Growth, Development and Productivity of Corn Under Irrigation
with Wastewater from Poultry Farms on Meadow Soils of Tashkent
Region
Mansur Tukhtamishev
a
, Nematulla Xudaybergenov
b
, Shavkat Abdurahimov
c
and Umbetali Sultanov
d
Tashkent State Agrarian University, 100140, University str. 2, Tashkent, Uzbekistan
Keywords: Corn Productivity, Poultry Wastewater, Irrigation Suitability.
Abstract:
The article highlights the composition of wastewater from poultry farms and their suitability for
irrigation of agricultural crops. It was found that the chemical demand of wastewater from poultry
farms is 480-850 mg O2/l, which indicates high pollution with organic products. Coarse and fine
substances vary within 430-720 mg/l, and the biochemical oxygen demand on the fifth day (BOD
5
)
is within 0.39-0.74 g O
2
/l, and at the time of mass discharges of wastewater it reached 15-1.6 g
O
2
/l. The titer of E. coli was equal to 10-6, the number of microbes fluctuated between 48.5 x 106
and 61.6 x 106. Determination of the suitability of wastewater based on generally accepted methods
showed that they are quite suitable for irrigation of agricultural crops without additional
melioration measures.
1 INTRODUCTION
Water for irrigation in the conditions of the arid zone
of Central Asia, including the Republic of
Uzbekistan, is a necessary factor in agriculture. In the
Republic of Uzbekistan, the main factor in food
security is irrigated agriculture. Free water resources
are needed to expand the area of irrigated agriculture,
although the existing water resources in the republic
can expand the area of irrigated agriculture by 4.8
million hectares. With the existing level of irrigation
technology, there is a severe shortage of irrigation
water (Tukhtamishev et al., 2021).
Anthropogenic transformations of water in the
region have already reached global proportions: the
intensive development of irrigated agriculture in the
second half of the 20th century led to a significant
increase in water withdrawal from the Syr Darya and
Amu Darya basins, which caused the shallowing of
the Aral Sea. Currently, the volume of the sea is only
a
https://orcid.org/0009-0002-9350-8892
b
https://orcid.org/0009-0002-1600-1991
c
https://orcid.org/0009-0007-2412-6088
d
https://orcid.org/0009-0007-2372-9768
28% of the 1960 figure. A. Kurtov argues that the lack
of water for the Republic of Uzbekistan is a disaster
in the literal sense of the word: due to the lack of
water in a number of regions of the republic,
especially in Karakalpakstan, we can already talk
about a social and economic crisis (Tukhtamishev et
al., 2021). There is not enough water not only for
agricultural purposes, but also for purely domestic
needs. If before 2000, low-water years in the region
were observed every 6-8 years, then at present this
phenomenon is repeated every 3-4 years. In 2018 and
2019, water availability decreased significantly
(Tukhtamishev et al., 2022).
A pressing issue at the current stage of economic
and social development of the republic is
environmental protection and, in particular,
eliminating the danger of negative impact on it from
the growing volume of wastewater from poultry
enterprises. One of the polluters of the republic's
water bodies is the intensively developing poultry
Tukhtamishev, M., Xudaybergenov, N., Abdurahimov, S. and Sultanov, U.
Growth, Development and Productivity of Corn Under Irrigation with Wastewater from Poultry Farms on Meadow Soils of Tashkent Region.
DOI: 10.5220/0014268900004738
Paper published under CC license (CC BY-NC-ND 4.0)
In Proceedings of the 4th International Conference on Research of Agricultural and Food Technologies (I-CRAFT 2024), pages 345-350
ISBN: 978-989-758-773-3; ISSN: 3051-7710
Proceedings Copyright © 2025 by SCITEPRESS Science and Technology Publications, Lda.
345
farms and enterprises. The artificial treatment
facilities used are often ineffective, retaining only 50-
60% of the ingredients found in wastewater, since the
technological process of mechanical and biological
treatment at treatment facilities functions poorly due
to their unsatisfactory operation, imperfection of the
technological process of treatment itself, and they
operate with a greater overload. Therefore, soil
neutralization of wastewater and its use for irrigation
of fodder and grain crops seems very promising from
the national economic and hygienic positions, which
allows increasing water supply, land productivity and
is a powerful means of increasing soil fertility, as well
as an effective way of their additional purification in
natural conditions (Tukhtamishev et al., 2022). In
general, wastewater from poultry farms in the
republic can be used to irrigate and fertilize 10-12
thousand hectares of land. However, the problem of
using wastewater for irrigation of agricultural crops
requires a regional approach, i.e. it is necessary to
take into account the characteristics of the soil and
hydrogeological conditions of the territory
(Musirmonov et al., 2023, Juliev et al., 2023). In
connection with the above, special attention is paid to
the productive use of available water resources in the
republic. On November 27, 2017, the decree of the
President of the Republic of Uzbekistan "On the state
program for the development of irrigation in 2018-
2019 and improving the melioration state of irrigated
lands" was adopted. According to this decree, a
number of measures are being carried out, including
the introduction of water-saving irrigation
technologies.
In the conditions of a severe shortage of irrigation
water, the Tashkent State Agrarian University pays
special attention to conducting research work on
issues of more careful and productive use of the
existing water resources, including local runoff.Level
of study of the issue. In the CIS republics, including
the former All-Union Scientific and Production
Association VNPO Progress (All-Union Scientific
Research Institute for Agricultural Crops), Volgograd
Agricultural and Ukrainian Hydromelioration
Institutes, Uzbek Research Institute of Sanitation,
Hygiene and Occupational Diseases and other
institutions, numerous studies have been conducted to
study the suitability of domestic and livestock
wastewater for irrigation of agricultural crops.
However, scientific research on the issue of
utilization of wastewater from poultry farms has been
almost not conducted (Tukhtamishev et al., 2020).
The purpose of the research: to study the
composition and suitability of wastewater from
poultry farms for irrigation of agricultural crops in
various soil and hydrogeological conditions of the
republic as an effective measure to prevent pollution
of water resources and save river water, to determine
their impact on the growth, development and yield of
cultivated crops, the sanitary and hygienic condition
of irrigation fields.
Research objectives: to establish the influence of
irrigation with wastewater from poultry farms on the
growth, development and yield of cultivated forage
and grain crops.
Objects of research: the objects of research are
wastewater from poultry farms and feed and grain
crops irrigated by them in meadow and gray soil
conditions of the Tashkent region.
2 MATERIALS AND METHODS
The materials of the conducted research are wastewater
from the poultry farms Uzbekistan and
Urtachirchikparranda, located on gray and meadow
soils of the Tashkent region and the forage and grain
crops irrigated by them. The suitability of wastewater
for irrigation of agricultural crops was determined
according to Budanov, Mozheiko and Vorotnik,
Kelly, Eaton and Stebler, according to the method of
the US Department of Agriculture (SAR)
(Tukhtamishev et al., 2022).
3 RESULTS AND DISCUSSION
Long-term studies to determine the quality of
wastewater and their suitability for use in irrigation of
agricultural crops have shown the following:
wastewater from poultry farms is characterized by a
specific (often ammonia) odor, turbid color, slightly
alkaline reaction of the environment (pH = 7.1–7.3),
carbonate-sulphate, calcium-magnesium
composition, according to the classification of Yu. P.
Lebedev and had coarsely dispersed and finely
dispersed substances, which were contained in an
amount of 430–720 mg/l on average, therefore,
reusing wastewater in the production process or
discharging it into open water bodies without
thorough cleaning is unacceptable, since the
concentration of most ingredients in them exceeds the
maximum permissible for reuse and discharge into
water bodies (Tukhtamishev et al., 2020).
Oxidability (COD – chemical oxygen demand) is
of great importance when assessing the quality of
water for irrigation of agricultural crops. This
indicator characterizes the total content of organic
I-CRAFT 2024 - 4th International Conference on Research of Agricultural and Food Technologies
346
and inorganic substances in water that react with
strong oxidizers (Juliev et al., 2023). A high COD
value (480–850 mg O
2
/l) indicates high pollution of
wastewater (MPC for a reservoir is 30 mg/l) with
products of organic origin. The degree of pollution of
wastewater with organic matter contained in the form
of non-sedimenting suspended and colloidal particles
can also be determined by the content of oxygen
consumed for biochemical oxidation of these
substances in 1 liter of sample during the life of
aerobic bacteria. This indicator is called BOD
biochemical oxygen demand and it varied in the
discharged waters of poultry farms within the range
of 0.39–0.74 mg/l (the maximum permissible
concentration for a reservoir is 3 mg/l) on the fifth day
(BOD
5
), and at the time of salvo discharges of
wastewater it reached 1.5–1.6 g O
2
/l, i.e. the quality
of the discharged water deteriorated almost twofold
(Table 1).
Table 1: Characteristics of wastewater from poultry farms and river water supplied for irrigation of agricultural crops.
Indicators Unit of measurement
PF Uzbekistan
Urtachirchik Parranda
2018 y. 2019 y. 2020 y.
Wastewater from poultr
y
farms
1
р
Н
7,3 7,2 7,2 7,1
2 Suspended solids m
g
/l 430 650 720 580
3 COD m
g
/l 480 750 800 850
4 BPK
5
mg/l 1100
390
1500
680
1430
610
1200
760
5 Total nitro
g
en m
g
/l 70,7 61,4 56,5 66,4
6 Total phosphorus mg/l 0,2 0,2 0,4 0,6
7 Gross potassium m
g
/l 14,5 11,1 12,6 23,7
8 Calcium m
g
/l 58,5 50,0 53,5 69,2
9 Magnesiu
m
mg/l 68,4 75,6 54,3 30,6
10 Sodiu
m
m
g
/l 21,8 20,9 14,7 37,9
11 Chlorine m
g
/l 16,7 32,8 22,4 23,6
12 Sulfates mg/l 95,4 99,8 73,2 78,7
13 Bicarbonates m
g
/l 434,3 410,7 373,5 326,1
River wate
1
р
Н
7,3 7,5 7,4 7,3
2 Suspended solids m
g
/l 236,3 208,5 310,6 274,4
3 COD m
g
/l 23,4 14,3 18,8 28,6
4 BPK
5
mg/l 960
280
1120
430
1080
390
980
280
5 Total nitro
g
en m
g
/l 5,9 4,5 4,0 5,1
6 Total phosphorus mg/l 0,05 0,03 0,04 0,04
7 Gross potassium m
g
/l 3,3 2,5 2,6 3,5
In terms of nitrogen content, the wastewater is
characterized by high fertilizing value - from 51 to 87
mg/l, the potassium content varied within 10-32 mg/l.
Qualitative assessment of wastewater by the total
concentration of dissolved salts, the content of
chlorides, hydrocarbonates, biogenic elements, toxic
salts, environmental reaction (pH), anion-cation
composition and sodium adsorption coefficient
(SAR) shows that the wastewater of poultry farms is
quite suitable for irrigating corn grown for grain and
silage, winter wheat, alfalfa, combined crops of
alfalfa + oats, corn + soybeans + sunflower without
dilution and in dilutions with river water in ratios of
1: 1 and 1: 2, fodder beet on meadow and sierozem
soils without additional melioration measures (Table
2).
Growth, Development and Productivity of Corn Under Irrigation with Wastewater from Poultry Farms on Meadow Soils of Tashkent Region
347
Table 2: Assessment of the suitability of wastewater from poultry farms for irrigation of forage crops
Name of the method and its essence Poultr
y
farms
Uzbekistan Urtachirchik Parranda
1. According to Budanov:
1) Na : (Ca + Mg) ≤ 0,7
2
)
Na : Ca ≤ 1
0,09–0,11
0,24
0,37
0,27
0,48
2 According to Mozheiko and Vorotnik:
(
К + Na
)
∙ 100 :
(
Ca + M
g
+ Na
)
≤ 65%
11,87
13,47
27,26
3 According to the US Department of
Defense (SAR) method:
Na :
(Ca + Mg) : 2 ≤ 8
0,34–0,46
27,26
4 According to Kelly: Сa ∙100 : (Ca + +
Mg + Na + K) ≥ 35%
24,95
32,68
41,50
5 According to Eton:
(
СО
3
+ НСО
3
)
(
Са + + М
g
)
< 2,5
1,5
2,1
0,68
6 According to Stabler (К > 6)
К = 288 : (rNa + 4rCl)
61,94
100
66,0
In addition to the above ingredients, waste and river
water contains a large number of microorganisms that
require careful study when using water for irrigation
of agricultural crops. The results of sanitary and
bacteriological studies indicate that waste water used
for irrigation of agricultural crops was significantly
contaminated according to the studied indicators.
Thus, the titer of E. coli was equal to 10-6, the number
of microbes fluctuated between 48.5 x 106 and 61.6 x
106. At the same time, with each cubic meter of waste
water, from 48.5 x 1012 to 61.6 x 1012
microorganisms entered the field (Juliev et al., 2001).
After purification in artificial structures, these
indicators were respectively equal: the titer of E. coli
- 10-4, the number of microbes in 1 ml of water - from
40.9 x 106 to 52.0 x 106 pcs. River water was
characterized by the following indicators: the number
of microbes in 1 ml of water - from 3.7 x 106 to 4.5 x
106, and the coli titer - 0.0004.
In conclusion, it should be noted that wastewater
from poultry farms is quite suitable for irrigation of
agricultural crops, but the final suitability of
wastewater in terms of mineralization must be
clarified in the process of constant monitoring of the
accumulation of salts in the soil during the cultivation
of agricultural crops.
In addition to the accumulation of salts in the soil,
wastewater also has a fertilizing value, which
depends on the presence of nutrients and beneficial
microorganisms in it. When undergoing purification
at artificial facilities, a significant amount of
nutritional elements is lost; when they are discharged
into open water bodies, thousands of tons of fertilizers
are carried away; they would play a major role in soil
fertility and increasing the yield of cultivated crops.
As a result of the influx of large amounts of
nutrients and beneficial microorganisms during
irrigation of lands with wastewater, microbiological
processes are significantly enhanced, resulting in
improved soil fertility.
In our experiments, wastewater that underwent
mechanical treatment was used for irrigation of corn.
During the water supply, the amount of nutrients
(total nitrogen, phosphorus, and total potassium) was
determined. The data presented in Table 1 show that
the concentration of total nitrogen varied widely and
was from 51.3 to 86.8 mg/l during the irrigation
period, phosphorus was contained in insignificant
quantities – 0.2–0.8 mg/l, and potassium – 10.2–31.8
mg/l. Or: with each 1000 m3 of wastewater, 50–90 kg
of nitrogen, about 1 kg of phosphorus, and 10–32 kg
of potassium per hectare entered the field.
According to the classification of V.T. Dodolina
(1975), the wastewater from the Tashkent Poultry
Farm and the Urtachirchikparranda poultry farm, in
terms of nitrogen content, is classified as wastewater
of medium fertilizing value, and in terms of
potassium and phosphorus content, it is classified as
low.
These nutrients are in a dissolved and accessible
form, getting into the soil, they are easily absorbed by
plants, simultaneously solving the problems of water
and food regime for corn plants. In addition, many
organic substances and microorganisms get into the
soil with waste water, as a result of which
microbiological processes are activated and the
potential and effective fertility of the soil increases.
The calculations performed to determine the
amount of nutrients supplied to the field with
irrigation water showed that when irrigating corn with
wastewater at an irrigation rate of 3650–3900 m3/ha,
179–220 kg of nitrogen and 42–92 kg of potassium
were supplied to each hectare of crops (taking into
account the coefficient that takes into account the loss
I-CRAFT 2024 - 4th International Conference on Research of Agricultural and Food Technologies
348
of nutrients from runoff during irrigation, which is
0.85 for nitrogen and 1 for phosphorus and potassium.
At an irrigation rate of 4400–4650 m3/ha, 218–264
and 51–110 kg per hectare, respectively; under
dilution conditions at an irrigation rate of 3700–3930
m3/ha – 98–122 kg of nitrogen and 16–53 kg of
potassium, and at an irrigation rate of 4550–4620
m3/ha at 118–150 and 31–63 kg per hectare.
phosphorus was supplied with irrigation water in
insignificant quantities.
The use of poultry wastewater for feeder and
vegetation irrigation during winter wheat cultivation
on sierozem soils contributed to the improvement of
plant growth and development, and significantly
increased the yield of grain and straw. If, when
carrying out feeder and vegetation irrigation with
river water, the grain yield on average for 3 years was
45.2 c/ha and straw 56.5 c/ha, in the variant with
feeder irrigation with river water and vegetation
irrigation with wastewater, it was 51.0 and 64.2 c/ha,
respectively. In the variant where feeder irrigation
was carried out with wastewater and vegetation
irrigation with river water, 3.7 c of grain and 7.6 c of
straw were obtained more than in the control variant.
The highest yield 55.5 c/ha of grain and 70.2 c/ha
of straw was obtained in the variant with feeder and
vegetation irrigation with wastewater. When feeder
irrigation was carried out with river water, and
vegetation irrigation with wastewater diluted with
river water and vegetation irrigation with wastewater,
40.2 c/ha of grain and 50.9 c/ha of straw were
obtained, which is 5.0 and 5.6 c/ha less, respectively,
than in the control variant.
Diluted with river water and undiluted wastewater
from poultry farms, when used for irrigation in
combination with mineral fertilizers on meadow soils,
contributed to obtaining high yields of silage, grain
and air-dry leaf-stem mass of corn. The yield of silage
mass reached 530.6–608.3 and 564.2–641.1 c/ha,
respectively, against 508.4–564.3 c/ha, and grain
77.8–82.9 and 80.6–86.4 c/ha against 68.6–74.6 c/ha;
air-dry leaf-stem mass – 191.4–208.8 and 204.1–
255.3 c/ha against 182.3–198.4 c/ha in the control
variant.
It has been established that in the hot climate of
Uzbekistan, soils irrigated with wastewater become
clean to standard 10-15 days after irrigation. With
proper organization and implementation of surface
irrigation with wastewater, contamination of above-
ground plant organs and groundwater is completely
eliminated. In case of accidental contamination of
individual parts of plants, they can be considered
clean to standard 10-15 days after irrigation.
4 CONCLUSIONS
Our long-term studies confirm the feasibility and high
efficiency of cleaning and recycling wastewater in
agriculture by using it for irrigation of agricultural
lands, especially in the arid zone of Uzbekistan.
Wastewater from poultry farms is quite suitable for
irrigation of fodder and industrial crops without
additional melioration measures.
When irrigating with wastewater, a significant
amount of nutrients enters the field, which play a
major role in providing plants and improving soil
fertility. It is advisable to use the following
wastewater disposal scheme: sewerage - mechanical
treatment facility - storage ponds - irrigation fields.
Wastewater from poultry farms is quite suitable for
irrigating forage crops used to produce vitamin flour,
haylage, silage, forage, and forage root crops. The
most acceptable option for irrigation is the use of
diluted wastewater with river water in a 1:1 ratio in
combination with mineral fertilizers, since the soil
self-cleaning process occurs on the 15th day after
irrigation. Under the same conditions, for irrigation of
alfalfa in the 2nd and 3rd years of standing, diluted
wastewater from poultry farms with river water in a
1:1 or 1:2 ratio (one part wastewater and 1 or 2 parts
river water). In this case, the irrigation rate should be
set according to the alfalfa's need for water. In this
case, the irrigation scheme is 1-2-2-1. A single
irrigation rate is 900-1100 m3/ha.
On meadow soils with groundwater at a level of
2-2.5 m in the Chirchik-Angren Valley, it is advisable
to use wastewater from poultry farms diluted with
river water in a ratio of 1:1 for irrigation of corn
grown as a second crop after winter crops and the use
of mineral fertilizers (at a rate of N - 180, P
2
O
5
- 100
K
2
O - 90 kg / ha). The timing of irrigation should be
determined by the lower threshold of moisture in the
active soil layer of 70-75-65% of the soil's FPV. The
irrigation rate should be within 4.4-4.6 thousand m3 /
ha, inter-irrigation periods of 15-20 days. Vegetation
irrigation should be completed 15-20 days before
harvesting.
Irrigation and irrigation rates for cultivated crops
are determined by their total water consumption, and
irrigation times are determined by the moisture deficit
in the active soil layer. Irrigation rates for silage corn
are calculated at a lower soil moisture threshold of
75–80% of the maximum permissible moisture
content, for grain corn 70–75–65%. Irrigation rates
in meadow soil conditions should be 3.4–4.0 and 4.4–
4.6 thousand m3/ha, respectively. For forage alfalfa
of the first year of standing with four cuts on meadow
soils, the irrigation scheme should be 1-1-1-1, and for
Growth, Development and Productivity of Corn Under Irrigation with Wastewater from Poultry Farms on Meadow Soils of Tashkent Region
349
alfalfa of the second year and subsequent years with
five and six cuts 0-1-1-1-1 and 0-1-1-1-1-1 with
irrigation rates of 1000–1100 m3/ha and irrigation
rates from 4.0–4.4 to 5.0–5.5 thousand m3/ha.
The irrigation scheme for alfalfa in its first year of
growing on sierozem soils with deep groundwater
should be 1-2-2-1 with irrigation rates of 900–1100
m3/ha and irrigation rates of 5.4–6.6 thousand m
3
/ha,
and for alfalfa in its second year of growing and
subsequent years 0-1-2-2-1 with irrigation rates of
1000–1200 m
3
/ha and irrigation rates of 6.0–7.0
thousand m
3
/ha.
The irrigation regime for fodder beets consists of
5 irrigations with irrigation rates of 800–1300
thousand m3/ha and irrigation rates of 6.0–7.0
thousand m3/ha.
In conditions of meadow soils with groundwater
at a level of 1.5–1.8 m, after sowing wheat, it is
necessary to carry out feeder irrigation with
wastewater at a rate of 700–730 m
3
/ha and vegetation
irrigation with wastewater diluted with river water in
a ratio of 1:1 at a rate of 700–850 m
3
/ha and an
irrigation rate of 3080 (taking into account feeder
irrigation 3810) m
3
/ha.
Moisture-charging and fertilizing irrigation on gray
soils should be carried out in deep furrows according
to a dead-end scheme at a rate of 800-1000 m
3
/ha, and
they are stopped 2-3 weeks before sowing.
Monitoring the sanitary and hygienic condition of the
soil when using wastewater for irrigation is carried
out on the 15th day after irrigation. When irrigating
with wastewater, it is necessary to comply with
sanitary and anti-epidemic rules, especially in the first
20 days. When using wastewater for irrigation, the
inter-irrigation periods should be at least 15-20 days
to ensure the normal course of soil self-purification
processes. In case of a delay in the process of soil self-
purification from pathogenic microorganisms,
irrigation should be carried out with river water.
Vegetative irrigation with wastewater is completed
15-20 days before harvesting.
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