Analyze

Operations of transnational companies are affecting marginalized communities across the globe. As Kaswan had highlighted through examples of Union Carbide’s pesticide plant in India, as well as pollution associated with oil companies in Latin America, the implications of distributive environmental justice in such contexts are apparent yet difficult to address. Across international boundaries law enforcement becomes increasingly difficult, which is at the heart of the problem of my research topic. 

“The “right” scale will depend upon the nature of the harm being analyzed and purpose for which information is being gathered.” (Kaswan, p 29)

“Numerous studies, at a multiplicity of scales, analyze the distribution of a wide variety of land uses, as well as risk: what exposures, with what consequences, do people experience?” (Kaswan, p 33). 

This text builds on concepts of equality, bases for deviating from the core idea of equality, and the multiple contexts that define and shape distributive justice. Kaswan additionally advances the distributive environmental justice by outlining the different contexts, including historical land use patterns, government regulations, infrastructure, and enforcement and the implications that each of these dimensions have on contributing to distributive injustice. 

The main narrative of this text builds on foundational ideas on equality and extrapolates it further to establish how distributive environmental justice, its ideas and articulations, as well as its operationalization, has taken shape throughout the years. To outline these points, Kaswan outlines different cases of environmental disaster, and subsequent government responses, to showcase how government institutions have both upheld and endeavored to address distributive environmental inequality in the past decades.

Characterization of loss from Vietnam’s Ministry of Agriculture & Rural Development (2018) within the Evaluation report on 10-year implementation of the national policy for ‘agriculture-farmer-rural’ development [ not available for public view] 

• “ Aquaculture households have lost 503.2 million VND (21,665 USD) per household, then fishing households 231.3 million VND (9958 USD) per household, and coastal service households 102.0 million VND (4392 USD) per household. Note that both fishing and fish farming households lost similar por- tions of their total income, around 98 percent, even as fish farmers earn twice that of fishers on average. In a country where the average yearly income of rural households is 130 million VND or 5600 USD (MARD, 2018), losing an average of 11,000 USD per household is significant.” (Truong et al., 2021, p 8). 

Characterization of the compensation schemes adopted by Vietnam’s government:

• “According to a report by the Ministry of Finance in 2018, the government was able to provide direct cash compensation to those identified as being impacted across the four provinces. This is because of the settlement with Taiwan Formosa Plastics for 500 million USD. In addition to cash, the Vietnamese government gave over 19,000 tonnes of rice to impacted households in the months following the fish kill. The government also monitored the safety of the ocean environment. As the government switched from emergency relief to recovery support, more programmes were introduced including loan access, scholarships for students, health insurance, and livelihood training pro- grammes. The government also worked with the Fisheries Department and other relevant agencies to build environmental monitoring systems, provide consistent water testing, engage in food safety monitoring, and work towards ecological rehabilitation of aquatic stocks” (Truong et al., 2021, p 10). 

“Environmental disasters have a tendency to further increase work precarity, particularly in places that are highly dependent on eco- logical resources (Marschke et al., 2020). Livelihoods, as such, may need to transform rather than persist in the face of crises (Alexander, 2013).” (Truong, 2021, pg 3)

“ Vietnam has struggled with ineffective environmental regulatory programmes or insufficient enforcement capabilities to ensure adequate protection of the environment as Vietnam develops (Fortier, 2010). Environmental impact assessments (EIA), in general, are viewed as bureaucracy rather than as an important aspect of the development approval process (Wells-Dang et al., 2016).” (Truong, 2021, pg 4)

The narrative of the text highlights the following key points extrapolated from survey responses and interview participants:

• Impacts of the Formosa disaster on households vary by livelihood strategies, and were particularly amplified for poorer households, women, and households without diversified livelihood strategies. 

• Coping mechanisms of households primarily involved reducing household expenditures, accessing loans, adopting a new livelihood strategy, and expanding existing livelihood strategies. However, adoption rates of these coping mechanisms vary across households with livelihoods across the service, fishing, and fish farming enterprises. 

• Compensation, though cited to have ignited protests from parties not qualified for restitution, did offer substantial help to those who were able to receive compensation. Additionally, compensation delivery was delayed (between one to two years after the incident was reported), further escalating impacts across families without savings. 

• Economic recovery of household income 30 months after the Formosa incident indicates that the majority of households have recovered their livelihood activities. However, this does not take into account families who are no longer in the region (out migrated following the disaster prior to the inception of this study).

Authors of the publication have affiliations to the Hue University of Agriculture and Forestry and the School of International Development and Global Studies at the University of Ottawa, Canada. The funding for this study comes from the Vietnam National Foundation for Science and Technology Development.