Next Article in Journal
Spatiotemporal Analysis, Driving Force, and Simulation of Urban Expansion Along the Ethio–Djibouti Trade Corridor: The Cases of Dire Dawa City, Eastern Ethiopia
Previous Article in Journal
Artificial Intelligence in Higher Education: Predictive Analysis of Attitudes and Dependency Among Ecuadorian University Students
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Mining-Induced Environmental Degradation and Displacement in the Context of Ecosocial Work: A Qualitative Study in Rural Areas

by
Merve Akıncı
1,* and
Filiz Yıldırım
2
1
Independent Researcher, 06000 Ankara, Türkiye
2
Department of Social Work, Institute of Health Sciences, Ankara University, Keçiören, 06290 Ankara, Türkiye
*
Author to whom correspondence should be addressed.
Sustainability 2025, 17(17), 7757; https://doi.org/10.3390/su17177757
Submission received: 24 July 2025 / Revised: 16 August 2025 / Accepted: 27 August 2025 / Published: 28 August 2025
(This article belongs to the Section Pollution Prevention, Mitigation and Sustainability)

Abstract

The increasing demand to leverage mining for economic development poses severe risks to rural communities, especially in developing countries that are particularly vulnerable to its negative impacts. This study assesses the processes of mining-induced environmental degradation and displacement through the lens of two villages in Turkey and highlights the need for ecosocial work within these contexts. A qualitative case study design was adopted, involving 18 individuals from both villages who were recruited through snowball sampling. The data, collected through in-depth interviews and participant observation, were analyzed using reflexive thematic analysis with the help of MAXQDA 24 software. The findings reveal that mining-related environmental degradation has adversely affected not only the ecosystems of the villages but also their social and economic structures. Moreover, the study identifies the need to address multiple and overlapping challenges experienced by villagers in relation to displacement, including both material and psychosocial difficulties. This research is the first attempt to provide an empirical foundation for ecosocial work interventions at the micro, mezzo, and macro levels in the context of rural, mining-affected communities in Turkey. As such, it offers valuable insights into how ecosocial work can engage with these levels of intervention in rural settings.

1. Introduction

The expansion of mining worldwide reduces poverty, especially in developing countries, by providing economic opportunities and income streams [1,2]. However, environmental degradation from mining disproportionately impacts rural communities [3], intensifying the tension between development discourse and ecosocial cohesion across affected communities [4,5,6]. The consequences of mining include deforestation, pollution, the depletion of natural resources vital for people’s livelihoods [7,8], the deterioration of environmental esthetics, and species loss [1,9,10].
Extractive industries, such as coal mining, permanently disrupt the local ecosystem, which can undermine local economic activities and the long-term sustainability of community livelihoods [5,11]. Direct mining effects, such as soil loss, can limit or prevent agricultural activities in rural areas [6] because mining activities radically change the existing land cover, transforming it into an industry-oriented form of land use [12]. Thus, where non-agricultural employment opportunities are limited [13], mining weakens the livelihoods of natural-resource-dependent rural households [14].
Beyond environmental degradation, mining activities can forcibly or indirectly displace local communities, particularly in rural communities where strong bonds with land and established social networks are vital to well-being [15]. Risks include unemployment, impoverishment, marginalization, and deprived access to traditional food sources [16], as well as a loss of social capital [8,17,18]. Despite the growing interest in ecological crises that has made the natural environment more visible in social work [19,20,21,22], research on mining-induced ecosocial problems remains quite limited in the social work literature [23]. This area of focus, centered on ecological crises and sustainability, is often described using overlapping terms such as environmental social work, green social work, and ecosocial work—concepts that aim to place the natural environment at the core of social work practice [19,24]. This study adopts the term “ecosocial work” as it recognizes the intrinsic value of the natural environment and is shaped by a commitment to ecological justice [25].
Environmental degradation and displacement from mining stem from unsustainable economic activities, which involve both social and ecological destruction. They are directly related to the principles of ecological justice, sustainability, and degrowth advocated by ecosocial work [25]. Ecosocial work aims to protect the sustainability and biodiversity of the ecosystem. It focuses on the inequalities arising from the unfair allocation of environmental resources and risks and advocates for an understanding of ecological justice for all living things [26,27]. Rooted in environmental activism, ecosocial work is based on the view that human beings are part of nature and environmental problems are structural and political issues [28].
Social work bears an important responsibility toward the global economic structure that is beset by various social and ecological challenges [29,30]. Therefore, it should address both environmental and economic unsustainability, making economic transformation central in its sustainability agenda [29,31]. In this context, ecosocial work collectively considers social, ecological, and economic sustainability, suggesting that growth-oriented models lead to inequality and environmental destruction [28,32]. It attempts to systematically understand problems ranging from local to global in a “glocal” context. This approach aims to understand the origins of phenomena that affect individuals and communities and their relationship with sustainability [33]. As a practice-based approach, ecosocial work involves interventions at the micro, mezzo, and macro levels [25,26]. Although ecosocial work is a field of practice for social work rather than a theory [34], practice-oriented intervention development is lacking [19,35,36].
Investigating these issues—situated at the intersection of nature and human life—from a social work perspective is crucial for providing an evidence base for ecosocial practice at the micro (individuals and families), mezzo (groups and organizations), and macro (societal and structural) levels. Aiming to contribute to this evidence base across multiple levels of intervention, this study seeks to assess the processes of mining-induced environmental degradation and displacement from the perspectives of villagers directly affected in two rural communities in Turkey and to identify the resulting needs within the context of ecosocial work.

2. Literature Review

The increasing demands for minerals and supportive policies for the mining sector make developing countries attractive for mining investments [5]. However, mining entails various risks for developing countries: limited regulatory capacity, widespread corruption, and restricted access to justice for vulnerable communities negatively impacted by mining [37]. However, legal regulations in developing countries are increasingly being expanded to promote mining activities [38]. In 1985, Turkey liberalized its extractive industries to meet the demands of a growing economy, allowing foreign companies to obtain mining licenses [39].
Furthermore, with the comprehensive revision of Mining Law No. 3213 and Forest Law No. 6831, mining activities have been permitted even in the most valuable forested areas. Consequently, mining has become one of the main causes of deforestation in Turkey [9,40,41,42], with contributing factors including an inability to balance environmental protection with mining activities due to a dominant mining logic, the privatization of land and public spaces, and a lack of transparency [39,41]. In addition to deforestation, mining activities are also among the leading causes of air, water, and soil degradation in Turkey [43,44].
The mining-related environmental degradation and the expansion of such activities can directly and indirectly lead to the displacement of communities. The spatial transformation process that begins with the establishment of a mining site results in the dispossession of the land’s previous owners and its former uses [45]. Mining-induced displacement is characterized by the uncertainty created through the gradual expansion of projects over time, the continued residence of displaced people near mining sites, and the development of mutual dependencies between companies and communities [46]. This situation threatens housing and food security in mining communities, as well as the social support networks, livelihoods, and sustainability of affected populations [16,18,47]. Although mining-induced displacement occurs in developed nations, it does not commonly lead to unemployment, food insecurity, and homelessness [47].

3. Research Setting

This study was conducted in two coal-mining villages in the Manisa-Soma district of the Aegean Region of Turkey: Deniş and Eğnez. In Turkey, villages dependent on olive cultivation and located in areas with significant mineral reserves, such as Deniş and Eğnez, have long been losing their olive groves and natural habitats due to mining activities. In 1995, an amendment was made to Article 20 of Law No. 3573 on the Improvement of Olive Cultivation and the Grafting of Wild Olives [48], which prohibited the construction and operation of facilities that would hinder the development of olive groves within olive cultivation areas and within a minimum distance of three kilometers from such areas. This measure sought, at the normative level, to guarantee the absolute protection of olive-growing areas. In subsequent years, numerous legislative proposals were introduced in the Grand National Assembly of Turkey to relax this prohibition and to open olive-growing areas to mining activities. Most of these initiatives, however, failed to enter into force due to strong public opposition and judicial rulings.
In Turkey, the extraction and processing of minerals are predominantly carried out by private companies, while the legal ownership of mineral reserves remains vested in the state. Until 2022, private companies operating in villages near Deniş and Eğnez with mining licenses attempted to unlawfully cut down olive groves in expropriated areas. The Council of State immediately prohibited these practices, while the attempts at cutting triggered strong public backlash. Consequently, instead of directly cutting the olive trees in the expropriated lands of Deniş and Eğnez, the companies exerted pressure on local villagers, warning that the trees would be completely destroyed during excavation works in the mining concessions. Believing the loss to be inevitable and seeking at least to meet their household fuelwood needs, some villagers carried out the cutting themselves. In 2022, the Regulation Amending the Mining Regulation formally opened olive-growing areas to mining activities. This change significantly eroded the legal foundation of the protection principle established in 1995. The regulation remains contentious, and in 2025 the issue resurfaced in a new legislative proposal.
Although both villages have a long history of mining, land losses due to mining have become especially evident since 1985. In the last decade, expropriation has accelerated, with residential areas being acquired by companies. Although the state has expropriation authority in Turkey, private mining companies pay the villagers directly for their land because they are the ones conducting the mining activities. In this process, since the consent of landowners is not required under Expropriation Law No. 2942 [49], villagers lose their land for very low compensation and without meaningful involvement in the process. Importantly, the Turkish expropriation framework does not adopt a loss-compensation approach but provides payment for the market value of the property, without covering livelihood losses, relocation expenses, or other social and economic impacts of displacement.
This study was conducted after the formal processes, but the actual eviction process had not yet begun. The state was in the process of resettling the villagers. However, eligibility for these new settlements was subject to certain criteria, including income security. Consequently, some older people and women living alone in the villages did not meet the eligibility criteria. For the first time in their lives, they would be forced to leave their villages and pay rent for their premises. In both villages, only about half of the population was eligible for the new settlements. However, residences in the new settlement area were valued higher than the beneficiaries’ old homes and land in the villages. The new homes would thus require installment payments for nearly 20 years—a significant economic burden for the displaced villagers.

4. Method

4.1. Purpose and Research Questions

This qualitative case study aimed to assess mining-induced environmental degradation and displacement from the perspective of villagers and to identify the foundational requirements for ecosocial work interventions. To achieve these objectives, the following research questions were explored:
  • RQ1: How do villagers assess the impacts of mining-induced environmental degradation on the ecological system of their villages?
  • RQ2: How do villagers assess the impacts of mining-induced environmental degradation on their community?
  • RQ3: How do villagers assess the process of displacement caused by mining activities?
  • RQ4: How do villagers assess the resettlement practices in relation to the displacement process?

4.2. Participants

The purposive sample comprised 18 participants recruited using the maximum diversity method, which allows the identification of common themes through the inclusion of individuals with different characteristics related to the research topic, and reached through snowball sampling [50]. The selection criteria required participants to be over 18 years of age and permanent residents of either of the two villages. Other participants were identified through the local leaders of the two villages, who were designated as key informants. Seven participants were from Eğnez Village, and eleven were from Deniş Village. The sample comprised nine females and nine males. The participants’ ages ranged from 43 to 85 years.

4.3. Data Collection

Data were collected between March and November 2024 in two stages: first from Deniş Village and subsequently from Eğnez Village. The same procedures were followed in the data collection process in both villages. The research was conducted when villagers were preparing for displacement and resettlement. Although the evacuation had not yet officially begun, the villagers were preparing to relocate according to the official decision.
The maximum variation type of purposive sampling was used to reach participants who could provide rich insights into the research questions. The first author stayed in the villages for certain periods during fieldwork, conducted observations, and reached key participants through local leaders. The ongoing legal dispute between the villagers and the mining company led some residents to hesitate about participating. However, to reflect the current situation comprehensively, all individuals who volunteered were interviewed. Considering the stage of the displacement process and the prevailing atmosphere in the field, the expression of positive experiences was limited, and participants’ narratives mainly focused on the difficulties they faced. To minimize potential bias and enhance transparency, reflexivity—which enables the researcher to be aware of their own positionality and perspective and to assess the potential influence of these on the research process [51]—was actively applied at all stages, from data collection to analysis and interpretation.
Semi-structured in-depth interviews were conducted face-to-face. The functionality of the interview questions was tested by conducting two pilot interviews and obtaining expert opinions. Before starting the interviews, the participants were informed about the purpose and scope of the research, stating that the interviews would be recorded, and participants’ written consent was obtained. Follow-up interviews were conducted to fill in the gaps identified in the first interviews, and each participant was interviewed at least twice to deepen the narratives. Code names such as P1, P2, and so on were assigned to the participants to protect their identities. The data collection process was terminated when information power was considered attained [52]. Braun and Clarke (2021) state that conducting 6 to 16 interviews may be sufficient to achieve information power in thematic analysis [52]. The present study interviewed 18 participants.

4.4. Data Analysis

The data collected were analyzed using MAXQDA 2024 software, following Braun and Clarke’s (2019) reflexive thematic analysis approach [53]. MAXQDA was employed as an organizational tool to manage the dataset, facilitate systematic coding, and visually explore relationships between codes and themes. While the software supported the structuring and efficient retrieval of coded segments, all coding and theme development were carried out through the researchers’ iterative and interpretative engagement with the data. The process began with multiple readings of the interview transcripts and observation notes in MAXQDA to gain an in-depth understanding and develop familiarity with the data (i). The coding process was then initiated using MAXQDA 2024, and (ii) preliminary codes were generated, such as “water pollution,” “outmigration from villages,” and “loss of livelihoods’’. In the third step, (iii) potential themes were developed, such as “mining-induced environmental degradation” and “mining-induced displacement.” These were subsequently (iv) reviewed, (v) defined, and named in their final form as presented in the figures. Finally, the reflexive thematic analysis was completed by visualizing the findings in MAXQDA 24 through hierarchical code–subcode models and code relationship models, as shown in Figure 1, Figure 2, Figure 3, Figure 4 and Figure 5, resulting in the final version of the research report (vi). Dashed lines indicate the co-occurrence of subcodes, while line thickness represents the frequency of code overlap [54]. In addition, based on the findings, the ecosocial work intervention needs related to mining-induced environmental degradation and displacement were visualized at the micro, mezzo, and macro levels in Figure 6.

5. Findings

5.1. Reflections on the Impact of Mining Activities on the Villages’ Natural Environment

The theme that emerged in line with the first research question (RQ1) is related to the environmental degradation resulting from mines in villages. Mining activities have a significant effect on all elements of the ecosystem, including the degradation of natural land and aquatic ecosystems and water and air pollution. Air pollution is a salient environmental degradation problem in both villages, which are located in the immediate vicinity of the mining sites, due to dynamite explosions, coal dust produced during mining activities, and combustion events in the waste sites after mining (Figure 1).
“You can’t open your eyes in the summer; it is like Noah’s flood of dust. It is also harmful to health. You don’t have anything to sow.”
(P7)
“When the coal meets oxygen, it starts to burn… Since the mine is located in the north, it (coal dust) comes into the village with the wind. Dust, smoke, smell… There’s no place untouched by the dust. It becomes unbearable. It’s like poison…”
(P15)
Land degradation is one of the main environmental problems caused by mining activities in Deniş and Eğnez, threatening the environmental balance and livelihoods of rural communities. Primary examples include loss of fertile agricultural lands, the deterioration of natural roads, and landslides and collapses.
“Our land was mined and collapsed. We had wells in it; we had a lot of water. We had a beautiful garden in our field. We had a very good life. When the mine took over, our fields were restricted.”
(P18)
“The olive field collapsed into it… A sinkhole has formed… The mine gets coal from here. Below it was a sinkhole. You would think there’s an earthquake. Dynamite explodes from under it like this. Day and night. It’s like an earthquake is happening.”
(P5)
Water degradation also significantly impacts both villages (Figure 1). Mining activities require intensive use of water in processes such as coal washing, processing, and dust suppression, with waste landfills polluting groundwater and deteriorating water resources. In addition, explosives used to reach mineral deposits destroy natural waterways and divert them. The mining facilities established in the river and stream beds and the waste they leave have caused severe water insecurity in villages. The drying up of natural fountains, streams, and ponds has not only threatened the ecosystem but also negatively affected the livelihoods of the villagers.
“Because of the mine, dynamite is used at work. After that, there are slips. The water bed is deteriorating. The water is going elsewhere… Our livelihood has been restricted because there is no water.”
(P18)
“They dried up. There were two streams, and both dried up. They ended up inside the mining site. It used to be beautiful. Agriculture is over here. Farming no longer exists.”
(P9)
Evidently, air, soil, water, and biosphere degradation influence and exacerbate each other, as seen in Figure 1. Moreover, the deterioration of the village ecosystem threatens the food security of the villagers.
“Young people used to dip their baskets like this into the stream. The water would flow and the basket would fill with fish. You could just pick them up and eat them. Those fish were so delicious.”
(P6)
“There were a lot of live fish. We used to fish. There were carps. There were a lot of fish in it.”
(P9)
Another type of environmental degradation caused by mining activities in the villages is biosphere degradation. This type of degradation has also led to a decrease in the diversity of animals in the villages. This situation can be expressed both as an ecological problem and a threat to the livelihood of the villagers because the mine’s complete removal of natural vegetation did not leave any grazing land for the animals.
“There is damage to the water and everything. There is no place to herd animals now. There is nothing that has not been harmed. There were 50–60 cattle and goats in this village. There’s none left.”
(P2)
“I had 17 beehives this year in this mining area across the street. Yesterday, I went and looked and only 2 hives are left. Most of my bees have died, and have turned to dust.”
(P14)
“Dust has effects. Where will the bee land? Every collar is dusty. If it lands on the crown of the flower, there is dust; if it lands on the branch of the pine, there is dust. You go out to see the bee, but there are no bees here because of the dust.”
(P8)
The chemicals and coal dust contained in the dynamites used in the mines cause the plants to burn during the flowering period, impacting areas beyond the mine site, which damaged olive groves and other forest areas. When we visited the villagers’ olive groves, the leaves of the trees, olives, and other fruits were all covered with dust.
“They’re drying up badly. The olives have no joy.”
(P16)
“The fruit doesn’t survive because of this dust. You know, when the trees are in bloom—right at that moment—it releases some dust, ruins them, burns the blossoms… And when does it stick to these trees? It just dries them out.”
(P6)
Moreover, following the expropriation of forested areas and villagers’ agricultural lands, the private companies operating the mining sites demanded that the villagers cut down olive groves and other trees, which would ultimately be destroyed during excavation.
“We even cut the olive trees. We looked at it; it is going to the threshing (excavation) now. It will remain under the ground… I have a tree over there now. It’s maybe 700 or 800 years old over there. My father didn’t know when it was planted. My grandfather didn’t know when it was plated either. I mean, the tree trunk is about 2 m wide.”
(P12)
“I was glad when the state said that cutting down olive trees is prohibited. But what’s left anyway? They said it’s forbidden to cut them. The company doesn’t do the cutting itself. They have people cutting down the olive trees they planted themselves. Then it avoids taking any responsibility.”
(P16)
Figure 1. Hierarchical code–subcode and code relationships under the theme “Interpreting the impacts of mining in the context of the ecosystems of villages”.
Figure 1. Hierarchical code–subcode and code relationships under the theme “Interpreting the impacts of mining in the context of the ecosystems of villages”.
Sustainability 17 07757 g001

5.2. Societal Repercussions of Mining-Induced Environmental Degradation on Villages Prior to Displacement

In line with the second research question (RQ2) of this study, the effects of mining-induced environmental degradation on the demographic structure of the villages were examined. In this context, the villagers stated that even before the decision of displacement due to mining activities had been taken, people had started migrating from the villages mainly because of the difficulties experienced living in the villages. Migration from the villages is closely related to inefficient agriculture due to environmental degradation and the lack of alternative means of livelihood. During the field research, the sparse population in both villages attracted particular attention, with significantly fewer young people and children in the villages.
“It used to be crowded. Everything was good in the neighborhood. There are no people left. Everything is broken. There is nothing left. We don’t have any houses left. We don’t have any fields left.”
(P5)
“It was pretty crowded… Everyone started to migrate… Because we can’t farm.”
(P9)
Drying of water resources, deterioration of fields and agricultural lands, and destruction of forests and olive groves due to mining activities are among the main reasons for the cessation of agricultural production in villages, rendering some agricultural activities impossible. The yields of the remaining olive groves have significantly decreased due to coal dust and subsidence of the land, posing a threat to both the livelihoods and food security of the villagers.
“As long as there are collapses, for example, we can’t enter our farmland. It damages trees. We can’t get a yield from olives.”
(P4)
“Because of the dust, the plant burns. Nothing grows. Whatever you plant doesn’t grow… During the olive harvest, you can’t even see through the dust in the air. We keep wiping it off, but the dust keeps falling.”
(P7)
Before the adverse effects of the mining activities on agricultural production, the villagers could largely meet their food needs and earn income from what they produced, ensuring the food security and livelihood of their households. However, mining activities have undermined this way of life.
“Back then, we were farming. Farming is over now. Everything used to be in abundance in those days. Now, there’s no planting, no harvesting. It doesn’t work anyway because of the dust. Making a living has become much harder.”
(P7)
“It was very efficient… We had a field over there on 24 acres. We used to plant wheat for 1 year and not buy any flour for 2 years. Two years was enough.”
(P8)
Due to environmental degradation and migration, agricultural production and livestock farming have halted in the villages of Deniş and Eğnez. However, despite losing their livelihoods because of the mines, the villagers were not provided with sufficient opportunities or priority for employment in the mining sector.
“…I applied. Because of the expropriation. I said, hire me. Since you have expropriated my land, hire me. Do you know what they said? Show success in the exams. They just said, good luck.”
(P10)
“They need to employ someone who is in need here. I’m the one bearing the dust here. This was a mistake from the start. If a protocol had been signed at the notary with the company, then we would have had something in hand, an opportunity. They would have had to give a job to every citizen in this village who said, ‘I will work.’”
(P4)
Another example of the economic losses caused by mining activities within the context of this research is the damage to houses. In particular, the progressive underground work in Eğnez under the settlement area has caused cracks to appear in the villagers’ houses.
“There are a lot of cracks in the houses. I evacuated the house, for example.”
(P4)
“We are in a difficult situation. Some are afraid that the houses will collapse. There are a lot of cracks in some people’s houses, because of the mine. They’re getting coal out of it.”
(P5)
Mining has also negatively impacted their well-being. For instance, the villagers start their day with the sound of dynamite. Food contamination and air pollution are directly related to the deterioration in well-being. Moreover, the safety of villagers is jeopardized by the damage to houses and fields caused by landslides.
“Part of the olive grove slid down the slope. Some of it is still intact. I still go there and harvest olives. We asked the mining company about it. They said, ‘We do not accept any responsibility. If it collapses or anything happens, you can only harvest from the stable part’. So now, we only pick olives from the part that’s still safe…”
(P1)
“We go to the fields to harvest olives, but we’re afraid we might fall into a crack. Not going isn’t an option either. Our husbands go to plow the land, and we don’t know if they’ll come back or not—nothing is certain.”
(P5)
Furthermore, before the displacement process, that is, during the negotiation process with the companies, significant polarizations and new disputes emerged among the villagers. During the field research, these profound social divisions resulting from mining activities and displacement processes were evident in both villages. These divisions underscore the complex social consequences of mining-induced displacement.
“We’re split in two. After that, there were fights, everything happened…”
(P13)
“I mean, we are ignorant. The village was divided into two, some bought a house and some did not. We talked a lot at the time, but people talked like that, someone talked like that…”
(P15)
Figure 2. Hierarchical code–subcode and code relationships under the theme “Before displacement: The social and economic hardships caused by the mine in the village”.
Figure 2. Hierarchical code–subcode and code relationships under the theme “Before displacement: The social and economic hardships caused by the mine in the village”.
Sustainability 17 07757 g002

5.3. “Is It Easy to Leave Your Ancestral Homeland?”: Material and Spiritual Losses

In this study, two themes emerged in line with the third research question (RQ3). The first theme is related to the ecological grief of the villagers for the loss of their village and therefore the attachment they developed to their village and their physical environment. The second theme is related to other material and moral losses experienced by the villagers due to mining.

5.3.1. Place Attachment and Ecological Grief in the Context of Displacement

The first theme is related to the strong sense of place that stands out in the participants’ narratives (Figure 3). Participants stated that they had deep ties to their villages, referring to the lives they spent there, the importance of their ancestral lands, and the emotional bond they felt with their villages. This deep attachment to place indicates that the village represents not only a physical location but also a deeply embedded part of their identity, ancestry, and history. Despite the environmental and social problems caused by mining, they struggled to leave their villages.
“This (land) is from our grandfather and grandmother. Children hold a branch, dig the soil, do something. They don’t know the value of the land; the land is invaluable.”
(P8)
“Is it easy to leave your parents’ homeland?”
(P3)
“Your childhood was here… I know it, I’ve lived it here. Turkey is my homeland, yes, but Eğnez is like my second homeland. I was born here, lived here, and spent my youth here.”
(P17)
Moreover, displacement results in the loss of mosques and cemeteries, which villagers are hesitant to move, especially owing to religious reasons, despite being granted permission to do so.
“Our cemetery will remain. Where could we even take it? It’s heartbreaking, deeply painful. So much pain. So much pain…”
(P1)
“My soul is here, and my funeral will be here. The graves are full of our ancestors. If you go into the city, when you come here, when you enter the house, we say ‘Oh well!’”
(P5)
This study reveals an interaction between eco-grief, eco-spirituality, and displacement. Specifically, this eco-grief experienced by the villagers is often intertwined with beliefs and practices that emphasize the interconnectedness of man and nature, that is, eco-spirituality. Participants expressed the emotional hardships they experienced due to mining-induced environmental degradation and displacement, often referring to the connection they established with their natural environment. This situation became particularly evident when participants spoke about the emotional distress, they experienced upon having to cut down their olive trees.
“How will my hand reach out and cut the olive trees? I sat down with my wife and said [to my tree], ‘Well, I watered you a lot, but this is fate’. My wife started crying, but what could I do? We cut it.”
(P10)
Figure 3. Hierarchical code–subcode and code relationships under the theme “When thinking about the post-displacement period…”.
Figure 3. Hierarchical code–subcode and code relationships under the theme “When thinking about the post-displacement period…”.
Sustainability 17 07757 g003

5.3.2. Villagers’ Material Losses and Loss of Social Support Networks in the Context of Displacement

Mining-induced displacement is closely related to the social and economic effects that follow the dispossession of individuals. This study identified psychosocial difficulties related to displacement. The villagers understood the significance of the loss of their social support networks (Figure 4).
“There are 55 people’s homes—that’s the saddest part. Behind that, there are 55 to 60 households. These households are left outside… So, what will those people do? No matter what, they are my fellow villagers. They’ve known me for years—they know my ways, my habits, my character, they know everything. I can’t be friends with someone new just like that. It would take 20 years to build that kind of bond.”
(P15)
Moreover, older villagers may be unable to grow old in their villages. The resettlement houses being built for older villagers are significantly more expensive than the expropriated homes they once owned, and many of them cannot take on new debt. Consequently, villagers may be forced into long-term debt that lasts up to 20 years.
“Now I can’t get a house there. I’ll have to go into debt. I’m already 61 years old. How am I supposed to save that money and pay it off at this age?”
(P1)
“You see, this is what really upsets me. Every day I go to bed and wake up thinking: where will I go, where will I stay? Where will I find a place to live? That’s my constant worry. What can I do? This anxiety even comes into my dreams.”
(P7)
Villagers also face financial losses. Those at risk of being homeless, landless, and without olive trees (dispossession) are compensated with only one house, which they will have to pay for nearly 20 years. The compensation paid for their houses, fields, and olive groves is insufficient to afford a new house in the relocated village. Therefore, this situation creates new vulnerabilities for the villagers. The fears about the displacement process for older and lonely individuals, especially single older women, which were not present in their verbal expressions, were clearly observed during the research.
“We didn’t ask for money—if only they had built houses like our own. We didn’t want money… Even my children and I are in debt now.”
(P5)
“Rent…. They say rents are also very expensive… I receive an old-age pension. Should I pay rent with it or take care of myself?”
(P7)
“They bought my house for 300 thousand liras, and now the new house will be around one million. How am I supposed to pay one million? I have no pension, no job, no income.”
(P14)
As the findings reveal, ownership of land is a crucial factor that protects the villagers against food insecurity, which is now likely to grow because they will lose their land, houses, and barns but will be compensated with only houses in the newly built villages.
“Everything is so expensive now. But here, we have our garden, and we make our own cheese and yogurt. The hens lay five eggs a day, and that’s enough.”
(P16)
“Now we grow at least onions and garlic to eat ourselves. How are we going to do it there? We have quince in our courtyard, we have everything. What are we going to do there?”
(P6)
Figure 4. Hierarchical code–subcode and code relationships under the theme “Displacement: Exploring material and emotional losses”.
Figure 4. Hierarchical code–subcode and code relationships under the theme “Displacement: Exploring material and emotional losses”.
Sustainability 17 07757 g004

5.4. Exploring the Process of Mining-Induced Displacement and Resettlement from the Perspective of the Villagers

The final theme emerging in line with the fourth research question (RQ4) is related to the processes of displacement and resettlement. This study considers ecological injustice—power imbalances that perpetuate injustice to both the natural environment and vulnerable populations—especially prominent in the displacement and resettlement processes. Therefore, the inability of the villagers to benefit from mining, the lack of adequate consideration of the needs and interests of the villagers, and power imbalances between the villagers and the mining companies are considered ecological injustices (Figure 5).
“If I was born and raised on that land and now, I’m paying the price for it, then of course I have the right to benefit from it.”
(P9)
“They sell coal under the name of this village. But no one gives anything to the village.”
(P17)
In addition, the problem of injustice and power imbalance has led to the exclusion of villagers from decision-making processes. Although they were directly affected by the expropriation process, their access to accurate information about the process was very limited.
“… Why is this drilling (drilling for the mine) being installed? You know, what are you doing here? They set it up by drilling boreholes. But we don’t know why. Are they looking for water, or are they looking for coal? They don’t explain. They don’t explain this to the villagers. They say we are looking for water. They give an evasive answer. They’re passing it off.”
(P18)
In addition, property owners do not seek the consent of villagers in the expropriation process. Meanwhile, the villagers do not have the right to object to relinquishing their property due to the Expropriation Law (1983). They can only apply for legal recourse regarding the level of compensation for their property. However, even if they file a lawsuit, the compensation paid does not change or is only slightly increased.
“They passed a law from the Council of Ministers in our mining area. You can’t stand against the decision in the parliament…”
(P4)
“I didn’t have a chance to say no. The court process continued. The company said you can also file a complaint. ‘The court channel is open, but I am confiscating the field’, he said. He went into the field, and we couldn’t intervene… You can’t interfere at all… He doesn’t even ask you…”
(P12)
Villagers reported struggling to navigate court processes, with most giving up on litigation due to a lack of familiarity with the legal processes, insufficient resources to hire lawyers, and long-drawn-out legal processes. Moreover, the long bureaucratic procedures involved in the relocation and resettlement processes have exacerbated the situation for the villagers.
“The company hired 5 lawyers for you and sued you. What are you going to do? You don’t have any lawyers…”
(P12)
“It takes a long time. Now the district court has concluded. The local court gave us a value, and they paid our money. We did not accept those values; we appealed. We don’t know what will come out in the appeal, and from there, it will still go all the way to the Supreme Court.”
(P14)
This study highlights the need to build communities for villagers, who lack a common strategy against mining-induced displacement. Their inability to come together and attract public attention has prevented their voices from being heard.
“She didn’t resist, in our village, my daughter didn’t resist…”
(P7)
“… How are you going to put your foot down, girl? When there is no unity…”
(P13)
Figure 5. Hierarchical code–subcode and code relationships under the theme “Considering the displacement and resettlement process: The helplessness of the village community”.
Figure 5. Hierarchical code–subcode and code relationships under the theme “Considering the displacement and resettlement process: The helplessness of the village community”.
Sustainability 17 07757 g005

6. Discussion

This study assessed mining-induced environmental degradation and displacement from the perspective of two Turkish villages currently experiencing these issues. The findings highlight the multidimensional adverse impacts of mining activities in rural areas. The research reveals the connection between mining operations and deforestation, land degradation, biodiversity loss, depletion of natural resources, and air, soil, and water pollution [9,40,43,44], thereby showing how these activities threaten the livelihoods of rural communities in particular [7,18,55]. As ecosocial work emphasizes, this relationship can be interpreted as evidence that environmental sustainability and social well-being are deeply interconnected [24,26]. These challenges may be seen as an opportunity for ecosocial practitioners to develop interventions that promote the sustainable livelihoods of individuals and, by extension, communities.
The way mining activities harm farmers’ natural and human capital, disrupting the ability of rural households to sustain their lives [11,18], and exacerbate existing vulnerabilities by causing displacement [56], is closely related to the notion of ecological justice, which lies at the core of ecosocial work. Ecological justice highlights that those most affected by environmental degradation are often communities left vulnerable due to structural inequalities and limited participation in decision-making processes [57,58]. As this research shows, rural communities dependent on common lands and with limited power to defend their rights are disproportionately impacted by mining-related environmental destruction and displacement [6,59]. Ecosocial work frames these injustices not only through a human rights lens but also through a holistic conception of justice—ecological justice—which considers both human and ecosystem well-being [60]. In this context, ecosocial practitioners are responsible not only for supporting rights-based advocacy and developing interventions to build the resilience of rural communities but also for protecting the integrity and rights of the natural environment.
Ecosocial work acknowledges that environmental degradation is a form of injustice rooted in structural inequalities [61,62]. Thus, anti-oppressive intervention is a vital dimension of ecosocial practice [32,34]. As demonstrated by this study, land is often purchased after the discovery of mineral reserves; however, when deemed necessary, the state resorts to expropriation on the grounds of public interest without the consent of landowners [63]. Such land acquisition processes force local communities to abandon their ancestral lands, resulting in the loss of homes, property, and traditional livelihoods [64]. Displaced individuals and communities often face multidimensional problems such as land loss, lack of access to resources, housing and income insecurity, weakening of social support networks, food insecurity, rights violations, and spiritual hardship [16,47]. Therefore, it is essential for ecosocial workers to work in solidarity with individuals, groups, and communities to expose oppressive structures, strengthen rights-based advocacy, and support active community participation in decision-making processes.
Unjust distribution of benefits from mining projects and depriving communities of adequate compensation or fair resettlement deepens the problem of injustice [65]. As this research also demonstrates, merely paying the value of land and houses is not sufficient for communities displaced by mining [66]. Compensation should also be provided for other losses, such as cultural values that may be lost during displacement. However, in developing countries, mining-related displacement often results in inadequate compensation. This inadequacy and injustice primarily stem from the lack of negotiation with displaced and resettled people [16,67,68]. As is the case in this study, mining companies often exclude rural communities from decision-making processes [69]. This situation should be seen by ecosocial practitioners not only as a problem area but also as an intervention space requiring a political stance against structural inequalities, a strengthening of rights-based advocacy, and leadership for justice [60]. Additionally, ecosocial workers may collaborate with local communities in efforts such as environmental advocacy, community-based initiatives, voluntary resource mobilization, and coalition building to help prevent mining-related environmental degradation [70].
As the present research also shows, population decline and intra-community conflicts resulting from mining activities over time contribute to the weakening of social bonds [8,71]. Especially after displacement, communities experience the loss of social relations and sacred places, which in many cases is considered more significant than material losses [16,18,72]. Therefore, the most devastating risk in mining-induced displacement is community disintegration caused by the loss of informal support networks that sustain livelihoods [73]. Furthermore, for individuals with a strong attachment to place, relocation to another region is often undesirable. Environment-transforming activities like mining may be perceived as threats due to the deep emotional and spiritual ties local populations have with their surroundings [74]. For them, place transcends the physical realm and represents a shared space of existence where the natural environment, social relations, and spiritual meanings converge [45].
Mining companies, in addition to the physical destruction they cause, also negatively affect the cultural and spiritual relationships that communities have with the land [8] (Mactaggart et al., 2016). As this study illustrates, rural communities’ ecospiritual bonds with the land are damaged in the face of environmental degradation and displacement. This has brought ecological grief to the forefront. As an emotional response to the loss of cherished places, species, and ecosystems, ecological grief may lead to feelings of despair, fear, and identity loss [75]. However, ecological mourning is not an emotion that should be suppressed. On the contrary, it can foster resilience and serve as a foundation for meaningful action. Such transformation can be enabled through professional support and collective action [76]. In this context, ecosocial work offers a framework for integrating eco-spiritual connections into social work interventions. This approach can serve as a foundation for advocating not only for human rights but also for the rights of nature [77].

7. Conclusions

This study reveals that in cases of mining-induced environmental degradation and displacement in rural areas, there is a critical need for multidimensional ecosocial work interventions at the micro, mezzo, and macro levels. At the micro level, psychosocial support services are essential to help individuals and families cope with the emotional impacts of mining-related environmental degradation and displacement, such as trauma, grief, and ecological loss. These interventions should take into account individuals’ spiritual connections with nature. Additionally, the destruction of villagers’ livelihoods has led to increased economic vulnerability, making it necessary to co-develop alternative and sustainable livelihood strategies with local communities. At the mezzo level, developing collaboration-based interventions with organizations focused on environmental sustainability has emerged as a key responsibility for ecosocial workers. In this context, supporting capacity- and skill-building processes among diverse and disadvantaged groups stands out as a crucial area of mezzo-level intervention. At the macro level, political and societal interventions are needed to address structural inequalities and to strengthen the collective rights of rural communities. Given that displacement weakens social ties, rebuilding community relations through grassroots organizing, collective action, and legal advocacy is vital—not only to make rights-based demands visible but also to support the restoration of disrupted community cohesion. However, these levels are not separated by rigid boundaries; rather, the interventions are often intertwined and mutually reinforcing. As illustrated in Figure 6, what lies at the intersection of all levels is the advocacy for ecological justice, which acknowledges the interdependence of human well-being and environmental sustainability, and reflects a commitment to justice for all living beings.
Figure 6. Ecosocial work interventions addressing mining-induced environmental degradation and displacement.
Figure 6. Ecosocial work interventions addressing mining-induced environmental degradation and displacement.
Sustainability 17 07757 g006
An important limitation of this study was the significant migration of the younger population to urban centers due to mining-induced environmental degradation, which made it difficult to reach them. Additionally, it was observed that some villagers were hesitant to participate in the study due to fear of private mining companies. Future research could explore the lives of displaced villagers in their new settlements after the relocation process is completed, in order to more comprehensively examine the social, economic, and emotional impacts of resettlement. In this context, longitudinal studies and research focusing on the psychological dimensions, which could not be addressed in depth in the present study, are especially needed.

Author Contributions

Conceptualization, M.A. and F.Y.; methodology, M.A.; investigation, M.A.; data analysis, M.A.; writing—original draft preparation, M.A.; writing—review and editing, M.A. and F.Y.; supervision, F.Y. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Ethical approval for the present study was obtained from the Ethics Committee of Ankara University on 4 March 2024, with the decision number 56786525-050.04.04.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

Due to confidentiality and privacy concerns, the data supporting this study are not available.

Acknowledgments

This article was compiled from the doctoral thesis of the first author at the Department of Social Work, Institute of Health Sciences, Ankara University. It was compiled under the supervision of the second author.

Conflicts of Interest

The authors declare no competing financial or personal interests related to this work.

References

  1. Morley, J.; Buchanan, G.; Mitchard, E.T.A.; Keane, A. Quasi-experimental analysis of new mining developments as a driver of deforestation in Zambia. Sci. Rep. 2022, 12, 18252. [Google Scholar] [CrossRef] [Scilit] [PubMed]
  2. Nguyen, N.; Boruff, B.; Tonts, M. Fool’s Gold: Understanding Social, Economic and Environmental Impacts from Gold Mining in Quang Nam Province, Vietnam. Sustainability 2018, 10, 1355. [Google Scholar] [CrossRef] [Scilit]
  3. Brown, D.; Bégou, B.; Clement, F.; Coolsaet, B.; Darmet, L.; Gingembre, M.; Harmáčková, Z.V.; Martin, A.; Nohlová, B.; Barnaud, C. Conceptualising rural environmental justice in Europe in an age of climate-influenced landscape transformations. J. Rural. Stud. 2024, 110, 103371. [Google Scholar] [CrossRef] [Scilit]
  4. Annor, F.; Annor, S.; Abdul-Nasiru, I. “In my own land, I am treated like a foreigner”: Mining-induced challenges and psychological distress among farmers in Ghanaian mining communities. Soc. Nat. Resour. 2024, 37, 1359–1377. [Google Scholar] [CrossRef] [Scilit]
  5. Hota, P.; Behera, B. Opencast coal mining and sustainable local livelihoods in Odisha, India. Miner. Econ. 2016, 29, 1–13. [Google Scholar] [CrossRef] [Scilit]
  6. Oskarsson, P.; Krishnan, R.; Lahiri-Dutt, K. Living with coal in India: A temporal study of livelihood changes. Extr. Ind. Soc. 2024, 17, 101437. [Google Scholar] [CrossRef] [Scilit]
  7. Hinojosa, L. Change in rural livelihoods in the Andes: Do extractive industries make any difference? Community Dev. J. 2013, 48, 421–436. [Google Scholar] [CrossRef] [Scilit]
  8. Mactaggart, F.; McDermott, L.; Tynan, A.; Gericke, C. Examining health and well-being outcomes associated with mining activity in rural communities of high-income countries: A systematic review. Aust. J. Rural Health 2016, 24, 230–237. [Google Scholar] [CrossRef] [Scilit]
  9. Gençay, G.; Durkaya, B. What is meant by land-use change? Effects of mining activities on forest and climate change. Environ. Monit. Assess. 2023, 195, 778. [Google Scholar] [CrossRef] [Scilit]
  10. Takam Tiamgne, X.; Kalaba, F.K.; Nyirenda, V.R. Mining and socio-ecological systems: A systematic review of Sub-Saharan Africa. Resour. Policy 2022, 78, 102947. [Google Scholar] [CrossRef] [Scilit]
  11. Zhao, Q.; Niu, K. Blessings or curses?–The bittersweet impacts of the mining industry on rural livelihoods in China. J. Clean. Prod. 2023, 421, 138548. [Google Scholar] [CrossRef] [Scilit]
  12. Owen, J.R.; Kemp, D.; Lechner, A.M.; Ern, M.A.L.; Lèbre, É.; Mudd, G.M.; Macklin, M.G.; Saputra, M.R.U.; Witra, T.; Bebbington, A. Increasing mine waste will induce land cover change that results in ecological degradation and human displacement. J. Environ. Manag. 2024, 351, 119691. [Google Scholar] [CrossRef] [Scilit] [PubMed]
  13. Oware Twerefoo, P. Mining-induced displacement and resettlement policies and local people’s livelihoods in Ghana. Dev. Pract. 2021, 31, 816–827. [Google Scholar] [CrossRef] [Scilit]
  14. Mtero, F. Rural livelihoods, large-scale mining and agrarian change in Mapela, Limpopo, South Africa. Resour. Policy 2017, 53, 190–200. [Google Scholar] [CrossRef] [Scilit]
  15. Gukurume, S.; Tombindo, F. Mining-induced displacement and livelihood resilience: The case of Marange, Zimbabwe. Extr. Ind. Soc. 2023, 13, 101210. [Google Scholar] [CrossRef] [Scilit]
  16. Manduna, K. Extractive industries indigenisation, displacement and vulnerabilities: The case of Arda Transau, Zimbabwe. Extr. Ind. Soc. 2023, 14, 101223. [Google Scholar] [CrossRef] [Scilit]
  17. Khan, G.D.; Temocin, P. Human Right-based Understanding of Mining-Induced Displacement and Resettlement: A Review of the Literature and Synthesis. RAIS J. Soc. Sci. 2022, 6, 20–29. [Google Scholar]
  18. Ofori, R.; Takyi, S.A.; Amponsah, O.; Gagakuma, D. Mining-induced displacement and resettlement in Ghana: An assessment of the prospects and challenges in selected mining communities. Soc. Netw. Anal. Min. 2023, 13, 61. [Google Scholar] [CrossRef] [Scilit]
  19. Boetto, H.; Bowles, W.; Närhi, K.; Powers, M. Raising awareness of transformative ecosocial work: Participatory action research with Australian practitioners. Int. J. Soc. Welf. 2020, 29, 300–309. [Google Scholar] [CrossRef] [Scilit]
  20. Gray, M.; Coates, J. Changing values and valuing change: Toward an ecospiritual perspective in social work. Int. Soc. Work 2013, 56, 356–368. [Google Scholar] [CrossRef] [Scilit]
  21. Parra Ramajo, B.; Prat Bau, N. The Responsibilities of Social Work for Ecosocial Justice. Soc. Sci. 2024, 13, 589. [Google Scholar] [CrossRef] [Scilit]
  22. Powers, M.; Schmitz, C.; Beckwith Moritz, M. Preparing social workers for ecosocial work practice and community building. J. Community Pract. 2019, 27, 446–459. [Google Scholar] [CrossRef] [Scilit]
  23. Kvam, A.; Willett, J. “Mining is like a search and destroy mission”: The case of Silver City. J. Community Pract. 2019, 27, 388–403. [Google Scholar] [CrossRef] [Scilit]
  24. Nöjd, T.; Kannasoja, S.; Niemi, P.; Ranta-Tyrkkö, S.; Närhi, K. Ecosocial work among social welfare professionals in Finland: Key learnings for future practice. Int. J. Soc. Welf. 2024, 33, 732–744. [Google Scholar] [CrossRef] [Scilit]
  25. Boetto, H. A Transformative Eco-Social Model: Challenging Modernist Assumptions in Social Work. Br. J. Soc. Work 2016, 47, 48–67. [Google Scholar] [CrossRef] [Scilit]
  26. Boetto, H. Promoting sustainable development in the Australian Murray-Darling basin: Envisioning an EcoSocial work approach. Sustain. Dev. 2025, 33, 904–915. [Google Scholar] [CrossRef] [Scilit]
  27. Chang, E.; Sjöberg, S.; Turunen, P.; Rambaree, K. A call for ecosocial community work: Challenges and possibilities for ecosocial work in local neighbourhoods in Sweden. Eur. J. Soc. Work. 2025, 1–17. [Google Scholar] [CrossRef] [Scilit]
  28. Närhi, K.; Matthies, A.-L.; Stamm, I.; Hirvilammi, T. Social work practitioners’ views of ecosocial work. J. Soc. Work. 2025. [Google Scholar] [CrossRef] [Scilit]
  29. Matthies, A.; Peeters, J.; Hirvilammi, T.; Stamm, I. Ecosocial innovations enabling social work to promote new forms of sustainable economy. Int. J. Soc. Welf. 2020, 29, 378–389. [Google Scholar] [CrossRef] [Scilit]
  30. Närhi, K.; Matthies, A.-L. The ecosocial approach in social work as a framework for structural social work. Int. Soc. Work. 2018, 61, 490–502. [Google Scholar] [CrossRef] [Scilit]
  31. Boetto, H.; Bowles, W.; Ramsay, S.; Shephard, M.; Cordoba, P.S. Australian perspectives on environmental practice: A national survey with human service professionals. J. Soc. Work 2024, 24, 746–776. [Google Scholar] [CrossRef] [Scilit]
  32. Shackelford, A.; Rao, S.; Krings, A.; Frances, K. Abolitionism and Ecosocial Work: Towards Equity, Liberation and Environmental Justice. Br. J. Soc. Work 2024, 54, 1402–1419. [Google Scholar] [CrossRef] [Scilit]
  33. Ranta-Tyrkkö, S.; Forde, C.; Lievens, P. Introduction: Addressing the role of the social professions in the sustainability transition. In Teaching and Learning in Ecosocial Work: Concepts, Methods and Practice; Forde, C., Ranta-Tyrkkö, S., Lievens, P., Rambaree, K., Belchior-Rocha, H., Eds.; Springer Nature: Cham, Switzerland, 2024; pp. 17–37. [Google Scholar]
  34. Wang, P.; Altanbulag, A. A concern for eco-social sustainability: Background, concept, values, and perspectives of eco-social work. Cogent Soc. Sci. 2022, 8, 2093035. [Google Scholar] [CrossRef] [Scilit]
  35. Cashwell, S. Bringing Environmental Justice to the Practice Setting: Putting the Environment in Person-in-Environment. J. Hum. Rights Soc. Work 2024. [Google Scholar] [CrossRef] [Scilit]
  36. Teixeira, S.; Mathias, J.; Krings, A. The future of environmental social work: Looking to community initiatives for models of prevention. J. Community Pract. 2019, 27, 414–429. [Google Scholar] [CrossRef] [Scilit]
  37. Boone Barrera, E. Extractive Industries and Investor–State Arbitration: Enforcing Home Standards Abroad. Sustainability 2019, 11, 6963. [Google Scholar] [CrossRef] [Scilit]
  38. Jacka, J.K. The Anthropology of Mining: The Social and Environmental Impacts of Resource Extraction in the Mineral Age. Annu. Rev. Anthropol. 2018, 47, 61–77. [Google Scholar] [CrossRef] [Scilit]
  39. Christensen, M.; Christensen, C. From the Gezi Park Protests to the Akbelen Forest: Care in the Context of Democracy and Political Dissent. Environ. Commun. 2024, 18, 173–177. [Google Scholar] [CrossRef] [Scilit]
  40. Atmiş, E.; Yıldız, D.; Erdönmez, C. A different dimension in deforestation and forest degradation: Non-forestry uses of forests in Turkey. Land. Use Policy 2024, 139, 107086. [Google Scholar] [CrossRef] [Scilit]
  41. Elvan, O.D. The legal environmental risk analysis (LERA) sample of mining and the environment in Turkish legislation. Resour. Policy 2013, 38, 252–257. [Google Scholar] [CrossRef] [Scilit]
  42. Günşen, H.B.; Atmiş, E. Analysis of forest change and deforestation in Turkey. Int. For. Rev. 2019, 21, 182–194. [Google Scholar] [CrossRef] [Scilit]
  43. Arkoc, O.; Ucar, S.; Ozcan, C. Assessment of impact of coal mining on ground and surface waters in Tozaklı coal field, Kırklareli, northeast of Thrace, Turkey. Environ. Earth Sci. 2016, 75, 514. [Google Scholar] [CrossRef] [Scilit]
  44. Tozsin, G.; Öztaş, T. Plant nutrient contents and spatial distribution patterns of toxic element concentrations in mine site soils. Turk. J. Agric. For. 2023, 47, 124–131. [Google Scholar] [CrossRef] [Scilit]
  45. Askland, H.H. A dying village: Mining and the experiential condition of displacement. Extr. Ind. Soc. 2018, 5, 230–236. [Google Scholar] [CrossRef] [Scilit]
  46. Owen, J.R.; Kemp, D. Mining-induced displacement and resettlement: A critical appraisal. J. Clean. Prod. 2015, 87, 478–488. [Google Scholar] [CrossRef] [Scilit]
  47. Huang, Q.; Khan, G.D.; Yoshida, Y. Assessing Health and Dietary Issues of Households Displaced Due to the Aynak Copper Mine Project, Afghanistan. Extr. Ind. Soc. 2023, 15, 101299. [Google Scholar] [CrossRef] [Scilit]
  48. Official Gazette of the Republic of Türkiye. Law No. 3573 on the Improvement of Olive Cultivation and the Grafting of Wild Olives. Turkey. 1939. Available online: https://www.mevzuat.gov.tr/mevzuatmetin/1.3.3573.pdf (accessed on 14 August 2025).
  49. Official Gazette of the Republic of Türkiye. Law No. 2942 on Expropriation (as Amended by Law No. 4650). Türkiye. 1983. Available online: https://www.mevzuat.gov.tr/mevzuat?MevzuatNo=2942&MevzuatTur=1&MevzuatTertip=5 (accessed on 14 August 2025).
  50. Yıldırım, A.; Şimşek, H. Sosyal Bilimlerde Nitel Araştırma Yöntemleri, 11th ed.; Seçkin Yayıncılık: Ankara, Türkiye, 2018. [Google Scholar]
  51. Ide, Y.; Beddoe, L. Challenging perspectives: Reflexivity as a critical approach to qualitative social work research. Qual. Soc. Work 2024, 23, 725–740. [Google Scholar] [CrossRef] [Scilit]
  52. Braun, V.; Clarke, V. To saturate or not to saturate? Questioning data saturation as a useful concept for thematic analysis and sample-size rationales. Qual. Res. Sport Exerc. Health 2021, 13, 201–216. [Google Scholar] [CrossRef] [Scilit]
  53. Braun, V.; Clarke, V. Reflecting on reflexive thematic analysis. Qual. Res. Sport Exerc. Health 2019, 11, 589–597. [Google Scholar] [CrossRef] [Scilit]
  54. VERBI Software. MAXQDA 2018 Manual 2018. Available online: https://www.maxqda.com/download/manuals/MAX2018-Online-Manual-Complete-EN.pdf (accessed on 9 August 2025).
  55. Sosa, M.; Boelens, R.; Zwarteveen, M. The Influence of Large Mining: Restructuring Water Rights among Rural Communities in Apurimac, Peru. Hum. Organ. 2017, 76, 215–226. [Google Scholar] [CrossRef] [Scilit]
  56. Lèbre, É.; Stringer, M.; Svobodova, K.; Owen, J.R.; Kemp, D.; Côte, C.; Arratia-Solar, A.; Valenta, R.K. The social and environmental complexities of extracting energy transition metals. Nat. Commun. 2020, 11, 4823. [Google Scholar] [CrossRef] [Scilit] [PubMed]
  57. Gray, M.; Coates, J. Environmental ethics for social work: Social work’s responsibility to the non-human world. Int. J. Soc. Welf. 2012, 21, 239–247. [Google Scholar] [CrossRef] [Scilit]
  58. Gray, M.; Coates, J.; Hetheington, T. (Eds.) Introduction: Overview of the last ten years and typology of ESW. In Environmental Social Work; Routledge: London, UK, 2013; pp. 1–29. [Google Scholar]
  59. Matanzima, J. Displaced by the transition: The political ecology of climate change mitigation, displacements and Lithium extraction in Zimbabwe. Extr. Ind. Soc. 2024, 20, 101572. [Google Scholar] [CrossRef] [Scilit]
  60. Ramsay, S.; Boddy, J. Environmental social work: A concept analysis. Br. J. Soc. Work 2016, 47, 68–86. [Google Scholar] [CrossRef] [Scilit]
  61. Besthorn, F.H.; McMillen, D.P. The oppression of women and nature: Ecofeminism as a framework for an expanded ecological social work. Fam. Soc. J. Contemp. Soc. Serv. 2002, 83, 221–232. [Google Scholar] [CrossRef] [Scilit]
  62. Willett, J. Micro disasters: Expanding the social work conceptualization of disasters. Int. Soc. Work 2019, 62, 133–145. [Google Scholar] [CrossRef] [Scilit]
  63. Baddianaah, I.; Baatuuwie, B.N.; Adongo, R. Socio-demographic factors affecting artisanal and small-scale mining (galamsey) operations in Ghana. Heliyon 2022, 8, e09039. [Google Scholar] [CrossRef] [Scilit]
  64. Mondal, R.; Mistri, B. Impact of displacement on place attachment, landscape value and trust in the Sonepur–Bazari open cast coal mining area, Raniganj Coalfield, West Bengal. GeoJournal 2022, 87, 3187–3201. [Google Scholar] [CrossRef] [Scilit]
  65. Manduna, K. Are mining-induced displacement and resettlement losses compensable? Evidence and lessons from mining communities in Zimbabwe. Extr. Ind. Soc. 2023, 15, 101281. [Google Scholar] [CrossRef] [Scilit]
  66. Wilson, S.A. Mining-induced displacement and resettlement: The case of rutile mining communities in Sierra Leone. J. Sustain. Min. 2019, 18, 67–76. [Google Scholar] [CrossRef] [Scilit]
  67. Magazzino, C. The impact of conflicts in the mining industry: A case study of a gold mining dispute in Greece. Resour. Policy 2024, 97, 105292. [Google Scholar] [CrossRef] [Scilit]
  68. Opoku, C.B.; Kwofie, J.; Asirifi, M.A.P. Critical factors impacting psychosocial well-being of mining-induced displaced and resettled persons in Ghana. Extr. Ind. Soc. 2024, 19, 101499. [Google Scholar] [CrossRef] [Scilit]
  69. Huang, X.; Faysse, N.; Ren, X. A multi-stakeholder platform involving a mining company and neighbouring villages in China: Back to development issues. Resour. Policy 2017, 51, 243–250. [Google Scholar] [CrossRef] [Scilit]
  70. Androff, D.; Fike, C.; Rorke, J. Greening Social Work Education: Teaching Environmental Rights and Sustainability in Community Practice. J. Soc. Work Educ. 2017, 53, 399–413. [Google Scholar] [CrossRef] [Scilit]
  71. Bell, S.E. “There ain’t no bond in town like there used to be”: The destruction of social capital in the West Virginia Coalfields 1. Sociol. Forum 2009, 24, 631–657. [Google Scholar] [CrossRef] [Scilit]
  72. Khan, G.D.; Yoshida, Y.; Katayanagi, M.; Hotak, N.; Caro-Burnett, J. Mining-induced displacement and resettlement in Afghanistan’s Aynak mining community: Exploring the right to fair compensation. Resour. Policy 2021, 74, 102285. [Google Scholar] [CrossRef] [Scilit]
  73. Ghosh, D. Aspects of development: Voices from predisplacement site in Eastern India. Extr. Ind. Soc. 2024, 19, 101517. [Google Scholar] [CrossRef] [Scilit]
  74. Walker, I.; Leviston, Z.; Price, J.; Devine-Wright, P. Responses to a worsening environment: Relative deprivation mediates between place attachments and behaviour. Eur. J. Soc. Psychol. 2015, 45, 833–846. [Google Scholar] [CrossRef] [Scilit]
  75. Qiu, S.; Qiu, J. From individual resilience to collective response: Reframing ecological emotions as catalysts for holistic environmental engagement. Front. Psychol. 2024, 15, 1363418. [Google Scholar] [CrossRef] [Scilit]
  76. Ágoston, C.; Urbán, R.; Nagy, B.; Csaba, B.; Kőváry, Z.; Kovács, K.; Varga, A.; Dúll, A.; Mónus, F.; Shaw, C.A.; et al. The psychological consequences of the ecological crisis: Three new questionnaires to assess eco-anxiety, eco-guilt, and ecological grief. Clim. Risk Manag. 2022, 37, 100441. [Google Scholar] [CrossRef] [Scilit]
  77. Chigangaidze, R.K. The environment has rights: Eco-spiritual social work through ubuntu philosophy and Pachamama: A commentary. Int. Soc. Work 2023, 66, 1059–1063. [Google Scholar] [CrossRef] [Scilit]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Akıncı, M.; Yıldırım, F. Mining-Induced Environmental Degradation and Displacement in the Context of Ecosocial Work: A Qualitative Study in Rural Areas. Sustainability 2025, 17, 7757. https://doi.org/10.3390/su17177757

AMA Style

Akıncı M, Yıldırım F. Mining-Induced Environmental Degradation and Displacement in the Context of Ecosocial Work: A Qualitative Study in Rural Areas. Sustainability. 2025; 17(17):7757. https://doi.org/10.3390/su17177757

Chicago/Turabian Style

Akıncı, Merve, and Filiz Yıldırım. 2025. "Mining-Induced Environmental Degradation and Displacement in the Context of Ecosocial Work: A Qualitative Study in Rural Areas" Sustainability 17, no. 17: 7757. https://doi.org/10.3390/su17177757

APA Style

Akıncı, M., & Yıldırım, F. (2025). Mining-Induced Environmental Degradation and Displacement in the Context of Ecosocial Work: A Qualitative Study in Rural Areas. Sustainability, 17(17), 7757. https://doi.org/10.3390/su17177757

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop