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Central Protectionism in China: The “Central SOE Problem” in Environmental Governance

Published online by Cambridge University Press:  18 August 2017

Sarah Eaton
Affiliation:
University of Göttingen. Email: [email protected].
Genia Kostka
Affiliation:
Free University of Berlin. Email: [email protected].
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Abstract

This article examines the so-called “central State Owned Enterprise (SOE) problem” in China's environmental governance system, namely central SOEs' defiance of environmental regulation. We present evidence showing that, in the last decade, central SOEs have been the source of a large number of serious pollution incidents and have often failed to comply with environmental guidelines and regulations. Central SOEs in the electricity generation and oil and gas industries are particularly culpable, with six firms alone accounting for 62 per cent of all 2,370 reported violations (2004–2016). We argue that a combination of “central protectionism” of state-owned national champions and insufficient regulatory capacity in the environmental bureaucracy have provided state firms under central management with both incentives and opportunities to shirk on environmental regulations. Yet, while the institutions of central protectionism are deeply rooted, countervailing forces within the complex Chinese state are also gaining momentum. In spite of the considerable regulatory challenges, officials in the environment bureaucracy display increasing resolve and ingenuity in trying to strengthen their enforcement capacity.

摘要

本文检视了中国环境治理系统中所谓的 “中央企业问题”, 即央企违反环保法规的现象。笔者将提供证据证明在过去十年中, 央企已成为大量严重污染事故的始作俑者, 而且常常无法遵守环境保护的指导方针和法律法规。发电、石油和天然气行业中的央企尤其难辞其咎, 在 2004 年到 2016 年上报的 2370 起违规事件中, 单单 6 家这些行业中的央企就占了62%。笔者认为, 对国家重点企业的 “中央保护主义” 以及环保机构监管能力的不足, 使得在中央管理下国有企业既有动机也有机会逃开环保法规的制约。然而, 尽管中央保护主义的机制根深蒂固, 其对抗力量在中国复杂的国家政治中也蓄势待发。尽管监管上面临着艰巨挑战, 环保机构的官员展现了他们在增强自身执法能力上日益增长的决心和智慧。

Type
Special Section on Central–Local Relations and Environmental Governance in China
Copyright
Copyright © SOAS University of London 2017 

2013 was a pretty good year for China's state-owned oil and gas giant, Sinopec. The company climbed two spots on the Fortune Global 500 list to finish as the world's third-largest firm. Sinopec was also recognized for its efforts in pursuing green and low-carbon development with receipt of the Green China Corporate Social Responsibility Excellence Award. The latter distinction would have come as surprising news to many in China accustomed to hearing about polluting emissions belching out from Sinopec refineries, pipeline leaks and myriad other environmental violations. Indeed, just ten days prior to receiving the award, a leaking Sinopec pipeline in the port city of Qingdao caught fire, causing a blast and oil spill that resulted in the deaths of 62 people.Footnote 1

Are Sinopec's misdeeds just an ugly blemish on an otherwise clean environmental record for China's central state-owned enterprises (SOEs)? Aside from some positive analysis of the contribution of China's largest SOEs to recent energy efficiency gains in China, we know surprisingly little about the environmental behaviour of state firms under central management.Footnote 2 This constitutes a gap in the literature on China's environmental politics because central SOEs, as extremely large firms concentrated in resource-intensive industries, wield an enormous ecological footprint. In this article, we present evidence showing that central SOEs have been the source of a large number of environmental rule violations as well as serious pollution incidents within China. Large central SOEs in the electricity generation and oil and gas industries are particularly culpable, with six firms alone accounting for 62 per cent of all 2,370 reported violations in the database.

We argue that a combination of “central protectionism” of state-owned national champions paired with insufficient regulatory capacity in the environmental bureaucracy have provided central SOEs with both ample incentives and opportunities to shirk on environmental regulations. Further, we find evidence of overlap between central and local protectionism of central SOEs. While China's State-owned Assets Supervision and Administration Commission (SASAC) tacitly encourages its firms to prioritize the attainment of traditional industrial policy goals (scale expansion and profitability) above all else, including environmental protection, local governments are also often complicit in the national champions' environmental misdeeds. Faced with ambitious growth targets, revenue shortfalls and pressure to maintain or boost employment levels, local officials may also be incentivized to turn a blind eye to central SOE pollution.

Drawing from an original database documenting central SOEs' non-compliance with environmental regulations as well as fieldwork interviews, we also examine current efforts to address the “central SOE problem” (yang qi wenti 央企问题). While the institutions of central protectionism remain firmly rooted, there are concurrent countervailing trends within the complex Chinese state. Officials in the environmental bureaucracy display increasing resolve and ingenuity in trying to enforce environmental rules on recalcitrant central SOEs. They make innovative use of new governance mechanisms including using media and internet platforms to name and shame polluters; charging higher pollution fees; taking polluters to court; removing industrial subsidies; and shifting enforcement activities from local Environmental Protection Bureaus (EPBs) up to higher-ranked officials.

Reports of Central SOE Non-Compliance with Environmental Regulations

The database catalogues 2,370 instances of non-compliance by central SOEs and their local subsidiaries between 2004 and 2016. The severity of these incidents ranges from procedural violations (chengxu weifa 程序违法) to major industrial accidents causing severe pollution, injury and death.Footnote 3 The database entries include company name, province, industry, year of pollution event and type of pollution. We also gathered, where possible, background information about the methods employed by local EPBs and other officials working in the environmental bureaucracy to elicit compliance and redress from central SOEs in their localities.

In compiling the database we drew from a number of sources to ensure maximum coverage. The majority of cases (2,255) come from the Institute of Public and Environmental Affairs (IPE) corporate environmental performance web portal.Footnote 4 The portal gathers monthly reports on firms' environmental violations from China's local EPBs. We also reviewed an online database of the Ministry of Environmental Protection (MEP) covering 204 key environmental cases between January 2014 and 2015.Footnote 5 An online crowd-sourced map of pollution incidents in China was also reviewed.Footnote 6 Finally, we conducted keyword searches of individual central SOEs in the CNKI China Core Newspapers Full-Text Database as well as on online search engines to uncover media reports on major instances of central SOE pollution.

The database has some shortcomings as a measure of the “central SOE problem.” First, the list is not a complete record of pollution cases involving central SOEs. Given their economic and political clout, we can assume that some instances of central SOE non-compliance have been kept from the media and out of official records. In addition, in the media reports we collected, there is typically minimal information provided about the factors behind central SOE non-compliance. They also usually do not contain rich detail about the official responses to non-compliance. Our data also does not provide insight into the environmental misdeeds of central SOEs relative to those of local SOEs, private, mixed- and foreign-invested firms. While imperfect, our data does lend insight into general trends regarding central SOE non-compliance with environmental regulations, including regional trends, most common violation types, most affected industries, frequent offender firms and official responses to rule violations.

The analysis also draws upon extensive fieldwork between 2010 and 2012. Fieldwork was conducted at the central, provincial, municipal and county/district levels in Beijing, Hunan, Inner Mongolia, Jiangsu, Shandong and Shanxi. In total, the authors conducted more than 190 semi-structured interviews with government officials, business managers and civil society representatives. Collecting data from multiple administrative levels was helpful in shedding light on how environmental policies “trickle-down” from the national level to the county and district levels. The fieldwork studied China's environmental policy and governance system in general, with a particular focus on China's cadre rotation scheme and environmental policy implementationFootnote 7 and China's environmental target system.Footnote 8 During the fieldwork, the topic of the “central SOE problem” emerged as a common governance problem in different localities. In addition to interviews, the analysis draws from government policy documents and media reports and available secondary sources.

The reported cases of non-compliance by SOEs were distributed across 30 provinces/autonomous regions (Figure 1). There is a high degree of inter-provincial variation. The highest number of cases was reported in Shandong (255), followed by Xinjiang (173) and Jiangsu (160). The provinces/regions with the fewest reports of central SOE environmental violations are Tianjin (15), Qinghai (12) and Hainan (7). The large number of reports from Shandong reflects the many violations within the Shandong electricity generation sector (176 cases), where large coal power providers failed to use the required desulphurization equipment. While the source of this variation is not a focus of our analysis, and awaits in-depth future fieldwork-based and quantitative research, the results of basic correlation analysis using provincial-level data from the National Bureau of Statistics suggest a number of possible dependencies.Footnote 9 As one might expect, the reported violation cases were higher in provinces with a heavy SOE sector and a large proportion of GDP from industry.Footnote 10

Source: Authors' Central SOE Environmental Violation Database, 2016. (Colour online)

Figure 1: Reported Cases of Central SOE Non-compliance with Environmental Regulations (by Province/Region)

Reported incidents also differ by industrial sector (Figure 2). The electricity generation sector is the largest contributor (45 per cent). Other high-polluting sectors include oil and gas (17 per cent), steel (8 per cent), mining (7 per cent) and metals and minerals (5 per cent). The high proportion of cases in the electricity generation sector reflects the failure of coal-fired power plants to meet pollution control standards for desulphurization, denitrification and dust elimination. These firms' reported pollution cases are typically the result of falling below sulphur dioxide (SO2), nitrogen oxides (NOx) and soot emission standards.

Source: Authors' Central SOE Environmental Violation Database, 2016. (Colour online)

Figure 2: Sectoral Distribution (N = 2,370)

Among the reported incidents and type of environmental non-compliance, air pollution accounts for 60 per cent of all violations, followed by water (26 per cent) (Figure 3). Procedural violations such as starting a project without completing an environmental impact evaluation, account for one in ten of such reports.

Source: Authors' Central SOE Environmental Violation Database, 2016. (Colour online)

Figure 3: Type of Pollution (N = 2,370)

For reasons outlined above, the most commonly encountered companies in the database include four of the main electricity generation firms (Guodian, Huadian, Huaneng and Datang), followed by the two major oil and gas SOEs (Sinopec and CNPC). Oil and gas firms were often cited for excessive emissions of NOx and dust along with other pollutants. These six firms alone account for 62 per cent of all 2,370 reports in the database. The top ten polluters make up 78 per cent of the total (Table 1).

Table 1: Most Frequently Listed SOEs in the Database (N = 2,370)

Source:

Authors' Central SOE Environmental Violation Database, 2016.

In sum, our analysis shows that Sinopec's environmental violations are by no means anomalous. Since 2004, central SOEs have been the source of a large number of violations and serious pollution incidents across China. National champions in the electricity generation and oil and gas industries are especially to blame, together accounting for almost two-thirds of the violations in our database. In the following section, we turn to an examination of the factors behind central SOE non-compliance before looking at state efforts to regulate these firms more effectively.

What Are the Sources of Environmental Non-Compliance?

What cracks in China's environmental governance system allow for these breaches of regulation? Of course, central SOEs are hardly the only businesses in China to routinely violate environmental rules. In fact, previous work indicates that small, privately owned or former township and village enterprise (TVE) polluters are the usual suspects in this regard.Footnote 11 The existing literature has identified local interests and preferences, fragmented bureaucracies, underfunded and poorly trained EPBs, and inadequate monitoring capabilities as key factors behind environmental violations in industry.Footnote 12 Yet, SOEs exist in an institutional environment quite distinct from that of private, mixed- and foreign invested-enterprises—a context in which, one might expect, enterprise managers would be strongly inclined to adhere to state directives. Indeed, given the existence of a revolving door between central SOE management and top leadership roles in the government and the Communist Party, the dual identity of many SOE managers as business leaders and promotion-hopeful officials could be expected to exert a strong pull to compliance. An analysis of the environmental behaviour of large SOEs versus that of firms of other ownership type provides some qualified support for this view.Footnote 13 Equally, one could assume that close ties between state firms and high-ranking officials furnish the conditions for non-compliance, the assumption behind previous research as well as ours here.Footnote 14 We argue that two pathologies of this institutional setting, weak enforcement capacity and central protectionism, help to explain the implementation gap in the state-owned industrial sector.

Weak enforcement capacity: administrative rank asymmetries, insufficient resources

At local levels, government officials often have insufficient regulatory capacity to enforce unwelcome regulations on central SOEs operating in their jurisdiction. In a complex system of governance in which SOEs under the authority of the central government answer to bureaucrats in Beijing and not to local authorities, central SOEs have ample de facto opportunities to shirk on environmental measures demanded by local governments. Such administrative-rank problems are made more complicated by the fact that managers of central SOEs themselves also often hold concurrent positions of power within local government and Party organizations. Officials in the environmental bureaucracy in different localities reported that this “central SOE problem” is a frequent source of frustration for local authorities trying to meet their increasingly binding obligations under the “green” national plans.

For instance, one leading official from the Economic Commission in a heavy industry-intensive district in Shanxi province discussed the difficulties of eliciting compliance on energy efficiency initiatives from central- and provincial-level SOEs in his jurisdiction, which together accounted for 60 per cent of energy consumption of above-scale (guimo yishang 规模以上) enterprises.Footnote 15 In the context of the 11th and 12th Five-Year Plans' (FYP) ambitious targets on energy efficiency, officials had directed their attention to the highest energy consumers in the district, two state-owned electricity generation enterprises. Yet, because they were both owned by North China Grid Company (itself a subsidiary of State Grid, a central SOE), the sticks at hand proved feeble. Local officials had appealed, first, to the municipal level for assistance in “coordination” (xietiao 协调) with the enterprise, then gone up to the provincial level, and finally all the way to State Grid headquarters in Beijing – all to no avail. Local officials also voiced concern that pushing too hard against these SOEs could lead to recriminations in the form of power cuts to the district.

Even at the central level, insufficient authority and power vis-à-vis central SOEs is a problem that environmental authorities face, a point vividly made in Chai Jing's 柴静 hit documentary about China's environmental crisis, Under the Dome (Qiongding zhi xia 穹顶之下).Footnote 16 In conversation with a central MEP official on the topic of the difficulties of enforcing fuel standard regulations on powerful central SOEs, Chai asks if the MEP is effectively powerless, to which the reply is “Nowadays I don't dare open my mouth for fear that people will see I have no teeth.” And an official from the imposing National Development and Reform Commission (NDRC) concedes “You can't control them [the major state-owned oil players] … [t]hey don't pay us any mind.”

Central SOEs are difficult for central bureaucrats to police, in part due to the high administrative rank (jibie 级别) many state firms' CEOs carry, an unanticipated legacy of Zhu Rongji's sweeping, and heavily resisted, efforts to rationalize the central government in the late 1990s.Footnote 17 Indeed, in 2010, of the approximately 120 SASAC SOEs in existence, fully 54 of the heads of these firms enjoy full ministerial rank.Footnote 18 While many of these regulatory bodies, including the MEP, have now been upgraded to full ministerial status in order to mitigate this problem of rank, interviewees in Beijing described the high rank of SOE heads as a factor that continues to frustrate the impartial enforcement of regulations.Footnote 19 Regulation scholar Wang Junhao summarized the difficult predicament of regulatory bodies this way: “The cat wants to catch the mouse, but the mouse is bigger than the cat.”Footnote 20

In contrast to key agencies in the economic system (xitong系统), especially SASAC, the weak capacity of the environmental bureaucracy vis-à-vis central SOEs is also the result of insufficient resources and a high monitoring burden. To a large degree, SASAC's power is derived from its shared responsibility with the Communist Party Organization Department for carrying out the annual performance evaluations of SOE senior managers. MEP is not involved in these evaluation exercises and consequently does not wield much leverage over enterprise heads. Especially at local levels, where the burden of environmental oversight lies, EPBs are notoriously underresourced. Officials in industrial localities, in particular, have a high supervision burden and typically small, ill-equipped inspection teams.Footnote 21

Insufficient incentives to comply: central protectionism

Official protection of polluting local firms has often been blamed for weak enforcement of environmental regulations at sub-national levels and constitutes a key argument in favour of centralizing environmental enforcement in China.Footnote 22 The phenomenon of “local protectionism” (difang baohu zhuyi 地方保护主义) results from cronyism as well as goal conflict between economic growth and environmental protection, with the former typically winning out.Footnote 23 Local protectionism is seen to be particularly resistant and deeply rooted in cities dominated by large, polluting firms.Footnote 24 We submit that, for central SOEs, a counterpart to this local protectionism exists.Footnote 25 Officials in the central economic bureaucracy, principally SASAC, provide a measure of shelter for chronic polluters within SASAC's ranks by incentivizing senior SOE managers to look upon the achievement of traditional industrial policy goals such as profitability, scale, market share and efficiency – and not compliance with environmental regulations – as the sine qua non of a positive enterprise performance evaluation and possible promotion for managers themselves.

As subjects of a long-standing industrial policy programme that aims at creating global players in key sectors, central SOEs face tacit, yet nonetheless strong, incentives to shirk on environmental rules that would harm their economic performance. Beginning in the late 1980s, central policymakers introduced a series of policies which had, as their common aim, the establishment and nurturing of large, state-controlled business groups in key industries.Footnote 26 Selected state-owned “trial” enterprise groups, many of which are now under SASAC authority, are relentlessly called upon to “go bigger and go stronger” (zuo da zuo qiang 做大做强) via scaling up and striving to attain global standards of competitiveness. SASAC has primary responsibility for “maintaining and increasing the value of state assets” (bao zhi zeng zhi 保值增值) and carries this out by way of annual evaluations and the subsequent ranking of central SOEs in which, until fairly recently, profitability and return on equity were the main criteria.Footnote 27 Critics of the system have argued that SASAC's strong “maintaining and increasing the value of state assets” mandate effectively incentivizes SOEs to blindly pursue profitability. It comprises one of the main reasons that many of the central SOEs that have shot up the ranks of the Forbes Global 500 in the last decade remain protected state monopolies.Footnote 28

Promotion criteria for central SOE managers seem to reflect the primacy of these traditional industrial policy goals. A Human Resource (HR) manager from one of the SASAC oil majors near the top of the Global 500 said, shortly after the beginning of the “green” 12th FYP, that environmental performance remained relatively unimportant for promotion decisions in oil and gas companies.Footnote 29 Citing the case of an official promoted from Tianjin, the manager's positive evaluation in this instance rested on perceptions of him as an effective controller of costs. While energy consumption had been reduced under his watch, these energy savings were framed as incidental to cost savings. And environmental accidents have sometimes been treated fairly lightly by the companies. The HR manager mentioned a case in Sha'anxi in which 200 tons of a pollutant was leaked and the official in charge received just 18 months of probation.Footnote 30

While traditional industrial policy goals remain predominant, SASAC has begun to modify its system of SOE oversight and guidance in ways that could encourage greener behaviour in the state industrial sector in the future. Developed in early 2008, SASAC regulations first encouraged and then mandated (from 2011) that central SOEs produce annual Corporate Social Responsibility (CSR) reports which include discussion of efforts to upgrade resource efficiency and environmental protection.Footnote 31 And, in 2010, SASAC enfolded energy savings and emissions reductions work (jieneng jianpai 节能减排) into the evaluation system for SOE heads. From the first unveiling of SASAC's CSR regulations, however, observers have wondered whether this is an exercise, first and foremost, in “window dressing.”Footnote 32 At present, a deficiency of the CSR system is that only a tiny minority of reports published by Chinese companies on the Shanghai and Shenzhen exchanges are actually certified by an independent third party – reportedly just 5.1 per cent in 2014.Footnote 33

Two important implications flow from the existence of central protectionism in environmental governance. First, the logics of central and local protectionism are not mutually exclusive and they actually frequently overlap. That is, local government officials may be incentivized to turn a blind eye to central SOE environmental violations because of the leverage these enterprises wield as providers of essential services such as electricity (as in the Shanxi example cited above), sources of local employment and, to a lesser extent, government revenue. The high standing of central SOE managers in local Party and business networks can also frustrate enforcement efforts. Second, this finding aligns with recent work arguing that the centre itself, and not only China's much-maligned local governments, bears a heavy responsibility for the country's runaway industrial pollution.Footnote 34 By tacitly encouraging its national champions to pursue growth and profitability at all costs, the centre effectively undermines environmental protection efforts. In the remainder of the article, however, we qualify this claim. We see China's centre, like Walt Whitman's self, as large and containing multitudes. While one face of the state contributes to central SOE pollution, another works to contain and eliminate it.

Current Mechanisms to Pressure Central SOEs into Compliance

While the SASAC system provides a degree of cover to central SOE polluters, there is, at the same time, increasing pressure to comply with environmental rules emanating from other state organizations and agents. In other words, fragmented authoritarianism is in play.Footnote 35 We have argued that the prevailing incentives in the SASAC system are such that, in circumstances in which the attainment of industrial policy and environmental protection goals are in a zero-sum relationship, industrial policy will tend to trump green goals. At the same time, developments in the environmental governance system linked to the state's ever-increasing emphasis on greening growth are (slowly and unsteadily) raising the costs of non-compliance for polluting firms, even the largest and most politically powerful among them.

There are important efforts at the central level to strengthen environmental enforcement capacity. Following its administrative upgrade from vice-ministerial to ministerial rank in 2008, central officials in the MEP have worked to tighten oversight of enterprises, including central SOEs. In August 2013, MEP announced that it would cease approvals for new projects by oil giants PetroChina and Sinopec as punishment for having fallen short of environmental targets in connection with a programme to install denitrification units in coal-fired boilers.Footnote 36 The following year, MEP began publishing monthly reports on environmental violation cases. The names of companies that fail to correct misdeeds remain on an internet blacklist that is shared with corporate lending institutions. In addition, 15,000 factories – among them a large number of SOEs – are now required to report real-time figures on air and water emissions. The information is made public on a website as well as on a mobile phone app that more than 3 million Chinese people are said to have downloaded.Footnote 37 Officials hope that by giving the public the tools to keep tabs on neighbouring factories, they have issued “a warning to all of the 15,000 companies on the pollution map.”Footnote 38 Finally, since inspection teams often face great difficulty in carrying out assessments of polluting firms, the ministry has also begun using drones to conduct site inspections.

Yet, despite such measures, MEP still faces dogged resistance from central SOEs. Such firms have been known to disregard use even of the MEP's sharpest implements, including “stop production orders” (tingzhi shengchan de yaoqiu 停止生产的要求). For instance, Anshan Iron and Steel (Angang) was placed on a national blacklist after ignoring a stop production order issued from the Liaoning provincial EPB in connection with the company's refusal to replace coke ovens and dust removal equipment that were not up to code. An MEP official commenting on the case said: “This is the result of polluting with impunity. Central SOEs and SOEs ought to take the lead on environmental issues. However, the reality is cause for worry.”Footnote 39

New developments in governance are also evident at sub-national levels. Below, we use the case studies of Lanzhou (Gansu) and Anqing (Anhui), taken from our database, to illustrate an incipient, if still rare, boldness among local EPBs in trying to hold central state firms to account. Some local officials make use of an expanding menu of governance mechanisms in the effort to discipline firms. They levy higher pollution fees, take polluters to court and use the removal of subsidies as a stick to achieve compliance with environmental rules. And when their own tools are insufficient, they shift enforcement activities from local EPBs up to higher-ranked officials. We also see local EPBs, like MEP at the central level, increasingly trying to leverage the force of China's widening “green public sphere” by making instances of central SOE pollution public.Footnote 40 In particular, local government officials increasingly make clever use of media power and information technology platforms to leverage the force of public pressure directly on polluting state firms.

In Lanzhou, for instance, EPB officials have drawn on media glare to apply pressure to a serial polluter. In early 2015, EPB officials released a statement to the media harshly criticizing PetroChina for air pollution and calling on it to curb pollution and issue an apology to Lanzhou citizens. This naming and shaming of PetroChina, the biggest employer and tax contributor in Lanzhou, was a bold move for environmental officials in this less-developed city. It is also striking that the local EPB seems to have acted without prior approval of the Lanzhou mayor, who later said that he had not been made aware of the EPB press conference beforehand.Footnote 41

A number of factors shaped Lanzhou's confrontational stance. First, the January 2015 pollution was by no means an isolated event. Conflicts between PetroChina and local officials began in 2006 when a plant explosion caused a huge fire and killed 11 workers.Footnote 42 Tensions were renewed in spring and summer 2014, when a benzene leak contaminated Lanzhou's water supply and a number of industrial fires at PetroChina's refinery plants worsened air pollution.Footnote 43 In total, four serious pollution incidents were reported, none of which was punished with fines or criminal or civil charges.Footnote 44 Throughout 2014, PetroChina avoided addressing its poor environmental pollution record and instead claimed that incidents of leakage or pollution were normal and unavoidable for such a large-scale enterprise. Thus, when the fifth incident within a year occurred in early January 2015, Lanzhou's EPB director would have faced significant pressure to gain some form of redress. The director may have also been under a high degree of personal pressure since, in the past five years, two consecutive directors of Lanzhou's EPB had been dismissed due to failure to rein in pollution.Footnote 45 The EPB's public criticism may also have been a bid to force PetroChina to move a refinery into a new industrial park zone outside Lanzhou city.Footnote 46

Emboldened by tougher legal punishments for polluters, other local EPBs have begun to issue substantially higher pollution fees. In June 2013, Anqing's local EPB charged the central SOE Sinopec (Anqing) with a 90,000-yuan fine for air pollution, following a major production accident that led to polluting emissions. This event was one of the first of its kind, as local EPBs typically have no authority to charge pollution fees to central SOEs. It was seen as a daring move since, as is often the case, the firm's general manager held a political post in the locality (as a member of the Anqing Municipality Standing Committee). To mitigate the administrative rank problem, Anqing city announced that the issue would be taken up by a vice-mayor who, in turn, initiated contact with the MEP.Footnote 47 Ultimately, Sinopec relented and paid the fine. The Anqing case was widely reported in the media, and could be a signal to other local EPBs to be more bold in addressing the “central SOE problem.” However, even this boldness must be seen in context: a fine of 90,000 yuan is not especially punitive for the likes of Sinopec. Further, the sum does not fully reflect the considerable local ecological and health damage resulting from the pollution.

Two factors help to explain why the municipal EPB in Anqing took a bold stance vis-à-vis Sinopec. First, public monitoring was certainly an important stimulus. Following the industrial accident in May 2013, many Anqing citizens complained about the resulting pollution and posted pictures on the internet. Second, the municipal EPB changed leadership in early 2013 with the appointment of a high-ranked local leader – a former vice mayor – as director of the municipal EPB. The newly appointed leader frequently visited the provincial EPB bureau and the national MEP in order to gain upper-level government support. This unusual combination of a powerful local EPB head, together with support directly from the central level, made issuing the fee politically possible.Footnote 48

Of course, this unusual combination of a powerful EPB head with an active local civil society would make the Anqing approach difficult to replicate in a more typical locality. Nevertheless, institutional reforms linked to China's “war on pollution” have brought new instruments into existence that, at the very least, expand the menu of such formal enforcement options available to local bureaucrats. In particular, amendments to China's Environmental Protection Law (huanbao fa 环保法), in effect since 1 January 2015, removed the previous cap on pollution fines and also established a provision for charging penalties on a daily basis to enterprises that do not comply with environmental regulations. In 2015, for instance, aluminium manufacturer Chalco, the eighth-most frequent polluter in our database, was charged under this new system in Zibo city (Shandong).Footnote 49

We also see some localities making use of industrial policy tools to punish polluters, particularly those in the power sector. A number of central SOEs in the power generation industry have collected government subsidies for the purchase of desulphurization facilities, but then failed to ensure proper running of the equipment so that flue gas continues to have high amounts of SO2, a known cause of respiratory illnesses among other adverse health effects. Some local Development and Reform Commission (DRC) officials, responsible for such subsidy programmes, have begun to take action against these firms. For instance, a local DRC in Inner Mongolia discovered, in 2014, that a company in the Huaneng Group had failed to put desulphurization facilities into proper operation. Officials reduced the subsidies the company was receiving for desulphurized electricity and issued them with a fine of 17 million yuan.Footnote 50

Local environmental authorities have also sometimes appealed to courts to step in against non-compliant SOEs. After years of oil leakage causing serious water and soil pollution, a PetroChina subsidiary operating in the Changqing oil field (Sha'anxi) was charged with pollution fees of more than 110 million yuan and ordered to pay compensation of 850 million yuan for water and soil losses. After refusing to pay, the EPB appealed for help from authorities higher up, but even provincial leaders failed in their efforts. (The vice-governor of the province stepped in to coordinate the unsettled environmental fine payment between PetroChina and the Yulin City government but was unsuccessful.) In October 2013, officials then successfully appealed to a district court to freeze the oil field's 22 bank accounts. The move brought PetroChina back into talks with government over eco-compensation and the courts ultimately unfroze those accounts.Footnote 51

The above cases are evidence of both change and continuity in environmental governance. They show us that new governance mechanisms that aim to bring substantial punishments to bear on polluters, have, at least in formal terms, increased the state's coercive capacity vis-à-vis polluting central SOEs. But these innovations in the formal architecture of the environmental bureaucracy, while laudable, are incapable of budging the status quo on their own. Indeed, the examples we have of local officials manoeuvring against central SOE polluters are newsworthy precisely because they are rare. What these exceptions to the rule tell us is that informal politics (still) matters. Anqing's victory against Sinopec is particularly telling in this regard. It is safe to say that had the EPB head not been a powerful local figure—very much an exception to the local rule of politically weak EPB heads—Sinopec would have escaped punishment. For this reason, we should perhaps not expect any obvious demonstration of effect across China, at least in the immediate future. At the same time, it would be a mistake to understate the importance of these institutional reforms in the context of ever-increasing support for environmental protection within both the Chinese state and society.

Conclusion

The literature on environmental governance in China has often excoriated the local state for protecting polluters and failing to implement the centre's environmental rules and plans. Our research joins that of Ran's in highlighting the culpability of the centre in the so-called environmental implementation gap.Footnote 52 While our data does not allow us to comment on the frequency or severity of environmental violations relative to firms of other ownership type, it does unequivocally show that central SOEs have been the source of a large number of serious pollution incidents across China. SASAC firms in the power generation and oil and gas industries, in particular, have contributed to China's environmental crisis in different regions through the emission of pollutants that contaminate the air, water and soil.

And, in all likelihood, our evidence represents only the tip of the iceberg. This is so because the logics of local and central protectionism often overlap. China's revenue- and job-hungry localities have a strong incentive to sweep these firms' environmental violations under the rug. In addition to local officials' propensity to turn a blind eye to pollution from SASAC firms for economic reasons, the embeddedness of SOE managers in local patron–client networks also works against the impartial enforcement of environmental rules. For these reasons, the cases in our database may be the exceptions to the rule of keeping quiet about central SOE pollution.

Our analysis also offers insight into what is behind such central protectionism. First, SASAC firms are incentivized, above all, to increase their scale and improve profitability in order to “go big and go strong” in global markets. While SASAC has begun to incorporate environmental measures into its evaluation system, at present, green incentives within the central SOE system remain overshadowed by traditional industrial policy goals. In contrast to one recent analysis, we remain sceptical of the view that SASAC represents the best hope for greening central SOE behaviour.Footnote 53 Second, central SOEs are simply too big and too powerful for officials in the environmental bureaucracy to regulate. Central SOEs' high administrative rank, economic clout and guanxi 关系 ties to political elites combine to present extreme challenges in holding them to account for environmental violations. Nonetheless, environmental officials' innovative use of new governance mechanisms affords a measure of hope.

Finally, an implication of our article is that the “central SOE problem” is an increasing source of strain in central–local relations and environmental governance. While local officials have displayed ingenuity and resolve in dealing with non-compliant SOEs, these efforts remain few and far between and are often ineffective. As society's demands for environmental protection grow louder and as green targets in cadre performance evaluations continue to harden, local officials will face increasing pressure to effectively regulate business, including central SOEs. Providing lasting solutions to this central SOE problem will involve both substantially improving the regulatory capacity of the environmental bureaucracy and significantly strengthening central SOEs' incentives to pursue cleaner production. In other words, this will involve nothing less than reducing the cognitive dissonance within the Chinese state by minimizing the goal conflict between its economic and environmental systems.

Biographical notes

Sarah Eaton is professor of modern Chinese society and economy at the University of Göttingen.

Genia Kostka is professor of Chinese politics at the Free University of Berlin.

Footnotes

1 Xinhua, 13 January 2014.

3 The most frequent form of procedural violation are issued when firms begin new projects without first completing an approved environmental impact evaluation. Other common procedural violations include failing to attend mandatory training on environmental practice and failure to comply with environmental directives regarding, e.g. proper storage of environmentally hazardous materials.

4 The IPE web portal can be accessed here: http://www.ipe.org.cn/pollution/corporation.aspx.

6 The China Environmental Accidents and Protests Crowdmap can be accessed here: https://chinaenvironment.crowdmap.com.

7 Eaton and Kostka Reference Eaton and Kostka2014.

9 China Statistical Yearbook 2014.

10 The reported pollution incidents by central SOE correlate highly with provincial revenues from industrial SOEs (correlation coefficient R = 0.69), provincial investments in the treatment of industrial pollution (correlation coefficient R = 0.65), presence of foreign firms (here measured by the value of total exports and imports; correlation coefficient R = 0.56), production of electricity (R = 0.58), industrial GDP (correlation coefficient R = 0.48), and presence of private firms (R = 0.44). Violation cases at the provincial level were far less closely correlated with waste water pollution (R = 0.34), GDP per capita (R = 0.13), urban disposable income (R = 0.11) and with the share of urban population (R = −0.03).

13 Li and Chan Reference Li and Chan2016.

14 Lo and Tang Reference Lo and Tang2006, 204.

15 Interview No. 24, 27. September 2011, Shanxi.

17 Walter and Howie Reference Walter and Howie2010; Brødsgaard Reference Brødsgaard2012.

18 Brødsgaard Reference Brødsgaard2012.

19 Interview No. 8, 18. September 2011, Beijing.

20 Wang, Xiao and Tang Reference Wang, Xingzhi and Yaojia2008, 57.

22 Van Rooij, Zhu, Li and Wang Reference Van Rooij, Qiaoqiao, Na and Qiliang2017.

25 Wang, Yuhua Reference Wang2016.

27 In 2010 the system shifted to include Economic Value-Added measures in order to apply pressure to those SOE managers who have posted impressive financial performance on the backs of cheap policy loans from state-owned financial institutions and direct state subsidies.

28 Kan 27 September Reference Kan2008.

29 Interview No. 8, 18. September 2011, Beijing.

31 Lin Reference Lin2010, 72.

33 China Environmental Review, 21 April 2015.

35 Lieberthal and Oksenberg Reference Lieberthal and Oksenberg1988; Mertha Reference Mertha2009.

36 Ng and Li 29 August Reference Ng and Jing2013.

37 The app was developed by prominent environmentalist Ma Jun's NGO, the Institute of Public & Environmental Affairs.

38 Goering 17 April Reference Goering2015.

39 Sina 29 July 2014.

40 Yang and Calhoun Reference Yang and Calhoun2007.

41 Liu 12 January Reference Liu2015.

42 Database Case 92.

43 Database Case 35.

44 Li 27 January Reference Li2015.

45 China Council for International Cooperation on Environment and Development 4 December 2014.

46 Since 2011, the Lanzhou government had requested that PetroChina move the facility to an industrial park on the outskirts of the city, but the company is reportedly unwilling to pay for the approximately 60 billion yuan in associated costs, a sum which the government claims it also cannot afford. See Li 27 January 2015.

47 Xinhua 21 June 2013; Jiangnan Wanbao 12 June 2013.

48 CNR Financial Review 2013; Banyuetan Network Reference Network2013.

49 Database Case 51; Sina 3 February 2015.

50 Database Cases 6–8.

51 Database Cases 37–38.

References

Network, Banyuetan. 2013. “Huanbao ju chufa yangqi, he shi bu zai shi xinwen?” (EBP penalizes central SOE, when is it no longer news?) http://www.gesep.com/Hot/show_183_339809.html. Accessed 26 August 2015.Google Scholar
Brødsgaard, Kjeld Erik. 2012. “Politics and business group formation in China: the Party in control?The China Quarterly 211, 624648.CrossRefGoogle Scholar
Chai, Jing. 2015. “Qiong ding zhi xia” (Under the Dome).Google Scholar
China Council for International Cooperation on Environment and Development. 2014. “Four Lanzhou enterprises are notified due to air pollution and two leaders are held accountable,” 4 December, http://www.cciced.net/encciced/newscenter/latestnews/201312/t20131204_264357.html. Accessed 10 May 2015.Google Scholar
China Environmental Review . 2015. “New environmental law herald dawn for corporate social responsibility in China,” 21 April, http://www.chinaeconomicreview.com/sustainable-finance. Accessed 10 May 2015.Google Scholar
China Statistical Yearbook . 2014. National Bureau of Statistics of China.Google Scholar
CNR Financial Review . 2013. “Anqing huanbao ju shouci xiang yangqi kai fadan ping: Jianli ti zhi quebao duli zhifa” (Anqing Environmental Protection Agency tickets a central SOE for the first time the first time), 11 June, http://finance.cnr.cn/jjpl/201306/t20130611_512797916.shtml. Accessed 26 August 2015.Google Scholar
Eaton, Sarah. 2016. The Advance of the State in China: State–Market Relations in the Reform Era. Cambridge, UK: Cambridge University Press.Google Scholar
Eaton, Sarah, and Kostka, Genia. 2014. “Authoritarian environmentalism undermined? Local leaders’ time horizons and environmental policy implementation in China.” The China Quarterly 218, 359380.Google Scholar
Goering, Laurie. 2015. “Data app pushes Chinese factories to cut pollution,” Business Insider, 17 April, http://www.businessinsider.com/r-data-app-pushes-chinese-factories-to-cut-pollution-2015-4?IR=T. Accessed 10 May 2015.Google Scholar
Jahiel, Abigail R. 1997. “The contradictory impact of reform on environmental protection in China.” The China Quarterly 149, 81103.Google Scholar
Jahiel, Abigail R. 1998. “The organization of environmental protection in China.” The China Quarterly 156, 757787.CrossRefGoogle Scholar
Jiangnan Wanbao. 2013. “Zhongshihua fengonsi jianchang 40 nian – di yi ci chi huanbao fa dan” (Sinopec subsidiary receives first green fine after 40 years in business), 12 June, http://news.jnwb.net/2013/0612/62898.shtml, Accessed 10 May 2015.Google Scholar
Jing, Ke, Price, Lynn, Ohshita, Stephanie, Fridley, David, Khanna, Nina Zheng, Zhou, Nan and Levine, Mark. 2012. “China's industrial energy consumption trends and impacts of the top-1000 enterprises energy-saving program and the ten key energy-saving projects.” Energy Policy 50, 562569.Google Scholar
Kan, Kaili. 2008. “Shichang jingji zhong de zhengfu zuoyong: Guoziwei wei shenme bixu tuixiao” (The function of government in a market economy: why SASAC must be abolished), 27 September, Presentation to the “Price System and Monopoly Sector Reform” Forum, Beijing University.Google Scholar
Kostka, Genia, and Hobbs, Will. 2012. “Local energy efficiency policy implementation in China: bridging the gap between national priorities and local interests.” The China Quarterly 211, 765785.CrossRefGoogle Scholar
Kostka, Genia. 2014. “Barriers to the implementation of environmental policies at the local level in China.” World Bank Policy Research Working Paper No. WPS 7016. Washington, DC: World Bank Group. http://documents.worldbank.org/curated/en/2014/08/20144757/barriers-implementation-environmental-policies-local-level-china. Accessed 4 April 2016.Google Scholar
Kostka, Genia. 2016. “Command without control: the case of China's environmental target system.” Regulation and Governance 10, 5874.Google Scholar
Lieberthal, Kenneth, and Oksenberg, Michel. 1988. Policy Making in China: Leaders, Structures, and Processes. Princeton, NJ: Princeton University Press.Google Scholar
Li, Xiaojun, and Chan, Christina Gai-Wai. 2016. “Who pollutes? Ownership type and environmental performance of Chinese firms.” Journal of Contemporary China 25(98), 248263.Google Scholar
Li, Yan. 2015. “Lanzhou shames CNPC unit for pollution crises,” Caixin, 27 January, http://english.caixin.com/2015-01-27/100779009.html. Accessed 10 May 2015.Google Scholar
Lin, Li-Wen. 2010. “Corporate social responsibility in China: window dressing or structural change?Berkeley Journal of International Law 28(1), 137.Google Scholar
Liu, Xin. 2015. “Govt slams SOE over pollution,” Global Times, 12 January, http://www.globaltimes.cn/content/901300.shtml. Accessed 10 May 2015.Google Scholar
Lo, Carlos Wing-Hung, and Tang, Shui-Yan. 2006. “Institutional reform, economic changes and local environmental management in China: the case of Guangdong province.” Environmental Politics 15(2), 190210.Google Scholar
Lo, Kevin, Li, He and Wang, Mark. 2015. “Energy conservation in China's energy-intensive enterprises: an empirical study of the Ten-Thousand Enterprises Program.” Energy for Sustainable Development 27, 105111.Google Scholar
Lorentzen, Peter, Landry, Pierre and Yasuda, John. 2014. “Undermining authoritarian innovation: the power of China's industrial giants.” The Journal of Politics 76(1), 182194.Google Scholar
Mertha, Andrew. 2009. “‘Fragmented authoritarianism 2.0’: political pluralization in the Chinese policy process.” The China Quarterly 200, 9951012.Google Scholar
Ng, Eric, and Jing, Li. 2013. “Oil giants barred from new projects after missing pollution targets,” South China Morning Post, 29 August, http://www.scmp.com/business/companies/article/1300306/china-environment-ministry-suspends-some-approvals-sinopec-cnpc. Accessed 10 May 2015.Google Scholar
Nolan, Peter. 2001. China and the Global Economy: National Champions, Industrial Policy and the Big Business Revolution. Houndsmill: Palgrave.Google Scholar
Price, Lynn, Wang, Xuejun and Yun, Jiang. 2010. “The challenge of reducing energy consumption of the top-1000 largest industrial enterprises in China.” Energy Policy 38(11), 6485–98.Google Scholar
Ran, Ran. 2013. “Perverse incentive structure and policy implementation gap in China's local environmental politics.” Journal of Environmental Policy and Planning 15(1), 1739.CrossRefGoogle Scholar
Ran, Ran. 2017. “Understanding blame politics in China's decentralized system of environmental governance: actors, strategies and context.The China Quarterly, special section “Central-local relations and environmental governance in China.”Google Scholar
Sina. 2014. “Angang deng duo yangqi shang huanbaobu heibang” (Angang and many central SOEs enter MEP's blacklist), 29 July, http://finance.sina.com.cn/stock/s/20140729/075819847480.shtml. Accessed 10 May 2015.Google Scholar
Sina. 2015. “Zhonglü shandong gongsi chaoliao paifang bei fa” (Chalco Shandong fined for excessive emissions), 3 February, http://finance.sina.com.cn/chanjing/gsnews/20150203/025921459437.shtml. Accessed 10 May 2015.Google Scholar
Sutherland, Dylan. 2003. China's Large Enterprises and the Challenge of Late Industrialisation. London: Routledge Curzon.Google Scholar
Tang, Shui Yan, Lo, Carlos Wing Hung, Cheung, Kai Chee and Lo, Jack Man Keung. 1997. “Institutional constraints on environmental management in urban China: environmental impact assessment in Guangzhou and Shanghai.” The China Quarterly 152, 863874.Google Scholar
Van Rooij, Benjamin. 2006. “Implementation of Chinese environmental law: regular enforcement and political campaigns.Development and Change 37(1), 5774.Google Scholar
Van Rooij, Benjamin, and Lo, Carlos Wing-Hung. 2010. “Fragile convergence: understanding variation in the enforcement of China's industrial pollution law.” Law and Policy 32(1), 1437.Google Scholar
Van Rooij, Benjamin, Qiaoqiao, Zhu, Na, Li and Qiliang, Wang. 2017. “Centralizing trends and pollution law enforcement in China.” The China Quarterly, special section “Central-local relations and environmental governance in China.”Google Scholar
Walter, Carl E., and Howie, Fraser J.T. 2010. Red Capitalism: The Fragile Financial Foundation of China's Extraordinary Rise. Singapore: John Wiley.Google Scholar
Wang, Alex L. 2015. “Chinese state capitalism and the environment.” In Milhaupt, Curtis and Liebman, Benjamin (eds.), Regulating the Visible Hand? The Institutional Implications of Chinese State Capitalism. Oxford: Oxford University Press.Google Scholar
Wang, Hua, and Jin, Yanhong. 2002. “Industrial ownership and environmental performance: evidence from China.” World Bank Policy Research Working Paper 2936, World Bank.Google Scholar
Wang, Junhao, Xingzhi, Xiao and Yaojia, Tang. 2008. Zhongguo longduanxing hangye guanzhi jigou de sheli yu yunxing jizhi (The establishment and operation of regulatory agencies in China's monopoly industries). Beijing: Commercial Press.Google Scholar
Wang, Yuhua. 2016. “Beyond local protectionism: China's state–business relations in the last two decades.” The China Quarterly 226, 319341.CrossRefGoogle Scholar
Wang, Xuejun. 2006. “Top-1000 enterprises energy efficiency program: policy design and implementation.” Supporting Documentation for the Energy Foundation's Forum on Implementing China's 2010 20 Percent Energy Efficiency Target, 9–10 November 2006.Google Scholar
Xinhua. 2013. “Ticketing central SOEs – local EPBs dare to hit Tigers,” 21 June, http://news.xinhuanet.com/2013-06/21/c_116235896.htm. Accessed 10 May 2015.Google Scholar
Xinhua. 2013. “Local government seeks eco-compensation from oil producer,” 8 December, http://news.xinhuanet.com/english/indepth/2013-12/08/c_132950735.htm. Accessed 10 May 2015.Google Scholar
Xinhua. 2014. “Sinopec pledges compensation over Qingdao pipeline blasts,” 1 January, http://news.xinhuanet.com/english/china/2014-01/13/c_133040853.htm. Accessed 3 April 2016.Google Scholar
Yang, Guobin, and Calhoun, Craig. 2007. “Media, civil society, and the rise of a green public sphere in China.” China Information 21(2), 211236.CrossRefGoogle Scholar
Figure 0

Figure 1: Reported Cases of Central SOE Non-compliance with Environmental Regulations (by Province/Region)

Source:Authors' Central SOE Environmental Violation Database, 2016. (Colour online)
Figure 1

Figure 2: Sectoral Distribution (N = 2,370)

Source:Authors' Central SOE Environmental Violation Database, 2016. (Colour online)
Figure 2

Figure 3: Type of Pollution (N = 2,370)

Source:Authors' Central SOE Environmental Violation Database, 2016. (Colour online)
Figure 3

Table 1: Most Frequently Listed SOEs in the Database (N = 2,370)