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Local and Global Aspects of Coal in the ASEAN Countries

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By 2020, coal mining and power generation had been growing in Southeast Asia for decades and were projected to rise to new heights of prominence in regional energy systems, weakening the energy security of all states in the region except Indonesia, jeopardizing the NDCs of the ASEAN states under the Paris Agreement and deepening existing domestic political fault lines. Coal utilization has well-known public health, agricultural, water security and economic consequences, many of which are magnified in Southeast Asia, with its high population density and limited wind and arable land. Paradoxically, the short-sighted focus on affordability imposes significant longer-term economic risks on these states as renewable energy prices fall, while ASEAN markets for such energy sources remain underutilized.
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Local and Global Aspects of Coal in the ASEAN Countries
Haakon Fossum Sagbakken, Aidai Isataeva, Indra Overland, Aloysius Damar Pranadi, Beni
Suryadi and Roman Vakulchuk
Full citation:
Haakon Fossum Sagbakken, Aidai Isataeva, Indra Overland, Aloysius Damar Pranadi, Beni
Suryadi and Roman Vakulchuk (2021). ‘Local and global aspects of coal in the ASEAN
Countries’, in Stella Tsani and Indra Øverland (eds), Handbook of Sustainable Politics and
Economics of Natural Resources, Cheltenham: Edward Elgar, pp. 45–63.
45
4. Local and global aspects of coal in the ASEAN
countries1
Haakon Fossum Sagbakken, Aidai Isataeva, Indra Overland,
Aloysius Damar Pranadi, Beni Suryadi and Roman
Vakulchuk
1 THE ENVIRONMENTAL, HEALTH AND ECONOMIC
IMPACTS OF COAL
The global energy system is currently undergoing a rapid transition, with profound conse-
quences for the fossil fuel industries, perhaps most notably the one with the highest green-
house gas emissions – coal. Having played a major role in recent decades, especially in rapidly
growing emerging economies such as China and India, coal is being phased out across much of
the world, as its environmental and health impacts have become prohibitively costly while its
supposed economic advantages are rapidly disappearing as its relative affordability is under-
mined by the falling cost of renewable energy in many parts of the world (Finkelman and Tian,
2018; Gimon et al., 2019; Hendryx, Zullig and Luo, 2020; Kerimray et al., 2017; Rauner et al.,
2020; Strasert, Teh and Cohan, 2019). Coal also has disproportionally large negative environ-
mental and economic externalities in that its emissions degrade local agricultural, water and
human resources (Bhuiyan et al., 2010; Hota and Behera, 2015). Coal’s water requirements
also put pressure on already strained water resources in places such as India, to the extent
that water shortages render coal plants themselves unreliable (Wang et al., 2019, p. 3164).
However, despite falling in status and despite their commitments under the Paris Agreement,
coal is still favoured by many large developing countries and exposes them to significant
economic and stranded asset risks as the cost of coal is being rapidly undercut by renewable
energy technologies (Clark, Zucker and Urpelainen, 2020; Edenhofer et al., 2018, p. 2).
A significant body of research has examined the health, environmental and economic
impact of coal use across the developing and developed world in recent years (Amster, 2021;
Amster and Lew Levy, 2019; Henneman, Choirat and Zigler, 2019; Johnsen, LaRiviere and
Wolff, 2019; Kravchenko and Lyerly, 2018; Munawer, 2018; Wang et al., 2019; Xiao et al.,
2020). The negative health and environmental effects of coal are well known, with some
concluding that the costs outweigh the short-term economic benefits (Rauner et al., 2020,
p. 308). Others have pointed to the direct risks of coal plants becoming stranded assets due to
rapidly changing energy markets as well as public pressure to adopt more stringent pollution
1 This is an open access work distributed under the Creative Commons Attribution
-NonCommercial-NoDerivatives 4.0 Unported (https:// creativecommons .org/ licenses/ by -nc -nd/ 4 .0/ ).
Users can redistribute the work for non-commercial purposes, as long as it is passed along unchanged
and in whole, as detailed in the License. Edward Elgar Publishing Ltd must be clearly credited as the
rights holder for publication of the original work. Any translation or adaptation of the original content
requires the written authorization of Edward Elgar Publishing Ltd.
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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46 Handbook of sustainable politics and economics of natural resources
standards (Caldecott, Dericks and Mitchell, 2015). Environmentally, local emissions and
waste from coal plants poison agricultural fields and local water supplies, a problem that is
magnified with subcritical plants often built in developing countries due to their lower cost.
This can cause not only a loss in livelihoods, but also migration or even forced resettlement.
Emissions from coal plants have proven deleterious effects on human health (Buchanan,
Burt and Orris, 2014, p. 266; Burt, Orris and Buchanan, 2013, p. 2; Chen et al., 2014, p. 736;
Finkelman and Tian, 2018, p. 579; Munawer, 2018, p. 87; Silva and da Boit, 2011, p. 187). In
addition, coal consumption entails coal mining, which is a hazardous occupation with not only
long-term health impacts on workers but also putting them at high risk of accidents (Hendryx,
2015, p. 823). As coal use grows, so necessarily does mining and the frequency of accidents,
as has been observed in the case of China for decades (Dhillon, 2010, p. 68). Mining accidents
tend to be more frequent in developing countries due to lower security requirements and more
labour-intensive methods of extraction.
The international community has developed few tools for pressuring and assisting coun-
tries to phase out coal (Ayling and Gunningham, 2017; Green, 2018; Kalkuhl et al., 2019;
Richardson, 2017; Trinks et al., 2018). Recent studies point out that intergovernmental initi-
atives aimed at attaching a stigma to coal suffer from a lack of member states among major
coal-consuming countries (Blondeel, Van de Graaf and Haesebrouck, 2020, p. 3). They are
mainly developing countries with newer coal plants with longer remaining lifespans (Jewell et
al., 2019). No national government has yet put restrictions on coal power as part of its foreign
policy towards other states. Nor are there any mechanisms for punishing countries that fail to
abide by their commitments under the Paris Agreement because they build new coal power
plants, such as by massively expanding coal (Karlsson-Vinkhuyzen et al., 2018; Kemp, 2018;
United Nations Framework Convention on Climate Change [UNFCCC], 2015). Thus, for
the time being, effective political and social opposition to coal power plants is more likely to
play out in national and local arenas than at the global level, as most national governments
must in some way take public sentiment into account when making energy policy (Overland,
2018). Local resistance to coal exists in various forms in many countries, from Australia
(Higginbotham et al., 2010) to Bangladesh, to Turkey (Arsel, Akbulut and Adaman, 2015).
Such dynamics have become particularly apparent in countries seeing rapid expansion of coal
power, several of which are members of the Association of Southeast Asian Nations (ASEAN).
2 COAL IN THE ASEAN COUNTRIES
Against this backdrop, the ASEAN member states have been enthusiastically embracing coal
in recent years. As much of the world is pivoting away from fossil fuels, many Southeast Asian
countries have been rapidly expanding their use of coal to meet the region’s rising energy
consumption, chiefly the projected rise in demand for electricity (Clark et al., 2020; Overland
et al., 2021). In 2019, coal demand was projected to grow 5 per cent annually in Southeast Asia
through 2023, the highest growth rate in the world. Along with Chinese and Indian demand,
this has contributed to maintaining a high level of coal consumption globally (Figures 4.1 and
4.2) (International Energy Agency [IEA], 2019a).
As regional gas and oil reserves rapidly deplete, the ASEAN countries have made a sharp
turn towards coal (ASEAN Centre for Energy [ACE], 2017, p. 2; Cornot-Gandolphe, 2016,
p. 3; Shi, 2016, p. 678). Figure 4.1 shows that in 2019 the IEA projected that ASEAN demand
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Note: Mtce = million tonnes of carbon equivalent. China is omitted as its dominant role in global coal
consumption would distort the graph.
Source: IEA (2019b).
Figure 4.1 Coal consumption by selected regions/countries, 2017–24
Source: IEA (2019b).
Figure 4.2 Projected compound average annual growth rate (CAAGR) of coal
consumption 2017–24
Local and global aspects of coal in the ASEAN countries 47
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Note: Coal does not play a significant role in Singapore and Brunei Darussalam, hence their exclusion from
Figure 4.3.
Source: ACE database 2019.
Figure 4.3 Annual installed capacity of coal power plants in the ASEAN member states,
2005–17
48 Handbook of sustainable politics and economics of natural resources
for coal would overtake that of the EU by 2022 (IEA, 2019b). The same year, IEA estimated
that, while the rest of the world, on average, is phasing out or limiting new coal plants, ASEAN
coal demand will grow by 3 per cent every year until 2040, building on the rapid pace of
deployment since the turn of the millennium.
In 2018, ASEAN was the only part of the world in which coal’s share in the electricity
generation mix increased (IEA, 2019b, p. 20). As shown in Figure 4.2, ASEAN’s coal con-
sumption has been predicted to increase more rapidly than that of any other major region and
significantly faster than China from 2018 to 2024 (ibid.). Indonesia and Vietnam are the main
drivers of this trend. From 2000 to 2018, the share of coal in the ASEAN electricity generation
mix doubled, and currently accounts for 40 per cent, a level that the IEA predicts will be stable
until at least 2040 (IEA, 2019c). The net addition of 90 gigawatts (GW) of coal power in
ASEAN from 2019 to 2040 contrasts starkly with global energy transition trends (IEA, 2019c).
Within the shorter period from 2008 to 2017, a staggering 39 990 megawatts (MW) of
coal power capacity were added in the ASEAN countries (ACE, 2019). Paradoxically, and as
shown in Figure 4.3, ASEAN’s installed coal power capacity grew rapidly at the same time
as the threat of climate change became an increasingly prominent public policy concern and
a threat to sustainable development in the years preceding the Paris Agreement. Indonesia
and Vietnam were the two main contributors (Figure 4.3). Indonesia alone raised the installed
capacity of its coal-fired power plants by 17 920 MW from 2008 to 2017, with Vietnam adding
12 513 MW during the same period. In the decade from 2008 to 2018, the compound annual
growth rate (CAGR) of coal consumption in ASEAN was 7.8 per cent, dwarfing any other
major consuming region in the world (IEA, 2019b, p. 15).
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Local and global aspects of coal in the ASEAN countries 49
The IEA predicted in 2019 that coal would replace gas as the main energy source for
power generation in Southeast Asia by 2030 (IEA, 2019c, p. 62). As shown in Figure 4.4,
demand is driven chiefly by Indonesia, Vietnam and the Philippines, but with Myanmar,
Malaysia and Laos also including coal as a key component of their future energy systems
(see also International Renewable Energy Agency [IRENA], 2018, p. 34). Myanmar’s Energy
Master Plan envisions coal providing 30 per cent of electricity production by 2030 (IEA,
2020a). However, with almost 50 per cent of the population still lacking access to electricity
in 2019 (IEA, 2019c), Myanmar also has a unique opportunity to avoid such a coal-centric
scenario when undertaking grid planning (Sternagel, 2018). It could utilize its high renewable
energy potential instead (Vakulchuk et al., 2017). Even Cambodia, which lacks significant
domestic energy resources, signed a power purchasing agreement (PPA) in 2019 for large
coal-generated electricity imports from Laos for the coming decades (Vanda, 2019), despite
the latter’s established image as a mainly hydropower-exporting country and its aspirations to
become the hydropower ‘battery of Southeast Asia’ (Watcharejyothin and Shrestha, 2009; Yu,
He and Phousavanh, 2019). Coal is a non-existent part of the energy system of Brunei and is
negligible in the electricity production in Singapore (less than 1 per cent), although these coun-
tries will also remain dependent on fossil fuels for the foreseeable future (IEA, 2020b, 2020c;
Quek et al., 2018). It is also noteworthy that almost all the current and planned new coal plants
in the ASEAN countries, with the exception of Malaysia, are the least efficient subcritical type
of power plants (Climate Analytics, 2019, p. 42).
ASEAN’s coal expansion is a potential lifeline for both the regional and global coal indus-
tries. Arguably, regional coal utilization is particularly in the interest of Indonesia, which holds
some of the world’s largest reserves and stands to enhance its already dominant position in
the global export market. Indonesia was the world’s largest exporter of coal in 2018, having
jostled with Australia for the top spot in the preceding years, and accounted for double the
volume of that of the third-largest exporter, Russia, in that year (IEA, 2019a). This may be
of particular importance to Indonesia since its status as a net oil exporter has waned with the
depletion of its reserves and lack of new major discoveries.
Demand for coal is projected to exceed domestic reserves in all ASEAN countries except
Indonesia. Thus, Southeast Asian demand would also help maintain the global coal industry
(World Coal Association [WCA], 2019). Australian coal exporters and Japanese and Korean
coal plant construction firms face significantly less stringent environmental standards in
ASEAN than in their home markets (Jong, 2019a; Zhao and Alexandroff, 2019, p. 518). The
Southeast Asian coal sector is also attractive to Chinese coal plant builders, as they are likely
to face more stringent emissions standards and domestic demand is projected to taper off in the
coming years (Yuan et al., 2018, p. 443). Hence, Chinese firms already have a major presence
in the Indonesian and Vietnamese coal sectors (Shearer, Brown and Buckley, 2019). Thai
firms have also become active players in the Greater Mekong Region, seeking to construct
power plants in Myanmar for electricity exports back to Thailand (Sternagel, 2018). Due to
the unpopularity of coal plants in Thailand, Thai investors have already constructed a coal
power plant in Laos which will mainly supply the Thai electricity grid (Deboonme, 2012).
Such circuitous transnational plans and preference for frontier markets such as Laos and
Myanmar despite the high transmission costs back to Thailand underline the social costs and
risks that coal power already faces in Thailand and the multifaceted pressures on the industry
in Southeast Asia.
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Source: Global Energy Monitor (2020).
Figure 4.4 Coal-powered plants by province across ASEAN
50 Handbook of sustainable politics and economics of natural resources
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Local and global aspects of coal in the ASEAN countries 51
3 THE IMPACT AND RISKS OF BETTING ON COAL IN
SOUTHEAST ASIA
Coal-centric policy planning exposes the ASEAN countries to significant economic risks.
The current hazards and future risks of coal as an energy source have been examined at both
regional and national levels in Southeast Asia (Shi, 2016). The Carbon Tracker Initiative has
noted that the combination of steadily lower prices for renewables and higher standards for
particle emissions driven by public discontent with coal plant pollution will likely make coal
less economic than solar power in Indonesia, the Philippines and Vietnam within less than
a decade, despite the fact that these countries are planning the greatest expansions in coal
capacity in Southeast Asia (Carbon Tracker, 2018a, 2018b, 2018c). By 2025, rapidly rising
domestic demand for electricity in Indonesia might curtail the ability to maintain current
export levels as domestic consumption eats up the supply (Cornot-Gandolphe, 2017, p. 2).
Another element of uncertainty is foreign investor scepticism about unpredictable and costly
royalties (ibid., p. 23).
As a consequence of these developments and prospects, other ASEAN countries that are
expanding their dependency on coal, and thus increasing their reliance on Indonesian policy-
making, face greater energy insecurity. Large importing countries, such as China and India,
although not projected to expand coal at the same pace as the ASEAN countries, will by virtue
of their size remain major competitors for Australian coal. Southeast Asia has already seen
competitive financing for coal plant projects dry up and be hampered by ambitious coal plans
in ASEAN in the past two years (IEA, 2019c). In sum, the reliability and affordability of coal
appear to hold largely illusory benefits for most ASEAN countries in the long run.
Even as the global climate crisis, international pressure to decarbonize and plummeting
costs of renewables make coal increasingly unpalatable and uneconomic, ASEAN leaders
continue to emphasize promotional campaigns for ‘clean coal’ and the ‘benefits of coal’ to
their general publics in joint communiqués from regional energy summits (see, for example,
ASEAN, 2019). However, despite the longstanding rhetoric and lack of specifics about the
supposed mitigating factors of ‘clean coal technologies’, as of 2020, ASEAN had only a single
ultra-supercritical coal power plant, Malaysia’s 100 MW Manjung 4. Thailand is planning to
refit an old coal plant with supercritical technology to provide 660 MW capacity, yet this plant
is, and will continue to be, powered by lignite, the least efficient and most environmentally
harmful form of coal. However, the maintenance of such plants is framed as environmentally
sound, as the particle emissions having the most hazardous effects on local public health will
be curtailed (Paiwan, 2019). Even in planned capacity additions, subcritical and supercritical
plants will account for the bulk of expansion up to 2040 (IEA, 2019c, p. 69). Coal mining,
which within ASEAN is concentrated in Indonesia, also poses significant risk of accidents, as
many mines lack proper security infrastructure and protective measures for workers (Anggoro
and Simorangkir, 2019).
The ASEAN member states have received due criticism for their coal expansion as it
undermines their international climate commitments (Clark et al., 2020; Overland et al., 2017;
Prakash, 2018). International organizations note that the region has significant untapped
renewable energy potential that could be exploited instead of coal (IEA, 2019c; IRENA, 2018).
A Massachusetts Institute of Technology study from 2018 estimated that ASEAN countries
must collectively cut emissions by 11 per cent by 2030, compared with the current trajectory,
to meet their nationally determined contributions (NDCs) under the Paris Agreement, which
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8F8::
52 Handbook of sustainable politics and economics of natural resources
are in many ASEAN states defined as being against business-as-usual (BAU) scenarios
(Fulton et al., 2018). While an 11 per cent cut would be significant, the projected role of coal as
providing over half of electricity demand in the Philippines and Vietnam by 2030 (ACE, 2017,
p. 15; Philippine Power Statistic, 2018) in this scenario underlines the future high growth of
emissions from the region even if the NDCs are met, at a time when much of the world is
aiming to reduce emissions in absolute terms. Berlin-based Climate Analytics, in cooperation
with the United Nations Environmental Programme (UNEP), estimated in 2019 that coal’s
share in electricity generation in ASEAN would have to fall below 8 per cent by 2030 to meet
the Paris Agreement’s targets of limiting the temperature rise to 2°C. The IEA projected that
the share will be about 40 per cent (IEA, 2019c, p. 65). Coal’s expansion is a deliberate result
of governments’ budget priorities, as public spending accounts for the bulk of investments in
new plants from 2014 to 2018 (ibid., p. 16). With current policies (as of 2020), ASEAN will
emit 2.4 gigatons of CO2 in 2040, overshooting any target in the Paris Agreement by a wide
margin, with coal being responsible for nearly 50 per cent of these emissions (ibid., p. 101).
However, the climate change impact is only part of the picture, as coal plants and mines have,
and will continue to have, an immediate impact on the local population, to which we turn in
the next sections.
3.1 Health Impacts of Coal in ASEAN
Coal-fired power plants also pose a more immediate threat to health and local economies
across the region. With much of Southeast Asia having little wind and limited space, the
abundance of coal-fired power plants in close proximity to population centres has had pro-
found public health implications. Respiratory diseases are a rapidly growing health hazard in
Southeast Asia due to forest fires, urban congestion and industrial emissions – with coal plants
playing an increasingly prominent role (Koplitz et al., 2016; Ming et al., 2018; Tacconi, 2016;
Taghizadeh-Hesary and Taghizadeh-Hesary, 2020). A 2017 study estimated annual excess
deaths from coal-induced surface air pollution at 19 880 in the region, projected to rise to
69 660 by 2030 at the current pace of power plant expansion (Koplitz et al., 2016, p. 1467).
In one commune in Vietnam, Ky Loi, cancer rates resulting from coal emissions have soared,
to the extent that in 2019 its 11 000 residents were scheduled to be resettled, paradoxically to
make more space for additional coal plants (Le, 2019).
3.2 Water, Agricultural and Economic Impacts
Coal plants represent a multifaceted threat to the water resources of Southeast Asia, with sig-
nificant health and agricultural implications. Coal plants require substantial water volumes for
cooling (Huang, Ma and Chen, 2017; Qadrdan et al., 2019; Zhang et al., 2017). A recent study
noted how many newly built Indian coal plants had to temporarily shut down due to water
shortages in recent years, and that the current Southeast Asian plans for coal expansion would
put further stress on the region’s already depleted water resources (Wang et al., 2019, p. 3164).
Coal plant waste also poses a threat to riverine livelihoods in the region, not only in terms of
contaminating drinking water but also undermining fisheries (Runivarajom, 2018). Coal plant
fly ash also poses a threat to water quality, impacting drinking water sources and irrigation.
More directly, ash from coal plants has already poisoned agricultural fields, triggering local
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
-EDBE8FEB8F3DBD8H2
8F8::
Local and global aspects of coal in the ASEAN countries 53
protests in Batang in Central Java (Darmawan, 2019), Kalimantan (Funfgeld, 2018, p. 223)
and multiple locations in Vietnam (Le, 2019).
Although difficult to measure quantitively before it is too late, coal plants may also pose
a threat to the tourism sector in Southeast Asia. For years, Thailand had been planning to
enhance electricity supplies to its southern provinces by means of new coal-fired power plants,
partly to meet demand as the tourism sector expanded. Yet, according to the provincial tourism
board, the choice of coal and its emissions may undermine the attractiveness of one of the
world’s tourism hotspots (The Nation Thailand, 2018a). Vietnam’s famous Ha Long Bay is
already facing ecological problems, with coal plants onshore in Quang Ninh Province and coal
shipping through the bay being amongst the major culprits (Tran, Pham Le and Le Thi, 2019).
Coal plants similarly risk undermining the tourism sector on Bali, with projects proposed for
construction near popular beaches and national parks (Greenpeace, 2018).
Coal mining has also had negative effects on local communities and agriculture in other
parts of Indonesia (Fatah, 2008). In East Kalimantan, land grabs and pollution have forced
local farmers to resettle as mining firms exploit the large reserves (Tondo and Siburian, 2019).
This trend is likely to intensify as this area holds a significant portion of Indonesia’s coal
reserves, and the Indonesian government plans to move the national capital there from Jakarta
in the 2020s (Shani, 2019).
4 EVOLVING RESISTANCE TO COAL POWER IN ASEAN
Faced with such implications and considering the rapid expansion of coal to date, it is not
surprising that opposition both to coal-fired power plants and coal mining has been growing
across the ASEAN region. Opposition ranges from local groups fearing for their health and
livelihoods to emerging nationwide campaigns emphasizing climate implications. The form
of resistance and the level of coordination amongst environmental groups and international
civil society in each country is shaped by the national socio-political conditions. This section
maps the heterogeneous opposition to coal-fired power plants in ASEAN states from 2010
to 2020, including the framing of grievances and the domestic socio-political dynamics that
shape both the nature and effectiveness of this resistance. As protests are ongoing and have,
to varying extents, already changed policy trajectories, we have scoured newspapers and other
news sources covering environmental, coal and mining issues in Southeast Asia in an attempt
to answer the following questions:
Is opposition localized to specific plants or mines (and thus fragmented) or national in
nature?
What is the format of the opposition (on-site protests, marches, online campaigns, etc.)?
Are grievances local, national or global in essence?
Which political constituencies and actors comprise the opposition to coal projects?
Have resistance efforts been successful at the local, provincial or national level?
Which social, political or economic conditions are prerequisites for successful resistance?
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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8F8::
54 Handbook of sustainable politics and economics of natural resources
4.1 Resistance to Coal Mining in Indonesia: A Fragmented Phenomenon
Southeast Asian opposition to coal mining is mainly concentrated in the countries with sig-
nificant coal reserves. ASEAN holds about 4 per cent of global proven recoverable reserves
(IRENA, 2018, p. 32); however, although demand is growing across much of the region,
the distribution of coal reserves is highly uneven. Indonesia is amongst the world’s top coal
exporters and holds over 80 per cent of ASEAN’s coal reserves, both hard coal and lignite
(ibid., p. 32). Coal mines have had a significant negative impact on local communities across
Indonesia for many decades, as insufficient legislation and enforcement have led to inadequate
safety standards, lax waste containment and lack of protection or compensation for local
communities (Ballard, 2001, p. 3). Due to the large size and de facto decentralized governance
of much of Indonesia outside Java, some mining projects were approved by local authorities
without complying fully with the national legal framework. Even regionally approved legisla-
tion to enhance mine safety has often been ineffective (Toumbourou et al., 2020).
However, Indonesia also has a rich history of environmental activism, which was treated
more leniently than other public expressions of discontent under the Suharto regime (1967–98)
(Brown and Spiegel, 2017, p. 108). This, coupled with the massive expansion in coal mining
and export in recent years, has prodded local Indonesian activists and the affected communities
to partner with international non-governmental organizations (NGOs) to protest against mines
in ecologically rich yet vulnerable areas such as Kalimantan (ibid., p. 106). Local opposition
to new coal mines in West Papua is also growing, with local activists fearing that their envi-
ronmental impact could further escalate the longstanding armed conflict in the restive province
(Firdaus, 2018). In early 2020, local activists won a legal victory when the Indonesian supreme
court ordered a mining permit in Central Kalimantan to be revoked on the grounds that it had
not gained the approval of local communities, whose opposition centred on the threats to their
livelihoods posed by the mine (Jong, 2020). The dispersed nature of Indonesian anti-mining
activism to some extent reflects the country’s vast and diverse geography, rendering coordina-
tion amongst impacted local communities difficult.
4.2 Anti-mining Activism in ASEAN
In Vietnam, which has the ASEAN’s second-largest reserves of hard coal after Indonesia, coal
mining is a hazardous activity. Yet, strong government control of the industrial sector appears
to have prevented systemic protests against coal mines, as shown in Table 4.1. Protests have
erupted over specific mining projects in the past, although chiefly due to foreign ownership
concerns and growing anti-Chinese sentiment (Lam, 2018). In contrast, Malaysia’s plans to
expand coal mining in Sabah encountered stiff opposition in 2018 (Table 4.1). Local NGOs,
coordinating with international environmentalist groups and regional political parties in
Sarawak and Sabah, argued that states in Malaysia should have greater influence over resource
management (Joibi, 2018). Local protests emphasizing regional rights have also taken place
in Myanmar, notably in Shan State (Table 4.1), where villagers have held peaceful protests
against new coal mines, focusing on local environmental degradation, although, in Myanmar’s
case, it also has an ethnic minority rights dimension (Mon, 2019; Sternagel, 2018).
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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8F8::
Table 4.1 Opposition to coal mining in Southeast Asia 2010–20
Presence of Protests Areas of Grievances Local or National Focus Policy Effects
Vietnam None found n/a n/a n/a
Malaysia At least one (Sabah) Agriculture, tourism, ecological
conservation
Supported by national political
parties
None found
Indonesia Widespread Degraded fisheries, agriculture,
livelihoods, tourism, public health
Protest march in Jakarta Suspended one
mining licence
Myanmar At least two (Shan State) Agriculture, livelihoods Local village-centric activism None found
Local and global aspects of coal in the ASEAN countries 55
4.3 Resistance to Coal-fired Power Plants in ASEAN
Protests against coal-fired power plants are also widespread in Indonesia (Table 4.1), and
they exhibit increasing signs of national and even international coordination. Importantly,
the Indonesian government has curtailed the authority of local government bodies to block
new licences for coal plants, preventing local residents from exerting political influence on
their local administrations to halt new projects (Jong, 2019b). This prevents the widespread
circumvention of national laws at the provincial level, but it also robs local activists of the
power to exert successful political pressure on their local authorities to halt new coal projects,
since it centralizes decision-making power in Jakarta. Nevertheless, protests in Indonesia have
been multifaceted and widespread, although not always massive, strongly emphasizing local
environmental and health impacts, even by protestors travelling to Jakarta to make their case
(Jong, 2019a). In some more remote provinces, police have brutally cracked down on protes-
tors (Karensa, 2016). In early 2017, over 2000 people from affected communities gathered in
Jakarta and marched against coal, highlighting its negative impact on local livelihoods and
health across the archipelago (Jatam, 2017). However, the links to climate change were not
clearly articulated, and 2000 protestors is not a very large crowd on an Indonesian scale.
Opposition to specific plants in Indonesia, Myanmar, the Philippines, Thailand and Vietnam
have all been spearheaded by locals concerned about the effects of coal emissions on the
immediate environment. Farmers in Batang in Indonesia expressed concerns about emissions
from a new nearby plant in 2019 poisoning their agricultural fields (Darmawan, 2019), as
did villagers in Karen State in Myanmar in the same year (Thant, 2019). In the latter case,
resistance was also triggered by the fact that the plant was intended to sell most of its elec-
tricity to the Thai market, with limited benefits or improved supply for the local community.
In Myanmar, local communities have formed organizations in recent years to protest specific
projects (Sternagel, 2018), which unfortunately has only caused coal plant construction firms
to pursue the project in another area. Villagers’ concerns about local waste effects led to
suspension of a plant in Karen State in 2018 (Environmental Justice Atlas, 2018). In previous
similar projects, local protestations proved unsuccessful (Win and Win, 2016). In Binh Thuan
Province, local health-focused protestors rallied in 2015 in a rare display of physical protest
in Vietnam and forced the Vietnamese government to impose superficial restrictions on
a new plant’s emissions (AP, 2015). However, a similar situation developed in the following
years about another planned coal plant in the province, although the small-scale protests by
that point were also emphasizing climate change as well as public health (Banktrack, 2020).
However, both the existing plant and planned project are still set to continue. Laos, with only
a single large coal plant as of 2020, has yet to see major protests, which is likely explained
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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8F8::
56 Handbook of sustainable politics and economics of natural resources
by the small size of the town close to the plant as well as the Laotian one-party system that
restricts almost all organized civic or environmental activism.
Interestingly, despite protests in 2010 and 2011 against new plants, Malaysia has not seen
major efforts by activists to stop new coal plants in recent years even though coal is an impor-
tant source of power and will continue to remain so in the coming decades. This is not to say
Malaysia does not have its fair share of climate or environmental activism, but this appears
thus far to be focused on issues other than coal plants, such as deforestation and the country’s
large palm oil industry (Ocharoenchai, 2019).
Environmental activism and anti-coal protests have also been growing an online presence.
Vietnam, in which the ruling socialist party controls most traditional media outlets and prohib-
its mass public protests, has seen a stronger presence of online campaigns against coal power,
with national pop culture celebrities participating (Mekong Eye, 2016). However, the nature
of the Vietnamese political system has limited any mass protests, local or provincial, despite
massive environmental damage caused by coal emissions and waste in recent years (Tran
et al., 2019). Nevertheless, there have been recent cases of NGOs successfully lobbying the
government to limit future expansions, despite environmental activism carrying great risks in
Vietnam (Bangkok Post, 2020). There have also been occasional climate protests in Vietnam,
yet these have been rare and not focused on coal, but rather more broadly on air pollution
(Palatino, 2019).
The Philippines has arguably seen the most cohesive environmentalist pushback against
coal in the ASEAN region. A key facet of Philippine activism is the emergence of national
campaigns that have put pressure on both the central government and local administrations
in recent years. Piglas Batangas! Piglas Pilipinas!, a national campaign launched by civil
society groups in 2016, has organized demonstrations against various projects across the
country, including large protest marches. Importantly, this initiative has ties to broader global
climate activist networks. As the Philippine government has rapidly expanded the import and
use of coal, local and nationally coordinated opposition has been growing, emphasizing the
health, economic and climate change implications. Local churches have played a key role in
organizing local communities to stage protests and launch petitions (Bugnot, 2018). The most
noteworthy example of a multifaceted opposition effort to coal plants in the region, in terms
of complex socio-political coordination as well as the multifaceted nature of grievances, has
taken place in two provinces in the Philippines: Negros Oriental and Negros Occidental. These
provinces make up the nation’s fourth-largest island, Negros in the Visayas, and effectively
forced a phase-out of coal plants and proposed projects in 2018 and 2019, with the governors
involved citing both local health concerns and the threat of climate change (Partlow, 2019;
San Jose, 2019). The persistence of local youth protest initiatives, coupled with national
exposure through national environmental networks, has likely played a significant role in
pressing through this policy change. Despite this, coal remains a key priority for the Duterte
administration, which touts its properties as ‘clean energy’ necessary to ensure energy security
(Thomas, 2019). Ironically, almost all coal consumed in the country is imported, rendering its
contribution to energy security questionable (Philippine Power Statistic, 2018).
Thailand has also seen an increasingly nationally coordinated anti-coal network of activists
emerge in recent years, emphasizing both local health and economic concerns as well as
climate change. In September 2019, as part of the Global Climate Strike action, approximately
150 petitioners carried out a ‘die-in’ demonstration representing death from climate change
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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8F8::
Table 4.2 Opposition to coal-fired power plants in Southeast Asia 2010–20
Local and/or
National Focus
Grievances Format of Opposition Centre–Periphery Government
Dynamic
Policy Effect/Changes
Vietnam National Health Online None – highly stratified None
Indonesia Local Health
Livelihoods
Local protests
Protest march in
Jakarta
Local government
marginalized
None
Philippines Local and
national
Climate
Health
Livelihoods
Local protests
National
demonstrations
Local governments in two
cases instrumental in anti-
coal policy adoption
Successful local policy
moratoriums
Thailand Local Health
Tourism
Climate change
Livelihoods
Local protests
National protests
Local tourism associations
side with demonstrators
Successful suspension
of two new projects
Myanmar Local Health
Livelihoods
Local protests Local governments at odds
with protestors
Successful prevention
of at least one plant
Note: Cambodia, Laos and Malaysia were omitted because no data were found.
Local and global aspects of coal in the ASEAN countries 57
outside the Thai Ministry of Natural Resources and Environment, demanding coal to be
phased out in the country (Palatino, 2019).
In late 2018, after years of protests and public hearings, the Electricity Generating Authority
of Thailand (EGAT) indefinitely postponed the construction of coal power plants in Songkhla
and Krabi in the southern part of the country in favour of increased reliance on natural gas
(The Nation Thailand, 2018a). The protests included publicized hunger strikes in Bangkok
(Bangkok Post, 2018), and were driven by a number of relevant arguments. These ranged from
local residents citing public health concerns, threats to fisheries and the area’s tourism sector,
to local NGOs framing the issue in terms of climate change (The Nation Thailand, 2018b). In
Krabi, the local tourism board was also highly sceptical of the proposed plants, as the region
constitutes the heartland of the Thai tourist industry.
Resistance to coal power in Southeast Asia is longstanding and multifaceted, shaped by
geographic, political, economic, social and technological factors. The level of organized and
successful protests correlates with political systems, especially the accountability and policy-
making powers of regional and local authorities. While a more open system in the Philippines
produced local policy changes and enabled national coordination, the stratified Vietnamese
political system has contributed to a more muted activism, yet online campaigns have partly
filled the void. Protests in Indonesia have rarely produced policy changes in Jakarta, partly
due to coordination difficulties and partly to weak enforcement of existing policies. Fears of
losing agricultural, hunting and riverine livelihoods dominate in almost all anti-coal discourses
across the region, but the threat coal poses to highly profitable industries such as tourism
has also catalysed opposition. Climate-focused activism against coal is a facet of Thai and
Philippine politics but is otherwise still nascent in most of Southeast Asia, although it is on the
rise (Table 4.2).
088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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8F8::
58 Handbook of sustainable politics and economics of natural resources
5 CONCLUSIONS
By 2020, coal mining and power generation had been growing in Southeast Asia for decades
and were projected to rise to new heights of prominence in regional energy systems, weaken-
ing the energy security of all states in the region except Indonesia, jeopardizing the NDCs of
the ASEAN states under the Paris Agreement and deepening existing domestic political fault
lines. Coal utilization has well-known public health, agricultural, water security and economic
consequences, many of which are magnified in Southeast Asia, with its high population
density and limited wind and arable land. Paradoxically, the short-sighted focus on affordabil-
ity imposes significant longer-term economic risks on these states as renewable energy prices
fall, while ASEAN markets for such energy sources remain underutilized. Encouragingly, and
likely partly spurred by sustained public resistance to coal and calls for climate action, EGAT
in late 2019 announced that coal would account for only 12 per cent of power generation in
2037 in Thailand (Theepara and Praiwan, 2019).
Coal mining, no less hazardous in Southeast Asia than elsewhere, has triggered widespread
locally organized protests in Indonesia, although not yet in Vietnam. While protestors have
only achieved minor victories in some Indonesian cases, coordination amongst communities
across the archipelago is increasing, and a nationally organized campaign in cooperation with
international civil society might have a greater impact on Indonesia’s coal-centric energy
trajectory.
Coal plants and opposition to them are intertwined with existing socio-political fault lines:
ethnic minority rights in Indonesia and Myanmar and regional political divides in Malaysia
and Thailand. In Vietnam, the top-down one-party system blocks many protest avenues, which
has triggered more creative and less overt forms of resistance against new coal-fired power
plants. Opposition to coal across the region is heterogeneous, but trending towards greater
national coordination and international cooperation amongst activist networks and even local
governments. Local concerns continue to drive most protests, with the Philippines represent-
ing a more well-articulated pattern that links local and national environmental issues to climate
change. International civil society organizations aiming to exert pressure on governments to
reform their energy systems would do well to work more closely with activists on the ground
in regions similar to Southeast Asia to shed an international spotlight on these issues, provide
an international platform for local initiatives, make their case and form networks for collective
action. This case shows how international actors as well as regional activists would stand to
benefit substantially from closer cooperation, which has significant potential to pressure gov-
ernments to abandon coal in Indonesia, Malaysia and Thailand. The international community
has few direct tools or platforms through which pressure can be exerted on states to recon-
figure their energy systems. Thus, the most viable option to effect change is through national
and international coordination with global environmentalist NGOs, which can help harness,
consolidate and empower the local efforts of Southeast Asian communities by linking local
concerns with national policy trajectories to combat climate change.
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088AED/EI898AAD818H881DF83FB8DBEI-88FF8D8,DIF88D5E8D78AIB:IA 
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