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How does visualizing allows us to set the parameters to make the future vision a reality?

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.

In this fascinating review, the authors show how environmental justice is reproductive justice (following the water protectors at Standing Rock) and how this intersection reshapes understandings of the environment, embodiment, and exposure. I was particularly interested in the concepts of social and cultural re/production, and how we might think about this in light of Austin's rapid gentrification. They discuss an intersectional approach as a multi-scalar approach, from climate change to chemical exposure in the home - and I think this could be extended to a inter/multi-generational approach to justice (esp given our focus on renewables). The authors show how the RJ framework rethinks the individualism of reproductive choice as the right to conceive and bear children in conditions of social justice and human flourishing - then how does the current energy system (and future energy transitions) negate or create these conditions, and for whom? If we think about biological/cultural reproduction, how do we also incorporate the concept of reproductive labor into our analysis? Finally, I think they make an important point about the harms of documentation, and it would be great to hear everyone's thoughts (Esp those who have participated in earlier field campuses) on what the goal and ethics of our knowledge production are?

Thinking through this article and Vermeylen's, something we might consider in ATX is how we conceptualize community itself. It is so easy in EJ-contexts to make communities our object of study and analysis, which can erase identities and exclusions within them...

How is ecological harm and gentrification experienced by LGBTQ people in Austin? Women? Etcetera?