Photovoltaic Sustainability: Environmental Impact and Optimal Site Selection

Jeremy Tan
7 min readAug 21, 2021

Once plagued by high unit costs, rendering large scale roll out infeasible, solar photovoltaic technology has finally begun to penetrate consumer and industrial power generation markets. For all types of renewable energy generation, it is important to understand the overall environmental impact and sustainability of the energy source, which can be analysed through the lens of an Energy Life Cycle Analysis and an optimal site selection methodology for such technology.

With more photovoltaic systems being installed on top of private homes, Tesla giga factories, and in solar farms, it is important to understand any potential long-term environmental impacts that large scale implementation of photovoltaic technology might have. Furthermore, installing solar panels is often a long-term commitment due to their 25–30-year life spans and warrants careful consideration when selecting where to set them up.

Energy Life Cycle Analysis

An Energy Life Cycle Analysis (ELCA) is one of several ways to analyse the environmental impact that a particular technology produces and allows for a quick comparison to other technology. It quantifies the Energy Pay Back Time (EPBT), the number of years taken for the system to produce the same amount of energy used in manufacturing, operating, and decommissioning the technology. The lifecycle of most technology can be divided into an upstream, core, and downstream phase shown in Figure 1.

Figure 1: Different phases of a solar photovoltaic panel’s lifecycle

Manufacturing crystalline photovoltaic panels is an energy intensive process which dominates the lifecycle analysis as it constitutes between 50–75% of the cumulative energy demand associated with photovoltaic technology, shown in Figure 2 [1][2]. Solar panels require extremely high purity silicon, colloquially known as ‘9N’ or up to 99.9999999% purity compared to the 99.99% purity required for electronics grade silicon [3]. To put this into context, consider an average suburban house that can accommodate 40 m² of solar panels, roughly half the size of a badminton court. The total energy required to purify the silicon, cut the silicon into wafers, process and assemble the cells is approximately 48 GJ, which is the same as amount of energy that an average UK household consumes in approximately 10 months [2][4]. Similarly, the entire manufacturing process would release approximately 279 kg of CO2 emissions, roughly the same carbon footprint as 3 direct flights from London to Frankfurt [5].

Figure 2: Energy input and CO2 emissions for various manufacturing steps for 1 PV module — diagram by Luo et al. [2]

More recent ELCA studies on solar photovoltaics, that examine the energy consumption of the upstream, core, and downstream phases, quote Energy Pay Back Times in the range of 1.01–2.3 years [2][6]. In comparison, offshore and onshore wind energy usually have EPBTs of 5–11 months [7]. One way to lessen the environmental burden of implementing solar photovoltaic energy is to further develop recycling processes for the aluminium scrap, glass scrap, and silicon. This will be of increasing importance as more solar panels will be reaching the end of their 25–30-year lifespan in coming years.

Figure 3: Breakdown of the different layers in a solar panel — illustration by Eco Green Energy [12]

The recycling process for solar panels can be divided into disassembly, delamination, and material separation. Presently, due to various manufacturer’s designs, solar panels require manual disassembly. As the technology matures and an optimal design has been determined, disassembly processes can be further streamlined. Delamination involves removing the glass coverings and Ethyl Vinyl Acrylate (EVA) from the silicon solar cells themselves shown in Figure 3, which protects the solar cells against air and moisture. A common method to achieve this is to heat the modules to temperatures of 450–600 °C allowing the EVA layer to breakdown via thermal decomposition, enabling the recovery of the glass and direct reuse of the silicon cells [11]. Presently, the only method to achieve material separation is through chemical etching which uses chemicals such as bromine gas and nitric, hydrofluoric, and ethanoic acid to further separate the silicon from the other metal and glass compounds [13]. The delamination and material separation steps produce harmful gases and liquid waste products respectively, and further research into alternative methods may be required to mitigate these by-products.

Optimal Site Selection

Manufacturing solar panels is a resource intensive process, and therefore it is imperative to ensure that solar panels are placed in optimal locations to maximize electricity production whilst minimizing environmental impact. A common method to identify these locations is to prepare climate and terrain maps, assign a weighting to each map layer, and then produce a composite map based on the different weights of each map layer.

Geographic Information System (GIS) software has been widely implemented to identify suitable preliminary locations for construction of wind farms, solar farms, and other power generation sources. Amongst numerous studies, the following factors were consistently considered when determining the optimal site selection: distance to roads, distance to transmission lines, amount of solar irradiation, slope of terrain, land use, temperature, and humidity [8][9].

The GIS software is used to prepare maps of these input parameters and score them between 0 and 1 through fuzzy classification techniques, usually where a score closer to 1 indicates a stronger suitability, illustrated in Figure 4. Based on the seven factors above, the ideal location would be one that is close to access roads and transmission lines so that transportation and connection costs are minimised. Favoured locations exhibit low sloping terrain such that construction costs are minimised, and low temperature and humidity levels but high levels of solar irradiation to maximize solar panel performance.

Figure 4: Fuzzified suitability map of Iran’s Fars province scoring relative humidity and distance to road between 0 and 1 — diagram by Mokarram et al. [10]

The simplest and easiest method to implement to determine the weighting of each factor, is the Additional Hierarchical Process (AHP) method which essentially compares the importance of one factor against another in a 7x7 matrix based on the factors above. Naturally, some factors are in competition with each other, as possible locations which are in close proximity to roads may be situated in urban or densely populated residential areas rendering the possibility of large solar farms unlikely. Similarly, mountainous regions are often such that the performance of solar photovoltaic panels is improved. However, these locations are usually far from power transmission lines which makes construction difficult. Ultimately, this algorithm considers these contrasting factors and produces a weighting for each factor between 0 and 1.

Once a satisfactory weighting for each map layer is obtained, a composite map can be constructed which will help readers to quickly visualize suitable locations based on the various influencing factors, shown in Figure 5, with scores closer to 1 indicating a stronger suitability [10].

Figure 5: Composite map indicating that the southern regions of Iran’s Fars province are strongly suited for solar farms — diagram by Mokarram et al. [10]

Conclusion

Make no mistake, solar photovoltaic energy is a promising form of clean energy and will play an instrumental role in helping many countries reach net zero by 2050. However, it is important to understand the environmental impacts that are associated with its production and operation so that we can strategically deploy them in optimal locations to maximise their energy output. Development of economical recycling processes is necessary to keep pace with the increased uptake of solar photovoltaic energy and the looming expiry of existing solar panels.

While most homeowners may not have the luxury of choosing where to install solar panels, aside from their own rooftop or backyard, this is an important consideration for large solar farms or factories that wish to use solar energy to offset their energy consumption. Furthermore, with increased uptake in installing renewable energy generation sources, this will inevitably result in real-estate competition for construction of these projects. The prudent use of site selection studies to guide policy makers and corporations will play a big role as we rise to the challenge of ensuring a greener future.

References

  1. de Wild-Schoten M. Energy payback time and carbon footprint of commercial photovoltaic systems. Solar Energy Materials & Solar Cells. 2013 September; 119: 296–305.

2. Luo W, Khoo YS, Kumar A, Sze J, Li Y, Tan YS, et al. A comparative life-cycle assessment of photovoltaic electricity generation in Singapore by multicrystalline silicon technologies. Solar Energy Materials and Solar Cells. 2018 January; 174: 157–162.

3. De Rooij D. Sinovoltaics. [Online].; 2019 [cited 2021 February 25. Available from: https://sinovoltaics.com/learning-center/solar-cells/silicon-si-solar-cells-produced/#:~:text=The%20Si%20used%20in%20the,process%20which%20requires%20repeated%20refining.

4. UK Power. UK Power. [Online].; 2020 [cited 2021 February 25. Available from: https://www.ukpower.co.uk/home_energy/average-household-gas-and-electricity-usage.

5. Carbon Footprint. Carbon Footprint Calculator. [Online].; 2020 [cited 2021 February 25. Available from: https://calculator.carbonfootprint.com/calculator.aspx?tab=3.

6. Wu P, Ma X, Ji J, Ma Y. Review on life cycle assessment of enegy payback of solar photovoltaic systems and a case study. In ICAE2016; 2017; Beijing. p. 68–74.

7. Bonou A, Laurent A, Olsen S. Life cycle assessment of onshore and offshore wind energy-from theory to application. Applied Energy. 2016 October; 180: 327–337.

8. Ghose D, Naskar S, Shabbiruddin , Sadeghzadeh M, El Haj Assad M, Nabipour N. Siting high solar potential areas using Q-GIS in West Bengal, India. Sustainable Energy Technologies and Assessments. 2020 December; 42: 1–11.

9. Uyan M. GIS-based solar farms site selection using analytic hierarchy process (AHP) in Karapinar region, Konya/Turkey. Renewable and Sustainable Energy Reviews. 2013 December; 28: 11–17.

10. Mokarram M, Mokarram M, Khosravi M, Saber A, Rahideh A. Determination of the optimal location for constructing solar photovoltaic farms based on multi-criteria decision system and Dempster–Shafer theory. Scientific Reports. 2020 May; 10: 17.

11. Deng R, Chang N, Zi O, Chee MC. A techno-economic review of silicon photovoltaic module recycling. Renewable and Sustainable Energy Reviews. 2019 July; 109: 532–550.

12. Eco-Green Energy. Eco Green Energy. [Online].; 2019 [cited 2021 April 15. Available from: https://www.eco-greenenergy.com/what-is-the-eva/#:~:text=EVA%20is%20ethylene%20vinyl%20acetate,film%20around%20the%20solar%20cells.

13. Maani T, Celik I, Heben M, Ellingons R, Apul D. Environmental impacts of recycling crystalline silicon (c-SI) and cadmium telluride (CDTE) solar panels. Science of The Total Environment. 2020 September; 735.

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Jeremy Tan

Mechanical Engineering graduate from Imperial College London interested in learning about Climate Tech, Climate Policy, and coding!