Biochemical oxygen demand (BOD5) and ammonium concentrations for 2010-2023. have increased in the downstream sections of Armenian rivers during the period. The main sources of TQP5 and ammonium pollution are untreated or insufficiently treated municipal wastewater, which, together with agricultural runoff due to the lack of treatment plants, are discharged directly into rivers.
TQP5 and ammonium concentrations are mainly stable at monitoring points upstream of settlements.
The average ammonium concentration at monitoring points downstream of settlements increased by 93% (from 1.4 to 2.7 mg N/l) between 2008 and 2023.
The average TQP5 concentration at monitoring points downstream of settlements increased by 22% (from 3.2 to 3.9 mg O2/l) between 2008 and 2023.
In 2023, the maximum number of monitoring points with high ammonium concentrations was falls in the Hrazdan and Akhuryan watershed management areas (WBA).
Relatively high levels of TQP5 in 2023 were mainly recorded in the South, Akhuryan and Hrazdan WBAs.
Data sources:
Data was provided by the Ministry of Environment of the Republic of Armenia under the ENI SEIS II East project activities
(C10, C11) Water quality indicator, by observation points and years provided by ArmStatBank
Note: The number of river observation points is 45 (21 observation points are located below settlements and 24 observation points are located above settlements), representing 22 rivers. The graphic on the right shows the averaged time series without the 55th observation point.
Data sources:
Data was provided by the Ministry of Environment of the Republic of Armenia under the ENI SEIS II East project activities
(C10, C11) Water quality indicator, by observation points and years provided by ArmStatBank
Note: The number of river observation points is 45 (21 observation points are located below settlements and 24 observation points are located above settlements), representing 22 rivers. The graphic on the right shows the averaged time series without the 55th observation point.
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Data sources:
Data was provided by the Ministry of Environment of the Republic of Armenia under the ENI SEIS II East project activities
(C10, C11) Water quality indicator, by observation points and years provided by ArmStatBank
Note: Water quality classes determined by TQP5 (left) and ammonium (right) according to the average annual concentrations of river monitoring points in 2023 (Akhuryan, Araratyan, Hrazdan, Northern, Sevan, Southern RBDs). The number of monitoring points in the corresponding RBD is given in brackets. The national assessment system has been applied. For information on the relevant national norms, see the indicator description in the "National Target" section.
BOD5 and ammonium are the main indicators for the characterization of organic water pollution. BOD5 shows how much dissolved oxygen is used to break down organic matter in the water. Concentrations of these indicators usually increase as a result of the absence of wastewater treatment plants, organic pollution of industrial and agricultural runoff. Organic pollution can lead to deoxidation of river water, increase in ammonium concentration, and extinction of fish and invertebrates. The main source of organic matter in Armenia is wastewater (untreated or insufficiently treated), which is discharged directly into rivers due to the lack of treatment plants.
2010-2021 Average concentrations of BOD5 and ammonium increased at observation sites downstream of settlements due to untreated domestic wastewater and agricultural runoff. 2010-2021 in observation points located below settlements, the average concentration of BOD5 increased by 53%, and the concentration of ammonium increased by more than 2 times. Average concentrations of BOD5 and ammonium are relatively more stable at observation points above settlements. This means that in less populated areas, there is less municipal wastewater. Involved in all 45 observation points in 2010-2021. growth is slightly lower than at observation points below settlements.
Hrazdan River is one of the longest and most polluted rivers in Armenia. The effect of the lack of a sewage treatment plant is especially noticeable at observation point 55, which is the first observation point after the city of Yerevan (the capital of Armenia, about 1 million people) and characterizes the communal-domestic impact of the city on the river. This fact has a large effect on the averaged time series, especially for ammonium. In 2021, the average ammonium concentration at observation points downstream of settlements is more than 2 times higher when observation point 55 is included. The difference between the averaged results with and without observation point 55 increases over time. For BOD5 the difference is smaller, but again there is a time-dependent increasing trend, which means that BOD5 increases more at observation point 55 than at the other observation points.
Figure 4 - Rivers – BOD5 (2023) |
Figure 5 - Rivers – Ammonium (2023) |
Data sources:
The maps was provided by the "Hydrometeorology and Monitoring Center" SNCO of the Ministry of Environment.
Note: Distribution of river monitoring observation points according to water quality classes with BOD5 (left) and ammonium (right) in 6 water basin management areas of the Republic of Armenia (Akhuryan, Araratyan, Hrazdan, Northern, Sevan, Southern) based on the annual average concentrations of 2021. In parentheses are the number of monitoring observation points in the respective WTP. A national assessment system was applied. For information on the relevant national norms, see the indicator profile in the "National Target" section.
The class system is the same as the one used in the EEA indicator WAT 002- Oxygen consuming substances European rivers. See the indicator specification section there for further information.
Note: Distribution of river monitoring observation points according to ammonium concentration classes in 6 water basin management areas of the Republic of Armenia (Akhuryan, Araratyan, Hrazdan, Northern, Sevan, Southern), based on the annual average concentrations of 2021.
In 2021, the mean BOD5 for observation points below settlements is 64% higher than for observation points above settlements, which in particular reflects the discharge of untreated wastewater. The difference is much larger for ammonium, where in 2021 the average values for sites below settlements are 5 times higher than the average values for sites above settlements (and a corresponding 9 times higher, including site 55).
In 2021, the water quality at observation points N38 of the Karkachun River of the Akhuryan WTP and N344 of the Karchevan River of the Southern WTP, according to the national water quality norms, was assessed as "bad" due to the high concentration of BOD5 and other indicators.
According to the average ammonium concentrations in 2021, monitoring sites below settlements are mostly of "inadequate" or "poor" quality. High concentrations of ammonium were observed in most observation points of Hrazdan WTP, N4 of Pambak River in Northern WTP, N38 of Karkachun River in Akhuryan WTP, N344 of Karchevan River in South WTP and N107 of Vararak River, where the water quality was assessed as "poor". due to other indicators as well.
In general, the highest concentration of BOD5 and ammonium in 2021 is observed in the Hrazdan River at the observation point downstream of Yerevan city (observation point 55). The Hrazdan River Basin is the most populated river basin in Armenia, dominated by observation points with "poor" water quality and especially ammonium pollution.
C-10 indicator - Biochemical oxygen demand (BOD5) and ammonium concentration in rivers
The annual average BOD after five days of incubation (BOD5) at 20 degrees Celsius is expressed in mg of O2/litre; the ammonium concentration is expressed in mg of N/litre.
Large quantities of organic matter (microbes and decaying organic waste) can result in reduced chemical and biological quality of river water, impaired biodiversity of aquatic communities, and microbiological contamination that can affect the quality of drinking and bathing water. Sources of organic matter are discharges from wastewater, industrial effluents and agricultural runoff. Organic pollution leads to higher rates of metabolic processes that demand oxygen. This could result in the development of water zones without oxygen (anaerobic conditions). The transformation of nitrogen to reduced forms under anaerobic conditions, in turn, leads to increased concentrations of ammonium, which is toxic to aquatic life above certain concentrations, depending on water temperature, salinity and pH.
Context description
National policy context
This Code regulates water relations in the field of use, protection and development of water resources for guaranteed, adequate and safe supply of water for the population, protection of the environment and promotion of the rational development of the water fund of the country.
Requires “on establishing the norms for assuring water quality of each Water Basin Management District, depending upon local peculiarities”.
International policy context
The UNECE-WHO/Europe Protocol on Water and Health aims to protect human health by better water management and by reducing water-related diseases. The Protocol provides a framework to translate into practice the human rights to water and sanitation and to implement SDG 6. Armenia has signed the Water and Health Protocol in 1999, however, ratification is under the process and not finalized yet.
Targets
National targets
The norms for some parameters according to Government Decision №75-N:
Parameter | Water Classes | ||||
I (high) | II (good) | III (moderate) | IV (poor) | V (bad) | |
Ammonium (mg NH4-N/l) | <0.2 | 0.2-0.4 | 0.4-1.2 | 1.2-2.4 | >2.4 |
BOD (mg O2/l) | <3.0 | 3.0-5.0 | 5.0-9.0 | 9.0-18 | >18 |
International targets
The UN Sustainable Development Goal 6 target 6.3 aims to achieve, by 2030, improve water quality by reducing pollution, eliminating dumping and minimizing release of hazardous chemicals and materials, halving the proportion of untreated wastewater and substantially increasing recycling and safe reuse globally.
Related policy documents
Methodology for indicator calculation
The monitoring programme for BOD5 and ammonium concentrations in rivers is structured to take into account the spatial and temporal dynamics of the indicators. The monitoring sites are located both before and after settlements, which provides information both on background concentrations and the influence of the settlements. The number of rivers sites is 45 (21 sites above settlements and 23 below), representing 22 rivers. The monitoring frequency is 7-12 per year, covering all hydrological phases.
The chemical analyses are carried out at the Laboratory of Environmental Monitoring and Information Center of the Ministry of Environment of the Republic of Armenia.
Annual time series for each site are calculated by averaging the values for individual samples per year. Aggregated time series are calculated as the average of the individual annual time series. For rivers separate aggregations are made for river sites above and below settlements.
Methodology for gap filling
For time series and trend analyses, only series that are complete (i.e. no missing values in the site data series) are used. This is to ensure that the aggregated data series are consistent, i.e. including the same sites throughout the time series. In this way assessments are based on actual changes in concentration, and not changes in the number of sites. Hence, no gap filling has been applied.
Methodology references
Methodology uncertainty
No methodological uncertainty has been specified.
Data sets uncertainty
No uncertainty has been specified.
Rationale uncertainty
Biochemical oxygen demand and total ammonium are well suited for illustrating water pollution with oxygen consumption. However, using annual average values may not fully illustrate the severity of low oxygen conditions.
Indicator Set UNECE regional environmental indicators-C10 and European Environment Agency Core Set of Indicators – CSI 019 |
Date: 13.02.2023 Authors: Shahnazaryan Gayane Zatikyan Anna |
Indicator Title
C10- BOD and concentration of ammonium in rivers