Alternative energy technologies such as photovoltaic modules (Figure 1) are becoming more popular around the world. In 2008, for the first time, worldwide investments in alternative energy sources drew more investors than fossil fuels, netting $155 billion in net capital against $110 billion of new investment in oil, natural gas and coal. Solar power alone generated $6.5 billion in worldwide revenue in 2004, and is expected to almost triple that with projected revenues of $18.5 billion for 2010.
Alternative energy technologies are becoming increasingly popular throughout the world due to greater awareness and concerns regarding pollution, and global climate change. Alternative energy technologies offer a new option for obtaining useful energy from sources that have less environmental impact on the planet. But how much less?
A previous published review of the net energy analysis of silicon-based photovoltaics[1] found that all types of silicon (amorphous, polycrystalline and single crystal)-based PV generated far more energy over their lifetime than is used in their production. All modern silicon PV pay for themselves in terms of energy in less than 5 years - even in highly suboptimal deployment scenarios.
This article explores all of the environmental impacts associated with the production and lifetime use of silicon photovoltaic (PV) panels.
What is a Life Cycle Assessment (LCA)?[edit | edit source]
A Life Cycle Assessment (LCA) evaluates the environmental impacts of a product or process from production to disposal.[2] An LCA investigates the material and energy inputs required to produce and use a product, the emissions associated with its use, and the environmental impacts of disposal or recycling. The LCA may also investigate external costs, such as environmental mitigation, that are made necessary by the production or use of a product.[3]
Silicon PV panel Life Cycle Assessment[edit | edit source]
The following section contains a brief lifecycle analysis of silicon PV panels. The lifecycle factors discussed include: the energy required for production, the lifecycle carbon dioxide emissions, and all of the pollution emissions generated throughout a PV panels useful life from: transportation, installation, operation, and disposal.
Energy requirements for production[edit | edit source]
Manufacturing photovoltaics is overwhelmingly the most energy intensive step of installed PV modules. As seen in Figure 2, large amounts of energy are used to convert silica sand into the high purity silicon required for photovoltaic wafers. The assembling of the PV modules is another resource intensive step with the addition of high energy content aluminum framing and glass roofing.
The environmental impact of a silicon photovoltaic module involves the production of three main components: the frame, the module, and balance-of-system components such as the rack and inverter.[3] Greenhouse gases are caused mostly by module production (81%), followed by the balance of system (12%) and frame (7%)[3]). Resource requirements of the production cycle are summarized in Figure 3.
Lifecycle carbon dioxide emissions[edit | edit source]
Lifecycle carbon dioxide emissions refer to the emissions caused by the production, transportation, or installation of materials related to photovoltaic systems. In addition to the modules themselves, the typical installation includes electrical cable and a metal rack. Ground-mounted photovoltaic systems also include a concrete foundation. Remote installations may require additional infrastructure for transmission of electricity to the local electrical grid. In addition to materials, a life cycle analysis should include carbon dioxide emitted from vehicles during the transportation of photovoltaic modules between the factory, the warehouse, and the installation site. Figure 4 compares the relative contributions of these factors to the lifetime carbon dioxide impacts of five types of photovoltaic modules.[5]
Transportation emissions[edit | edit source]
Transportation accounts for about 9% of lifecycle emissions of photovoltaics.[5] Photovoltaic modules, racks, and balance-of-system hardware (such as cables, connectors, and mounting brackets) are frequently produced overseas and transported to the United States by ship.[6]Within the United States, these components are transported by truck to distribution centers and eventually to the installation site.
Installation emissions[edit | edit source]
Emissions associated with installation include vehicle emissions, material consumption, and electricity consumption associated with local construction activities to install the system. These activities generate less than 1% of total lifecycle emissions of the photovoltaic system.[6]
Operation emissions[edit | edit source]
There are no air or water emissions generated during the use of PV modules. Airsheds are impacted during the construction of PV modules from solvent and alcohol emissions that contribute to photochemical ozone formation. Watersheds are impacted by the construction of modules from extraction of natural resources such as quartz, silicon carbide, glass, and aluminum. Overall, replacement of current worldwide grid electricity with central PV systems would lead to 89-98% reductions in greenhouse gas emissions, criteria pollutants, heavy metals, and radioactive species.[7]
Disposal emissions[edit | edit source]
The disposal of silicon photovoltaic modules has not caused significant impacts because large-scale installations have only been in use since the mid-1980's and photovoltaic modules have lifetimes of at least 30 years.[8] Fthenakis et al. (2005)[2] specifically identified a lack of available data on the disposal or recycling of photovoltaic modules, so this topic warrants more thorough investigation.
LCA of photovoltaics compared to other energy sources[edit | edit source]
Total lifecycle emissions associated with photovoltaic energy production are slightly higher (as of 2006, this has significantly lowered now) than those of nuclear power but lower than those of fossil fuel energy production. Lifecycle greenhouse gas emissions of several energy generation technologies are listed below:[3]
- Silicon PV: 45 g/kWh
- Coal: 900 g/kWh
- Natural gas: 400-439 g/kWh
- Nuclear: 20-40 g/kWh
During their 20-30 year lifetimes, solar modules generate more electricity than was consumed during their production. The energy payback time quantifies the minimum useful life required for a solar module to generate the energy that was used to produce the module. As shown in Table 1, the average energy payback time is 3-6 years.
Country | Town | Solar radiation (kWh/m2) |
Latitude | Altitude (m) |
Annual production (kWh/kWp) |
EPBT |
ERF |
---|---|---|---|---|---|---|---|
Australia | Sydney | 1614 | 33.55 | 1 | 1319 | 3.728 | 7.5 |
Austria | Vienna | 1108 | 48.2 | 186 | 906 | 5.428 | 5.2 |
Belgium | Brussels | 946 | 50.5 | 77 | 788 | 6.241 | 4.5 |
Canada | Ottawa | 1377 | 45.25 | 75 | 1188 | 4.14 | 6.8 |
Czech Republic | Prague | 1000 | 50.06 | 261 | 818 | 6.012 | 4.7 |
Denmark | Copenhagen | 985 | 55.75 | 1 | 850 | 5.786 | 4.8 |
Finland | Helsinki | 956 | 60.13 | 0 | 825 | 5.961 | 4.7 |
France | Paris | 1057 | 48.52 | 32 | 872 | 5.64 | 5 |
France | Marseille | 1540 | 43.18 | 7 | 1317 | 3.734 | 7.5 |
Germany | Berlin | 999 | 52.32 | 35 | 839 | 5.862 | 4.8 |
Germany | Munich | 1143 | 48.21 | 515 | 960 | 5.123 | 5.5 |
Greece | Athens | 1563 | 38 | 139 | 1278 | 3.848 | 7.3 |
Hungary | Budapest | 1198 | 47.3 | 103 | 988 | 4.978 | 5.6 |
Ireland | Dublin | 948 | 53.2 | 9 | 811 | 6.064 | 4.6 |
Italy | Rome | 1552 | 41.53 | 15 | 1315 | 3.74 | 7.5 |
Italy | Milan | 1251 | 45.28 | 103 | 1032 | 4.765 | 5.9 |
Japan | Tokyo | 1168 | 35.4 | 14 | 955 | 5.15 | 5.4 |
Republic of Korea | Seoul | 1215 | 37.3 | 30 | 1002 | 4.908 | 5.7 |
Luxembourg | Luxembourg | 1035 | 49.62 | 295 | 862 | 5.705 | 4.9 |
The Netherlands | Amsterdam | 1045 | 52.21 | 1 | 886 | 5.551 | 5 |
New Zeland | Wellington | 1412 | 41.17 | 21 | 1175 | 4.185 | 6.7 |
Norway | Oslo | 967 | 59.56 | 13 | 870 | 5.653 | 5 |
Portugal | Lisbon | 1682 | 35.44 | 16 | 1388 | 3.543 | 7.9 |
Spain | Madrid | 1660 | 40.25 | 589 | 1394 | 3.528 | 7.9 |
Spain | Sevilla | 1754 | 37.24 | 5 | 1460 | 3.368 | 8.3 |
Sweden | Stockholm | 980 | 59.21 | 16 | 860 | 5.718 | 4.9 |
Switzerland | Bern | 1117 | 46.57 | 524 | 922 | 5.334 | 5.2 |
Turkey | Ankara | 1697 | 39.55 | 1102 | 1400 | 3.513 | 8 |
United Kingdom | London | 955 | 51.3 | 20 | 788 | 6.241 | 4.5 |
United Kingdom | Edinburgh | 890 | 55.57 | 32 | 754 | 6.522 | 4.3 |
United States | Washington | 1487 | 38.52 | 14 | 1249 | 3.937 | 7.1 |
Examples[edit | edit source]
References[edit | edit source]
- ↑ J. Pearce and A. Lau, "Net Energy Analysis For Sustainable Energy Production From Silicon Based Solar Cells", Proceedings of American Society of Mechanical Engineers Solar 2002: Sunrise on the Reliable Energy Economy, editor R. Cambell-Howe, 2002.pdf
- ↑ 2.0 2.1 Fthenakis, V. M., E. A. Alsema, and M. J. de Wild-Scholten (2005), Life cycle assessment of photovoltaics: Perceptions, needs, and challenges, IEEE Photovoltaics Specialists Conference, Orlando, Florida.
- ↑ 3.0 3.1 3.2 3.3 Fthenakis, V., and E. Alsema (2006), Photovoltaics energy payback times, greenhouse gas emissions and external costs: 2004-early 2005 status, Progress in Photovoltaics, 14, 275-280.
- ↑ 4.0 4.1 4.2 Life cycle assessment of photovoltaic electricity generation, A. Stoppato, Energy, Volume 33, Issue 2, February 2008, Pages 224-232
- ↑ 5.0 5.1 5.2 Ito, M., K. Kato, K. Komoto, T. Kichimi, and K. Kurokawa (2007), A comparative study on cost and life-cycle analysis for 100 MW very large-scale PV (VLS-PV) systems in deserts using m-Si, a-Si, CdTe, and CIS modules, Progress in Photovoltaics, 16, 17-30
- ↑ 6.0 6.1 Ito, M., K. Kato, K. Komoto, T. Kichimi, and K. Kurokawa (2007), A comparative study on cost and life-cycle analysis for 100 MW very large-scale PV (VLS-PV) systems in deserts using m-Si, a-Si, CdTe, and CIS modules, Progress in Photovoltaics, 16, 17-30
- ↑ Fthenakis, V., Kim, H., and E. Alsema (2008), Emissions from Photovoltaics Life Cycles. Environmental Science Technology, 42, 2168-2174.
- ↑ Luque, A., and S. Hegedus (2003), Handbook of Photovoltaic Science and Engineering, Wiley, Hoboken, NJ.