Groundwater quantity

The quantity of groundwater in Switzerland fluctuates during the year, but is stable in the long term.

Groundwater quantity is the total amount of water available underground in Switzerland. This groundwater is used for a variety of purposes, including water supply, agriculture, industry, geothermal energy, as well as for ecosystems. Groundwater quantity is monitored by continuous measurement of groundwater levels and spring discharges. Data are collected at around 100 NAQUA National Groundwater Monitoring sites. The monitoring sites reflect the different geological and hydrological conditions in Switzerland.

Current status reflects precipitation trends of previous months

Groundwater levels and spring discharges reflect the weather conditions at the surface, though in an attenuated form and with a time lag. Spatial and geological factors influence the intensity and speed of aquifer fluctuations.

Long periods of rainfall – especially in winter – increase groundwater recharge. In contrast, prolonged periods of drought – particularly in summer and autumn – can result in low groundwater levels and spring discharges. The groundwater quantity observed at any given time therefore reflects the weather conditions of the last few weeks or months.

Long-term trend is stable

Long-term weather patterns (temperature and precipitation) in Switzerland are often correlated with periodic, multi-year fluctuations in groundwater levels, as well as regular low- and high-level water situations that can persist over weeks and months. Within this general pattern, significant regional differences are the norm.

Recently, the dry years of 2003, 2011, 2015, 2018, 2019, 2020, 2022 and 2023 in particular have led to low groundwater levels and spring discharges. In contrast, years with above-average precipitation (e.g. 1999–2002, 2021) generally resulted in high groundwater levels and spring discharges.

The intensity of high- and low-level situations varies depending on the aquifer's location and the properties of the subsurface. For example, groundwater reserves connected to watercourses react quickly to heavy rainfall, whereas deeper groundwater reserves generally do not react to individual rainfall events and only show a small level change after a few months of prolonged rainfall or drought.

High 2022: 12 Normal 2022: 57 Low 2022: 31 High 2021: 35 Normal 2021: 50 Low 2021: 15 High 2020: 21 Normal 2020: 53 Low 2020: 26 High 2019: 17 Normal 2019: 51 Low 2019: 32 High 2018: 17 Normal 2018: 51 Low 2018: 32 High 2017: 7 Normal 2017: 63 Low 2017: 30 High 2016: 25 Normal 2016: 59 Low 2016: 16 High 2015: 12 Normal 2015: 72 Low 2015: 16 High 2014: 20 Normal 2014: 75 Low 2014: 5 High 2013: 21 Normal 2013: 75 Low 2013: 4 High 2012: 16 Normal 2012: 72 Low 2012: 12 High 2011: 4 Normal 2011: 63 Low 2011: 33 High 2010: 14 Normal 2010: 59 Low 2010: 27 High 2009: 13 Normal 2009: 67 Low 2009: 20 High 2008: 19 Normal 2008: 69 Low 2008: 12 High 2007: 24 Normal 2007: 62 Low 2007: 14 High 2006: 23 Normal 2006: 50 Low 2006: 27 High 2005: 9 Normal 2005: 43 Low 2005: 48 High 2004: 9 Normal 2004: 66 Low 2004: 25 High 2003: 15 Normal 2003: 49 Low 2003: 36 High 2002: 30 Normal 2002: 60 Low 2002: 10 High 2001: 48 Normal 2001: 48 Low 2001: 4 High 2000: 29 Normal 2000: 62 Low 2000: 9 High 1999: 41 Normal 1999: 47 Low 1999: 12 High 1998: 9 Normal 1998: 47 Low 1998: 44 High 1997: 8 Normal 1997: 61 Low 1997: 31 High 1996: 10 Normal 1996: 63 Low 1996: 27 High 1995: 37 Normal 1995: 48 Low 1995: 15
Percentage of monitoring stations at which low, normal and high groundwater levels and/or spring discharge rates were recorded in each year.

Data for the graph: Excel
Source: Federal Office for the Environment

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Last modification 02.07.2024

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