Authors

  • А. Аkhmedova
    Hydrometeorological Research Institute

DOI:

https://doi.org/10.71337/inlibrary.uz.ijai.115519

Abstract

The article presents the results of research on the hydrological and hydrochemical regimes of the Chirchik river. This research is devoted to a scientific or practical problem, such as insufficient effectiveness of existing monitoring. Factual data on the concentration of pollutants, most often exceeding the maximum permissible concentrations, are presented. An analysis of the study of the spatial distribution of pollutants (PV) along the river length is presented, which allows for the identification of the most polluted areas. The dependence of the concentration of pollutants on the water content of the year was considered.

 

 

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УДК

556.535.8

FEATURES OF THE HYDROLOGICAL AND HYDROCHEMICAL REGIMES OF

THE CHIRCHIK RIVER UNDER CLIMATE CHANGE CONDITIONS

А.Аkhmedova

Hydrometeorological Research Institute,

t.akhmedova1962@gmail.com

Abstract:

The article presents the results of research on the hydrological and hydrochemical

regimes of the Chirchik river. This research is devoted to a scientific or practical problem, such

as insufficient effectiveness of existing monitoring. Factual data on the concentration of

pollutants, most often exceeding the maximum permissible concentrations, are presented. An

analysis of the study of the spatial distribution of pollutants (PV) along the river length is

presented, which allows for the identification of the most polluted areas. The dependence of the

concentration of pollutants on the water content of the year was considered.

Key words

: pollution, quality, water resources, anthropogenic factor, river, petroleum products,

wastewater, industry, utilities, multi-water, water consumption.

Introduction.

The problem of rational use of water resources and their protection from

pollution is one of the pressing problems of our time.

The decree of the President of the Republic of Uzbekistan states: "The increase in the discharge

of pollutants into water bodies leads to the pollution of open watercourses and, as a

consequence, causes irreparable damage to aquatic flora and fauna, as well as affects public

health"[1].

Currently, there is a need to assess and predict the quality of river water. Currently, there is a

need to assess and predict the quality of river waters, and primarily transboundary rivers. This

also applies to the transboundary Syrdarya River. The issues of protecting and sustainably using

transboundary water resources of the river basin concern the interests of many people living in

the region. This problem is especially relevant for regions with a tense water balance, where the

development of an economic sector may be hindered not only by the quantitative but also by the

qualitative depletion of water resources. Such regions include the Chirchik River basin. The

Chirchik River with its tributaries enters the Syr Darya River basin and is its right-bank

tributary.

After the Chirchik River flows into the Syr Darya River, the territory of the Republic of

Kazakhstan begins after 90 km. Therefore, the Chirchik River's pollution can significantly

affect the water quality in the lower reaches of the Syr Darya River.

Due to the intensive use of the Chirchik River basin's water resources for various purposes and

the discharge of untreated or poorly treated wastewater into the river, the quality of both surface


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and groundwater is deteriorating over time. In some areas, the river water has become

unsuitable not only for fish farming, which places stricter demands on water quality, but also

for domestic and drinking water supply.

Object of research. The Chirchik River basin is located in the north-eastern part of the Republic

of Uzbekistan. (Fig. 1). From a hydrological point of view, the river belongs to the most well-

studied river basins of Central Asia.

Fig-1. Location of the study object

The basin area of the river is 14900 km2, length -161 km [10]. The river flows through an area

with intensive economic activity. Even in the drain formation zone, there are objects that are

sources of pollution. The Chirchik River basin district is the largest industrial center of

Uzbekistan. The main place in its complex economic complex is occupied by industry and

agriculture. Here, almost all the republic's machine-building products serving cotton growing

and the cotton processing industry are produced, and machines for the mining, chemical, food,

and light industries are manufactured.

Multidisciplinary agriculture occupies an important place in the district's economy. The

total area of irrigated land in the Tashkent region is 399.2 thousand hectares, which is 9.15% of

the total area of the Republic. About 4 million people live in cities, more than 1 million in rural

areas, the population density here is very high - about 200 people per 1 km2. The entire

economy of the region is closely linked to the intensification of water use. The high degree of

Chirchik River water use leads to its intensive pollution by wastewater discharges. In the

prospective plans for the development of the sectors of the republic's economy, the issue of

water source purity will be a primary problem as the basis of balance in the ecological situation

of the basin [2].

Household wastewater, industrial wastewater, and agricultural wastewater have a

significant impact on water quality. These factors have a noticeable impact on the nature of

surface water pollution.

One of the significant sources of river water pollution is also the discharge of collector-

drainage waters from numerous irrigated areas of the Tashkent region. Irrigated lands in the


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Tashkent region are mostly not saline, so the existing collector network can fully handle land

leaching.

The most characteristic features of the climate of this territory are its continentality, as well

as the abundance of heat throughout the growing season. In the foothills, an average of 435-514

mm of precipitation falls annually, while in the mountains it is 895 mm and more. In the plains,

there is a shortage of moisture in most years. In summer, in July-August, there is practically no

precipitation. Changes in Air Temperature and Precipitation Using the Tashkent Meteorological

Station as an Example Meteorological observations have been conducted since the late 19th

century. Figure 1 shows graphs of Tashkent GMS for as an example 2013-2023

Figure 1. Average long-term trend of average

air temperature for 2013-2023

Changes in air temperature at this station are

observed in a positive trend. Over 150 years, the average annual air temperature in Tashkent

has increased by 1.2°C. During periods of warming, the amount of atmospheric precipitation

has not undergone significant changes [12].

Subject of research

. Study of the spatial (along the river) distribution of pollutants (PV). This

is of greatest interest, as it allows us to identify the most polluted areas, hypothesize possible

sources of pollution, and subsequently identify them, as well as propose measures for protection

from pollution and cleaning.

Materials used

. In this study, the results of ground data from Uzhydromet's hydrological posts

and water quality observation points in the Tashkent region were used [4]

Research methods

. The work used mathematical statistics, cartographic methods, and

generalized methods for assessing the hydroecological state of the water div.

Main results and their discussions

. To characterize the hydrological regime, we selected a

series of observations of water flow at the Gazalkent hydropost from 1991 to 2021. The upper

watershed of the Chirchik river mouth is outside the zone of anthropogenic influence and

characterizes the natural regime of the river [11].


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Figure 2 Chronological course of average annual water discharges of the Chirchik River

for 1991-2021 (Gazalkent)

A negative trend is observed in the changes in average annual water discharges for the Chirchik

River (Figure 2). During the period under study, the hydrological regime of the studied rivers

was characterized as follows: low-water - 2008 and high-water - 1994, and medium-water -

2015.

Fig. 3. Spatial change in nitrite concentration over the characteristic years in the Chirchik River

Analysis of the obtained data on the intra-annual distribution of water discharges showed that

the Chirchik River floods occur in May-August. This depends on the type of river feeding. As

the Chirchik River belongs to the snowy-glacial type of feeding, it is due to the peak flow

during the summer months due to the melting of glaciers (see Figure 3).


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Fig. 4 Situational diagram of the Chirchik River with an indication of water

quality monitoring points

To date, the state of surface water quality of the Chirchik River is assessed at 9 observation

points of the Uzhydromet (see Figure 1), and for the study of water quality, we have selected 6

main channels on the Chirchik River from its upper reaches to the mouth

1. Gazalkent city - 0.3 km above Gazalkent city;

2. Chirchik city - 0.5 km below the city, 3.0 km below the "Maxam-Chirchik" JSC wastewater

discharge;

3. Tashkent city - higher than the city;

4. Tashkent city - within the city limits, 3 km below the Sergeli industrial zone embankment;

5. Novomikhaylovka settlement, 1.6 km below the settlement;

6. Chinoz city - 3.5 km from the mouth (Figure 4).

Based on the results [2,7,8,9] and our own research, CОD (chemical oxygen demand- an

integral indicator of water quality characterizing the content of difficult-to-oxidize organic

substances), BOC

5

(biological oxygen consumption over five days - an indicator characterizing

the content of easily-oxidizing organic substances) were adopted as the main controlled

indicators. In addition, the actual concentrations of petroleum products, from heavy metal ions -

copper ions, nitrogen-containing pollutants of both industrial and organic origin (nitrates,

nitrites, ammonia) were studied.

One of the important integral indicators characterizing the state of water quality is the

biological oxygen consumption (BOC). By the magnitude of this indicator, one can judge the

presence of easily oxidizing organic substances in water. However, throughout the entire

Chirchik riverbed, the concentration of BOC and COD does not exceed the maximum

permissible concentration (MPC). Figure 5 shows the distribution of average long-term BPK

and CPK values along the length of the Chirchik River [4].


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Fig. 5

Average long-term change in the concentration of pollutants

along

the Chirchik River

-

концентрация ЗВ

- MPC

It can be confidently stated that Chirchik and its industrial zone, as well as the territory of the

city of Tashkent, have a strong influence on the quality of surface waters to increase the content

of BOC and COD. Analyzing the visual information of the river from the "Maxam-Chirchik"

JSC wastewater discharge point to the "Novomikhailovka" dam, the largest amount of easily

oxidized organic matter enters the river.

Moreover, taking into account the peculiarities of economic activity in this section of the

river, it can be assumed that the main sources of pollution by such organic substances are

agriculture and communal-domestic services. The largest contribution to the pollution of the

river with organic substances in this area is made by these two industries.

The change in oil product concentrations along the river's length shows that the most

urbanized sections of the river contribute the most to surface water pollution. In Figure 5, the


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pollution zones are clearly distinguished. Moreover, the Tashkent city zone contributes the most

to river water pollution. The trend of increasing oil product concentration from the "Maxam-

Chirchik" dam to the "Chinaz" dam indicates insufficient reliable protection of the water source

from this type of pollution.

The main sources of ammonium nitrogen in the Chirchik River basin appear to be

concentrated in the upper reaches above the "Maxam Chirchik" JSC discharge - 0.51 mg/dm

3

.

Below this channel or such sources are absent or do not have any significant impact on water

quality. For this very reason, the spatial distribution graph appears so flat, with a clearly

expressed tendency to decrease concentration below the 2nd channel towards the mouth of the

river (see Figure 5).

A high content of copper ions in a section, where it would seem that at least they should

not be found in high concentrations (1.90 μg/dm3), may indicate either natural pollution or a

non-specific source of copper ions entering surface waters. These may be either abandoned

workings or tailings from old processing plants.

Regarding the sharp increase in the concentration of copper ions in section 2, this

increase is apparently related to the discharge of industrial wastewater in this area, or to the old

wastewater collectors containing high concentrations of copper ions in the industrial areas of

Chirchik city, and their possible leaks, including filtration losses. If we consider the age of the

deposits, the geology of the riverbed base, and the close relationship between the surface and

underground tributaries of the Chirchik River, the appearance of increased concentrations of

copper ions along the entire length of the river is not surprising.

Table 1

Limits of fluctuation of pollutants in the water of the Chirchik River (1991-2021)

Hydraulic

solutions

COD

BOC

petroleum

products

nitrites

copper

min

max

min

max min

max

min

max

min max

1

1,5

4,82

0,39

1,72 0,01

0,14

0,001

0,08

0,01

3,6

2

2,6

12,6

1,04

5,12 0,02

0,18

0,019

0,36

0,9

4,4

3

3,93

9,3

1,38

6,2 0,04

0,19

0,04

0,137

0,3

4,3

4

3,81

12,7

1,62

6,35 0,02

0,11

0,08

0,358

0,01

3,4

5

2,6

12,68 1,62

4,53 0,01

0,24

0,014

0,201

0,5

3,8

6

3,8

13,37 1,27

5,29 0,01

0,24

0,004

0,328

0,6

4,2

REM

15,0мг/дм3

3,0мг/дм3

0,02мг/дм3

0,02мг/дм3

1,0

мкг/дм3

Along the river's length, a steady increase in nitrate nitrogen concentration is observed from the

upper reaches to the mouth, and throughout the entire river, the nitrate nitrogen concentration

does not exceed the REM [5].

Discussion.

The constant increase in concentration from the upper reaches to the lower

ones, starting from the city of Gazalkent towards the city of Tashkent, with all certainty,

indicates a constant increase in the volume of pollutants containing nitrite forms of nitrogen-

containing substances entering surface waters (Table 1).

Based on the analysis of changes in nitrite nitrogen concentrations in the surface waters

of the Chirchik River, it can be said with a certain degree of certainty that the main sources of


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pollution by this form of nitrogen-containing pollutants are concentrated in the section of the

river below the "Maxam-Chirchik" JSC discharge and above Tashkent city, and the increased

nitrite content in the Chinoz channel may be caused by discharges of polluted wastewater.

Considering that the main source of such pollution in the conditions of the Chirchik

River basin is wastewater containing fecal pollutants, it can be said that the protection of

surface waters from untreated or poorly treated municipal wastewater is unsatisfactory.

Fig. 6. Spatial change in nitrite concentration over characteristic years

(Chirchik River, Gazalkent gauging station)

In Figure 6, it was established that in high-water years, the nitrite concentration decreases

(increase in REC 1.6 times), in medium-water years (increase in REC 4.9 times), and

conversely, in low-water years, the concentration value increases (increase in REC 7 times).

This indicates that under changing climate conditions, the river's sanitary condition depends on

the year's water content. The lower the water content, the higher the concentration of pollutants.

In order to maintain a favorable ecological situation and the required water quality in the lower

reaches of the Chirchik River, special discharges of the minimum water volume along the

riverbed are provided, which is called sanitary (ecological) discharge [6]

Conclusion.

1. The analyses we conducted allowed us to determine the list of pollutants (nitrites,

petroleum products, and copper ions) that most often exceed the maximum permissible

concentrations and have a dominant influence on the formation of surface water quality

indicators in the Chirchik River.

2. Based on the results of the analysis of the spatial distribution of pollutants, it was

possible to identify the most polluted areas (Chirchik, Tashkent, and Chinoz cities) and possible

sources of pollution (wastewater discharge from the "Suv ta'minot" branch of the Chirchik

Aeration Station, the Bektemir treatment plant, and the "Maxam-Chirchik" JSC treatment plant).

These results allow for their further identification and, moreover, to propose measures for

protection from pollution or cleaning.


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3. Water contaminated with untreated municipal and domestic wastewater can serve as a

cause of infectious diseases and even their epidemics. In the mouth of the river, pond fishing is

developed: in artificially created shallow water bodies, separated by temporary dams from the

main channel of the Chirchik River. Pollution can cause significant damage to the fish

population.

4. The banks of the Chirchik River are densely populated and, as our surveys have

shown, have numerous restaurants, unauthorized quarries, cafes, and dacha buildings with small

poultry and livestock farms. All household wastewater, including fecal wastewater, is

discharged into the river without any treatment; of course, no account is taken of all these

numerous discharges, and the water quality in the Chirchik River deteriorates from them,

especially in terms of nitrogen-containing substances. The "Maxam-Chirchik" plant, Chirchik

city's aeration station, and the Bektemir treatment plant, Salar aeration station have significant

impact on their concentration.

5.

It has been established that in high-water years, the nitrite concentration decreases,

and conversely, in low-water years, the concentration value increases. This suggests that under

changing climate conditions, the river's sanitary condition depends on the year's water content.

REFERENCES:

1. Decree of the President of the Republic of Uzbekistan UP No. 5863 dated October 30,

2019 "On approval of the concept of environmental protection of the Republic of

Uzbekistan until 2030”.

2. Axmedova T.A., Shetinnikov A.A. Current ecological state of the Chirchik River // Jurnal

“Ekologicheskiy vestnik” №3, Tashkent. 2017.— P.40-43.

3. Axmedova T.A., Vidineeva Ye.M., Gafurov A.A. Flooding of the Chirchik River by

Biogenic Vessels / Proceedings of the International Scientific and Practical Conference

“Modern Problems of Hydrogeology and Monitoring of the Environment in the SNG

Transit Environment” -Sankt-Peterburg, 22-24 October. 2020 у. — P 289-293.

4. Hydrological yearbook. Vol.5. River basins of Central Asia. Issue 9. Uzhydromet. 1991-

2021у

5. 6. Methodological principles for assessing and regulating anthropogenic impact on the

quality of surface waters // Edited by A.V.Karausheva. -L.: Gidrometeizdat.1987. —286 p.

6. 7. Markin V.N., Ratkovich L.D., Sokolova S.A. Integrated use of water resources and

protection of water bodies // Moscow. 2015. 316 p.

7. 8. Rubinova F.E. Ivanov Yu.N. Water quality of the rivers of the Aral Sea basin and its

change under the influence of economic activity. Tashkent, 2005. —185 p.

8. 9. Chembarisov E.I., Raximov M.N. Features of hydrological and hydrochemical

monitoring of surface waters of the middle reaches of the Syr Darya River.Tashkent,

«Navruz». 2019. —91p.

9. 10. Shilkrot G.S., Yasinskiy S.V. Spatiotemporal variability of nutrient flow and water

quality in a small river //Vodnie resursi, 2002. tom 29. №3. — P.343-349.

10. 11.Shuls V.L. Rivers of Central Asia. L.: Gidrometeoizdat 1965.- 691p.

11. 12. Akhmedova T, Akramova I., Radjabov A., Mavlyanova D. Assessment of the hydro-

ecological state of piedmont rivers of the Republic of Uzbekistan in the context of climate

change, International Scientific Conference "Construction Mechanics, Hydraulics and


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Water Resources Engineering". Tashkent

April 25, 2020

ID: 16f3802e-8427-4b16-87a1-

40964dfdf2d8 DOI 10.1088/1757-899X/883/1/012010.

12. 13.Keiser О. Bewertung und Entwicklung urbaner FlieBgewasser. Freiburg i. Br.: Institut

fur Landespflege, 2005. 280 p.

References

Decree of the President of the Republic of Uzbekistan UP No. 5863 dated October 30, 2019 "On approval of the concept of environmental protection of the Republic of Uzbekistan until 2030”.

Axmedova T.A., Shetinnikov A.A. Current ecological state of the Chirchik River // Jurnal “Ekologicheskiy vestnik” №3, Tashkent. 2017.— P.40-43.

Axmedova T.A., Vidineeva Ye.M., Gafurov A.A. Flooding of the Chirchik River by Biogenic Vessels / Proceedings of the International Scientific and Practical Conference “Modern Problems of Hydrogeology and Monitoring of the Environment in the SNG Transit Environment” -Sankt-Peterburg, 22-24 October. 2020 у. — P 289-293.

Hydrological yearbook. Vol.5. River basins of Central Asia. Issue 9. Uzhydromet. 1991-2021у

Methodological principles for assessing and regulating anthropogenic impact on the quality of surface waters // Edited by A.V.Karausheva. -L.: Gidrometeizdat.1987. —286 p.

Markin V.N., Ratkovich L.D., Sokolova S.A. Integrated use of water resources and protection of water bodies // Moscow. 2015. 316 p.

Rubinova F.E. Ivanov Yu.N. Water quality of the rivers of the Aral Sea basin and its change under the influence of economic activity. Tashkent, 2005. —185 p.

Chembarisov E.I., Raximov M.N. Features of hydrological and hydrochemical monitoring of surface waters of the middle reaches of the Syr Darya River.Tashkent, «Navruz». 2019. —91p.

Shilkrot G.S., Yasinskiy S.V. Spatiotemporal variability of nutrient flow and water quality in a small river //Vodnie resursi, 2002. tom 29. №3. — P.343-349.

Shuls V.L. Rivers of Central Asia. L.: Gidrometeoizdat 1965.- 691p.

Akhmedova T, Akramova I., Radjabov A., Mavlyanova D. Assessment of the hydro-ecological state of piedmont rivers of the Republic of Uzbekistan in the context of climate change, International Scientific Conference "Construction Mechanics, Hydraulics and Water Resources Engineering". Tashkent April 25, 2020 ID: 16f3802e-8427-4b16-87a1-40964dfdf2d8 DOI 10.1088/1757-899X/883/1/012010.

Keiser О. Bewertung und Entwicklung urbaner FlieBgewasser. Freiburg i. Br.: Institut fur Landespflege, 2005. 280 p.