Authors

  • Tulkin Rajabov
    Karshi State Technical University
  • Umida Allaerova
    Karshi State Technical University

DOI:

https://doi.org/10.71337/inlibrary.uz.ijai.120136

Abstract

One of the most urgent problems in the conditions of the resistance is the improvement of soil reclamation, prevention of secondary salinization, combating salinization, improvement of soil fertility, and maintaining the ecological state of the demand.

 

 

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MELIORATIVE STATUS OF IRRIGATED SOILS AND WAYS TO INCREASE

PRODUCTIVITY

Tulkin Tilakovich Rajabov

Associate Professor of the Department of "Technology of Cultivation and Processing of

Agricultural Products" of Karshi State Technical University

Allaerova Umida Akramkulovna

Student of Karshi State Technical University QXT-427-22-group

Аннотация:

Қарши дашти шароитида энг долзарб муаммолардан бири тупроқ

мелиорациясини яхшилаш, иккиламчи шўрланишни олдини олиш, шўрланишга қарши

курашиш, тупроқнинг балл бонитетини яхшилаш, экологик ҳолатини талаб даражасида

сақлаш.

Калит сўзлар: с

уғориш, сингиш, тупроқ, унумдорлик, туз, дехкончилик, агротехник,

шўрланиш, сув, сизоб, гектар, минераллаш.

Аннотация:

В условях Каршинской степи один из основных проблем является улучщить

мелиоративное состояние почв, предотвратит вторичное засоление почв, принимать

меры борьбы против засоление, улучщить бонитета почв и охрана естественное

экологического состояния природы.

Ключевые слова:

орошение, поглощение, почва, плодородие, соль, земледелие,

агротехника, засоление, вода, просачивание, гектары, минерализация.

Annotation:

One of the most urgent problems in the conditions of the resistance is the

improvement of soil reclamation, prevention of secondary salinization, combating salinization,

improvement of soil fertility, and maintaining the ecological state of the demand.

Key words:

irrigation, absorption, soil, fertility, salt, farming, agrotechnics, salinity, water,

seepage, hectares, mineralization.

Assessment of the melioration status of irrigated soils in the Karshi steppe conditions,

the formation of undesirable secondary salinization processes during their use, and the

composition and characteristics of measures necessary to eliminate these factors depend on the

analysis of natural factors. Disruption of agrotechnical processes Irrigation has a significant

impact on soil properties, as it increases soil moisture and brings dissolved salts into the water.

Irrigation water penetrates the soil, changing the water regime, and secondary salinization

occurs due to improper use of irrigation water.

One of the most important tasks facing agricultural workers is to improve soil

condition, prevent secondary salinization, combat salinization, maintain soil fertility, its

economic efficiency, ecological condition at the required level, and organize natural protection.

More than 45 percent of the 515.08 thousand hectares of irrigated agricultural land are

saline to varying degrees, which indicates a 4 percent decrease in saline areas compared to 2012.

In recent years, great attention has been paid to improving the reclamation condition of irrigated


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agricultural lands in the region. In 2012, 66 hectares, in 2014 - 71 hectares, in 2014 - 71

hectares, in 2014 - 160 hectares, in 2014 - 140 hectares. As of 2018, it has covered 1020

hectares. In 2012, 194.05 thousand hectares, in 2014 - 222.37 thousand hectares, in 2016 -

203.98 thousand hectares, in 2018 - 203.13 thousand hectares оrganized. In 2012, the area of

​ ​ 3-5 meters above sea level was 320.92 thousand hectares, in 2014 - 292.24 thousand

hectares, in 2016 - 309.95 thousand hectares. The indicator covers an area of ​ ​ 280.79

thousand hectares, and it is known that the water level in this valley ranges from 62.23 percent

to 54.52 percent.

In the analysis of mineral water levels in groundwater, the area of ​ ​ mineral water

levels per 1 liter of water was 102.51 hectares in 2012, 102.62 hectares in 2014, 102.62 hectares

in 2016, 98.8 hectares in 2016. In 2018, the area was 100.85 hectares, which is 1.62 times more

than in 2012.

During this period, the area with groundwater mineralization of 1-3 grams per liter also

decreased from 134.32 thousand hectares to 121.16 thousand hectares, or from 26.05% to

23.52%, or 2.53%. The area with a groundwater mineralization level of more than 3.0 grams

per liter was 278.83 hectares at the beginning of 2012, while by the end of 2018 this figure had

increased to 293.07 hectares or from 54.07 percent to 56.90 percent, that is, by 2.93 percent

over this period.

Table 1

Changes in groundwater levels

Sizob

waters

surface. m

2012

2014

2016

2018

a

thousand

to

%

a

thousand

to

%

a

thousand

to

%

a

thousand

to

%

<1

0,03

0,01

0,03

0,01

0,11

0,02

0,09

0,02

1-1,5

0,66

0,14

0,71

0,14

1,40

0,27

1,02

0,20

1,5-2,0

8,50

1,69

7,76

1,51

10,64

2,06

9,92

1,92

2,0-3,0

185,55

35,98

214,61

41,64

193,34

37,52 223,26

43,34

3,0-5,0

204,14

39,59

185,58

36,01

192,10

37,27 164,60

31,96

>5

116,78

22,64

106,66

20,70

117,85

22,86 116,19

22,56

Total

515,66

100

515,35

100

515,44

100

515,08

100

Over the years, a decrease in the amount of salts in the area with a groundwater

mineralization level of up to 3 grams per liter has been observed, while an increase in the area

with a groundwater mineralization level of more than 3 grams per liter has been observed.

As a result, it was observed that the amount of harmful salts in the upper layers of the

soil decreased, moderately and strongly saline areas became weakly saline, and weakly saline

areas became non-saline (Table 2).

Table 2

Changes in the area of saline aquifers with varying degrees of salinity

Salts

micdori, g

2012

2014

2016

2018

a

thousand

%

a

thousand

%

a

thousand

%

a

thousand

%


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to

to

to

to

<1 г

102,51

19,88

96,78

18,78 96,78

18,78 100,85

19,58

1-3 г

134,32

26,05

120,47

23,37 120,47

23,37 121,16

23,52

>3 г

278,83

54,07

298,19

57,85 298,19

57,85 293,07

56,90

Total

515,66

100

515,44

100

515,44

100

515,08

100

It was found that the area of non-saline soils in the irrigated areas of the region is

increasing, while the area of weak, medium, strong and saline soils is decreasing from year to

year. Non-saline soils increased from 272.87 thousand hectares in 2012 to 280.33 in 2018

(Table 3).

The area of land with medium, strong and very strong (saline) soils decreased

proportionally from 47.86; 12.84 thousand hectares in 2012 to 39.85; 10.23 thousand hectares

in 2018. It is seen that during these years the area of land requiring salt leaching and

improvement of soil melioration (strong saline and saline) decreased from 12.84 thousand

hectares to 10.23 thousand hectares or 20.33 percent.

In recent years, due to improved land reclamation, proper salt leaching, and irrigation,

the area of weakly, moderately, and strongly saline and brackish lands has significantly

decreased, leading to an increase in non-saline areas.

One of the main factors is the increased performance and efficiency of inter-district,

inter-farm and closed-bed collector-drainage networks in the irrigated farming areas of

Kashkadarya region. The total length of collector-drainage networks was 14,466.81 kilometers

in 2012, and by January 1, 2017, this figure was equal to 15,213.33 kilometers. According to

the above, it was found that the per hectare of irrigated area increased from 28.045

pagonometers to 29.56 pagonometers.

It is worth noting that in recent years, the decrease in the cost of production and the

increase in the level of profitability in districts such as Kasbi, Karshi, Koson, and Nishan,

which have a high production volume, are an example of this.

Thus, as a result of maintaining an acceptable level of syzyb waters (around 3 meters), their low

salinity (1-3 g/l), mineralization of irrigation water (0.7-1.8 g/l), agrotechnical and land

reclamation activities the total saline area of ​ ​ the 515.08 thousand hectares of total irrigated

area in the region decreased from 242.9 thousand hectares to 230.5 thousand hectares, or 12,400

hectares.

The total amount of irrigation water received for irrigation in the region was 4434.32

million cubic meters, and its dry residue per liter was 1.0475 grams. At the same time, the total

amount of salt introduced with irrigation water amounted to 5221.73 thousand tons in dry

residue.

During the year, the amount of groundwater discharged through the collector-drainage

networks amounted to 1434.19 cubic meters. The mineralization level of the collector-drainage

waters was 3.9588 per liter of groundwater in terms of dry residue. 7055.82 thousand tons of

salt were discharged from the collector-drainage networks and irrigation waters and soil layers.

When comparing the amount of salt entering through irrigation water with the amount of salt

removed through collector-drainage networks, it was found that 1,626.76 thousand tons of

excess salt was removed from the soil layers. This is the case in the Nishan, Mubarak, Karshi,

and Mirishkor districts of the region. On the contrary, in districts such as Koson, Kamashi, and


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Kasbi, the difference between the amount of salt entering with irrigation water and the amount

of salt leaving through collector-drainage networks changed negatively, or in the above-

mentioned districts, 169.98; 90.57 and 103.67 tons of harmful salts remained in the soil layers,

respectively (Table 4).

Table 4

Water-salt balance in the irrigated areas of the region in 2016

D

ist

ric

ts

Introduction

flowed

salts

(tons)

solid

residue

Output part

Salts

released

(tons)

Changes

in

the

amount of

salts (ton

+-)

solid

residue. +-

the

amount of

water

taken

from the

district

border

(mln. m3)

salt content

of irrigation

water, gr/l

solid

residue

stay

tight

salinity

of

raw

water

(gr/l)

1

Guzor

247,30

1,46

361,06

98,03

6,37

624,26

-263,19

2

Karshi

421,022

1,66

698,90

146,64

5,05

739,80

-40,90

3

Koson

656,32

1,54

1010,73

183,57

4,58

840,75

169,98

4

Kitob

105,66

0,29

30,64

3,80

0,566

2,15

28,49

5

Kamashi

290,23

1,17

339,57

42,38

5,88

249,00

90,57

6

Mirishkor 683,27

1,28

874,59

240,64

4,97

1195,68

-321,09

7

Muborak

279,75

1,25

349,69

195,49

5,56

1086,92

-737,24

8

Nishon

569,45

0,96

546,67

271,09

5,22

1415,09

-868,42

9

Kasbi

507,25

1,19

603,63

159,66

4,43

707,29

103,67

10 Chirokchi 259,74

0,58

150,65

36,59

1,69

61,84

88,81

11 Shaxrisabz 181,2

0,42

76,10

4,26

0,69

2,94

73,16

12 Yakkabog

233,12

0,77

179,50

52,04

2,5

130,10

49,40

By region

4434,32

1,0475

5221,73

1434,19 3,9588

7055,82

2004,08

By correctly organizing the water-salt balance of the irrigated areas, it is necessary to

achieve a positive change in the water-salt balance, that is, the amount of salts in the incoming

water and soil should be less than the amount of salt leaving through the collector-drainage

networks. It is desirable that the balance of water-salt exchange from irrigated areas is at least

equal.

To date, 279.56 thousand hectares of the total irrigated area are considered good, and

219.95 thousand hectares are considered satisfactory, or 97.06 percent.

It should be noted that it is desirable to organize the water-salt balance of the irrigated lands

correctly, to achieve that the amount of salts in the water and soil entering through the irrigation

water does not exceed the amount of salt leaving it.

Based on the presidential decrees, the entrepreneurial use and protection of irrigated lands

primarily involves the correct application of agro-ameliorative measures, maintaining the level

of its mineralization within acceptable limits, and the use of existing mains, it is recommended

to repair inter-district and internal household collector-drainage networks, coordinate the flow


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of stormwater in them, and use local and mineral fertilizers in accordance with scientifically

developed recommendations.

REFERENCES:

1.

Isaev, S., Rajabov, T., Goziev, G., & Khojasov, A. (2021). Effect of fertilizer application on

the ‘Bukhara-102’variety of cotton yield in salt-affected cotton fields of Uzbekistan. In E3S

Web of Conferences (Vol. 258, p. 03015). EDP Sciences.

2.

Isaev, S., Rajabov, T., & Dolidudko, A. (2018). Influence of inorganic fertilizers on cotton

crop yield in saline soils. Bulletin of Science and Practice.

3.

Исаев, С., & Ражабов, Т. (2008). Тақирсимон тупроқлар шароитида субирригация

усулида суғрилганда ғўза ҳосилдорлигига таъсири. О’zbeison qishloq xo’jaligi, (3), 11-

12.

4.

Ражабов, Т. Я., Ражабов, Т. Т., & Ходиева, С. А. (2022). ҒЎЗАНИНГ ЮҚОРИ

ҲОСИЛДОРЛИГИГА

СУҒОРИШ

ВА

ЎҒИТЛАШ

МЕЪЁРЛАРИНИНГ

БОҒЛИҚЛИГИ. Инновацион технологиялар, 1(1 (45)), 84-87.

5.

Ражабов, Т. (2023). ҒЎЗАДАН ЮҚОРИ ҲОСИЛ ОЛИШДА ТАЪСИР ЭТУВЧИ

ОМИЛЛАР. Евразийский журнал медицинских и естественных наук, 3(10), 99-102.

6.

Abdivokhidovich, I. Z., Tilakovich, R. T., & Pirmat, N. (2022). EFFECTIVE

STANDARDS AND TERMS OF APPLICATION OF ATLANTIS HERBICIDE IN

GRAIN PRODUCTION IN THE SOUTH OF UZBEKISTAN.

7.

Abdivohidovich IZ, Tilakovich RT O'zbekiston sharoitida gerbitsid Atlantis 3,6% va

o'g'itlardan foydalanishning kuzgi bug'doy hosiliga ta'siri //Miasto Przyszłości. – 2024. – T.

55. – S. 142-144.

8.

Abdivohidovich IZ, Tilakovich RT, Pirmat N. Atlantis gerbitsidini O'zbekiston janubida

don etishtirishda qo'llashning samarali standartlari va shartlari //Yevropa qishloq xo'jaligi va

qishloq ta'limi jurnali. – T. 3. – №. 4. – S. 15-17.

9.

Chorshanbiyev N., Musayev M., Qo'ziboyev A. INGICHKA TOLALI G'O'ZA

NAVLARINING TARQALISHI VA OZIGA XOSLIGI //Академические исследования в

современной науке. – 2022. – Т. 1. – №. 14. – С. 109-111.

10.

Abdivokhidovich I. Z., Samandarovich M. M. Effect of the Use of Herbicide and Fertilizer

on Economic Efficiency in the Growth of Winter Wheat //European Scholar Journal. – 2021.

– Т. 2. – №. 7. – С. 8-9.

11.

Rajabov T. T., Qarshiyev A. E., Xojamurotov A. S. IRRIGATSIYA EROZIYASIGA

CHALINGAN YERLARDA TUPROQNING HAJM MASSASINI O ‘ZGARISHI VA KO

‘CHAT QALINLIGI //American Journal of multifunctional publishing. – 2024. – Т. 1. – №.

2. – С. 11-15.

References

Isaev, S., Rajabov, T., Goziev, G., & Khojasov, A. (2021). Effect of fertilizer application on the ‘Bukhara-102’variety of cotton yield in salt-affected cotton fields of Uzbekistan. In E3S Web of Conferences (Vol. 258, p. 03015). EDP Sciences.

Isaev, S., Rajabov, T., & Dolidudko, A. (2018). Influence of inorganic fertilizers on cotton crop yield in saline soils. Bulletin of Science and Practice.

Исаев, С., & Ражабов, Т. (2008). Тақирсимон тупроқлар шароитида субирригация усулида суғрилганда ғўза ҳосилдорлигига таъсири. О’zbeison qishloq xo’jaligi, (3), 11-12.

Ражабов, Т. Я., Ражабов, Т. Т., & Ходиева, С. А. (2022). ҒЎЗАНИНГ ЮҚОРИ ҲОСИЛДОРЛИГИГА СУҒОРИШ ВА ЎҒИТЛАШ МЕЪЁРЛАРИНИНГ БОҒЛИҚЛИГИ. Инновацион технологиялар, 1(1 (45)), 84-87.

Ражабов, Т. (2023). ҒЎЗАДАН ЮҚОРИ ҲОСИЛ ОЛИШДА ТАЪСИР ЭТУВЧИ ОМИЛЛАР. Евразийский журнал медицинских и естественных наук, 3(10), 99-102.

Abdivokhidovich, I. Z., Tilakovich, R. T., & Pirmat, N. (2022). EFFECTIVE STANDARDS AND TERMS OF APPLICATION OF ATLANTIS HERBICIDE IN GRAIN PRODUCTION IN THE SOUTH OF UZBEKISTAN.

Abdivohidovich IZ, Tilakovich RT O'zbekiston sharoitida gerbitsid Atlantis 3,6% va o'g'itlardan foydalanishning kuzgi bug'doy hosiliga ta'siri //Miasto Przyszłości. – 2024. – T. 55. – S. 142-144.

Abdivohidovich IZ, Tilakovich RT, Pirmat N. Atlantis gerbitsidini O'zbekiston janubida don etishtirishda qo'llashning samarali standartlari va shartlari //Yevropa qishloq xo'jaligi va qishloq ta'limi jurnali. – T. 3. – №. 4. – S. 15-17.

Chorshanbiyev N., Musayev M., Qo'ziboyev A. INGICHKA TOLALI G'O'ZA NAVLARINING TARQALISHI VA OZIGA XOSLIGI //Академические исследования в современной науке. – 2022. – Т. 1. – №. 14. – С. 109-111.

Abdivokhidovich I. Z., Samandarovich M. M. Effect of the Use of Herbicide and Fertilizer on Economic Efficiency in the Growth of Winter Wheat //European Scholar Journal. – 2021. – Т. 2. – №. 7. – С. 8-9.

Rajabov T. T., Qarshiyev A. E., Xojamurotov A. S. IRRIGATSIYA EROZIYASIGA CHALINGAN YERLARDA TUPROQNING HAJM MASSASINI O ‘ZGARISHI VA KO ‘CHAT QALINLIGI //American Journal of multifunctional publishing. – 2024. – Т. 1. – №. 2. – С. 11-15.