Urban Environmental Governance and Conflict Resolution: A Case Study of Sustainable Development Challenges in Semarang, Indonesia

Rapid urban development has forced local governments to attract investors to invest in their areas. However, these activities not only provide economic benefits but also trigger environmental changes in the area. In some cases, local governments often choose pro-investment strategies to promote urban development, but these strategies are often implemented amidst weak environmental regulations and oversight [1, 2]. While urban development can boost the economy, it often leaves environmental problems such as environmental degradation and social displacement if environmental protection is not strictly enforced. Addressing the conflict between economic growth and environmental protection is currently a governance challenge. In the case of Semarang, Indonesia, industrialization and infrastructure projects have repeatedly triggered conflicts that resulted in pollution, land-use change, and geotechnical hazards [3, 4].

The conflicts mentioned in the literature above demonstrate larger trends in inequality regarding resource allocation, inequities related to power, and failures in policy formation [5, 6]. In addition to their ecological nature, these conflicts are deeply embedded within larger socio-political structures [7, 8]. Hence, an understanding of governance and the way government agencies deal with complexity, uncertainty and conflicting interests in the face of asymmetric power is essential in understanding these disputes. Such insight provides the foundation for the development of Theory of Environmental Conflict Resolution (ECR) [9, 10].

There are two broad approaches to ECR that have emerged from the existing literature. The first is a process focused approach which emphasizes successful process-oriented outcomes of ECR including representation of stakeholders, development of trust, collaborative dialogue, and compliance with the law [2, 11]. The other is an outcome focused approach which emphasizes successful outcome oriented elements of ECR such as stability of agreements, de-escalation of conflicts and the feasibility of implementing agreements [2, 12]. Each of these approaches is based on the premise that multi-actor involvement and negotiated settlements will result in long-term, sustainable and legitimate solutions.

Most of the currently dominant literature pertaining to ECR is positioned within a governance context characterized by strong institutions, predictability of legal enforcement and formal, systematic mediation as would be found in North America and Australia [13, 14]. Collaborative governance is enhanced by accountability of institutions and clarity of regulation, as compared to rapidly developing cities in the process of urbanization and development, where collaborative governance has typically occurred through various means including hybrid and informal governance structures, and with political mediation [15-17]. Recent international studies have highlighted several structural limitations of conventional hybrid governance models in developing countries. First, research from urban political economy has found that coalitions between governments and private investors often shape land-use decisions, biasing development toward capital-intensive projects. In these cases, environmental governance is subordinated to economic growth. Second, studies on environmental justice have shown that participatory mechanisms do not always address power imbalances, they can legitimize unequal outcomes if structural inequalities still in the participatory process. Third, research on adaptive and polycentric governance has found that, while multi-level and networked arrangements can enhance resilience, their effectiveness depends on the coherence and accountability of institutions. Taken together, these issues raise questions about the adequacy of the ECR model [18, 19].

Understanding dispute resolution is crucial for how governments make decisions and address environmental issues, and whether dispute management processes still exhibit multi-centric, multi-network, and multi-actor characteristics. Therefore, understanding environmental dispute resolution mechanisms will aid in understanding ongoing environmental governance.

In many developing cities, dispute resolution mechanisms may appear with multi-actor and deliberative, but they serve as reactive instruments for social stabilization rather than as a means for substantive environmental restoration. Empirical evidence from Indonesia supports this concern. While the national laws that regulate environmental practices provide for mediation as an option to resolve disputes that involve environmental issues, enforcement is often weak, and most disputes remain unresolved or are only partially resolved. This fact creates the environment for reviewing several of the environmental conflicts in Semarang [19, 20].

This research will evaluate the theoretical underpinnings of ECR. By assessing certain environmental conflict situations in Semarang, the research will identify specific environmental conflict situations in Semarang and will then assess those environmental conflicts in relation to their context. In addition to being different situations, there is a common pattern of reactive mediation in relation to the several environmental conflict situations in Semarang that are reviewed.

The research finds that ECR as practiced in Semarang has created a gap between the procedural inclusiveness of governance as compared to substantive environmental protection. Although ECR processes appear to be deliberative and are conducted by multiple actors, outcomes of ECR generally emphasise social stability through monetary compensation and administrative adjustments as compared to ecological restoration. There is a need to extend existing ECR perspectives to include political-economic alignment; institutional fragmentation; and growth-oriented governance as additional analytical variables.

By situating the Semarang case within a broader context regarding governance theory and urban political economy research, this research paper will make three contributions to the sustainable development discourse.

• Contributes to the reconceptualization of ECR in the context of developing cities as a hybrid governance mechanism shaped by growth coalitions.
• Distinguishes between dispute stabilization and environmental restoration as distinct outcome categories.
• Offers a context-sensitive analytical lens for assessing ECR in rapidly growing cities.

Through these refinements, this study expands theoretical understanding of environmental governance beyond procedural participation. It addresses the structural factors that hinder sustainable transformation. Despite the abundance of ECR studies, research on how political-economic alignment shapes mediation outcomes in rapidly urbanizing cities is currently very limited.

1.1 Conceptual framework

ECR has been viewed as a governance mechanism for addressing complex environmental disputes through inclusive participation, negotiation, and mediated agreements. The main model assumes that multi-actor engagement, transparency, and deliberative processes enhance legitimacy and produce sustainable outcomes. Success is measured by process-oriented indicators, such as stakeholder representation and trust-building, and by outcome-oriented indicators, such as agreement stability and dispute reduction.

However, this model rests on several implicit premises, namely the assumption that decision-making institutions are stable and have strong enforcement of laws for legal and environmental protection. The model assumes that stakeholder participation balances power between the parties. It also assumes that negotiated agreements prioritize ecological restoration, rather than simply social compromise.

These assumptions may not hold in rapidly urbanizing cities in developing countries. Governance is often fragmented, priorities are driven by growth, and negotiations are informal. Environmental justice findings suggest that participation does not equate to influence. When municipal and private interests are misaligned, participatory processes can legitimize outcomes. Thus, participatory processes can still lead to environmental damage, suggesting that participation alone is insufficient for successful ECR.

Frameworks that prioritize stability for and reduction of conflict through outcomes-oriented practices may hide significant differences between two very different outcomes, dispute stabilization and environmental restoration. Politically sensitive cases have highlighted how agreements can reduce social tensions through compensation, relocation and/or technical improvements, but do not necessarily result in achieving ecological restoration or reduction of long-term environmental risks. In situations where stabilization occurs without prior ecological restoration left in place, urban ecosystems are susceptible to environmental degradation over time.

Urban political economy literature has shown that cities typically use growth-oriented strategies and create partnerships, in order to create greater economic competitiveness. As a result, investment-related issues can influence environmental governance and limit the involvement of environmental institutions at the initial stages of development (e.g., during the local government decision making process). According to polycentric governance theory, there is a need to coordinate across several levels and integrate the respective networks of governance. However, without institutional coherence, multi-actor collaboration has resulted in increased fragmentation and lack of accountability.

From the explanation above, it can be concluded that environmental conflict is a conflict involving unequal resource allocation, unequal decision-making processes, and power imbalances within society that impact social and environmental issues. To address this gap, this study conceptualizes ECR in the context of developing cities as a governance process influenced by procedural inclusiveness and structural factors related to governance orientation, power configuration, and institutional capacity. The conceptual diagram presented in Figure 1 synthesizes these analytical refinements. This diagram does not introduce new empirical claims but organizes empirical findings from the Semarang case into a structured framework to evaluate how dispute resolution processes relate to substantive environmental outcomes.

Figure 1. Analytical framework used in this study

In this study, dispute stabilization refers to outcomes that reduce social tension through compensation, relocation, or administrative settlement without substantially changing environmental conditions.

Ecological restoration, by contrast, refers to outcomes involving rehabilitation of environmental systems, preventive land-use reform, or long-term environmental risk reduction.

This section applies the analytical framework developed in this study to the three selected cases in Semarang, Indonesia. Rather than describing each case sequentially, the analysis is organized around the structural dimensions developed in Section 1.

3.1 Empirical flow of Environmental Conflict Resolution in Semarang

Environmental dispute resolution in Indonesia formally operates under Law No. 32/2009 on Environmental Protection and Management, which allows mediation and alternative dispute resolution mechanisms outside litigation. At the municipal level, environmental governance in Semarang involved multiple institutions, including local environmental agencies, municipal authorities, parliament (DPRD), and ad hoc mediation teams formed during disputes.

However, the cases examined in this study indicate that mediation was often conducted through informal negotiation and politically facilitated arrangements rather than through independent certified mediators. Environmental agencies also tended to become involved after conflicts escalated rather than during upstream planning stages.

Two cases involved actual changes in environmental quality, while one case concerned a potential change in environmental quality that had not yet fully materialized. Nevertheless, a common pattern of ECR can be identified across the three cases.

First, the conflict usually started with complaints from surrounding inhabitants where projects or planned activities were conducted by private sectors, often explicitly or implicitly supported by the municipality.

Second, because there was no fixed and accessible mechanism for filing complaints other than a costly legal suit, the common method used by the community was to march on the street, organize demonstrations to the city hall or the House of Representatives, and attract wider public attention through media coverage.

Figure 2. Empirical flow of Environmental Conflict Resolution (ECR) in Semarang

Third, responses to these protests varied, but in general the greater the media coverage, the higher the level of government involvement in the settlement process. In several cases, local government created ad hoc teams or relied on informal mediation facilitated by local officials.

Finally, the common result of environmental conflicts was focused more on the provision of compensation for the casualties of environmental degradation, often accompanied by the provision of wells, houses, or other facilities. These measures did not really address environmental rehabilitation. As long as the complainants no longer expressed their complaints, the conflict was generally considered solved.

The overall sequence of the ECR process in Semarang is summarized in Figure 2, which illustrates the predominantly reactive, downstream pattern observed across the cases.

3.2 Structural dimensions of Environmental Conflict Resolution

3.2.1 Governance orientation

In all three cases, urban governance reflects a development-oriented trajectory, albeit with varying manifestations.

In the Tapak River case, industrial activities were permitted near rural settlements without effective environmental oversight from the outset. Public pollution reports did not trigger immediate law enforcement action. City government intervention only occurred after sustained public protests and viral media coverage. Environmental protection measures, including the installation of a wastewater treatment plant, were introduced as corrective rather than preventive safeguards.

Regarding the case study of the Golf Course project, the exchange of green open space with development through investment showed the orientation of governance being economically-oriented. The municipality agreed to give its approval for the construction of a new golf course proposed by PT Putra Wahid Sejahtera in exchange for rights to develop SGC. The residents, NGOs, academics, and environmental activists objected to the plan due to the fact that the area acted as a significant green open space and water catchment area. Despite the protests of the community and the investigation conducted by the DPRD into environmental impact assessments and land valuation, the land swap eventually took place. The environmental agencies were only active when confronted with community resistance.

As for the case of Gumpilsari landslide, the approval of new golf course development came before the evaluation of potential slope stabilization efforts. With the repeated occurrence of landslides in the Old Gombel region, it was the residents who considered them as development-related issues, whereas the developer and the authorities regarded them as purely natural events. The government's response concentrated on the matters of relocation and compensation; the other problems were left out.

In many cases, environmental protection mechanisms do exist, but they are largely reactive. Governance orientation appears to influence how and when ECR processes are activated.

3.2.2 Power alignment

The power structure of participating entities represents the second structural component of community stakeholder participation. All three projects indicated that both development permits and major planning decisions were made prior to the comprehensive involvement of the community. The development decisions that occurred during the few development planning phases only included the coordination of the City with private investors, while the Environmental agencies were involved in an insignificant upstream capacity. The mediation process was executed mostly by government officials of the communities being affected, as opposed to being conducted by independent mediators.

In the case of the Tapak River, the affected community members relied on NGOs and continued protests as a means to obtain improvements. However, due to their economic vulnerability and fragmented representation, the affected community members were unable to exert bargaining power, and many chose to sell their land to the developer and relocate. In the case of the Golf Course, the affected community members demonstrated public resistance and initiated parliamentary debate; however, the final decision to approve the land swap was still executed. In Gumpilsari, the affected residents accepted relocation under a lack of substantive discussion and without alternatives. All three affected communities had limited avenues by which to influence the broader land use policy.

The aforementioned trends suggest that community participation does not always equate to an equal amount of bargaining power. The gaps in community participation with existing structures create unequal outcomes for the affected communities.

3.2.3 Institutional capacity

Institutional fragmentation plays a significant role in shaping the dynamics that underlie conflict resolution. While there is a formal mediation mechanism provided for in the national law, there were no independent certified mediators who were available to the study. Due to there being a limited level of inter-departmental coordination, the majority of the instances of mediation between parties were conducted informally, and ad hoc working groups would be formed to deal with individual disputes only as they arose.

Figure 3. The unfinished mechanism of Semarang environmental governance

In terms of the Tapak case, enforcement of environmental laws by relevant governmental authorities did not occur until there were a number of community protests from those affected due to the escalating form of dispute. In the Golf Course case, environmental authorities did not play a significant role in the initial decision-making process involving the swap of land between two parties. In the Gumpilsari case, government agencies did not respond to the dispute between the two parties until after a disaster had occurred.

The Environmental Impact Management Agency (Badan Pengelolaan Dampak Lingkungan) was typically unavailable during the upstream planning phase and would be involved only after public protests began or a disaster occurred. As a result of this reactive approach to environmental management, there exists a disparity between the intention of regulatory structures and the implementation of those structures in practice. This also illustrates the "unfinished mechanism" of environmental governance present in Semarang, or the existence of regulatory structures that have not been fully implemented in practice (see Figure 3).

3.2.4 Outcome typology

Applying the analytical framework reveals similar trends across the cases analysed.

For example, the Tapak River case involved some regulatory reform with the installation of a wastewater treatment plant along with some assistance from the government with an ecological restoration of the river; however, this did not occur. In the Golf Course case, political stabilisation is achieved through the administrative approval of a land swap despite the environmental opposition, without the ecological rehabilitation being completed. In the case of Gumpilsari, urgent housing requirements were satisfied through the relocation and rental assistance but did not contain any ecological rehabilitation nor changes to the policies of stabilising slopes.

The overall outcome of all three cases was centred on compensation to the affected community; generally accompanied by the provision of wells, housing or other facilities to assist the community. In many cases, the response addressed very little in relation to the root cause of the environmental problem nor to the ecological rehabilitation required. A dominant pattern is to stabilise the compensatory and regulatory elements rather than create ecological reform through structural methods.

3.3 Cross-case synthesis

In most instances, a structural disconnect has arisen between procedural inclusion and substantive environmental protections. While community protests (or NGO participation), technical assistance and parliamentary oversight were part of many dispute resolution processes, the results of these processes were primarily compensatory or regulatory rather than transformational in nature.

Although the environmental degradation of natural resources has been partially addressed through regulatory mechanisms, this degradation could not be fully reversed. In addition, there were limited opportunities for institutional reform within the framework of these processes. Thus, the role of ECR within the City of Semarang was primarily one of stabilizing disputes rather than enabling sustainability transformation.

This research study looks into the theory on ECR as a governing model used in rapidly expanding cities like Semarang. Findings from this research study have shown that while the YG appears to be multi-stakeholder and deliberative in nature, its resulting outcome is primarily based on governance systems that promote long-term development and collaborative engagement between the city and the private sector. As a result, the primary ECR resolution method utilised is to use compensation and technical corrections to stabilise the community rather than to restore the environment holistically.

This paper extends ECR theory in three ways. It adds to existing ECR theories by introducing two new structural variables (governance orientation and power congruence) that shape ECR mediation outcomes. It also distinguishes between social and ecological restoration by explaining that the stability of an agreement should not be confused with the sustainability of a community's environmental problem resolution. Lastly, it demonstrates the inadequacy of polycentric governance structures where fragmented institutions control upstream intervention strategies. In other words, the process of settling environmental conflicts in Semarang will lead only to settling the dispute between many parties to the conflict without repairing the damage to the environment. For sustainable urban development, conflict resolution mechanisms must move beyond reactive mediation toward integrated, preventive, and ecologically accountable with governance structures. The analysis is limited to three cases in Semarang within a single metropolitan context, and its findings should be interpreted as analytical generalizations rather than statistical representations.

Future research should examine this analytical extension in comparative urban contexts to assess its broader applicability across rapidly developing cities. These findings highlight the importance of integrating environmental governance capacity into urban development planning so that conflict resolution contributes not only to social stabilization but also to long-term ecological sustainability. Therefore, the need to have a specific body, whether from the government or civil society, that is also concerned with the quality of the environment would help complete the process as part of environmental governance.