Natural gas electric power plants

There are primarily three types of natural gas-fired electric power plants: natural gas combined cycle (NGCC) power plants, gas combustion turbines and gas-fired steam turbines. While gas turbines are directly driven by hot combustion gases, an NGCC plant first uses a gas combustion turbine to generate electricity and then uses the waste heat to create steam to generate more electricity in a steam turbine. Because gas combustion turbines require no cooling, as there is no steam to be condensed, the overall combined cycle system requires much less water for cooling than traditional steam turbine technologies. According to Macknick et al. (2012), water use values (median) of natural gas-fired power plants are shown in Table 2.3.

According to the US Energy Information Administration (2012), more than 80% of natural gas-fired power plants in the US are NGCC plants. Gas turbine and steam turbine power plants account for less than 10% each.

Table 2.3 Water use at natural gas-fired power plants

Once-through

Closed-loop

Air-cooling

Withdrawal

Consumption

Withdrawal

Consumption

Withdrawal

Consumption

NGCC

11380

100

253

198

2

2

Steam

35000

240

1203

826

2

2

Source: Macknick et al., 2012.

Concentrated solar power (CSP) plants

Concentrated solar power (CSP) requires larger amounts of water at the operational stage compared to other commonly used renewable energies (i.e. solar PV and wind). Both CSP and solar photovoltaic (solar PV) require water to clean the mirrors and panels, as dust can reduce the system efficiency. Water intensity for mirror and panel washing ranges from 0.08 to 0.15 m3 MWlr1 (Bracken et al., 2015). Such variation depends on the frequency of cleaning, which is decided by the site conditions, such as soil and dust properties, vegetation, air pollution, wind speed and direction, humidity and temperature, as well as precipitation characteristics (i.e. intensity, frequency and duration). Other factors are panel/mirrors orientation and angle of tilt; glazing properties also have impacts on the cleaning frequency (Sarver, Al-Qaraghuli and Kazmerski. 2013).

Apart from cleaning needs, the thermal cycle of parabolic trough, linear Fresnel and power tower CSP technologies are essentially the same as those used in coal and nuclear power plants and therefore require water for cooling purposes as well as boiler makeup, as in a coal-fired power plant.

Dish systems do not generally require water for cooling, nor for steam cycle operations, but do require a small amount to wash the concentrators.

References

AQUASTAT. (1998). AQUASTAT definitions. Rome. Italy: FAO.

Bakken. T. H.. Killingtveit, A. and Alfredsen, K. (2017). The water footprint of hydropower production - state of the art and methodological challenges. Global Challenges, l.p. 1600018.

Bakken. T. H„ Killingtveit, A.. Engeland, K„ Alfredsen. K. and Harby. A. (2013). Water consumption from hydropower plants - review of published estimates and an assessment of the concept. Hydrology' and Earth System Sciences. 17. pp.3983-4000.

Bakken. T. H.. Modahl, I. S., Raadal, H. L., Bustos, A. A. and Amoy, S. (2016). Allocation of water consumption in multipurpose reservoirs. Water Policy, 18(4), pp. 1-17.

Bracken, N.. Macknick, J.. Tovar-Hastings. A., Komor, P, Gerritsen, M. and Mehta, S. (2015). Concentrating solar power and water issues in the US Southwest. Golden. CO: National Renewable Energy Laboratory (NREL).

Byers. E. A., Hall. J. W.. Amezaga. J. M., O’Donnell. G. M. and Leathard. A. (2016). Water and climate risks to power generation with carbon capture and storage. Environmental Research Letters, 11, p. 024011.

Canyon Hydro. (2013). Guide to hydropower: An introduction to hydropower concepts and planning. Deming: Canyon Hydro.

China Electricity Council (CEC). (2012). Notification of energy efficiency benchmarking and competition data of 2012 national 600MW thermal power units (in Chinese). Beijing, China: CEC.

China Electricity Council (CEC). (2013). Notification of energy efficiency benchmarking and competition data of 2013 national 300MW thermal power units (in Chinese). Beijing. China: CEC.

East China Electric Power Design Institute. (2012). Investigation on designed water withdrawal and water consumption statistics of Shanghais big thermal power plants. (Internal materials). Shanghai. China.

Electric Power Research Institute (EPRI). (2004). Comparison of alternate cooling technologies for U.S. power plants: Economic, environmental, and other tradeoffs. Palo Alto. CA: EPRI.

Energy Information Administration (EIA). (2012). Annual electric utility’ data. Washington. DC: EIA.

Energy Information Administration (EIA). (2019). Average tested heat rates by prime mover and energy source, 200S-201S. Washington, DC: EIA.

Forster, H. and Lilliestam, J. (2009). Modelling thermoelectric power generation in view of climate change. Regional Environmental Change, 10(4). pp. 327-338.

Hogeboom, R.. Knock, L. and Hoekstra. A. Y. (2018). The blue water footprint of the world’s artificial reservoirs for hydroelectricity, irrigation, residential and industrial water supply, flood protection, fishing and recreation. Advances in Water Resources, 113, pp. 285-294.

Jiang, D. and Ramaswami. A. (2015). The •thirsty' water-electricity nexus: Field data on the scale and seasonality of thermoelectric power generation’s water intensity in China. Environmental Research Letters, 10. p. 024015.

Liao. X. W. Hall. J. W. and Eyre, N. (2017). Water for energy in China. In: L. M. Pereira et al., eds., Food, energy’ and water sustainability’: Emergent governance strategies. London: Earthscan, Routledge.

Liu, J., Zhao. D.. Gerbens-Leenes. P. W. and Guan. D. (2015). China’s rising hydropower demand challenges water sector. Scientific Reports, 5, p. 11446.

Macknick. J.. Sattler, S., Averyt, K., Clemmer, S. and Rogers. J. (2012). The water implications of generating electricity: Water use across the United States based on different electricity pathways through 2050. Environmental Research Letters, 7, p. 045803.

Mekonnen, M. M. and Hoekstra. A. Y. (2012). The blue water footprint of electricity from hydropower. Hydrology’ and Earth System Sciences, 16, pp. 179-187.

Nazari-Heris. M. and Mohammadi-Ivatloo, B. (2017). Design of small hydro generation systems. In: G. B. Gharehpetian and S. Mohammad Mousavi Agah, eds.. Distributed generation systems - design, operation and grid integration. Oxford: Butterworth-Heinemann.

Raptis, C. E., Boucher. J. M. and Pfister. S. (2017). Assessing the environmental impacts of freshwater thermal pollution from global power generation in LCA. Science of the Total Environment, 580. pp. 1014-1026.

Raptis, C. E. and Pfister. S. (2016). Global freshwater thermal emissions from steamelectric power plants with once-through cooling systems. Energy’, 97, pp. 46-57.

Raptis, C. E., Van Vliet, M. T. H. and Pfister. S. (2016). Global thermal pollution of rivers from thermoelectric power plants. Environmental Research Letters, 11. p. 104011.

Rochelle, G. T. (2009). Amine scrubbing for CO, capture. Science, 325(5948). pp. 1652-1654.

Sarver, T-, Al-Qaragliuli. A. and Kazmerski, L. L. (2013). A comprehensive review of the impact of dust on the use of solar energy: History, investigations, results, literature, and mitigation approaches. Renewable and Sustainable Energy Reviews, 22, pp. 698-733.

Scherer, L. and Pfister, S. (2016). Global water footprint assessment of hydropower. Renewable Energy, 99, pp. 711-720.

Stone, J. C., Singleton, F. D. Jr, Gadkowski, M„ Salewicz, A. and Sikorski. W. (1982). Water demand for generating electricity: a mathematical programming approach with application in Poland. International Institute for Applied Systems Analysis. Laxenburg, Austria.

Webster. M.. Donohoo. P. and Palmintier, B. (2013). Water-CO2 trade-offs in electricity generation planning. Nature Climate Change, 3, pp. 1029-1032.

World Nuclear Association. (2013). Cooling power plants. London. Available at: www.world-nuclear.org/information-library/current-and-future-generation/cool ing-power-plants.aspx#.Udx22awzZqM.

World Resource Institute. (2015). Opportunities to reduce water use and greenhouse gas emissions in the Chinese power sector. Beijing. China: World Resource Institute.

Zhai. H. and Rubin, E. S. (2010). Performance and cost of wet and dry cooling systems for pulverized coal power plants with and without carbon capture and storage. Energy Policy, 38(10), pp. 5653-5660.

Zhai. H.. Rubin, E. S. and Versteeg P. L. (2011). Water use at pulverized coal power plants with post-combustion carbon capture and storage. Environmental Science & Technology, 45, pp. 2479-2485.

Zhang, C. and Anadon. L. D. (2013). Life cycle water use of energy production and its environmental impacts in China. Environmental Science & Technology, 47. pp. 14459-14467.

Zhang, C., Anadon, L. D., Mo. H.. Zhao, Z. and Liu, Z. (2014). Water-carbon tradeoff' in China's coal power industry. Environmental Science & Technology', 48. pp. 11082-11089.

Zhao, D. and Liu, J. (2015). A new approach to assessing the water footprint of hydroelectricity power based on allocation of water footprints among reservoir ecosystem services. Physics and Chemistry of the Earth, pp. 40-46, 79-82.

 
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