly the flagship IAFCP
initiative. Its initial budget of $30 million has been increased twice to reach $47
million or about half of the IAFCP total (see footnote 17). A second pilot (the
Sumatra Forest Carbon Partnership) is budgeted at $30 million, but is still at a
very early stage (Tapp 2011).
Following the KFCP announcement, a scoping mission took place in November
2007, and thereafter a “Framework Design Mission” was undertaken. Its May
2008 report retained the original targets while introducing a demonstration
objective (IAFCP 2008a, p. 1).
The KFCP project design document (PDD) was finalised in June 2009 (KFCP
2009). According to it, the project was to be implemented within a peat dome of
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120,000 ha in the Ex-Mega Rice Project area in Kapuas District in Central
Kalimantan (see Figure 1). Most of this area is deep peat. The KFCP location falls
largely within Mantangai sub-district and comprises two distinct areas: Block A
Northwest (50,000 ha), mostly deforested and drained by a 300 km network of
canals, and Block E (70,000 ha), which is forested although severely degraded by
logging and draining, both by traditional informal canals (handil) and by the
large Neraka Canal which extends 15 km into the area. The project area includes
seven villages. The area is designated as “production forest” but is expected to
be re-classified as a protected area (KFCP 2009, p. 3).
Figure 1: Ex-Mega Rice Project area of Central Kalimantan and KFCP project location
Above left: The EMRP area is divided administratively into 5 areas: Blocks A, B, C, D and E. The KFCP project location can be seen in the upper area, straddling Block E and Block A Northwest (NW). Source: KFCP 2009: ix) Above right: KFCP project location, largely in Mantangai sub-district. Note the extensive drainage canals throughout Block A NW. The project location is about 65 km from north to south and 20 km across at the main canal dividing the two blocks. The main locations for initial interventions are Mantangai Hulu and Katunjung villages (southern and northern ends of Block A NW respectively). The vertical canal in Block E is Neraka Canal, which is the subject of a major planned project intervention. Source: IAFCP 2010a.
The project as defined in the 2009 PDD is quite different to the one announced in
2007. KFCP was officially re-positioned as a demonstration or pilot project. The
official objective of the KFCP was now: “To demonstrate a credible, equitable,
and effective approach to reducing greenhouse gas emissions from deforestation
and forest degradation, including from the degradation of peatlands, that can
inform a post-2012 global climate change agreement and enable Indonesia’s
meaningful participation in future international carbon markets” (KFCP 2009, p.
2). By contrast, the initial announcement made no mention of KFCP as a
demonstration project and instead positioned it as valuable in its own right – an
“example of practical climate change action that could deliver immediate and
tangible benefits” (Downer 2007).
Consistent with this change, the use of quantitative objectives is greatly
downplayed in the 2009 PDD. The closest it comes to having a quantitative target
is an indication that available funding would support re-planting of 3,000 ha in
Block A (KFCP 2009, p. 29).10 There are no other quantitative targets.11 For
example, the PDD does not estimate how much of the peat forest in Block E
would be preserved by the project.12 We were informed by AusAID staff in
February 2012 that it was now expected that 25,000 hectares would be re-
flooded in Block A. This is just over one-tenth of the original target of re-flooding
200,000 hectares.
Why was there this dramatic downsizing and re-positioning of KFCP?
First, the money allocated to the task was simply inadequate. It seems that, the
detailed targets notwithstanding, there was little technical work undertaken
10. The original target for planting was 100 million trees. The PDD indicates that one tree will be planted every 9 square metres. This implies that the 3,000 hectares of re-planting would require about 3 million trees. An additional (unspecified) amount of trees would be re-planted in Block E “to facilitate regeneration”. 11. One adviser explained to us that even the 3,000 hectare figure did not represent a target project outcome. As a demonstration project KFCP aspired not to rehabilitate significant areas of peatland, but simply to show how this could be done. Therefore the number of hectares rehabilitated was of no particular significance. 12. At one point, the PDD states that additional funding is needed to protect “protecting remaining forest cover,” suggesting that in fact this is not part of the $30 million project. (KFCP, 2009, p.56)
13
prior to the 2007 announcement.13 More careful work undertaken in the course
of project design shows a deep mismatch between initial funding and targets.
The 2009 project design document notes that costs of rehabilitation through
tree-planting alone are $1,112 per hectare. Thus rehabilitating 200,000 ha, as
per the initial level of ambition, would cost some $222 million, plus the cost of
flooding.
Second, the funding from other partners that was anticipated to flow to the
project never materialised. The initial announcement stated an aim of increasing
project funding from the $30 million contributed by Australia “to raise up to
$100 million in funding over four years by working with other countries,
international non-government organisations and the private sector” (Downer,
2007). The announcement stated that “The partnership has already attracted
financial backing from BHP Billiton, which has joined as a founding partner and
will focus its contribution on the protection of forested peat lands of high
conservation value.” However, although a senior BHP Billiton representative
participated in the project launch, that company seems to have played no further
role in the project at all. Nor have any other partners come forward.
This is not surprising, since fundraising does not now feature prominently as
part of KFCP’s brief. Fundraising is included as one project sub-component.
However, the risk matrix for the project in the 2009 PDD indicates that it is likely
that external funds will not materialise. However, the PDD rates this as being
only of “minor” consequence, and therefore a low risk overall in terms of
importance. If the view was that the funds probably would not emerge, but that
this did not really matter, then clearly little effort would go into fundraising.
Consistent with this, no funds have in fact been raised. Note that putting
substantial effort into fundraising would also be inconsistent with the view of
KFCP as a REDD demonstration project, under which scaling-up would occur not
through project-specific fundraising, but through REDD markets.
13. Minister Downer mentioned at the press conference after the launch that the KFCP initiative came out of discussions he and then Indonesian Foreign Minister Wirajuda had had in Manila just a few weeks prior to the announcement (Downer 2007a).
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Third, there were other demands on Australia’s $30 million. In the project
design, less than $20 million was actually committed to tasks related to
rehabilitating and preserving peatland. The rest went to REDD “readiness
activities,” namely, efforts to measure greenhouse gas emissions from peatlands,
establish baselines, develop government REDD capacity, and to other technical
assistance and overheads.
Fourth, the agreement at COP13 (the Bali November 2007 international climate
change conference) to develop a REDD program, and the call on all Parties to
undertake demonstration projects and readiness activities, provided a new
context within which it became attractive to reposition KFCP as a combined
demonstration/readiness project. Although the initial KFCP announcement had
no mention of the project being a demonstration or pilot one, the initial GIFC
announcement, which preceded it, did have as one its objectives the
“development of incentive-based pilot approaches” (AusAID 2007). Following
Bali, it made sense to give greater weight to this objective in the formulation of
KFCP.
Fifth, there was a change of government in Australia at the end of 2007. This
reduced the political salience of the original Downer announcement. The PDD for
KFCP makes no reference to the original targets, or even the original
announcement in 2007. Rather the history of KFCP is traced back to the 2008
announcement of the Indonesia Australia Forest Carbon Partnership, an
initiative of the then-current Rudd Government.
The Australian government has done little to signal the downsizing of the
project. The PDD itself is a public document, but this is thanks to the Finnish aid
agency, on whose website it can be found, in connection with a related Finnish
project.14 The PDD is not available on any Australian government agency
websites.
14. See http://formin.finland.fi/public/default.aspx?contentId=197837&nodeId=41939&contentlan=2&culture=en-US
15
Australian government websites show not the PDD but a KFCP “fact sheet,”
available on the Department of Climate Change and Energy Efficiency (DCCEE)
web-site. Unfortunately, this only perpetuates the myth that KFCP is about large-
scale rehabilitation and preservation:
“Initial work will aim to avoid deforestation of 50,000 ha of peat
swamp forest and rehabilitate an additional 50,000 ha of degraded
peatland to create a buffer around the existing forest and reduce
further degradation. These activities may be extended as other
funding becomes available. The location and types of activities under
the KFCP have been endorsed by Indonesia and Australia. Based on
the original funding target of $100 million, the KFCP aims to preserve
up to 70,000 ha of Kalimantan’s peat swamp forests and to re-flood,
rehabilitate and reforest 200,000 ha of degraded peatland.” (DCCEE
2011)
The fact sheet creates the impression that the project is still as Minister Downer
originally announced it. The numbers in the last sentence are precisely those
which Downer announced back in 2007, even though as far back as 2009 these
targets had been abandoned. Even the targets relating to “initial work” are far in
excess of what the project is currently designed to achieve (25,000 ha rather
than 50,000 ha is the current expectation for rehabilitation). Moreover, for the
reasons given above, the original funding target of $100 million is no longer
relevant.
Given the lack of effort to explain the shift in the project, it is not surprising that
expectations regarding ambitious targets persist, both in Australia and
Indonesia. Many continue to believe that the original targets still apply. They
were reported widely in the Indonesian media at the time of the announcement
(e.g. Antara 2007). They were also mentioned in the EMRP Master Plan of 2008,
which, in considering how the Inpres 2/2007 reforestation targets might be met,
noted the contribution that would be made by Australia’s proposed planting of
100 million trees under KFCP (Euroconsult and Deltares 2008, p. 57).
16
An article in the Canberra Times in June 2010 quoted the ambitious figures
mentioned above and asked why little progress had been made (Malone 2010),
while a December 2010 newspaper report in Indonesia covering Central
Kalimantan’s selection as a focal province for Norway’s assistance repeats the
claim that Australia is helping restore 100,000 ha of peatland in the province
(Reuters 2010). Some NGOs even continue to report that the project receives
funding from BHP (Lang 2011a).
Some Indonesians interviewed for this research who knew that the project had
been so greatly downsized tended to dismiss it for that reason. Those who found
out during the interview process that KFCP had been downsized were surprised.
It may be the case that project downsizing has reduced the prospects for project
sustainability. The KFCP fire management strategy recognises that most fires
occur close to canals,15 but the downsized project will only block an unspecified
portion of the 300 km of canals criss-crossing Block A NW, leaving the rest of it
highly vulnerable to the next El Nino. During the period 2002-2008, 5,270 fires
were recorded in the sub-district of Mantangai alone (CARE 2009, p. 10).
Earlier projects in the EMRP area, such as the Climate Change, Forests and
Peatlands in Indonesia project, active from 2002-2005, and the Central
Kalimantan Peatland Project, active from 2005-2008, do not seem to have
delivered sustainable outcomes. While project reports offer optimistic
assessments of the achievements of the projects (CCFPI 2005; CKPP 2008), local
people showed us failed project plantings lost to fire. A local community leader
advised that there was little doubt that the peatland would burn again when the
next dry season arrives. While KFCP is much bigger than either of these two
projects, whether it is big enough to reduce the risks of fire sweeping through
remains to be seen. The PDD stresses the need for a “whole of dome” approach,
15. The PDD provides compelling evidence in a map which shows 600 hotspots during the 2006 El Nino, concentrated along the canals in Block A NW.
17
but, in fact, with the downsizing of the project a substantial amount of the dome
is outside the scope of the project.16
4. Progress of a demonstration project: How has KFCP fared?
In this section we provide an overview of KFCP progress, after more than three
years of project implementation.
Apart from the issues discussed below relating to land tenure and the rights of
indigenous people, KFCP’s progress, or lack of it, has been little discussed.
AusAID’s 2010 performance report for Indonesia concludes on KFCP that
“Despite procedural delays, Australia’s first demonstration activity in Central
Kalimantan will make a significant contribution” (AusAID 2011, p. 39). An
independent review of Australian aid to Indonesia was undertaken in 2011 as a
background paper for the Independent Review of Aid Effectiveness. This paper
mentions delays with the Department of Forestry, but also highlights “Australia’s
well-advanced REDD demonstration on degraded peatlands” (Tapp 2011, p. 19).
In February 2012 in answer to a Senate Estimates question, AusAID reported
that KFCP had made “considerable progress” and was “producing outcomes”
(Commonwealth of Australia 2012, p. 111). Based on our research, these
assessments seem overly optimistic.
4.1. KFCP project design
KFCP commenced in January 2009 with a six-month “Early Implementation
Phase” from January to June 2009 followed by a three-year “Implementation
Phase” from July 2009 to June 2012.
The KFCP design comprises four project components to achieve the overall
demonstration objective of the project given in the previous section. They are
16. It is not easy to quantify how much. The dome comprises 120,000 ha, Block A NW is 50,000 ha, of which the project expects to re-flood some 25,000 ha. Block E is 70,000 ha, but how much of this is actually covered by the project is unclear (see footnote 12).
18
summarised below along with indicative budgets as per the design document
(KFCP 2009: Annex 8).17
1. Reduction of deforestation and degradation of peat swamp forest ($18.1 m):
This entails 60 per cent of project funds. It involves engagement with
communities, mapping of community land and property rights to address
customary land tenure issues, strategies to reduce the incidence of fires in the
area, developing methods to rehabilitate peatland and trialing these in selected
locations, blocking canals to re-flood peatland, rehabilitating degraded and
deforested areas by re-planting or encouraging natural regeneration, and
improving local peoples’ livelihoods (KFCP 2009, pp. 24-31).
2. Establishment of greenhouse emissions estimation and monitoring program and
its linking to the Indonesian National Carbon Accounting System – INCAS ($3.5 m):
This addresses the need for better scientific knowledge relating to peatland
emissions. It entails an initial methodological study of the requirements for
estimation of peatland emissions, development of a methodology for estimating
peatland reference emission levels (RELs), and developing RELs both for the
project location and for the larger EMRP area. It also entails peatland emission
monitoring and measurement, including measurement of emissions at project
sites before and after interventions, and applying the approaches developed
through the project to INCAS (KFCP 2009, pp. 31-35).
3. Demonstration of practical and effective REDD GHG payment mechanisms ($0.9
m): This component aims to develop and trial a REDD payment mechanism,
which in time would be used to channel REDD payments to those who achieved
emission reductions. It will take the form of a trust fund. Initially it will be used
on an input basis to pay communities for undertaking project tasks (such as tree
planting, canal blocking and fire management), and later on a performance basis
17. Components 1-4 total $24 m. Some $5.8 million of overheads (technical assistance, travel, etc) plus $1.6m for early implementation phase studies take the total cost to $31.4 million, which is the initial $30 million, plus an additional $1.4 million allocated for monitoring and measurement from other IAFCP funds. As noted, in December 2010, another $10 million was allocated to KFCP. We were informed that the latest budget is actually $47 million. However, we do not know which components have benefited from these budget increases, or by how much.
19
for maintaining dams, protecting forest or reducing the incidence of fire, all as a
proxy for future REDD payments (KFCP, 2009, pp. 35-39).
4. Development of REDD management/technical capacity and readiness at
provincial, district, sub-district and village levels ($1.5 m): This involves building
REDD capacity, management systems and institutions at all local levels
(province, district, sub-district and village to enable local participation in future
REDD carbon markets (KFCP, 2009, pp. 39-41).
4.2. KFCP progress to September 2011
This section summarizes progress under each of the four components.
4.2.1. Component 1: Reduction of deforestation and degradation of peat
swamp forest
A large amount of valuable preparatory work was undertaken during the early
implementation phase, aimed at providing a solid understanding of a range of
critical project issues. This included studies of the socio-economic profiles of the
local villages (e.g. (KFCP 2009a; KFCP 2009b); alternative livelihood options
(KFCP 2010a; KFCP 2010b); community issues relating to canal-blocking (KFCP
2009c); land tenure in the EMRP area (Galudra et al. 2009); peatland forest tree
species silviculture and propagation (IAFCP 2010a, pp. 73-74); and the role of
fire in local communities (KFCP 2009d). These studies were completed in a
timely manner, in many cases by experts already familiar with the area,
providing a strong conceptual basis for much of the work that followed.
However, preparatory studies are much easier to control and direct than actual
implementation, and as the project moved into implementation mode, progress
slowed considerably.
As at September 2011, after nearly three years of project implementation, little
evidence can be seen on the ground of any reductions in deforestation and forest
degradation. Blocking of the large canals in Block A has not commenced, nor has
blocking of Neraka Canal in Block E, despite the planned commencement date of
20
November 2010.18 The main reason for lack of progress in Block A NW has been
a delay in obtaining environmental clearance, discussed further below.
Permission from local land-holders for heavy excavating machinery to pass
across village land also needs to be obtained (IAFCP 2010b,)
Some progress has been made in relation to the small traditional hand-dug
canals (handil) scheduled for de–commissioning in Block E. Detailed design
work relating to over 100 small canals in the northeast of Block E was completed
at the end of 2010, and six were blocked as a demonstration activity in 2011.
According to project personnel working in the area, local people are generally
supportive of the canal-blocking efforts, although they have concerns regarding
the negative impact that canal-blocking may have on their livelihood activities.
The KFCP community engagement team is engaged in ongoing discussions with
communities on these issues.
Modest progress has been achieved in relation to rehabilitation of deforested
peatland. Following identification of suitable plant species, establishment of a
nursery and delivery of local training in planting techniques, experimental
plantings to test selected peat forest species were established in 2010 on two 25
hectare plots (KFCP 2010c; KFCP 2010d). In 2011, all seven project villages
were reportedly engaged in propagating plant species. As of February 2012,
AusAID reported that only 50,000 trees had been planted. A much larger number
of seedlings (1.3 million) were being raised in community nurseries, with some
$450,000 allocated for payments to villagers in this regard (Antara News 2011;
Australian Embassy 2011; Commonwealth of Australia 2012). 19
The strongest achievements to date have been in relation to community
engagement. Field officers based in project villages have engaged extensively
with communities to explain and win support for the REDD concept (“REDD
socialization”), to create awareness of the dangers of fire, to explain the aims and
objectives of the project, and to improve local livelihoods. Considerable success
18. All references to planned implementation dates refer to the indicative schedule provided in the 2009 PDD (KFCP 2009). 19. A report from a journalist who visited the area in November 2011 states that few plants had survived from the original 25 hectare plantings (Keller 2011). We are not in a position to verify this.
21
has been reported in improving incomes from local rubber production (IAFCP
2010b).
The project has, however, been subject to accusations by local Dayak people and
environmental NGOs that KFCP has denied Dayaks their human rights and
customary land rights, and failed to consult with them (AMAN 2011; FPP 2011).
In June 2011, local indigenous people signed statements both of opposition and
of support for KFCP. In some cases, the same people signed both letters (see
Lang 2011a; Lang 2011b). AusAID’s response asserts that it works closely with
indigenous leaders and communities (see Lang 2011c). One NGO has expressed
hope that given a supportive provincial context, KFCP should be able to make a
breakthrough in the recognition of community rights in land as well as
recognition and empowerment of the community’s own social institutions, but
others oppose KFCP and REDD generally (FOEI 2011; FPP 2011; Keller 2011;
Muliadi 2011; Satriastanti 2011a).
A major part of Component 1 is focused on fire prevention, which is at once the
greatest risk to peatlands and by far the cheapest mitigation option.20 The KFCP
fire prevention strategy entails re-flooding peatland by blocking canals, re-
establishing tree cover, developing alternative livelihood options, undertaking
fire prevention activities in high risk areas (i.e. close to human activity)
particularly along canals (since fires are closely associated with human activity),
and providing performance payments for achieving reductions in fires (CARE
2009; KFCP 2009, p. 23, Att. 7).
The challenge is considerable. A member of the KFCP project team advised that
local people still regarded fire as a tool for “cleaning” the land in preparation for
planting-out for rubber plantations or horticulture. A study of Katunjung village
reported that the community regarded fires as highly damaging and resulted in
health problems (Yayasan BOS 2007), but villagers informed us that only
financial incentives would protect the forest. The frank messages from local
20. Indonesia’s National Council on Climate Change, in its emission abatement cost curve analysis, estimated that peatland fire prevention would cost just US$ 0.35/tCO2e of emissions avoided (DNPI 2010: 17). The PDD states that the primary means to reduce deforestation and degradation of peatland is “by reducing fire risk and mitigating the frequency and severity of fire” (KFCP 2009: 4).
22
people indicated that only a long-term financing arrangement which provides
villagers with compensation and an alternative income source, particularly if
livelihood access is reduced through canal-blocking, will solve the problem.
This is precisely the strategy of KFCP, but little has been achieved so far. In the
project villages of Katunjung and Mantangai, KFCP has supported the
establishment of local Fire Management Units, production of fire awareness
materials, and community awareness workshops (Fire Management Unit KFCP
2011). As far as we understand, no payments have been made yet to
communities for fire prevention or management. A CARE project report notes
various problems with fire management including the unavailability of local
people due to their need to continue normal livelihood activities, and shortfalls
in training (CARE 2009, p. 29).
4.2.2. Component 2: Establishment of greenhouse emissions estimation and
monitoring program
Work on this component commenced well with two draft reports (Methodology
for Estimation for GHG Emissions from Tropical Peat Lands in Indonesia and a
Review of the science underpinning a methodology for GHG accounting in tropical
peat lands) completed in February 2010. Both reports identified significant gaps
in scientific knowledge which needed to be quickly addressed through further
research (IAFCP 2010b, p. 16). However, as of September 2011 the additional
work had not been undertaken, despite additional funding being allocated to
KFCP and IAFCP at Cancun in December 2010 (Combet 2010). As of September
2011, project and district-level RELs had not been developed. Certainly district
officials had no knowledge of any progress.
A peatland monitoring system is in place to measure peat depth, subsidence and
water levels (but not GHG emissions) on a monthly basis (IAFCP 2010a, p. 15).
We understand that some progress on remote sensing to determine forest cover
change has been made, and that an aerial survey to measure changes in peat
depth is expected to be undertaken in the near future. For above-ground carbon
emissions, the KFCP is dependent on the completion of INCAS protocols for
above-ground biomass assessment of peat swamp forests.
23
4.2.3. Component 3: Demonstration of practical and effective REDD
payment mechanisms
A payment mechanism to finance tree-planting was established in 2011. With
plant nurseries established in all project villages in 2011 and planting out of the
scheduled 1000 ha for that year under way, the payment mechanism was
launched by the District head in June 2011. This involved an initial payment of
Rp 635 million ($A72,000) for village labour inputs, followed by a second
payment of Rp 785 million ($A89,000) in September (Antara News 2011).
The PDD suggests that a trust fund be created to support disbursements for
several years post-KFCP (KFCP 2009, Attachment 5-3), and the need for fire risk
management support for at least 5-10 years is mentioned (KFCP 2009, pp. 7-4).
A capital injection of $8.7 million has reportedly been provided for the fund
(FOEI 2011, p. 8), presumably from the increased funding allocation to the
project.
4.2.4. Component 4: Development of REDD management/technical capacity
and readiness at provincial, district, sub-district and village levels
Mapping of the anticipated roles of various local government agencies in KFCP
and REDD was undertaken during the “Early Implementation” phase (KFCP
2009e). However, progress in building local institutional capacity was slow
during the first year of the project, with district and provincial officials
reportedly unprepared to convene required working group meetings, and
concerns at the provincial level over limited benefits to accrue to the province
from KFCP (IAFCP 2010b, p. 21). Following a visit to Australia by the Head of
Kapuas District, a much higher level of interest and enthusiasm become
apparent. In September 2011, however, no REDD capacity was evident at the
district level beyond the establishment of a KFCP working group. Officials said
they had no personnel available nor any technical capacity to undertake REDD-
related activity. At the provincial level, awareness of the work of KFCP was low,
despite the project being based in Palangkaraya, the provincial capital. Officials
were aware that the project was under way in Kapuas District, but were not
24
aware of any contribution the project was making towards REDD capacity
building at the provincial level.
4.3. Summary
After nearly three years of implementation, the achievements of KFCP are
modest. It has not yet demonstrated how deforestation and degradation of peat
swamp forest can be reduced (Component 1), largely because re-flooding
through large-canal-blocking has not commenced. Progress on GHG emissions
estimation and monitoring (Component 2) is patchy. Although an extensive
program of peatland monitoring is now in place, scientific work on peatland
emissions and development of RELs, a basic cornerstone of a REDD scheme, is
well behind schedule. Good results have been achieved in improvement of local
livelihoods. A payment mechanism (Component 3) is being utilised to pay for
labour inputs for re-planting. Community engagement has been intensively
pursued, although the project has been subject to some protests from indigenous
and community groups. Finally, little REDD management or technical capacity
building has been achieved at local or provincial levels (Component 4).
Planned project expenditure from the commencement of the `early
implementation’ phase through to June 2011 was $20,400,000 (KFCP 2009: Att.
8). Our understanding is that actual expenditure has been well below this figure.
In summary, apart from the preparatory studies, every aspect of the KFCP
project has been affected by major delays. As per the original timeline
developed for the project, reforestation (tree planting) was to commence in July
2010, and canal blocking was meant to commence in November 2010. The REL
baseline was also meant to be approved that month, and the monitoring program
was to be validated and operating. The REDD trust fund was to be established in
July 2010, and the REDD credit certification system operating in October 2010.
Overall, the project would seem to be more than a year behind schedule.
There are several causes for delay.
25
First and foremost, KFCP is a complex project, with multiple components and
requires a high level of interaction with local communities. Local community
consent is required in relation to fire-prevention activities, re-flooding and re-
planting. KFCP’s experience of delays relating to establishment of complex new
systems is consistent with the experience of other REDD projects as indicated in
the surveys of REDD projects noted in Section 1.
Second, Indonesian law requires a completed environmental impact assessment
(AMDAL) before any canal-blocking can commence. The AMDAL is intended to
meet not only various Indonesian Government requirements but also Australian
and World Bank requirements. Even agreement on the terms of reference
(TORs) for the AMDAL proved to be difficult, with the provincial government
unprepared to approve these until it had the support of the project district
(Kapuas), and the district not prepared to proceed until it had formal advice
(Surat Keputusan) from the Ministry of Forestry that it had approved the project
area. In the event, approval of the TORs was given in December 2010, but as at
February 2012, the EIA itself had still not been approved.
Third, it is clear that the relationship between IAFCP and the Ministry of
Forestry, though it may now be improving,21 has been a difficult one. This has led
to lengthy delays, including in relation to the AMDAL, peatland GHG monitoring
and REL development.
Fourth, the project has been involved in controversies: first, as mentioned
earlier, in relation to local communities and second in relation to canal blocking,
where some scientists have objected to the mechanical methods proposed for
this task (SEApeat 2011). It is possible that these controversies have added to
the delays.
At the November 2010 Cancun international climate change conference, the
Australian government announced an extension for KFCP by a year. In our
judgment, it is unlikely that the project, even in its scaled-back form, will be
complete by July 2013.
21. In September 2011, the Australian Ambassador and the Indonesian Ministry of Forestry paid a joint tree-planting visit to the KFCP (Australian Embassy 2011).
26
5. In the meantime: KFCP in context
As noted in the introduction, evaluation of KFCP as a demonstration project
cannot be restricted only to the progress which the project itself is making. It
also requires investigation of the broader context. The greater the rate of
deforestation and land conversion, the higher the costs of delay. Examining the
prospects for scaling-up KFCP also requires a broader analysis.
To complete our assessment of KFCP, we therefore now turn to an analysis of
recent developments in relation to: the global effort to establish an international
REDD framework; deforestation in Indonesia; and peatland conversion in Central
Kalimantan. Our focus is on the last three or four years.
5.1. REDD developments: uncertain prospects for an international
market
The longer-term prospects for KFCP to contribute to REDD in Indonesia depend
not only on the policy environment in Indonesia but on international REDD
negotiations. In contrast to the brighter prospects of a few years earlier, there
now appears to be little chance of an international REDD market being
established in the near future to scale up a successful KFCP pilot or to drive
REDD more generally in Indonesia.
First, following the 2011 Durban international climate change conference, a
global agreement on emission reductions is unlikely to enter into force before
2020 (Chestney 2011). Second, many of the components of an internationally
agreed REDD mechanism remain to be negotiated. The 2009 Copenhagen
Accord called for the immediate establishment of a REDD+ mechanism (UN
2010), but the detail of this was left to the 2010 Cancun conference. The Cancun
meeting in turn called for further work on REDD financing options, as did the
Durban conference. At least for peatlands there are some positive developments,
with the Durban conference agreeing to the inclusion of emissions from drained
peatland in a future REDD+ agreement (Tol 2011a), following discussions on the
issue in Cancun (Tol 2010; Tol 2011b).
27
More generally, there has been a shift in climate change negotiations away from
the sort of “top-down” approach represented by the Kyoto Protocol, to a less
formal but more inclusive “bottom-up” approach embedded in the Copenhagen
and Cancun accords. A bottom-up approach is less likely to lead to a treaty, and is
more likely to accommodate a range of approaches to reducing emissions, and
metrics for measuring effort. The implications for this shift are still unfolding.
However, it is certainly the case that in a bottom-up world, international
cooperation and trading are more likely to be bilateral and regional rather than
global.
This is not all negative. Countries’ bottom-up actions can be a source of REDD
funding. Australia’s passage of a carbon pricing scheme, which is envisaged from
2015 to allow trading of carbon credits, could provide a strong source of demand
for forestry credits from Indonesia.
It is also the case that public finance will play a greater role in a bottom-up
regime, at least for some time, as it will take longer for markets to evolve
organically than under a top-down template. Certainly most of the financing
currently being provided by developed to developing countries in relation to
climate change is through governments rather than markets. However, especially
with the fiscal crisis pervading the OECD, reliance on public finance is risky
(World Bank 2011c).
In summary, there could be sources of funding to scale-up REDD demonstration
projects such as KFCP, but there is considerable uncertainty and it will not be
through a global REDD market.
5.2. Indonesia’s campaign against deforestation: a losing battle?
Since Indonesia hosted the Bali UNFCCC meeting in December 2007, it has
continued to play a leading role among developing countries in relation to
reducing deforestation and tackling climate change more generally. At the
September 2009 G20 meeting in Pittsburgh, President Yudhoyono announced a
national goal for Indonesia of reducing emissions by 26 per cent against BAU by
2020, increasing to 41 per cent with international support (Yuhoyono 2009).
28
Achieving this target will depend largely on success with reducing emissions
from deforestation. Indonesia’s National Council on Climate Change (DNPI)
concluded that 75 per cent of Indonesia’s abatement opportunities lie in the
forest sector and deforested peatland. The DNPI estimated that emission
reductions of 566 Mt CO2e/yr could be achieved in this way (DNPI 2010). In
September 2011 President Yudhoyono re-affirmed his commitment to
addressing deforestation, saying that this would be a key priority for the
remaining three years of his presidency (Jakarta Globe 2011a).
Indonesia has received support from donors to pursue its goals, not only
Australia, but also more recently Norway. In May 2010, Norway and Indonesia
agreed on a $1 billion program in return for greater effort by Indonesia to
protect its forests (GON and GOI 2010). Under the agreement, Indonesia was to
develop a National REDD+ Strategy. This was released for a final round of public
comment in August 2011 (GOI 2011). The Norway agreement also provided for
a 2-year moratorium on new logging concessions. Central Kalimantan was
selected as the first trial province for Norway’s support.
Ambitious targets and support from donors notwithstanding, the difficulties of
actually reducing emissions from deforestation are acute for the range of reasons
set out in Section 2. Recent events and developments illustrate the force of the
drivers of deforestation in Indonesia.
Indonesia has implemented intensive efforts to address illegal logging,
particularly since 2005 (Daviet et al. 2010; Luttrell et al. 2011). But a detailed
2011 study found that enforcement operations in timber-producing areas were
undermined by vested interests and corruption, and that the extent of any
reductions in illegal logging remained uncertain (Luttrell et al. 2011, pp. 6-9, 53-
4). One study noted that illegal logging is still believed to comprise between 40-
61 per cent of all logging in Indonesia (Lawson and MacFaul 2010, p. xvii).
Although the Indonesian Government has made a major effort to address
corruption, with the establishment of the Corruption Eradication Commission
(KPK) among other measures, the problem remains pervasive. Reports abound
of instances of the Commission’s efforts being undermined (Kuncoro 2008; Barr
29
2010, pp. xii, 28-30). The forestry sector is particularly vulnerable to corruption,
at both national and local levels of government. An assessment by the KPK
pointed to inadequacies in various regulations which create opaqueness in the
definition of forest areas and allow widespread illegal logging and illegal mining
to persist (KPK 2010). In April 2011 it was estimated that 1,236 mining firms
and 537 oil palm plantation companies were operating illegally in Central, East
and West Kalimantan (Jakarta Globe 2011b). Another study showed that 20 per
cent of the forest loss over much the same period took place in areas where
clearing was prohibited or restricted (Broich 2011).
Oil palm is also a major driver of deforestation. As noted earlier, Indonesia is
already the world’s largest oil palm producer. The area under oil palm plantation
has increased from 6 mha in 2007 to 8 mha in 2009 (Jakarta Post 2009). The
Indonesian Environment ministry has estimated that 18 mha of new oil palm
plantations may be developed by 2020 (Verchot 2010, p. 7). 22 An NGO study
which compiled actual spatial planning data from provincial and district-level
land-use plans found that an additional 20 mha has already been proposed for oil
palm development (FPP/SawitWatch 2006, pp. 25-6). This poses great risks for
peatland given ongoing encroachment by oil palm plantations.
Returns from oil palm may out-compete those from carbon sequestration (World
Bank 2011a, pp. 40-41). A DNPI/McKinsey study of Central Kalimantan
estimated that a carbon price of US$30/tCO2e would be needed to avoid
deforestation for palm oil (DNPI 2010a, p. 17). The strong returns from oil palm
may help explain the Ministry of Forestry’s handling of the Rimba Raya voluntary
carbon sector project proposal. This project, which provided for 90,000 ha of
peatland in Central Kalimantan to be protected to generate carbon credits for
sale under voluntary carbon trading, had been under development for several
years. In mid-2011 the Ministry withdrew around half of the project area from
the enterprise rendering it non-viable, and re-allocating part of the land for oil
palm development despite it being on deep peat, which under Indonesian law is
protected (Fogarty 2011).
22. Against this, Agriculture Minister Suswono reportedly said that a total of 18 mha of land could be used for oil palm (Jakarta Post 2011).
30
Turning to the paper and pulpwood industries, the Ministry of Forestry is
planning for an additional 5 mha of industrial timber plantations to be
established by 2016, and is reportedly considering approvals for up to 12 new
pulp mills. But all previous efforts to increase timber plantations have fallen well
below expectations, and if the 12 new mills are created, a substantial demand
risk is likely to arise for illegally sourced timber as feedstock for these mills
(Verchot 2010, pp. 4-5). This would represent a re-play of the problem of
excessive capacity in Indonesia’s pulp mills driving illegal logging in the 1990s
(Barr 2001).23
One study found that 2 mha of carbon-rich peatland was lost between 2000 and
2009 (FWI 2011). Another study found that this was due mainly to expanding oil
palm and pulp and paper operations (Broich 2011).
Indonesia’s planning agency, Bappenas, has proposed a land-swap strategy
aimed at shifting concession-holders from peatlands to degraded mineral soils
(Bappenas 2009). The strategy notes that some 2.5 mha of deap peat is already
under forestry, plantation and other leases. While economically rational because
mineral soils are more productive for development than peat, especially deep
peat,24 there is little sign of this option gaining traction.25
Data on deforestation since 2005 is conflicting.26 An assessment based on NASA
satellite data for 2005-2010 found a downward trend, with annual deforestation
declining from 1.1 mha in 2006 to 0.76 mha in 2009 (Hammer et al 2010). A
2011 analysis of the ten-year period 2000-2009, again using satellite data,
23. Expansion of the paper and pulpwood industries is closely linked to an Indonesian strategy to achieve much of its emission reductions through reforestation and plantation development. Some 500,000 hectares of land are planned to be re-forested each year (Oktofani 2011). But the net effect of this effort would be a net increase rather than a decrease in carbon emissions (Sastriastanti 2011b). The issue was closely analysed by CIFOR, which found that the only setting in which a (small) positive sequestration effect would result was where plantations were established on already deforested mineral soils (Verchot et al. 2010). 24. A cost-benefit analysis found that to match the opportunity cost of oil palm plantations on degraded mineral soil forests, a carbon price of US$57/tCO2e would be needed, but that a price range from US$2-10 /tCO2e would be sufficient for plantations on degraded peat soils, given the carbon intensity of peatlands (Irawan et al. 2011). 25. There are many impediments to use of degraded land, including definitional issues, poor quality of data on degraded land, and problems arising from such lands already being occupied by spontaneous settlers giving rise to land claim issues (Luttrell et al 2011: 11). 26. Trends to 2005 were summarised in Section 2.
31
concluded that deforestation totalled 15 mha over the decade, averaging 1.5
mha/yr.
Measurement uncertainty notwithstanding, Indonesia’s current deforestation
rate would appear to be equal to or in excess of recent deforestation rates in
Brazil, where an estimated 746,400 ha (7,464 km2) was lost in 2008-09 and
700,000 ha in 2009-10 (INPE 2011).
While there is no doubt that parts of the Indonesian Government (including the
President) are committed to addressing deforestation, the challenge is immense.
Given the mixed results to date from Indonesian efforts to address a range of
systemic governance problems, and major expansion plans for oil palm, biofuels
and the paper and pulpwood industries, the prospects for reduced deforestation
and reductions in emissions from forests and peatland appear uncertain at best.
The conflicting forces at work are well-illustrated by the implementation of the
May 2010 Norway-Indonesia Letter of Intent, which includes an agreement that
a two-year moratorium on new concessions for conversion of peat and natural
forest would be implemented as of 1 January 2011 (GON and GOI 2010). On the
day before the moratorium was slated to take effect, the Minister for Forestry
approved 2.9 million ha of new concessions. Since these now had the status of
being “previously approved concessions”, they fell outside the provisions of the
moratorium under the agreement with Norway (Jakarta Post 2011b). In an
action which effectively amounted to laundering of past violations of
concessions, just 11 days after the moratorium actually took effect in May 2011,
the Minister of Forestry issued a decree authorising a change of status for 1.67
mha of land in Central Kalimantan from forest land to non-forest, thus opening
the way for oil palm plantations to be established (Greenomics 2011). And even
as President Yudhoyono signed the moratorium, a palm oil enterprise was
reported to be engaged in destroying peat forests in Central Kalimantan which
were subject to the moratorium (Telapak 2011).
32
5.3. Central Kalimantan: disappearing peat
Central Kalimantan, the location of the KFCP pilot, is not only the obvious
location for large-scale application of any methodology developed by KFCP, but
also a microcosm for the struggle in relation to deforestation across Indonesia.
Central Kalimantan has committed to sharply reduce its emissions. In 2010, the
National Council for Climate Change and the provincial government (DNPI and
GOCK 2010) released a paper proposing a low-carbon strategy which would
reduce peatland emissions by 141 Mt CO2e per year by 2030 through elimination
of fires and peatland rehabilitation, plus a further 135 Mt CO2e per year through
other forestry abatement (DNPI and GOCK 2010, pp. 13-16).27 As noted
previously, Central Kalimantan is the first demonstration province selected by
Norway for its $1 billion fund.
Yet prospects for reducing emissions in Central Kalimantan appear bleak. The
Forest Watch Indonesia 2011 satellite analysis mentioned earlier shows that
Central Kalimantan and the Sumatran oil palm province of Riau are Indonesia’s
deforestation hotspots. The report found that the greatest forest loss between
2000 and 2009 was in the four provinces of Kalimantan which lost 5.5 mha (out
of a national total of 15 mha), with Central Kalimantan suffering the great loss at
2 mha (FWI 2011; Jakarta Post 2011c).
In September 2011 preparation of a REDD+ strategy for Central Kalimantan was
under way (Ministry of Forestry 2011) as required under the Norway
agreement. However, a large part of the province is under mining, oil palm and
logging concessions, with much of the remainder in national parks (pers. comm.,
Arie Rompas, WALHI, 6 Sept 2011; see map in FOEI 2011:15). It is difficult to see
where the province’s low-carbon strategy might be implemented.
One indicator of the difficulties in tackling peatland emissions in Central
Kalimantan is the lack of progress with rehabilitation of the Ex-Mega Rice Project
(EMRP) area. In 2007, President Yudhoyono issued a decree (Presidential
Instruction 2/2007) requiring the rehabilitation and conservation of the area.
27. Its emissions in 2005 were estimated at 292 Mt CO2e, of which peatland emissions comprised 185 Mt CO2e and LULUCF another 101 Mt CO2e (DNPI 2010a: 13-16).
33
This was followed by development in 2008 of a comprehensive EMRP Master
Plan to achieve this goal. The Master Plan called for all existing permits for palm
oil plantations on deep peat to be revoked. These covered an area of 120,000 ha
and contravened Presidential Decree 32 of 1990 (GOI 1990), which bans
development on peat greater than 3 meters in depth. Most of them are in Block
C, which is one of the largest sections of the EMRP and which has a substantial
area of deep peat, and some are in Block B. The Plan called for Block C to be
zoned for protection and limited development (Euroconsult and Deltares 2008:
17-18, 35-6, 127). Since then, however, various drafts of a revised spatial plan
for Central Kalimantan have been prepared (though not yet finalised or
released), and the aspiration to protect Block C has largely been dropped
(Ministry of Forestry 2009, Ministry of Forestry 2010a). A large part of Block C
is to be allocated to production forest or “other uses” without any of the
protections proposed in the EMRP Master Plan. Parts of Block B are also
proposed for “other uses”. A number of oil palm plantations are now visible from
Google Earth in Block C. Plans to implement the EMRP Master Plan have been
dropped altogether.
Concerns have frequently been raised regarding abuses of the concession system
in the EMRP area and the province generally. In February 2011, the Ministry of
Forestry stated that only 67 plantation companies out of 352 operated legally in
Central Kalimantan, and only nine out of 615 mining concessions operated
legally (Jakarta Globe 2011c). The central government has indicated its
intentions to challenge these abuses, with a team of officials from a judicial task
force, the Ministry of Forestry and the Corruption Eradication Commission
launching an investigation into illegal activities. It was reported in February
2011 that 967 forestry firms in Central Kalimantan were reported to be under
investigation (Jakarta Post 2011d). No action has since been taken.
Interestingly, one of the criticisms leveled by NGOs at KFCP is precisely that it is,
in the words of one of them, “Missing the big picture of destruction”:
“... the KFCP project with a 120,000 hectares (half the size of
Australian Capital Territory or ACT) project area pales in comparison
34
with the 15.1 million hectares of the total area in central Kalimantan,
at least 83% of which will be converted or destroyed through either
oil palm, monoculture pulp plantations or mining permits issued by
the relevant authorities. ... Emissions from such a huge area will
drastically overwhelm the insignificant and small reduction from the
KFCP site...” (Muliadi 2011)28
The AusAID response is that KFCP is a demonstration project, and part of a
“broader suite of efforts” (De Lacy 2011). This is true, but it is also the case that
KFCP constitutes the largest component of the Australian forest carbon effort in
Indonesia. We are now in a position to ask whether this makes sense.
6. Discussion and conclusion
As stated in the introduction, we are interested in KFCP from two perspectives,
as an example of the role of “announceables” in the Australian aid program, and
as a source of lessons for REDD. We address these in turn.
We have not come across a formal discussion of an “announceable,” and for our
purposes it suffices to define it simply a project which is launched with fanfare.
An announcement culture is one in which aid announceables rather than results
are given prominence. KFCP was an announceable back in 2007, and its
experience shows the damage which an announcement culture does to the aid
program.
As we have shown, KFCP as implemented bears very little relation to the project
as announced. The former is not only much less ambitious than the latter; it is
also now primarily conceived of as a REDD demonstration project.
It would have made more sense to announce, at the outset, targets that were
broadly consistent with the funding that was being made available, and not to
have to subsequently downsize targets by an order of magnitude. If the original
targets were required to signal ambition, then they also should have been
28. Note the exaggeration in the size of the project area, due to the failure (discussed in Section 3) to communicate that the project has in fact been downsized.
35
labelled as long-term or aspirational, and more realistic targets indicated for
KFCP as a project.
It would also have been sensible for the Australian government to have been
more explicit about the subsequent change in orientation and ambition of the
project. That would at least have allowed a defence to be mounted for the
direction the project was now taking. One very simple step would have been for
the Project Design Document to be made public. That this document is not yet
available on an Australian Government website, and that the original targets
have been dropped in all project documents but continue to be emphasized in
the official KFCP fact-sheet stands in stark contrast to AusAID’s aspiration to be
“one of the most transparent aid donors in the world,” (Rudd 2011),
The lack of transparency surrounding KFCP is not just a breach of basic
principles of good aid. It also risks undermining the project’s prospects and
impact.
First, as discussed in Section 3, the quiet way in which the downsizing has been
done has closed off the opportunity for discussion of whether reducing the
ambition of the project has increased risks to sustainability
Second, it is unfortunate that, four years on from announcement, there is not a
single public review or evaluation of KFCP. There is no doubt that much learning
has gone on under KFCP. But that will remain private unless results and lessons
are shared. By contrast, there is already a public independent evaluation of the
Norway-Indonesia forestry agreement, financed by Norway, even though the
agreement was signed some two and a half years after KFCP commenced
(Caldecott et al, 2011).
And, third, when it does at last become known that KFCP is in fact much smaller
than originally announced it will be hard to counter the inevitable impression
that Australia is not serious about helping Indonesia stem deforestation.
In summary, the case of KFCP does indeed confirm the damage done to the aid
program by an announcement culture. Of course, aid is not the only aspect of
36
government subject to this culture (Tanner 2011; Daley and Edis 2011). But it is
plausible to argue that, given the intrinsic difficulty of monitoring overseas aid
projects, the aid program is particularly at risk from a focus on announcements
rather than results.
In relation to lessons for REDD, our analysis in Sections 4 and 5 allows three
conclusions to be drawn. First, KFCP is badly delayed, and further delays are at
least possible if not likely. Whether or not the project will ever achieve its limited
goals is unclear.
Second, in the interim, emissions from deforestation in Indonesia, and
particularly in Central Kalimantan, continue to be high, and peatland forest
continues to be drained and converted, probably irreversibly in the case of oil
palm, despite an array of government policies aimed at addressing the problem.
In particular, oil palm continues to be developed on the Ex Mega Rice Project
Area, where KFCP is also located, and the latest plans for the EMRP area show
much reduced ambition in terms of peatland rehabilitation and protection. The
longer the delay in KFCP, the less of EMRP will be available for preservation in
any eventual scale-up.
Third, the global REDD market which was intended to be the vehicle by which
KFCP would be scaled-up is further away than ever, though more public
financing has become available, and national carbon trading schemes, such as
Australia’s, may provide a source of international demand for forestry credits.
We consider the implications of these findings first in relation to KFCP and the
Indonesia context, and then in relation to global REDD efforts in general.
Our research findings imply that the manner in which KFCP has been shaped is
mistaken. Australian forest carbon policy has remained unchanged since 2008.
But, as Section 5 showed, much has changed since then. It is time for a re-think.
It is no longer plausible to proceed with REDD demonstration projects and
technical assistance in the hope that a REDD market will come along to allow
these to be scaled-up.
37
The problem is not so much that the prospects for an international REDD market
are poorer now than they were in 2007. Public funding and national carbon
markets could fill the gap.
The deeper problem is that the prospect of large-scale REDD funds is at the
current time too distant and uncertain to provide sufficiently strong incentives to
tackle the deep-seated drivers of deforestation in Indonesia. The result is that
deforestation continues unabated, and the global policy goal of reducing
emissions is defeated.
What should be done? There are no easy answers. The drivers of deforestation in
Indonesia are both powerful and deep, ranging from poor governance and
corruption, to a powerful industry lobby, and the strong economics of oil palm.
How to influence these drivers is unclear, and Australia’s influence is limited. 29
One appealing option is that Australia should put the problem of deforestation in
Indonesia in the “too hard” basket, and cease current efforts.
Certainly, there is no point continuing along current lines. The most that can be
hoped for from KFCP under current plans is the tenuous, possibly temporary
protection of a relatively small patch of peatland, which, against the backdrop of
the underlying trends of continued, large-scale peatland conversion and
deforestation in Indonesia, would be at best a symbolic victory and at worst
harmful by giving the false impression of progress.
At the same time, pulling out would also not be an easy decision. Australia is now
invested in Indonesia’s forestry sector, and has made important commitments to
the local and poor people of the project area in particular. If the decision is made
to continue, we have three suggestions for a radically re-shaped engagement.
First, the experience with KFCP to date is that progress with peatland
rehabilitation will be slow, and gains hard to make. If it makes sense for
Australia to invest in this area, then we should be prepared to stay engaged in
this endeavour over the long-term, by providing ongoing funding to ensure that
29. Howes and Wywroll (2012) characterise peatland reclamation as one of Asia’s “wicked” environmental problems, implying that there are no easy or definitive solutions.
38
any successes are not reversed, and to expand the area being reclaimed. It
certainly makes sense for Australia to look for additional funding partners, but
other partners will only come in if Australia stays engaged, and makes more
funding available.
Such a reorientation would return Australia to the original KFCP vision, which
was to support a significant reduction in emissions, not just to show that it is
possible, but rather, indeed primarily, for the emissions reduction thereby
obtained.
Second, if Australia decides to stay engaged, it needs to engage more in policy
dialogue, and put a much larger sum of money on the table. The Norwegian
intervention in Indonesia presents an alternative model of engagement at the
policy level, supported by a substantial financial investment. There is no
guarantee that the Norwegian approach will work. Indeed, as we showed in the
last section, it has already been severely challenged. And clearly one needs both
policy changes and pilots. However, Australia’s restriction of its activities to
pilots and technical work, and its lack of emphasis on policies is a weakness. A
different sort of engagement is needed, with much closer collaboration with
Norway. Australia cannot only welcome Indonesia’s announcements that it plans
to tackle deforestation (e.g., AusAID 2011:38-39). It also needs to encourage
Indonesia to do more to turn those announcements into reality, and to try to
inject a sense of urgency into the reform process. This can be done in part by
political pressure and dialogue in relation to the drivers of deforestation, but it
would also require that a large amount of money be placed on the table by
Australia to encourage action, as Norway has done, to be disbursed on the basis
of performance.
Third, Indonesia and Australia apparently agreed in November 2008 on a second
pilot (DCCEE 2011), though this has still not been finalised (AusAID 2011). The
second pilot would apparently be a more conventional avoided deforestation
project (not on peat lands). The findings of this research do not support such a
move. Australia already has its hands full with KFCP. The odds are stacked
39
against success. If it is worth continuing, Australia should engage more in policy
dialogue, not disperse its efforts through a second demonstration project.
Finally, what are the implications for the global REDD effort? We noted in the
introduction the absence of detailed appraisals of REDD demonstration projects.
This study appears to be the first, and it is not encouraging. Reducing emissions
from deforestation and degradation would seem to be a complex, difficult and
slow task. Demonstration projects such as KFCP are moving forward too slowly
when considered against the rapid rate of deforestation.
While other surveys of demonstration projects (surveyed in Section 1) raise a
number of issues around project performance similar to the ones we have noted
in KFCP, the conclusion we draw is quite different. The REDD surveys aim to
show how REDD can work better. Our conclusion of slow progress when
juxtaposed against rapid deforestation leads us to be more sceptical of the entire
REDD undertaking.
The initial idea embedded in the Bali Action Plan that demonstration projects
could “address the drivers of deforestation” (UNFCCC, 2007) appears to be
unrealistic. The drivers are simply too powerful and systemic to be amenable to
influence from demonstration projects. Demonstration projects are important,
but they need to be scaled-up and built on over time, and accompanied by
support and pressure for policy reforms.
40
9. Annex: List of persons consulted
November 2010 – January 2011
Grahame Applegate Forest and Climate Specialist, AusAID / IAFCP Jakarta
Fitrian Ardiansyah Adviser on Climate and Energy, WWF Indonesia, ANU
Pep Canadell Global Carbon Group, CSIRO Marine and Atmospheric Research, Member, KFCP Peat and GHG Group
George Collett M&E Specialist, IAFCP, Jakarta
Erwinsyah KFCP Coordinator, Palangkaraya
Gamma Galudra Centre for International Forestry Research, Bogor
Silje Haugland UNREDD Program, Jakarta
Dan Heldon First Secretary, Climate Change & Development, AusAID Jakarta
Aljosja Hooijer Consultant to KFCP, Deltares, Netherlands
Tim Jessup Forest and Climate Specialist, AusAID / IAFCP Jakarta
Hege Karsti Counsellor, Climate Change, Embassy of Norway, Jakarta
Rosenda Chandra Kasih WWF Indonesia, Palangkaraya, Central Kalimantan
Dhinie Kirei University of Palangkaraya, Central Kalimantan
Rogier Klavier UN-REDD Program, Jakarta
Nick Mawdsley Former team leader, Ex-Mega Rice Project Master Plan
Salim Mazouz Department of Treasury, Canberra, and consultant to Ministry of Finance, Jakarta
Peter McCawley Visiting Fellow, Indonesia Project, ANU
Medrilzam University of Queensland and Bappenas
Daniel Murdiyarso Centre for International Forestry Research, Bogor
Humala Pontas Director of Planning, Bappeda, Province of Central Kalimantan
Eko Pranandhita Chief of Operations, KFCP Palangkaraya
John Raison Chief Research Scientist, Ecosystem Sciences, CSIRO Canberra and Chair, KFCP Peat and GHG Group
Budi Rario District Bappeda, Kapuas District, Kapuas, Central Kalimantan
Jhanson Regalino KFCP, Kapuas District, Central Kalimantan
Neil Scotland Coordinator, IAFCP Jakarta
Herwasono Soedjito Fire, Research and Monitoring Manager, KFCP, Jakarta
Suhada Commodity marketing officer, KFCP, Kapuas District, Cedntral Kalimantan
Ibu Endang Suyatmi Community Engagement Officer, KFCP, Katunjung, Kapuas District, Central Kalimantan
Luca Tacconi Crawford School, ANU
Susanna Tol Wetlands International, Netherlands
Ibu Natalia Yaya Community Engagement Officer, KFCP, Mantangai Hulu, Kapuas District, Central Kalimantan
Wahjudi Wardojo The Nature Conservancy, Jakarta,
41
Pungky Widiaryanto Bappenas, Jakarta
Yuliana Wulan Indonesia Climate Change Trust Fund, Jakarta
Ichlas al Zaqie Manager Reforestation Block A, KFCP
September 2011
Dr Suwido Limin Centre for International Cooperation in Management of Tropical Peatlands (CIMTROP), University of Palangkaraya (UNPAR)
Pak Arie Rompas Director, WALHI Kalimantan Tengah
Pak Sepit Ketua, Dinas Kehutanan Provinsi Kalimantan Tengah
Pak Mursid Badan Lingkungan Hidup, Provinsi Kalimantan Tengah
Pak Saribi Bappeda, Kabupaten Kapuas
Pak Budi Rario Bappeda, Kabupaten Kapuas
Pak Angi Rohan Dewan Adat Dayak, Kapuas
Pak Nurhadi Yayasan Petak Danum Kapuas
Dr Yusurum Jagau University of Palangkaraya (UNPAR)
Pak Yuyu Rahayu Departemen Kehutanan, Jakarta
Pak Aloe Dohong University of Queensland
Pak Merilzam University of Queensland
Dr Peter McCawley Economic Adviser, Bappenas, Support for Economic Analysis Development in Indonesia (SEADI)
Pak Elfian Effendi Director, Greenomics, Jakarta
Pak Leonard Digna, Ibu Forest Watch Indonesia, Bogor
Frionny, Pak Sulton
Rogier Klavier UN-REDD Indonesia
Pak Hapsoro, Pak Abu Telapak Indonesia, Bogor
Bill Hellier Jakarta
42
8. References
AMAN, 2011 ‘Statement of Concern on REDD+ in Central Kalimantan, Indonesia: Indigenous Peoples Alliance of Archipelago – Central Kalimantan’ Chapter. 17 June 2011. Reported in REDD-Monitor, Jakarta. <http://www.redd-monitor.org/wordpress/wp-content/uploads/2011/06/AMAN-Kalteng-17-Juni-2011-on-REDD+-EN.pdf>
Angelsen, A, Ed., 2008 Moving Ahead with REDD: Issues, Options and Implications, Center for International Forestry Research, Bogor, Indonesia. <http://www.cifor.cgiar.org/publications/pdf_files/Books/BAngelsen0801.pdf>
Angelsen, A, Brown, S, Loisel, C, Peskett, L, Streck, C, & Zarin, D, 2009 Reducing Emissions from Deforestation and Forest Degradation (REDD): An Options Assessment Report, Meridian Institute for the Government of Norway. <http://www.REDD-OAR.org>
Antara, 2007 ‘President hopes RI-Australia partnership will improve people's welfare, protect orangutans’, Antara Newsagency, 9 September 2007. <http://www.mail-archive.com/cikeas@yahoogroups.com/msg04138.html>
Antara News, 2011 ’RI Minister, Australian envoy launch model REDD villages in C Kalimantan’, Antara News. <http://www.antaranews.com/en/news/75745/ri-minister-australian-envoy-launch-model-redd-villages-in-c-kalimantan>
Arnold, L, 2008 ‘Deforestation in Decentralised Indonesia: What’s Law Got to Do with It?’ Law, Environment and Development Journal, vol. 4 (2), pp. 77-101. <http://www.lead-journal.org/content/08075.pdf>
AusAID 2007 ‘Scope of initiative: Global Initiative of Forests and Climate’, Australian Government. <http://www.ausaid.gov.au/budget/budget07/budget_forests.pdf>
AusAID 2011 Indonesia Development Cooperation Report 2010, Australian Agency for International Development. Canberra. <http://www.ausaid.gov.au/publications/pdf/indonesia-development-cooperation-report-2010.pdf>
Australian Embassy 2011 Australian Ambassador and Minister for Forestry visit Central Kalimantan, Jakarta, Media release, 16 September 2011. <http://www.indonesia.embassy.gov.au/jakt/MR11_067.html.>
Australian Government 2008 ‘Reducing Emissions from Deforestation and Forest Degradation in Developing Countries (REDD)’. Submission to the AWG-LCA, UNFCCC. <http://www.climatechange.gov.au/en/government/initiatives/unfccc/~/media/submissions/international/Reducing-emissions-from-deforestation-and-forest-degradation-in-developing-countries-AUG-08.ashx.>
43
Bappenas 2009 Reducing carbon emissions from Indonesia’s peat lands. Interim Report of a Multi-Disciplinary Study, December 2009, Republic of Indonesia.
Barr, C 2001 Banking on sustainability: Structural adjustment and forestry reform in post-Suharto Indonesia, WWF Macroeconomics Program Office and CIFOR, Washington, DC., USA. <http://www.cifor.org/publications/pdf_files/books/profits.pdf>
Barr, C, Dermawan, A, Purnomo, H and Komarudin, H 2010 ‘Financial governance and Indonesia’s Reforestation Fund during the Soeharto and post-Soeharto periods, 1989–2009. A political economic analysis of lessons for REDD+.’ CIFOR Occasional Paper No. 52. Bogor, Indonesia. <http://www.cifor.org/publications/pdf_files/OccPapers/OP-52.pdf.>
Broich, M 2011 ‘Remotely sensed forest cover loss shows high spatial and temporal variation across Sumatera and Kalimantan, Indonesia 2000–2008,’ Environ. Res. Lett., 6 (January-March 2011) 014010. <http://iopscience.iop.org/1748-9326/6/1/014010/fulltext.>
Butler, A 2010 ‘Indonesia's plan to save its rainforests. An interview with Agus Purnomo and Yani Saloh, Special Assistants to the President of the Republic of Indonesia for Climate Change.’ Mongabay web-site. 14 June 2010. <http://news.mongabay.com/2010/0614-indonesia_purnomo_saloh.html>
Caldecott, J, Indrawan, M., Rinne, P. and Halonen, M, 2011, Indonesia-Norway REDD+ Partnership: first evaluation of deliverables, Final Report 3 May 2011. Gaia Consulting Ltd. <http://unredd.wordpress.com/2011/08/11/read-the-most-recent-report-on-the-indonesia-norway-redd-partnership/>
CARE 2009 Fire report. CARE Activity 2.7. Report prepared for KFCP. Unpublished report prepared for KFCP project.
Casson A 2000 The Hesitant Boom: Indonesia’s Oil Palm Sub-Sector in an Era of Economic Crisis and Political Change, Occasional Paper No. 29 CIFOR, Bogor Indonesia. <http://www.cifor.org/publications/pdf_files/casson.pdf>
CCFPI 2005 Climate Change Forests and Peatlands in Indonesia (CCFPI) Project Information Sheet. <http://www-personal.umich.edu/~thoumi/Research/Carbon/Forests/Forests,%20Peatlands/CCFPIProjInfoSheetNov2005.pdf>
Cerbu, G, Swallow, B, Thompson, D, 2010 ‘Locating REDD: A global survey and analysis of REDD readiness and demonstration activities’, Environmental Science and Policy Vol 14(2), March 2011: 1680180.). <http://www.sciencedirect.com/science/article/pii/S1462901110001176Chestney>
44
Chomitz, KMC, Buys, P, De Luca, G, Thomas, TS, Wertz-Kanounikoff, S 2007 Overview: At loggerheads? Agricultural expansion, poverty reduction, and environment in the tropical forests. World Bank, Washington.
CKPP 2008 Provisional Report of the Central Kalimantan Peatland Project, Palangka Raya, CKPP Consortium. Wetlands International, November 2008. <http://www.ckpp.org/Portals/16/CKPP%20products/CKPP%20Provisional%20Report%20ENG%20final.pdf>
Combet, G 2010 ‘The Hon Greg Combet AM MP, Minister for Climate Change and Energy Efficiency: High level segment statement to UN Climate Change Conference, Cancun, Mexico,’ Department of Climate Change, 10 December 2010. <http://www.climatechange.gov.au/minister/greg-combet/2010/major-speeches/December/sp20101210.aspx>
Commonwealth of Australia 2012, Proof Committee Hansard. Senate Foreign Affairs, Defence and Trade Legislation Committee Estimates. Thursday 16 February 2012. <http://parlinfo.aph.gov.au/parlInfo/download/committees/estimate/7afd22ed-c48e-4bfa-afdd-f0c6c22a0235/toc_pdf/Foreign%20Affairs,%20Defence%20and%20Trade%20Legislation%20Committee_2012_02_16_800.pdf;fileType=application%2Fpdf#search=%22committees/estimate/7afd22ed-c48e-4bfa-afdd-f0c6c22a0235/0000%22>
Corbera, E, Estrada, M, Brown, K, 2010 ‘Reducing greenhouse gas emissions from deforestation and forest degradation in developing countries: revisiting the assumptions,’ Climatic Change, vol. 100, pp. 355–388. DOI 10.1007/s10584-009-9773-1.
Creed, A and Nakhooda, S, 2011 REDD+ Finance Delivery: Lessons from Early Experience. Heinrich Boell Stiftung North America and Overseas Development Institute. <http://www.odi.org.uk/resources/docs/7481.pdf>
Daviet, F, Goers, L, MacFaul, L, Johnson, A, Stasio, K, 2010 Tracking Transformative Forest Actions to Reduce Emissions: An illegal logging case study., Washington DC, World Resources Institute Working Paper, July 2012. <http://www.wri.org/publication/tracking-transformative-forest-actions-to-reduce-emissions>
Daley, J ,Edis, T, Reichl, J, 2011 ‘Learning the hard way: Australia’s policies to reduce emissions,’ Grattan Institute, Melbourne. <http://www.grattan.edu.au/publications/077_report_energy_learning_the_hard_way.pdf >
DCCEE, 2011. Kalimantan Forests and Climate Partnership Fact Sheet. <http://www.climatechange.gov.au/government/initiatives/international-forest-carbon-initiative/~/media/publications/international/kfcp_factsheet.ashx>
45
De Lacy, J, 2011 RE: Community Concerns with the KFCP, AusAID Jakarta Office. Letter to S.E. Muliadi, 20 April 2011. <http://www.redd-monitor.org/2011/05/17/reply-from-ausaid-about-the-kalimantan-forests-and-climate-partnership/>
DNPI, 2010 Indonesia's Greenhouse Gas Abatement Cost Curve, Dewan Nasional Perubahan Iklim (National Council on Climate Change). <http://www.dnpi.go.id/report/DNPI-Media-Kit/reports/indonesia-ghg_abatement_cost_curve/Indonesia_ghg_cost_curve_english.pdf>
DNPI & GOCK, 2010 Creating low carbon prosperity in Central Kalimantan, Dewan Nasional Perubahan Iklim (National Council on Climate Change) and Government of Central Kalimantan. <http://photos.mongabay.com/10/central_kalimantan_report_small.pdf>
Downer, A 2007 ‘Indonesian Forests Partnership to Reduce Greenhouse Gas Emissions’, AusAID press release, dated 9 Sept 2007. <http://www.ausaid.gov.au/media/release.cfm?BC=Media&ID=2020_9057_2766_2273_327>
Downer, A 2007a ‘Joint press conference: Minister Downer, Minister Turnbull, President Yudhoyono (Indonesia)’, 9 September 2007. <http://parlinfo.aph.gov.au/parlInfo/download/media/pressrel/EIHO6/upload_binary/eiho62.pdf;fileType%3Dapplication%2Fpdf>
Easterly, W 2002 ‘The Cartel of Good Intentions: The Problem of Bureaucracy in Foreign Aid’, Journal of Policy Reform, vol. 5 (4), pp. 1-28.
Euroconsult & Deltares 2008 Master Plan for the Rehabilitation and Revitalisation of the Ex-Mega Rice Project Area in Central Kalimantan: Main Synthesis Report, October 2008. Undertaken by Euroconsult Mott Macdonald, and Deltares / Delft Hydraulics. A Joint Initiative of the Governments of Indonesia and the Netherlands. <http://www.geog.le.ac.uk/carbopeat/media/pdf/pub_technical_review%201-science.pdf>
FAO 2009, State of the world’s forests 2009 Food and Agriculture Organisation of the United Nations, Rome 2009. <http://www.fao.org/docrep/011/i0350e/i0350e00.HTM>
Fire Management Unit KFCP, 2011 Laporan Kemajuan Output 1.4: Ringkasan Kemajuan Unit FM, (Report on progress of Output 1.4: Summary of progress of FM Unit). Internal project document.
FOEI, 2011 In the REDD: Australia’s carbon offset project in Central Kalimantan, Amsterdam, Friends of the Earth International. <http://www.foei.org/en/resources/publications/pdfs/2011/in-the-redd-australias-carbon-offset-project-in-central-kalimantan>
46
Fogarty, D 2011 ‘How Indonesia crippled its own climate project’, Climate Spectator 17 August 2011. <http://www.climatespectator.com.au/commentary/how-indonesia-crippled-its-own-climate-project?utm_source=Climate%2BSpectator%2Bdaily&utm_medium=email&utm_campaign=Climate%2BSpectator%2Bdaily&utm_source=Climate+Spectator&utm_campaign=ed72836ff3-CSPEC_DAILY&utm_medium=email>
FPP, 2011 Central Kalimantan: REDD+ and the Kalimantan Forest Carbon Partnership (KFCP). Forest Peoples Programme. <http://www.forestpeoples.org/sites/fpp/files/publication/2011/10/central-kalimantan-briefing-2.pdf>
FPP/SawitWatch 2006 Promised Land: Palm Oil and Land Acquisition in Indonesia - Implications for Local Communities and Indigenous Peoples. Forest Peoples Programme and Sawit (oil palm) Watch. <http://archive.forestpeoples.org/documents/prv_sector/oil_palm/promised_land_eng.pdf>
FWI, 2011. Potret Keadaan hutan Indonesia periode tahun 2000-2009 (Portrait of the situation of Indonesia Forests, 2000-2009). Report by Forest Watch Indonesia, Bogor. <http://fwi.or.id/>
Galudra G., van Noordwijk, M., Suyanto, Idris Sardi and Ujjwal Pradhan, 2010Hot Spot of Emission and Confusion: Land Tenure Insecurity, Contested Policies and Competing Claims in the Central Kalimantan Ex-Mega Rice Project Area,. World Agroforestry Centre (ICRAF), Bogor, Indonesia. <http://www.worldagroforestry.org/downloads/publications/PDFS/WP16601.PDF>
Goers-Williams, L, Davis, C, Lupberger, S, Daviet, F, 2011 Getting Ready: A Review of the World Bank Forest Carbon Partnership Facility Readiness Preparation Proposals. World Resources Institute Working Paper October 2011. Washington DC. <http://www.wri.org/gfi>
GOI 1990 Keputusan Presiden No. 32 Tahun 1990 (Keppres 32/1990). Tentang : Pengelolaan Kawasan Lindung, 25 Juli 1990 (Presidential Decree 32/1990 regarding management of protected areas, 25 July 1990).
GOI 2010. National REDD+ Strategy, Draft 1, revised 23 September 2010. <http://www.un.or.id/sites/default/files/COMPLETEStranas1RevisedEng%20final%20version.pdf>
GOI, 2011 Strategi Nasional REDD+. (National REDD+ Strategy. Final draft for Online Public Disclosure), Bappenas, Jakarta. <http://www.ukp.go.id/informasi-publik/cat_view/21-redd>
GON & GOI, 2010 Letter of Intent between the Government of the Kingdom of Norway and the Government of the Republic of Indonesia on “Cooperation on
47
reducing greenhouse gas emissions from deforestation and forest degradation” 26, May 2010, Oslo, Norway. <http://www.norway.or.id/PageFiles/404362/Letter_of_Intent_Norway_Indonesia_26_May_2010.pdf>
Greenomics, 2011 Minister of Forestry proves Indonesia's moratorium is toothless. Report dated 27 June 2011. <http://www.greenomics.org/docs/Report_201106_IndonesiaMoratorium.pdf>
Habir, M, 2010 ‘Analysis: Who benefits from 2-year moratorium on forest clearing?’ Jakarta Post , 5 July 2010. <http://www.thejakartapost.com/news/2010/07/05/analysis-who-benefits-2year-moratorium-forest-clearing.html>
Hammer, D, Kraft, R, Wheeler, D, 2010 Forest clearing report: Indonesia Dec. 2005 - Sept 2010, Forest Monitoring for Action (FORMA). <http://www.cgdev.org/forma>
Hansen, CP, Lund, JF, Treue, T. 2009 ‘Neither fast, nor easy: The prospect of reduced emissions from deforestation and degradation (REDD) in Ghana’, International Forestry Review, Vol. 11(4), pp. 439-455.
Hansen, MC, Stehman, SV, Potapov, PV, Arunarwati, B, Stolle, F & Pittman, K, 2009 ‘Quantifying changes in the rates of forest clearing in Indonesia from 1990 to 2005 using remotely sensed data sets’, Environ Res Lett, vol. 4 (10), (1088/1748-9326/4/3/034001). <http://iopscience.iop.org/1748-9326/4/3/034001>
Hollway, S et al. 2011 Independent Review of Aid Effectiveness. Government of Australia, April 2011. <http://www.aidreview.gov.au/publications/aidreview.pdf.>
Hooijer, A, Silvius, M, Wosten, H & Page, S, 2006 PEAT-CO2, Assessment of CO2 emissions from drained peatlands in SE Asia. <http://www.forestcarbonportal.com/resource/peat-co2-assesment-co2-emissions-drained-peatlands-south-east-asia>
Howard, J, 2007 Australia to Lead the World: Global Initiative on Forests and Climate, Media release, 29 March 2007. <http://www.cifor.cgiar.org/publications/pdf_files/media/Howard%20Downer%20Turnbull%20Release.pdf>
Howes, S, 2009 ‘Cheap but not easy: the reduction of greenhouse gas emissions from deforestation and forest degradation in Papua New Guinea,’ Pacific Economic Bulletin, vol. 24 (1), pp. 130-143.
Howes, S. and P. Wyrwoll. 2012. Asia’s Wicked Environmental Problems. ADBI Working Paper 348. Tokyo: Asian Development Bank Institute.
48
<http://www.adbi.org/working-paper/2012/02/28/5009.asia.wicked.environmental.problems/>
IAFCP, 2008 Indonesia - Australia Forest Carbon Partnership. Agreement between Australian Prime Minister Kevin Rudd and Indonesian President Yudhoyono, dated 13 June 2008. Jakarta. <http://www.climatechange.gov.au/en/government/initiatives/international-forest-carbon-initiative/~/media/publications/international/indonesia-australia.ashx>
IAFCP 2008a Kalimantan Forests and Climate Partnership Framework Design Mission: Draft Report, 19 May 2008.
IAFCP 2010a IAFCP Rolling Prioritisation Plan Update July 2010 - June 2011.; Unpublished project document.
IAFCP 2010b IAFCP Quarterly Progress Report 1 July - 30 September 2010. Unpublished project document.
INPE 2011 INPE releases Amazon deforestation rate in 2010. National Institute for Space Research of Brazil (INPE), news release 3 October 2011. <http://www.inpe.br/ingles/news/news.php?Cod_Noticia=10>
Irawan, S, Tacconi, L & Ring, I, 2011 Stakeholders’ incentives for land-use change and REDD: The case of Indonesia, Crawford School of Economics and Government, The Australian National University. <http://apneg.anu.edu.au/pdf/2011/wp_apneg_002.pdf>
Jaenicke, J, Englhart, S, Siegart, F 2010 ‘Monitoring the effect of restoration measures in Indonesian peatlands by radar satellite imagery’, Journal of Environmental Management, vol. 92 (2011), pp. 630-638
Jakarta Globe, 2011a, ‘Indonesia President Vows to Protect Forests’, 27 September 2011. <http://www.thejakartaglobe.com/home/indonesia-president-vows-to-protect-forests/468159>
Jakarta Globe, 2011b ‘Illegal Logging, Mining Ravages Kalimantan, Costs Indonesia $36.4b’ Article dated 28 April 2011. <http://www.thejakartaglobe.com/nvironment/illegal-logging-mining-ravages-kalimantan-costs-indonesia-364b/437911>
Jakarta Globe, 2011c ‘Indonesia Makes Startling Admission on Forests’, Article dated 3 February 2011. <http://www.thejakartaglobe.com/home/indonesia-makes-startling-admission-on-forests/420396>
Jakarta Post, 2011a ‘Indonesia allocates 18 million hectares of land for palm oil’. <http://www.thejakartapost.com/news/2009/12/02/indonesia-allocates-18-million-hectares-land-palm-oil.html>
49
Jakarta Post, 2011b ‘Greenomics criticizes ministry for new decree’ Article dated 28 January 2011. <http://www.thejakartapost.com/news/2011/01/28/greenomics-criticizes-ministry-new-decree.html>
Jakarta Post, 2011c ‘15 million hectares of forests destroyed from 2000 to 2009: FWI’. Article dated 27 July 2011. <http://www.thejakartapost.com/news/2011/07/27/15-million-hectares-forests-destroyed-2000-2009-fwi.html>
Jakarta Post, 2011d ‘967 forestry firms under govt. scrutiny’. Article dated 2 Feb 2011, Jakarta. <http://www.thejakartapost.com/news/2011/02/02/967-forestry-firms-under-govt-scrutiny.html>
Kanninen, M et al 2007 Do Trees Grow on Money? The implications of deforestation research for policies to promote REDD, Center for International Forestry Research (CIFOR), Bogor, Indonesia. <http://www.cifor.org/publications/pdf_files/Books/BKanninen0701.pdf>
Keller, A 2011 ‘Money thrown out of the window’, Article in taz.de about the Kalimantan Forest and Climate Partnership. <http://www.redd-monitor.org/2011/12/02/money-thrown-out-of-the-window-article-in-taz-de-about-the-kalimantan-forest-and-climate-partnership/?utm_source=feedburner&utm_medium=email&utm_campaign=Feed%3A+Redd-monitor+%28REDD-Monitor%29>
KFCP 2009 Kalimantan Forests and Climate Partnership (KFCP) Design Document. <http://www.formin.fi/public/download.aspx?ID=61175&GUID=%7BD79AB65D-228B-4657-91F8-FA9724568E1F%7D>
KFCP 2009a Village Reconnaissance Report, Activity 2.2. CARE International, Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2009b Profil Katunjung: Bagian I: Seperti apa desa kami saat ini?(Profile of Katunjung: What is our village like at this point?). CARE International, Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2009c CARE Activity 2.14: Community Engagement In Blocking Canals. CARE International, Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2009d Fire Report. CARE Activity 2.7. CARE International, Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2009e Government Mapping Report. Activity 2.1. CARE International, Unpublished report for Kalimantan Forests and Climate Partnership.
50
KFCP 2010a Commodity Status report: Gemor. March 2010. GRM International (Teddy Kristedi and Johan Kieft) Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2010b Commodity status report: Rubber, March 2010. GRM International (Teddy Kristedi, Johan Kieft, and Frank Page). Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2010c Laporan Penananaman KFCP 2010. Laporan Pelaksanaan. Penanaman Blok A - Compartment B3 dan C3 Desa Katunjung dan Desa Mantangai Hulu. (Report on planting, KFCP 2010. Report on implementation of planting in Block A - COmpartment B3 and C3, Katunjung and Mantangai Hulu villages). Unpublished report for Kalimantan Forests and Climate Partnership.
KFCP 2010d Reforestation Highlight. Milestone 3: Reforestation of Block A. Undated 1-page note on progress. Unpublished report for Kalimantan Forests and Climate Partnership.
KPK, 2010 Siaran Pers: Paparan Hasil Kajian KPK tentang Kehutanan (Press release: Explanation of findings of KPK's investigations of forestry sector). Corruption Eradication Commission (Komisi Pemberantasan Korupsi). <http://www.kpk.go.id/modules/news/article.php?storyid=1726>
Kuncoro, A 2008 ‘Corruption Inc’, Inside Indonesia, Edition 92: Apr-Jul 2008. <http://www.insideindonesia.org/edition-92-apr-jul-2008/corruption-inc-25051082>
Lang, C 2011a ‘'Stop the Indonesia-Australia REDD+ project”: Indigenous Peoples’ opposition to the Kalimantan Forests and Climate Partnership’, REDD-Monitor.org. Article dated 15 June 2011. <http://www.redd-monitor.org/2011/06/15/stop-the-indonesia-australia-redd-project-indigenous-peoples-opposition-to-the-kalimantan-forests-and-climate-partnership/>
Lang, C 2011b Another statement about the Kalimantan Forests and Climate Partnership. Previous statement “not true”, Article dated 25 July 2011. <http://www.redd-monitor.org/2011/07/25/another-statement-about-the-kalimantan-forests-and-climate-partnership-previous-statement-not-true/#more-9066>
Lang, C 2011c ‘Reply from AusAID about the Kalimantan Forests and Climate Partnership’, REDD-Monitor. Article dated 17 May 2011. <http://www.redd-monitor.org/2011/05/17/reply-from-ausaid-about-the-kalimantan-forests-and-climate-partnership/>
Lawson, S and MacFaul L, 2010 Illegal logging and related trade. Indicators of the global response. Chatham House, London. <http://www.illegal-logging.info/uploads/CHillegalloggingpaperwebready1.pdf>
51
Li, TM 2011 ‘Centering labor in the land grab debate’, Journal of Peasant Studies, vol. 38 (2), pp. 281-298. <http://dx.doi.org/10.1080/03066150.2011.559009>
Luttrell, C, Obidzinski, K, Brockhaus, M, Muharrom, E, Petkova, E, Wardell, A & Halperin, J 2011 ‘Lessons for REDD+ from measures to control illegal logging in Indonesia’, CIFOR Working Paper 74, Jakarta and Bogor, Center for International Forestry Research. <http://www.cifor.org/publications/pdf_files/WPapers/WP74Obidzinski.pdf>
Madeira, E, Sills, E, Brockhaus, M, Verchot, L, Kanninen, M 2010 ‘What is a REDD+ pilot? A preliminary typology based on early actions in Indonesia’ Bogor Center for International Forestry Research. <http://www.cifor.org/publications/pdf_files/infobrief/3266-infobrief.pdf>
Malone, P 2010 ‘Swamp rehab project remains bogged’. Article dated 5 June 2010. Canberra Times, Canberra, Australia.
McCarthy, JA, Cramb, RA 2009 ‘Policy narratives, landholder engagement, and oil palm expansion on the Malaysian and Indonesian frontiers’, The Geographical Journal, vol. 175(2), pp. 112-123.
Ministry of Forestry 2008 ‘IFCA Consolidation Report: Reducing emissions from deforestation and forest degradation in Indonesia’, Forest Research and Develoment Agency, Ministry of Forestry, Republic of Indonesia. <http://www.forestcarbonpartnership.org/fcp/sites/forestcarbonpartnership.org/files/Documents/PDF/IFCA_Consolidation_report_REDD_Indonesia_0.pdf>
Ministry of Forestry 2009 ‘Peta Usulan perubahan kawasan hutan dalam revisi rencana tata ruang wilayah provinsi Kalimantan Tengah’, (Map of proposals to change forest areas as part of revisions to spatial plan for Central Kalimantan). Ministry of Forestry, Jakarta. 26 May 2009.
Ministry of Forestry 2010 ‘National Strategy REDD - Indonesia. Readiness Phase 2009 – 2012 and progress in implementation’ Ministry of Forestry, February 2010, Jakarta.
Ministry of Forestry 2010a ‘Peta perubahan peruntukan kawasan hutan menjadi bukan kawasan hutan, penunjukan areal bukan kawasan hutan menjadi kawasan hutan dan perubahan fungsi antar kawasan hutan di wilayah provinsi Kalimantan Tengah’, (Map of alterations to forest areas to become non-forest areas, designation of non-forest areas to become forest areas, and functional changes in forest areas in Central Kalimantan). Ministry of Forestry, Jakarta. 20 September 2010.
Ministry of Forestry 2011 ‘Kalimantan Tengah Akan Selesaikan Strategi Daerah REDD+ Dalam 2 Bulan’ (Central Kalimantan to complete regional REDD+ strategy within two months), Ministry of Forestry, Jakarta.<http://redd-indonesia.org/index.php?option=com_content&view=article&id=266:kalimantan
52
-tengah-akan-selesaikan-strategi-daerah-redd-dalam-2-bulan&catid=1:fokus-redd&Itemid=50>
Muliadi, SE 2011 ‘To the Australian Delegation to Central Kalimantan February 2011, RE: Community Concerns with the KFCP’, Letter dated 24 February 2011. Yayasan Petak Danum, Central Kalimantan. <http://www.redd-monitor.org/2011/02/27/community-concerns-with-the-kalimantan-forests-and-climate-partnership-no-rights-no-kcfp/>
Neilson, J 2010 ‘Who owns the carbon? Indonesia’s carbon stores spark international attention’, Article dated 22 Jan 2011 in Inside Indonesia: Indonesia's Environmental Challenges series. <http://www.insideindonesia.org/stories/who-owns-the-carbon-05091343>
NFA 2011 ‘Factbox: What UN climate talks agreed to in Durban,’ Climate Spectator, 12 December 2011. <http://www.climatespectator.com.au/news/factbox-what-un-climate-talks-agreed-durban>
Oktofani, E 2011 ‘Forest Concessions to Be Granted in Logged Land’, The Jakarta Globe, article dated, 2 January 2001. <http://www.thejakartaglobe.com/news/forest-concessions-to-be-granted-in-logged-land/414654>
Page, SE, Sieger, J, O’Rieley, J, Boehm, HDV, Jaya, A, Limin, S 2002, ‘The amount of carbon released from peat and forest fires in Indonesia during 1997’, Nature, vol. 420, pp. 61-65. <http://www.nature.com/nature/journal/v420/n6911/full/nature01131.html>
RECOFTC, 2010 Forests and climate change after Copenhagen. An Asia-Pacific perspective, Bangkok. <http://www.recoftc.org/site/uploads/content/pdf/FCC-after-Copenhagen_3_8.pdf>
REDD-net 2010, Catalysing REDD+ at the national level: Summary of experience so far. UK Department for International Development. <http://redd-net.org/files/Catalysing%20REDD%20at%20the%20national%20level.pdf>
Reuters, 2010 ‘Indonesia chooses climate pact pilot province’, Business Spectator, Article dated 30 Dec 2010. <http://www.businessspectator.com.au/bs.nsf/Article/Indonesia-chooses-climate-pact-pilot-province-CM9U3?OpenDocument&src=rab>
Rudd, K 2011 ‘Transparency in the Australian aid program’, Media Release, 23 November. <http://foreignminister.gov.au/releases/2011/kr_mr_111123b.html>
Satriastanti, F, 2011a, ‘Plantations, Mining and REDD a Threat: Dayak’, Article dated 25 October 2011, Jakarta Globe.
53
<http://www.thejakartaglobe.com/home/plantations-mining-and-redd-a-threat-dayak/473817>
Sastriastanti, F 2011b ‘Indonesian Forestry Plan Undermines Carbon Cuts: Greenomics’, Jakarta Globe, Article dated 11 January 2010. <http://www.thejakartaglobe.com/news/indonesian-forestry-plan-undermines-carbon-cuts-greenomics/352122>
SEApeat, 2011 ‘UNPAR’s Peat Scientists and Practitioners Reject KFCP’s Plan’, Article dated 6 July 2011. Sustainable Management of Peatland Forests in Southeast Asia (SEApeat). <http://www.aseanpeat.net/newsmaster.cfm?&menuid=11&action=view&retrieveid=12>
Tanner, L 2011 ‘Sideshow syndrome eroding democracy’, The Australian. <http://www.theaustralian.com.au/news/features/sideshow-syndrome-eroding-democracy/story-e6frg6z6-1226046757528>
Tapp, C, 2011 ‘Study of Australia's approach to aid in Indonesia: Final report’, A report to the Panel conducting the Independent Review of Aid Effectiveness. <http://www.aidreview.gov.au/publications/study-indonesia.pdf>
Telapak, 2011 ‘Caught REDD Handed: How Indonesia's logging moratorium was criminally compromised on Day One and Norway will profit’, Telapak. <http://www.telapak.org/images/stories/pdf/Caught_REDD_Handed_.pdf>
Tol, S, 2010. Cancún Climate Summit addresses emissions from peatlands - part II. <http://www.wetlands.org/NewsandEvents/NewsPressreleases/tabid/60/articleType/ArticleView/articleId/2534/Default.aspx>
Tol, S, 2011a. Durban Climate Summit enables carbon cuts from peatlands. <http://www.wetlands.org/News/tabid/66/articleType/ArticleView/articleId/2794/Default.aspx>
Tol, S. 2011b ‘RE: Cancun decisions in relation to peatland emissions’, E-mail to first author, dated 26 Jan 2011.
UNFCCC 2008, Decision CP.13 Bali Action Plan. United National Framework Convention on Climate Change. <http://unfccc.int/files/meetings/cop_13/application/pdf/cp_bali_action.pdf>
Verchot, L, Petkova, E, Obidzinski, K, Stibniati A, Yulyani E, Dermawan, A, Murdiyarso, D & Salwa, A 2010 Reducing forestry emissions in Indonesia, Bogor, Indonesia, CIFOR. <http://www.cifor.org/publications/pdf_files/Books/BVerchot0101.pdf>
Wertz-Kanounnikoff, S & Kongphan-Apirak, M 2009 Emerging REDD+. A preliminary survey of demonstration and readiness activities, Bogor, Indonesia.
54
<http://www.cifor.org/publications/pdf_files/WPapers/WP46Wertz-Kanounnikoff.pdf>
Westholm, L., Henders, S, Ostwald, M, & Mattsson, E 2009. Assessment of existing global financial initiatives and monitoring aspects of carbon sinks in forest ecosystems – The issue of REDD, Focali (Forest, Climate and Livelihood research network), Sweden. <http://www.focali.se/filer/Focali%20publication%202009_01.pdf>
World Bank 2008 Climate change in Indonesia: low carbon development options study. Phase 1 Status Report. Paper presented at the National Consultation on ‘A Regional Review of the Economic of Climate Change in South East Asia, Jakarta, Indonesia, 23–24 May. <http://www.esmap.org/esmap/sites/esmap.org/files/Final%20Low%20Carbon%20Dev%20Options%20Phase1_english_0.pdf>
World Bank 2010, Environmental, Economic and Social Impacts of Oil Palm in Indonesia: A Synthesis of Opportunities and Challenges. Discussion Paper, May 2010. <http://www.ifc.org/ifcext/agriconsultation.nsf/AttachmentsByTitle/WB+discussion+paper/$FILE/WB_Oil+Palm+SynthesisDiscussionPaperMay2010.pdf>
World Bank (Ed.) 2011a Rising Global Interest in Farmland: Can it yield sustainable and equitable benefits?, The World Bank, Washington.
World Bank 2011b The World Bank Group Framework and IFC Strategy for Engagement in the Palm Oil Sector. DRAFT FOR CONSULTATIONS. January 6, 2011. <http://www.ifc.org/ifcext/agriconsultation.nsf/AttachmentsByTitle/Jan6_Draft+Framework/$FILE/WBG+Framework+and+IFC+Strategy_draft+for+consultations.pdf>
World Bank 2011c, ‘Mobilizing Climate Finance’, A Paper prepared at the request of G20 Finance Ministers. <http://www.guardian.co.uk/environment/interactive/2011/sep/21/mobilising-climate-finance-report-g20>
WRI 2011 ‘Climate Analysis Indicators Tool (CAIT). Release 8.0.’ ,World Resources Institute. <http://cait.wri.org/cait.php?page=sectors>
Yayasan, BOS 2007 Profil Desa Program Konservasi Mawas, Desa Katunjung., Unpublished report for Kalimantan Forests and Climate Partnership.
Yuhoyono, S 2009 Intervention by H.E. DR. Susilo Bambang Yudhoyono, President of the Republic of Indonesia, on Climate Change, Pittsburgh, USA, G-20 Leaders Summit. <http://forestclimatecenter.org/files/2009-09-25%20Intervention%20by%20President%20SBY%20on%20Climate%20Change%20at%20the%20G-20%20Leaders%20Summit.pdf>
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