KAZALCI OKOLJA

Key message
Neutral

The values ​​of the parameters used to monitor the load of rivers with organic substances have decreased significantly since 1996. The observed decrease in organic load corresponds to the increase in the proportion of the population whose wastewater is treated in municipal and joint wastewater treatment plants. The load of rivers with nutrients varies significantly between river basins. The average nitrate values ​​in all river basins of the Danube river basin are higher than in the Soča and Adriatic river basins and above the values of the natural background.


The indicator shows the level of nutrient and organic matter loading of rivers due to human activities. Nitrate and orthophosphate are representative parameters for nutrient loading, and biochemical oxygen demand and ammonium are representative parameters for organic loading. The parameters were measured in water samples taken in the course of regular monitoring of surface water quality.

Nitrate and ortophosphate are the main nutrients required for the growth of algae, mosses and aquatic plants in rivers. In non-polluted waters they are present at very low concentrations that mostly depend on geological properties and soil types in the catchment area. These so called natural or background values range for nitrate in Slovenian rivers between 0.2 and 0.9 mg NO3-N/l depending on their ecological type. Background value for orthophosphate according to EEA is 0.01 mg PO4-P/L (EEA). Nitrate and orthophosphate concentrations in water that exceed background values are a result of human activities, mainly agriculture and urban/industrial wastewater discharge. The surplus of nutrients in rivers leads to a deterioration in the normal functioning of the ecosystem, reduced biodiversity and eutrophication, which is problematic mainly in standing or slowly running waters. High nitrate content may also compromise the quality of drinking water, which is no longer suitable for drinking when nitrate concentration exceeds 10 mg NO3-N/l (50 mg NO3/l).

Biochemical oxygen demand (BOD) and ammonium are the main indicators of organic water pollution. The values of both parameters are usually elevated as a result of urban and industrial wastewater discharge and leaching of nutrients from agricultural land. The BOD is the amount of dissolved oxygen (in mg O2/l) needed (i.e. demanded) by aerobic organisms to break down organic matter present in a given water sample at a certain temperature over a specific time period. It is usually expressed as BOD5, which tells us how much oxygen is consumed per litre of sample over 5 days of incubation at 20°C. Background values for BOD5 range between <1 and 1.4 mg O2/l in Slovenian rivers. In an aquatic environment, ammonium also represents an increased demand for oxygen. In the nitrification process, ammonium is converted (through oxidation) to nitrite and then to nitrate, thus contributing to the eutrophication process. In small quantities, nitrite is toxic to water organisms as is ammonium, which is derived from ammonium under certain conditions (a combination of water temperature, salinity and pH-value). Ammonium represents a risk for drinking water sources as well. Background value for ammonium according to EEA is 0,015 mg NH4-N/L.


Charts

Figure VD10-1: Average annual concentrations of nitrate (NO3) in rivers
Sources:

Standardised Database for Water Quality Monitoring, Slovenian Environment Agency (2025)

Show data
Mura[mg NO3/L] Drava[mg NO3/L] Sava[mg NO3/L] Soca[mg NO3/L] Adriatic rivers[mg NO3/L] Slovenia[mg NO3/L] background concentration (max)[mg NO3/L]
1996 1.65 1.53 1.22 0.88 0.73 1.20 0.90
1997 1.61 1.43 1.25 0.95 0.59 1.21 0.90
1998 1.58 1.52 1.11 0.92 0.77 1.14 0.90
1999 1.83 1.39 1.15 1.03 0.81 1.18 0.90
2000 1.42 1.42 1.12 0.87 0.79 1.11 0.90
2001 1.34 1.21 1.10 0.78 0.74 1.06 0.90
2002 1.65 1.14 1.09 1.01 0.97 1.11 0.90
2003 1.61 1.42 1.28 0.79 1.07 1.27 0.90
2004 1.44 1.73 1.18 0.94 1.16 1.24 0.90
2005 2.44 1.54 1.27 0.99 0.87 1.36 0.90
2006 3.34 1.85 1.32 1 0.73 1.55 0.90
2007 2.40 1.32 1.32 0.93 0.79 1.47 0.90
2008 1.89 1.23 1.09 0.97 0.64 1.19 0.90
2009 2.44 1.33 1.26 1.04 0.70 1.45 0.90
2010 2.17 1.41 1.18 0.93 0.58 1.35 0.90
2011 2.04 1.22 1.27 0.84 0.62 1.34 0.90
2012 2.02 1.17 1.17 1.16 0.62 1.30 0.90
2013 2.08 1.10 1.15 1.31 0.91 1.34 0.90
2014 2.30 1.15 1.16 1.38 0.61 1.36 0.90
2015 2.10 1.04 1.11 1.28 0.63 1.26 0.90
2016 2.09 1.21 1.08 1.03 0.48 1.22 0.90
2017 2.17 1.27 1.04 0.93 0.61 1.24 0.90
2018 2.37 1.24 1.07 0.96 0.59 1.30 0.90
2019 2.44 1.03 1.06 0.96 0.61 1.28 0.90
2020 2.07 1.14 1.16 0.79 0.45 1.28 0.90
2021 1.93 1.10 1.02 0.84 0.55 1.11 0.90
2022 2.30 1.03 0.99 0.75 0.84 1.12 0.90
2023 2.26 1.10 1 0.70 0.55 1.17 0.90
2024 2.23 0.97 1.01 0.78 0.73 1.17 0.90
Figure VD10-2: Average annual concentrations of orthophosphate (PO4) in rivers
Sources:

Standardised Database for Water Quality Monitoring, Slovenian Environment Agency (2025)

Show data
Mura[mg PO4-P/L] Drava[mg PO4-P/L] Sava[mg PO4-P/L] Soca[mg PO4-P/L] Adriatic rivers[mg PO4-P/L] Slovenia[mg PO4-P/L] background concentration[mg PO4-P/L]
1996 0.07 0.02 0.04 0.01 0.02 0.03 0.01
1997 0.04 0.02 0.03 0.01 0.01 0.03 0.01
1998 0.08 0.03 0.07 0.01 0.01 0.06 0.01
1999 0.07 0.03 0.05 0.01 0.02 0.05 0.01
2000 0.10 0.04 0.07 0.02 0.02 0.06 0.01
2001 0.14 0.03 0.07 0.01 0.02 0.06 0.01
2002 0.12 0.03 0.06 0.01 0.01 0.05 0.01
2003 0.16 0.02 0.09 0.01 0.01 0.08 0.01
2004 0.06 0.03 0.07 0.01 0.01 0.05 0.01
2005 0.12 0.03 0.05 0.01 0.01 0.05 0.01
2006 0.05 0.04 0.08 0.01 0.01 0.06 0.01
2007 0.12 0.04 0.10 0.01 0.01 0.08 0.01
2008 0.07 0.04 0.03 0.01 0.01 0.03 0.01
2009 0.04 0.06 0.04 0.01 0.02 0.04 0.01
2010 0.05 0.08 0.03 0.01 0.01 0.04 0.01
2011 0.05 0.05 0.05 0.01 0.01 0.04 0.01
2012 0.06 0.09 0.07 0.01 0.01 0.06 0.01
2013 0.04 0.07 0.04 0.02 0.01 0.05 0.01
2014 0.04 0.04 0.05 0.01 0.01 0.04 0.01
2015 0.06 0.03 0.08 0.01 0.02 0.06 0.01
2016 0.06 0.04 0.03 0.01 0.01 0.04 0.01
2017 0.07 0.05 0.04 0.01 0.01 0.04 0.01
2018 0.06 0.03 0.03 0.01 0.01 0.03 0.01
2019 0.07 0.04 0.03 0.01 0.01 0.04 0.01
2020 0.03 0.04 0.03 0.01 0.01 0.03 0.01
2021 0.06 0.03 0.05 0.01 0.01 0.04 0.01
2022 0.03 0.02 0.02 0.01 0.01 0.02 0.01
2023 0.03 0.02 0.01 0.01 0.01 0.02 0.01
2024 0.04 0.01 0.01 0.01 0.01 0.02 0.01
Figure VD10-3: Average annual values of biochemical oxygen demand (BOD5) in rivers
Sources:

Standardised Database for Water Quality Monitoring, Slovenian Environment Agency (2025)

Show data
Mura[mg O2/L] Drava[mg O2/L] Sava[mg O2/L] Soca[mg O2/L] Adriatic rivers[mg O2/L] Slovenia[mg O2/L] background concentration (max)[mg O2/L]
1996 4.70 3.20 3.30 2.10 1.90 3 1.40
1997 5.60 3.10 3.40 1.70 3.10 3.20 1.40
1998 4.80 2.60 2.70 1.80 2.20 2.70 1.40
1999 5 3 2.90 1.30 2.50 2.80 1.40
2000 6.20 2.30 2.90 2 2.10 2.80 1.40
2001 4.50 2.30 2.90 1.50 2.90 2.70 1.40
2002 5.30 3 2.70 2.10 3.10 2.90 1.40
2003 7.90 2.80 3.30 2.20 2.10 3.50 1.40
2004 6.10 2.20 3 1.60 1.50 3 1.40
2005 5.30 1.90 2.40 1.50 1.70 2.50 1.40
2006 1.90 1.90 1.70 0.90 1.60 1.60 1.40
2007 1.80 1.30 1.60 1.20 1.30 1.50 1.40
2008 1.50 1.50 1 0.90 1.10 1.10 1.40
2009 1.70 1.50 0.90 1 0.90 1.20 1.40
2010 1.50 1.70 1.10 0.90 1 1.30 1.40
2011 1.40 1.60 1.60 1 1.10 1.50 1.40
2012 1.50 2 1.50 0.70 1.20 1.50 1.40
2013 1.20 1.30 1.20 0.70 0.70 1.20 1.40
2014 1.30 1.10 1.20 1.10 1 1.20 1.40
2015 1.40 1.30 1 0.80 1.30 1.10 1.40
2016 1.30 1.40 0.80 1 1.20 1 1.40
2017 1.50 1.40 1 0.80 1.30 1.10 1.40
2018 1.60 1.20 1 0.70 1 1.10 1.40
2019 1.70 1.10 0.90 0.70 0.70 1.10 1.40
2020 1.50 1.30 1 0.60 0.80 1.10 1.40
2021 1.53 1.16 0.88 0.54 0.68 0.98 1.40
2022 1.85 1.45 0.92 1.13 1.22 1.14 1.40
2023 1.60 1.60 0.80 0.70 0.80 1 1.40
2024 1.60 1.10 0.70 0.90 1.20 1 1.40
Figure VD10-4: Average annual concentrations of ammonium (NH4) in rivers
Sources:

Standardised Database for Water Quality Monitoring, Slovenian Environment Agency (2025)

Show data
Mura[mg NH4-N/L] Drava[mg NH4-N/L] Sava[mg NH4-N/L] Soca[mg NH4-N/L] Adriatic rivers[mg NH4-N/L] Slovenia[mg NH4-N/L] background concentration[mg NH4-N/L]
1996 0.62 0.22 0.44 0.18 0.19 0.36 0.05
1997 0.54 0.22 0.63 0.13 0.16 0.47 0.05
1998 0.50 0.16 0.43 0.05 0.06 0.33 0.05
1999 0.30 0.16 0.24 0.02 0.15 0.20 0.05
2000 0.42 0.12 0.37 0.04 0.07 0.28 0.05
2001 0.30 0.11 0.29 0.03 0.18 0.22 0.05
2002 0.48 0.16 0.31 0.02 0.05 0.25 0.05
2003 0.57 0.13 0.36 0.05 0.06 0.30 0.05
2004 0.31 0.14 0.34 0.01 0.04 0.25 0.05
2005 0.21 0.14 0.26 0.02 0.04 0.19 0.05
2006 0.16 0.09 0.34 0.02 0.10 0.22 0.05
2007 0.14 0.08 0.23 0.02 0.07 0.16 0.05
2008 0.07 0.11 0.12 0.01 0.02 0.10 0.05
2009 0.13 0.14 0.24 0.03 0.01 0.18 0.05
2010 0.12 0.14 0.14 0.01 0.03 0.12 0.05
2011 0.10 0.15 0.36 0.02 0.03 0.24 0.05
2012 0.10 0.15 0.38 0.02 0.02 0.25 0.05
2013 0.07 0.08 0.20 0.02 0.01 0.13 0.05
2014 0.09 0.07 0.10 0.02 0.02 0.08 0.05
2015 0.07 0.03 0.05 0.02 0.02 0.05 0.05
2016 0.08 0.08 0.05 0.03 0.03 0.06 0.05
2017 0.12 0.09 0.08 0.01 0.03 0.07 0.05
2018 0.10 0.07 0.05 0.03 0.02 0.06 0.05
2019 0.12 0.11 0.08 0.01 0.01 0.09 0.05
2020 0.10 0.08 0.06 0.02 0.04 0.07 0.05
2021 0.17 0.06 0.05 0.04 0.01 0.07 0.05
2022 0.16 0.06 0.05 0.01 0.04 0.06 0.05
2023 0.12 0.07 0.04 0.02 0.03 0.05 0.05
2024 0.09 0.03 0.04 0.01 0.04 0.04 0.05

Methodology

Other sources and literature

  1. Knehtl M., Debeljak B., 2021. Priprava predloga mejnih vrednosti za vrednotenje ekološkega stanja vodotokov na podlagi izbranih fizikalno-kemijskih parametrov. Poročilo o delu za leto 2021. Inštitut za vode RS, Ljubljana.
  2. Ministrstvo za okolje in prostor, 2009. Vrednotenje ekološkega stanja površinskih voda s splošnimi fizikalno-kemijskimi elementi.
  3. Pravilnik o pitni vodi, Uradni list RS, št. 19/04, 35/04, 26/06, 92/06, 25/09, 74/15, 51/17, 61/23.
  4. Štupnikar N., Urbanič G., 2013. Metodologija vrednotenja ekološkega stanja s podpornimi fizikalno-kemijskimi elementi - vrednotenje na podlagi podlagi ortofosfata in razvršcanje vodnih teles rek na podlagi elementa kakovosti stanje hranil. Poročilo o delu za leto 2013. Inštitut za vode RS, Ljubljana.


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