Literature Analysis Empirical Literature review The study of environmental and sustainable issues in the mining industry has gained importance within the academic community during the last few years. There are several studies regarding the extensive interest on this topic which explore strategies of companies on sustainable issues (Sinding, 1999; Cowell et al., 1999; Warhurst and Noronha, 2000; Hilson and Murck, 2000; Warhurst, 2001; Hilson and Nayee, 2002; Newbold, 2006; Suppen et al., 2006; Van Zyl, 2007; Enríquez and Drummond, 2007; Mudd, 2010; Fonseca, 2010 and 2011; Dutta et al., 2012; Hassan and Ibrahim, 2012). A major argument against the mining sector contributing to sustainable development is that mineral resources are finite and non-renewable (Cowell et al., 1999) and therefore the opportunities for future generations to access these resources are reduced (WCED, 1987). Moreover, the main environmental disasters that have increased public concern over the last 40 years have mainly taken place in the mining and petroleum industries (Warhurst, 2001). Ghose (2003) has analyzed the environmental management plans in the small-scale mining industry in India. Evangelinos and Oku (2006) have examined the corporate environmental management of Greek mining companies and the process of gaining permission to operate. Berkel (2007) has defined an eco-efficiency framework for the Australian mining industry. Hilson and Murck (2000) point out that the mining industry can contribute to sustainable development by minimizing the environmental and social impacts throughout its lifecycle. Gibson (2000) suggests that any negative effect should be immediately remediated, which would improve the reputation of mining. And Barbara-Sánchez and Atienza-Sahuquillo (2010) suggest that environmental strategies focusing on energy conservation, waste reduction, pollution prevention, recycling and ecological product design lead to improvements in product quality, manufacturing cost reduction and entrance into new markets. Similarly, Driussi and Jansz (2006) state that some specific management practices such as environmental management systems, pollution prevention technologies and environmental training may assist companies to improve their accountability in relation to environmental issues. Other authors have studied the connections between environmental degradation and conflict, and have analyzed the relationships between environmental and social variables (resource scarcity, population growth, resource abundance, democracy, and poverty). They concluded that those countries undergoing important economic and political transitions (Esty et al., 1999), and those with limited economic and political resources (Timura, 2001), are more prone to internal violent conflicts. As Walton and Barnett (2008) state, environmental conflicts in developing countries are basically the result of unequal distribution of outcomes arising from environmental degradation and its related causes. Environmental issues have increasingly more influence on business strategies and therefore, in strategic decision-making (Rugman and Verbeke, 2000). Companies may seek only to comply with the law currently in force, or they may go further and adopt more proactive environmental practices that allow for sustainable competitive improvements (BarbaSánchez and Atienza-Sahuquillo, 2010). ENVIRONMENTAL CONFLICT A notion of conflict is arguably at the core of political ecology. Since then, political ecologists have continued to work on environment-related conflicts, broadening the scope of their enquiries through the range of actors, contexts, motives and “objects” as well as types of conflicts considered. Deploying a range of methods and conceptual frameworks, political ecologists are united by their commitment to offering critical perspectives on often taken-for-granted processes. Using multi-scalar, historically informed and culturally sensitive entitlement analyses, political ecology aims to complicate – if not overturn – simplistic narratives of environmental conflicts driven by “scarcity” or “greed”. Environmental conflict can be broadly understood as a social conflict relating to the environment. It can be a conflict over the environment, most notably in terms of access to and control over environmental resources (Ribot and Peluso 2003). These so-called “resource conflicts” are defined by Turner (2004: 863) as consisting of “social conflict (violent or nonviolent) associated with both struggles to gain access to natural resources and struggles resulting from the use of natural resources.” From a neo-Malthusian perspective, environmental conflicts also consist of conflicts resulting from environmental processes – especially resource scarcity supposedly putting strains on social relations – even if the conflict per se is not over those “scarce” environmental resources (Dalby 2002). A variant to this scarcity-driven argument is the so-called “resource curse”, according to which the exploitation of abundant resources in undiversified economic contexts results in high levels of large revenues and resource dependence that would increase vulnerability to conflicts by undermining the quality of institutions, exposing societies to economic shocks, and exacerbating tensions over the distribution of resource rents and more generally the costs and benefits of dominant resource sectors (Le Billon 2012). Geology of the Asosa region The major suture zone in the Southern Arabian–Nubian Shield has an oceanic affinity, containing sutures of meta-sediments of deep-sea marine sedimentary origins (trench sediments), volcanic rocks of calcalkaline (island-arc) origin and fragments of mafic to ultramafic rocks (ophiolites) of oceanic crustal origin. The sutures of former oceanic areas that have accreted to form the Arabian– Nubian Shield consist of linear schist belts, containing phyllitic to greenschist facies metasediments and meta-volcanics. The sutures in the accreted shield areas are the loci for major shear zones that commonly host gold deposits. The regional structural set-up of the western Ethiopian shield is shown by three phases of deformation-associated foliations, folding and lineation’s. The Assosa region is represented by the Kuluck shear zone . The area is also characterized by syn- and post-kinematic Neoproterozoic granitoid intrusions, Tertiary basalts and a lateritic cover (extensive over basaltic lavas). Important gold mineralization zones are hosted within quartz veins, schist units (amphibolite schist, quartz graphitic schist and quartzo-feldspathic sericite schist) and granitic gneiss. The ANS mineralization is dominated by orogenic gold, tantalum, niobium, tungsten, rare earth elements, Marble, uranium and tin. in the north of the region. Granitic gneiss samples also show anomalous gold (4–11 ppm), as do quartz feldspar biotite schist samples (3–9 ppm) and a quartz graphite schist sample (4 ppm). Analyzed stream sediment and soil samples also contain anomalous gold concentrations (up to 88 ppm and 4 ppm respectively). The source of the gold is thought to be the subvolcanic intrusions generated during subduction of oceanic crust at the trench, akin to mineralization in island-arc systems that we see today in more recent epithermal and porphyry type gold systems. In the north of the region, there is evidence for gold anomalies that correlate well with faults. These faults represent ridges relating to shear zone activity. Orogenic gold in veins concentrate in areas of transgressional shearing, strike-slip faulting and thrusting, as well as at margins and adjacent wall rocks associated with plutons. This suggests a structural control on the distribution of gold in this area. Goldbearing major faults of the ANS are interpreted to be the result of NW-directed compression forming N-trending sinistral transgressional faults and NE-trending thrust faults. Assosa lies within one such major north-trending sinistral deformation zone. The gold occurrences typically developed between about 650 Ma and 615 Ma, with gold-bearing quartzcarbonate veins commonly associated with late to post tectonic calc-alkaline diorite, granodiorite and granite intrusions emplaced at the end of the Nabitah orogeny (680–650 Ma). There are also anomalous zones at the edge of the basaltic plateau, which may relate to fluid development, migration and entrapment between different lithological units. The widespread geochemical anomaly associated with the mineralized schist units show that this is an extensive gold-bearing hydrothermal mineralizing system, supported by anomalous Cu, Fe, Ag, As, Se and Mo geochemistry. Due to the commonly observed coupled occurrence, the mobility of gold may also be controlled by the paragenesis of sulphides and other secondary minerals. Developing the ASM sector Ethiopia’s long history of artisanal mining spans three millennia. The gold deposits in Ethiopia’s rivers, for example, have been exploited for thousands of years by small scale miners. Today, artisanal and small scale mining (ASM) happens all around the country and still plays an extremely important role in Ethiopia. However, much artisanal mining activity remains informal, and historically the sector has not benefitted from much formal support or regulation from the Government. Developing and formalising the Artisanal and Small-Scale Mining sector has become a high priority both for Ethiopia’s Homegrown Reform Agenda and for the Ministry of Mines and Petroleum (MoMP). Significant reforms are underway to modernize artisanal and small scale mining, and transform it into a sustainable livelihood for its practitioners. These reforms will encourage responsible, inclusive small enterprises to engage safely and legally in the mining sector, and collaborate productively with large-scale mining enterprises. The reforms aim to increase ASM’s overall contribution to the Ethiopian economy, increase revenue collection, and create jobs. They also aim to make Ethiopia an increasingly attractive jurisdiction for large-scale investment and contribute to Ethiopia’s sustainable development(Artisanal and Small Scale Mining (ASM) in Ethiopia - MoMP). Ethiopia’s Artisanal, Special Small-Scale Mining National Strategy In order to accomplish these goals, Ethiopia has recently put in place a comprehensive Artisanal, Special Small-Scale Mining National Strategy. Its primary objective is to formalize the artisanal mining sector and promote responsible, inclusive and productive operations that contribute to sustainable development. In order to achieve this, the Government of Ethiopia has adopted a coordinated approach to deliver on the following key objectives: 1. Strengthen ASM governance so that it is an attractive and conducive jurisdiction for investment as part of the formal economy. Three aspects of good governance need to be strengthened; namely, law and regulation, structural management, and geosciences data. 2. Increase efficiency, productivity and competitiveness of local mineral producers at ASM level. This incorporates promoting access to capital, access to technology, and access to skilled labour. 3. Enhance value addition and maximise earnings by ensuring access to local processing facilities and markets and developing supplier and diversified businesses. 4. Foster an environmentally and socially responsible ASM sector that complies with appropriate environmental, community, health and safety standards. 5. Promote two important issues that crosscut in each of the other four objectives; namely, women’s fair participation and beneficiation in ASM and utilisation of indigenous knowledge. However, As artisanal mining increasingly requires digging or tunnelling, the environmental impact of artisanal mining is also on the increase. Unfortunately, few ASM miners are aware of the harmful effects of mining, which can cause deforestation (excessive tree felling), soil erosion and land degradation. In general, artisanal miners do not take any rehabilitative or restorative measures to ameliorate the environmental impacts caused by mining. The MoMP has taken steps to lessen the environmental impact of artisanal mining by providing a set of guidelines for artisanal miners, local communities surrounding artisanal mining sites and licensing authorities. Mining Legislation As a result of the political change that took place in 1991, a new economic policy has been introduced in the country. In the mining sector, the government has promulgated a new Mining Proclamation and Mining Income Tax Proclamation to encourage the participation of private capital in mineral prospecting, exploration and development activities. The new Mining and Mining Income Tax Proclamations were issued in June 1993. The Mining Regulations came into effect in April 1994. The Mining Proclamation No. 52/1993 and the Mining Income Tax Proclamation No. 53/1993 were amended in favor of investors in 1996. New proclamation is introduced in order to facilitate the market aspects of mining ‘Transaction of precious Minerals proclamation No…651’/2001. The Mining Operations Proclamation No. 678/2010 is further amended by Proclamation No. 1213/2020 which has come into effect as of 14th July 2020. This amendment has added two more situations in which no license may be granted or held in addition to the existing three, which are listed out by Article 11 (3) of Proclamation No. 678/2010. The new additions are: a non-citizen of Ethiopia will not be granted a license where such a person wishes to engage in “construction minerals excluding those used as raw materials and dimension stones such as sand, aggregate, selected materials, and others”. Similarly, a foreign investor who would like to engage in any placer mining operations is prohibited from obtaining or holding a license except where such a foreign investor “engage in large scale placer mining in partnership with a domestic investor holding a minimum of 25% share”. The amendment has deleted Article 51 of Proclamation No. 678/2010, which deals with “Rights and Obligations of the Holder of a Certificate of Professional Competence” and has replaced it with new provisions. Accordingly, the amended Article 51 (1) allows any Ethiopians or Foreign Nationals of Ethiopian Origin to engage in the provision of consultancy services in the mining sector, where they obtain the required competence certificate from the Ministry of Mines and Petroleum. Articles 51 (2) and (3) of the amendment allows any person (irrespective of their nationality) to engage in the mining sector for the provision of “technical services such as drilling, laboratory or residue stockpile separating services” and in the provision of “technical services in fieldwork such as health, camping, and catering services.” Finally, Article 82 of the amendment has added one provision in which it is provided so as “a mining license or mining agreement issued to a foreign investor or concluded with a foreign investor to mine construction minerals excluding those used as raw material and dimension stones such as sand, aggregate, selected materials, and others, including placer mining operation prior to the coming into effect of this [amendment] Proclamation to continue in force for the remaining period of their validity”. After the end of their validity period whether these licenses or the mining agreement will be renewed for a further period or not is to be treated as per the terms and conditions of Proclamation No. 1213/2020. Economic benefits Generally the mining sector in Ethiopia generates revenue from sales, taxes, royalty as well as generates foreign currency earnings and also saving of hard currency in substituting the imported mineral related inputs of the country. The mining service sector activities are also contributing for employment opportunity. In Ethiopia, over 80% of the population is engaged on Agriculture and related activities. The major export of the country also comes from the Agricultural sector. Even though the country is believed to have wide mineral potential, the contribution of the mining sector to the national economy has so far reached a maximum of 6%. The federal government has been collecting Royalty amount 48.5 Million Birr (4.4 Million USD) from the large scale production of gold every year for the last three years. The regional administration also collects Royalty from the small scale and artisanal production of precious minerals, industrial and construction materials. The total amount of Royalty collected by each region (nine regional states and two cities Administration) is in few tens of millions of Birr (up to three million US dollars). The amount of foreign currency earning is About 135 Million dollars every year for the last recent years from the sales of export of minerals such as gold, tantalite concentrate platinum, decorative dimension stones and gemstones. This export earning contributes up to 7-10 % of the total export foreign currency earnings of the country. According to information from the Ministry of finance and Economic development the contribution of the mining sector to the GDP before 1990’s was less than one percent; however, there is statistical worked out data from this ministry that the mining sector contributed 5.8% and 5.5% during the fiscal year 2007/8 and 2008/2009, respectively. (Ministry of Mines, 2009). Social Benefits Mineral sector employment opportunity is becoming significant for the local communities where there are mineral development activities in their near by areas, as well as for skilled and semi skilled citizens. The total estimated direct employment of skilled and unskilled human resource in the mineral sector is in hundreds of thousands of people of the country. This employment record is revealed in construction and industrial minerals quarries, open pit and underground gold mine, production of salts from brines and rock salts and the gemstone mining that the distribution of such activities are found all over the country. The formal artisanal mining activity also reduces the poverty level of millions daily life including 30 to 40 percent of the women participation. Roads, electric power from national grid and telecommunication infrastructures have been developed and/or upgraded due to the development of Gold, tantalum, salt and other major mining projects in different parts of the country. Different level of health service centers, schools as well as airstrips were built by the developers of the mine that provides service to the local community as well as the employees of the mining community. To some extent there is start to train local communities to engage in other form of business such as plantation of coffee and other trees, introducing agricultural activities (irrigation) where there had no such type of lifestyle in the area, small entrepreneurs engagement mainly providing services such as hotel, mini- markets, stationeries, etc to the Community, etc. (Ministry of Mines, 2009). Reforming the mining sector The Government of Ethiopia has set out a clear “Pathway to Prosperity” through its newest HomeGrown Economic Reform Agenda, enabling Ethiopia to reach the status of a middle-income country by 2030. Considerable progress has already been made. Double digit growth and over sixfold increase per capita during 2004-18 led to a 15 percentage points decline in the rate of poverty in Ethiopia (poverty headcount ratio of 39% of the population in 2004 to 24% of the population in 2018). A vital part of this ambitious agenda for the country is encouraging private sector investment, streamlining bureaucratic and regulatory procedures, updating policies, and building institutional capacity. This is especially true of the mining sector, which is a priority area for the reforms. Specific reforms for the mining sector that are currently underway are: Formalize and support artisanal and small-scale mining; Formalize and support artisanal and small-scale mining; Review gold pricing to reduce incentives for contraband trade; Address political and legal issues with local communities and incentivizing miners to engage and invest in local communities; Address technical and institutional barriers against large-scale mining projects; and Develop policies and institutional capacities to create a sustainable and inclusive mining sector with strengthened geological information and diversified product base with industrial input focus. Environmental impact assessment law Following the provisions of the environment policy, the Ethiopian government introduced the Environmental Impact Assessment Proclamation (Proclamation № 299 of 2002). The proclamation requires an EIA process for any planned development project or public policy which is likely to have a negative impact on the environment. With regard to development projects, the proclamation stipulates that no person shall commence implementation of a proposed project identified by directive as requiring EIA without first passing through environmental impact assessment process and obtaining authorization from the competent environmental agency (Art. 3(1)). In line with this, project proponents must undertake EIA and submit the report to the concerned environmental body, and, when implementing the project, fulfill the terms and conditions of the EIA authorization given to them (Art. 7). Moreover, the proclamation allows for the imposition of a fine between fifty-thousand and one hundred thousand birr on any project owner who commences implementation of a project without obtaining authorization from environmental agencies or who makes false presentation in the environmental impact assessment study report (Art. 18). Furthermore, the proclamation obliges licensing institutions, prior to issuing investment permits or operation license to projects, to ensure that the relevant environmental bodies have authorized the implementation of the projects (Art. 3). In addition, it requires such licensing institutions to suspend or cancel the permit or license they have issued for projects where the concerned environmental Policy Framework for EIA Until 1997, Ethiopia did not have a comprehensive environment policy as such. The Environmental Policy of Ethiopia was issued in1997 to provide overall guidance in the conservation and sustainable utilization of the country’s environmental resources in general. The overall objective of the environmental policy is to promote the sustainable social and economic development of the country through, inter alia, sustainable management and utilization of the natural resources of the country. Among the specific objectives the environmental policy seeks to achieve are ensuring the conservation, development and sustainable use of essential ecological processes and life support systems, biological diversity and renewable natural resources; and the empowerment and participation of the people in environmental management. The environmental policy lays the foundation for environmental impact assessment in the country. the environment policy stipulates the country’s policies regarding EIA. It provides for the enactment of a law which requires that an appropriate EIA and environmental audits be undertaken on private and state development projects; and the development of detailed technical guidelines that direct the undertaking of EIA and environmental audit in the various sectors. Furthermore, the environmental policy determines the scope and key elements of the EIA process. It states that EIA should consider not only physical and biological impacts, but also address social, socio-economic, political and cultural conditions; and those environmental audits should be undertaken at specified intervals during project implementation to ensure compliance with terms of EIA authorization. It also state that environmental impact statements should always include mitigation plans for environmental management problems and contingency plans incase of accidents; and that the EIA procedure should provide for an independent review and public comment on environmental impact statements before they are considered by decision-makers. While the environment policy provided the policy basis of EIA process in the country, it has one major limitation: it does not subject public instruments to the EIA requirement, Damtie, M. (2008). Occupational health and safety Small-scale mining is an important part of the social and economic infrastructure in many developing countries and should be accorded sufficient attention to ensure its continued contribution to local and national well-being. This contribution will not be fully realized until more attention is paid to improving the occupational health and safety of mineworkers and their communities. In several countries in Africa, Asia and Latin America, the small-scale production of gold and gemstones ranks in the top five of national production, yet small-scale mining is largely ignored as far as safety, health and the environment are concerned. Indeed, prevention measures for accidents or occupational safety, if they exist, are minimal and rarely enforced. Small-scale mining has a poor reputation for safety, but there is little data to support or rebut claims that it is inherently unsafe with high levels of fatal and disabling accidents. Rather, problems relating to occupational health are more serious and pervasive, touching all who work in and around smallscale mining and processing operations, and their families. As with most aspects of small-scale mining, occupational safety and health and environmental issues at the mine, at the processing plant and in the community are closely linked. Because the same people are often involved in both small-scale mining and processing, safety and health issues in these two parts of the mineral production process will be discussed together. Overshadowing them both, however, is the question of community health in the vicinity of smallscale mines, the poor state of which is frequently directly linked to the mining and processing activities. It is not possible to do other than highlight here this important issue as part of the overall social fabric of regions that are affected by smallscale mining. Mines and mining in Benishangul Gumuz Gold is produced in all the three zone administrations of Benishangul-Gumuz regional state. Except for Pawe woreda, the remaining 19 woredas are all gold producing. The areas that border Sudan and South Sudan, which include 9 of these 19 woredas, are where gold mining and trade in gold are actively taking place. Few people who pan for alluvial gold do so for more than six months at a time. Because the work is repetitive and only brings slow returns, it does not hold the attention of miners for long. Critical shortages and shortcomings of mining sites further deter long stays. For seasonal miners, agricultural seasons determined the time they can invest in mining. The physical and social structures of the mining operation also play a role, and this is where changes in present practices can be observed compared to studies conducted until the early 2010s. Two sites were visited in February 2020, Melahu in Sherkole woreda and Dulshatalo in Kurmuk woreda, and observations and accompanying interviews offer deeper insight into these practices. Similar to the mining sites in the Qeissan area, the two mining areas were located in poorly accessible areas without paved roads or telecommunication networks; electricity is only provided by generators. In Melahu, mining operations were subsequently largely manual. It was common for shafts of 40 m to be hand dug, with only a few miners having access to jackhammers that are powered by the generators.82 Transport was even more difficult than in Qeissan, given the absence of motorized vehicles and even pack animals; for example, a miner in Dulshatalo described how they must carry crushed gold ore on their shoulders for 40 minutes to reach the mills.83 But the existence of shafts also indicates a change in the social structure of mining sites. Sherkole woreda, for instance, is highly specialized in gold mining, with no significant farming activities in its 19 kebeles and children dropping out of school to enter into mining activities.84 With an overall population of about 25,000, each of the 19 administrative units has its own gold producer cooperative, licensed at the regional level by the mining agency, with a concession of 2 hectares of land for exploration and production.85 But family- and cooperative-based panning with the broad participation of women, children and elders has begun to give way to individual miners or groups of men digging shafts. Where there was only alluvial gold before, relatively easy to wash, depleting findings shifted the work to underground mines, a much more physically demanding task . Families washing gold together at the river are thus increasingly replaced by male-dominated mining sites. At the same time, no economic alternative arose for families thus disadvantaged and, as a consequence, not just the dependence on gold mining but also women’s dependence on income produced by males can be expected to increase The cooperatives were also intended to regulate operational details, such as the use of chemicals. When mercury was introduced around the mid-2000s, its use was only permitted for licensed cooperatives; it still remains illegal for individual artisanal miners to use chemicals in the washing process.86 Effectively, this cannot be enforced, however, due to a lack of monitoring capacities.87 The practice may have an even worse environmental impact than in the Sudanese mining areas, as much of the gold washing takes place in running water, such as Tumet river in Melahu, a tributary of the Blue Nile.88 In fact, a goldwasher in Melahu stated that they acquired mercury from Sudan, thereby bypassing regulatory systems in Ethiopia.89 Reference Tauli Corpuz, V. (1997). 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Typology of online shoppers. Journal of consumer marketing. MacKinnon, A. J., Duinker, P. N., Walker, T. R. (2018). The Application of Science in Environmental Impact Assessment. Routledge. https://www.iaia.org/pdf/IAIAMemberDocuments/Publications/Guidelines_Principles/Principles %20of%20IA.PDF |title=Principle of Environmental Impact Assessment Best Practice Holder, J., (2004), Environmental Assessment: The Regulation of Decision Making, Oxford University Press, New York; For a comparative discussion of the elements of various domestic EIA systems, see Christopher Wood Environmental Impact Assessment: A Comparative Review (2 ed, Prentice Hall, Harlow, 2002). Barba-Sánchez, V., & Atienza-Sahuquillo, C. (2010). Integration of the environment in managerial strategy: application of the resource-based theory of competitive advantage, dynamic capabilities and corporate social responsibilities. African Journal of Business Management, 4(6), 1155-1165. Damtie, M., & Bayou, M. (2008). Overview of environmental impact assessment in Ethiopia. Anthropol. Q, 45. Damtie, M. (2008). Overview of Environmental Impact Assessment in Ethiopia. Gaps and Challenges, MELCA Mahiber, …. Eccleston, Charles H. (2011). Environmental Impact Assessment: A Guide to Best Professional Practices. Chapter 5. ISBN 978-1439828731 Keili-et-al-March-2021-Policy-brief.pdf