(162c) Electricity Planning for Ecosystems and Society: A Spatial-Temporal Approach Considering Cost, Societal Benefit and Environmental Justice
AIChE Annual Meeting
2024
2024 AIChE Annual Meeting
Sustainable Engineering Forum
Sustainable Energy - Area Plenary
Monday, October 28, 2024 - 1:20pm to 1:45pm
We employ the Techno-Ecological Synergy (TES) framework that integrates traditional emission control equipment with natural ecosystem processes to remove carbon dioxide and hazardous air pollutants emitted by power plants. In this work, four traditional emission control technologies are considered: selective catalytic reducer, flue gas desulfurization, baghouse filter, and aqueous monoethanolamine (MEA) solution for removal of NO2, SO2, PM10, and CO2, respectively. Trees are considered as an ecological unit operation in this work. The capacity of trees is quantified by dry deposition flux which is related to vegetation parameters. Air pollution modeling performed by CALPUFF version 7, an advanced non-steady-state meteorological and air quality modeling system, was utilized to obtain the spatial concentration and dry deposition maps for NO2, SO2, and PM10 before and after land use change from original to tree covers. Besides, we used i-Tree Canopy to calculate carbon sequestration by trees, and the growth dynamics of trees were calculated by Forest Vegetation Simulator (FVS). To quantify societal costs, we obtain spatial social impact maps from BenMAP-CE, an open-source software tool designed to estimate the number of fatalities and illnesses attributable to air pollution. For incorporating environmental justice considerations, the block group level demographic index (calculated based on the average of five socioeconomic indicators; low-income, unemployment, limited English, less than high school education, and low life expectancy) was retrieved from EJScreen, an Environmental Protection Agency (EPA)'s tool for mapping and screening environmental justice concerns. This data was then integrated with our case study's specific geographic units using QGIS, ensuring a comprehensive analysis that aligns with our defined parameters. We conducted a case study over the region of Louisville, KY with nine power plants that utilize a mix of energy sources including coal, natural gas, and hydroelectric power. The optimization problem was formulated as a multi-objective mixed-integer linear program (MILP) and was solved in Julia by Gurobi solver to minimize engineering costs, societal costs, and environmental injustice. We explored three different scenario groups including conventional, techno-centric, and TES to find the best solution to balance the three objectives above and emission goals.
This work incorporates hourly electricity planning, emission control technologies, and spatial-temporal landscape design, in which the engineering systems work with nature in synergy to achieve both air quality and people-positive targets. The findings reveal that Techno-Ecological Synergy (TES) scenario groups demonstrate superior performance over time with lower overall costs. As trees become mature, their capacity to remove carbon dioxide and air pollutants will be higher than the demand of power plants, achieving greater environmental benefits by taking up additional carbon and emissions emitted by other sources. Furthermore, the cost of planting trees will be much less than traditional technologies. With the presence of more tree cover, electricity power plants will have more flexibility in running without the burden of worsening air quality during high-demand days. We also find out by setting additional objectives of social cost and environmental justice index, the results of time and location for tree planting can be very different: these objectives will prioritize reforestation at locations with high population densities and high percentages of minority groups and in the meantime start to plant trees at earlier years. From the Pareto front, we notice there are trade-offs between (1) engineering costs & social costs; (2) engineering costs & environmental justice index. The reason could be these locations have a relatively low dry deposition flux after land-use change according to air pollution modeling, so more trees and technologies are needed which makes the ecological and technological costs higher. However, people-positive is essential and our results show the necessity to consider it in decision-making. In summary, this work optimizes hourly electricity schedules, emission control technologies usage, time and locations for reforestation. It highlights the benefits of including trees as unit operations to improve air quality and emphasizes the significance of considering societal and minority groups in design strategies. Our aim is to foster a sustainable, nature-positive, and people-positive world, demonstrating how environmental solutions can be beneficial to both nature and diverse human communities .
Reference
- Climate change fuelled extreme weather in 2023; expect more records in 2024. World Weather Attribution (2023).
- United Nations Environment Programme. Emissions Gap Report 2023: Broken Record â Temperatures Hit New Highs, yet World Fails to Cut Emissions (Again). (United Nations Environment Programme, 2023). doi:10.59117/20.500.11822/43922.
- WHO fact sheets-Ambient(outdoor) air pollution. https://www.who.int/news-room/fact-sheets/detail/ambient-(outdoor)-air-quality-and-health.
- United States Environmental Protection Agency. Sources of Greenhouse Gas Emissions. https://www.epa.gov/ghgemissions/sources-greenhouse-gas-emissions.
- United States Environmental Protection Agency. Our Nationâs Air 2022.
- Wang, Y. et al. Location-specific strategies for eliminating US national racial-ethnic PM2.5 exposure inequality. Proc. Natl. Acad. Sci. U.S.A. 119, e2205548119 (2022).
- Pope, R., Wu, J. & Boone, C. Spatial patterns of air pollutants and social groups: a distributive environmental justice study in the phoenix metropolitan region of USA. Environmental Management 58, 753â766 (2016).
- Banzhaf, H. S., Ma, L. & Timmins, C. Environmental Justice: Establishing Causal Relationships. Annu. Rev. Resour. Econ. 11, 377â398 (2019).
- Nazari, M. E., Ardehali, M. M. & Jafari, S. Pumped-storage unit commitment with considerations for energy demand, economics, and environmental constraints. Energy 35, 4092â4101 (2010).
- Shuai Lu et al. Unit commitment considering generation flexibility and environmental constraints. in IEEE PES General Meeting 1â11 (IEEE, Minneapolis, MN, 2010). doi:10.1109/PES.2010.5589501.
- Bakshi, B. R., Ziv, G. & Lepech, M. D. Techno-Ecological Synergy: A Framework for Sustainable Engineering. Environ. Sci. Technol. 49, 1752â1760 (2015).
- Shah, U. & Bakshi, B. R. Toward Nature-Positive Manufacturing by Adapting Industrial Processes to Pollution Uptake by Vegetation. ACS Sustainable Chem. Eng. 9, 16709â16718 (2021).
- Charles, M. & Bakshi, B. R. Designing industrial landscapes for mitigating air pollution with spatiallyâexplicit technoâecological synergy. AIChE J 67, (2021).