Scinovex

Research article · 2025 · Full text

International Journal of Agriculture and Nutrition

Nitrogen dynamics and balance under organic and inorganic nutrient management in cotton

Mahsa Pirasteh

Volume 7(12) · Pages 89–92 · DOI: 10.33545/26646064.2025.v7.i12b.515 ↗

Research areasAgricultural Science and FertilizationSoil Carbon and Nitrogen DynamicsPlant Growth and Agriculture Techniques

↓ Read full-text PDF0 citations

Abstract

Author-written

Nitrogen is the nutrient cotton demands most, yet applying it efficiently remains a persistent challenge. This research compared organic and inorganic nitrogen sources at four rates (0, 40, 80, 120, and 160 kg N ha⁻¹) to track nitrogen dynamics and construct a field-scale N balance for irrigated cotton near Shiraz, Iran. Inorganic urea produced higher total N uptake than composted cattle manure at every non-zero rate, but the gap narrowed at 160 kg N ha⁻¹ (78.6 vs 62.1 kg N ha⁻¹). Apparent nitrogen recovery was consistently lower under organic management (31-39%) than under inorganic (42-49%). Soil residual mineral N at harvest was 27-44% greater in urea-treated plots, raising concerns about post-season leaching risk. The N balance showed that organic treatments retained more N in soil organic pools, while inorganic treatments lost a larger fraction to gaseous and leaching pathways. These results suggest that combining a moderate organic base with a small inorganic supplement may balance productivity with long-term soil-N conservation in arid-zone cotton.

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • Cotton has a high demand for nitrogen, with a single hectare producing 2.5 tonnes of seed cotton removing approximately 110-130 kg N from the soil-plant system. View evidence ↗

      Why it matters

      Cotton has a high demand for nitrogen, with a single hectare producing 2.5 tonnes of seed cotton removing approximately 110-130 kg N from the soil-plant system.

      In the paper's own words

      “Cotton is a nutrient-hungry crop, and nitrogen sits at the top of its shopping list. A single hectare producing 2.5 tonnes of seed cotton removes roughly 110-130 kg N from the soil-plant system”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Urea is the most common nitrogen source globally due to its cost and availability, but its fast-acting nature makes it susceptible to leaching and volatilization if over-applied. View evidence ↗

      Why it matters

      Urea is the most common nitrogen source globally due to its cost and availability, but its fast-acting nature makes it susceptible to leaching and volatilization if over-applied.

      In the paper's own words

      “Globally, urea remains the dominant N source for cotton. It is cheap, widely available, and fast-acting — qualities that also make it prone to volatilisation and leaching when applied in excess”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • In Iran's Fars Province, where 18% of national cotton is grown, the high pH and low organic matter of calcareous soils increase the risk of ammonia volatilization from urea. View evidence ↗

      Why it matters

      In Iran's Fars Province, where 18% of national cotton is grown, the high pH and low organic matter of calcareous soils increase the risk of ammonia volatilization from urea.

      In the paper's own words

      “Iran’s Fars Province grows about 18% of the country’s cotton on calcareous soils with high pH and low organic matter — conditions that amplify ammonia volatilisation from surface-applied urea”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aimed to compare how different application rates of organic and inorganic nitrogen sources affect nitrogen dynamics, crop uptake, and post-season balance in irrigated cotton. View evidence ↗

      The question

      The study aimed to compare how different application rates of organic and inorganic nitrogen sources affect nitrogen dynamics, crop uptake, and post-season balance in irrigated cotton.

      In the paper's own words

      “This research was set up to compare the nitrogen dynamics, crop uptake, and post-season balance of organic and inorganic N sources across a range of application rates in irrigated cotton at Shiraz.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • The researchers sought to find a management strategy that maintains crop yield while reducing the amount of residual mineral nitrogen that could be lost after the season. View evidence ↗

      The question

      The researchers sought to find a management strategy that maintains crop yield while reducing the amount of residual mineral nitrogen that could be lost after the season.

      In the paper's own words

      “The aim was to identify a management strategy that sustains yield while minimising residual mineral N left vulnerable to off-season losses.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  3. What they did

    • The experiment used a randomized complete block design with four replicates, testing five rates (0, 40, 80, 120, and 160 kg N ha⁻¹) of two sources: composted cattle manure (1.8% N) and urea (46% N). View evidence ↗

      What they did

      The experiment used a randomized complete block design with four replicates, testing five rates (0, 40, 80, 120, and 160 kg N ha⁻¹) of two sources: composted cattle manure (1.8% N) and urea (46% N).

      In the paper's own words

      “The trial used a randomised complete block design with two N source treatments (composted cattle manure, 1.8% N; and urea, 46% N) each at five rates (0, 40, 80, 120, 160 kg N ha⁻¹), giving ten treatment combinations replicated four times.”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • The study used the Varamin-76 cotton cultivar, sown on May 8, 2023, in 6 m × 4 m plots with 80 × 20 cm spacing. View evidence ↗

      What they did

      The study used the Varamin-76 cotton cultivar, sown on May 8, 2023, in 6 m × 4 m plots with 80 × 20 cm spacing.

      In the paper's own words

      “Cotton cultivar Varamin-76, a medium-staple upland type, was sown on 8 May 2023 at 80 × 20 cm spacing in plots of 6 m × 4 m.”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • Manure was added to the soil one week before sowing, while urea was applied in two equal splits at sowing and the first-square stage. View evidence ↗

      What they did

      Manure was added to the soil one week before sowing, while urea was applied in two equal splits at sowing and the first-square stage.

      In the paper's own words

      “Manure was incorporated one week before sowing; urea was split 50% at sowing and 50% at first-square stage.”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • Nitrogen balance was calculated by subtracting crop uptake, residual soil mineral N, and estimated gaseous losses from the sum of applied and initial soil mineral N. View evidence ↗

      What they did

      Nitrogen balance was calculated by subtracting crop uptake, residual soil mineral N, and estimated gaseous losses from the sum of applied and initial soil mineral N.

      In the paper's own words

      “The N balance for each plot was calculated as: N balance = (N applied + initial soil mineral N) - (crop N uptake + residual soil mineral N + estimated gaseous losses).”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
  4. What they found

    • Urea resulted in higher total nitrogen uptake than composted manure at all non-zero rates, though the difference was smallest at 160 kg N ha⁻¹ (78.6 vs 62.1 kg N ha⁻¹). View evidence ↗

      What they found

      Urea resulted in higher total nitrogen uptake than composted manure at all non-zero rates, though the difference was smallest at 160 kg N ha⁻¹ (78.6 vs 62.1 kg N ha⁻¹).

      In the paper's own words

      “Inorganic urea produced higher total N uptake than composted cattle manure at every non-zero rate, but the gap narrowed at 160 kg N ha⁻¹ (78.6 vs 62.1 kg N ha⁻¹).”

      Page 1

      Found in: Conclusion

      Read it in the full textOpen PDF at page 1 ↗
    • The apparent nitrogen recovery was lower for organic management (31-39%) compared to inorganic management (42-49%). View evidence ↗

      What they found

      The apparent nitrogen recovery was lower for organic management (31-39%) compared to inorganic management (42-49%).

      In the paper's own words

      “Apparent nitrogen recovery was consistently lower under organic management (31-39%) than under inorganic (42-49%).”

      Page 1

      Found in: Discussion

      Read it in the full textOpen PDF at page 1 ↗
    • Urea-treated plots had 27-44% more residual mineral nitrogen at harvest, which increases the risk of nitrogen leaching after the season. View evidence ↗

      What they found

      Urea-treated plots had 27-44% more residual mineral nitrogen at harvest, which increases the risk of nitrogen leaching after the season.

      In the paper's own words

      “Soil residual mineral N at harvest was 27-44% greater in urea-treated plots, raising concerns about post-season leaching risk.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • At the highest application rate, residual mineral nitrogen reached 68.9 kg ha⁻¹ with urea compared to 43.6 kg ha⁻¹ with organic manure. View evidence ↗

      What they found

      At the highest application rate, residual mineral nitrogen reached 68.9 kg ha⁻¹ with urea compared to 43.6 kg ha⁻¹ with organic manure.

      In the paper's own words

      “Residual mineral N accumulated faster under urea, reaching 68.9 kg ha⁻¹ at the highest rate versus 43.6 kg ha⁻¹ for organic”

      Page 3

      Found in: Comprehensive Interpretation

      Read it in the full textOpen PDF at page 3 ↗
  5. What it means

    • The authors suggest a blended strategy, such as 80 kg N ha⁻¹ of compost supplemented with 40 kg of inorganic N at the first square stage, to balance long-term soil health with peak crop demand. View evidence ↗

      What it means

      The authors suggest a blended strategy, such as 80 kg N ha⁻¹ of compost supplemented with 40 kg of inorganic N at the first square stage, to balance long-term soil health with peak crop demand.

      In the paper's own words

      “A blended strategy — say, 80 kg N ha⁻¹ from compost topped up with 40 kg inorganic N at first square — could capture the best of both worlds: a slow organic base that feeds the soil’s long-term N pool, plus a targeted mineral supplement during peak demand.”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗
    • For irrigated cotton in arid regions with calcareous soils, combining a moderate organic base with a small inorganic supplement is recommended as the most balanced approach. View evidence ↗

      What it means

      For irrigated cotton in arid regions with calcareous soils, combining a moderate organic base with a small inorganic supplement is recommended as the most balanced approach.

      In the paper's own words

      “Combining a moderate organic base with a small inorganic supplement at peak demand appears to be the most balanced approach for irrigated cotton on calcareous soils in arid regions.”

      Page 3

      Found in: Conclusion

      Read it in the full textOpen PDF at page 3 ↗
    • The authors state that multi-season trials are needed to determine if an integrated strategy maintains soil organic nitrogen without negatively impacting economic returns or fiber quality. View evidence ↗

      What it means

      The authors state that multi-season trials are needed to determine if an integrated strategy maintains soil organic nitrogen without negatively impacting economic returns or fiber quality.

      In the paper's own words

      “Further trials over multiple seasons would clarify whether this integrated strategy sustains soil organic N stocks without sacrificing fibre quality or economic returns.”

      Page 3

      Found in: Conclusion

      Read it in the full textOpen PDF at page 3 ↗

Visual summary

3 visuals

Illustrations explain the paper; charts are replotted from the paper's own table values.

AI-generated illustration
AI-generated conceptual illustration (cotton plants in calcareous soil). It explains the idea and does not show study data.↗ Enlarge
Blended Nitrogen Management Strategy
AI-generated conceptual illustration (cotton plants in calcareous soil). It explains the idea and does not show study data.

AI-generated conceptual illustration (cotton plants in calcareous soil). It explains the idea and does not show study data.

Open full-size image ↗

Blended Nitrogen Management Strategy

AI-generated conceptual illustration (cotton plants in calcareous soil). It explains the idea and does not show study data.

View source evidence ↗
Replotted from source data
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
Total N Uptake: Organic vs Inorganic vs Organic vs Inorganic vs Organic
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

Total N Uptake: Organic vs Inorganic vs Organic vs Inorganic vs Organic

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗
Replotted from source data
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
Residual Mineral N: Organic vs Inorganic vs Organic vs Inorganic vs Organic
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

Residual Mineral N: Organic vs Inorganic vs Organic vs Inorganic vs Organic

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗

Figures & tables

From the original paper
Nitrogen uptake, apparent N recovery, and residual soilTable 1Page 2Relationship between nitrogen applied and total N uptake for organic (circles, dashed) and inorganic (triangles, solid) sources inFigure 1Page 2Schematic representation of the nitrogen balance components under organic and inorganic nutrient management in cotton.Figure 2Page 3
FULL TEXT Original article · reflowed for reading

Introduction

Cotton is a nutrient-hungry crop, and nitrogen sits at the top of its shopping list. A single hectare producing 2.5 tonnes of seed cotton removes roughly 110-130 kg N from the soilplant system [1] . Getting that nitrogen in at the right rate and in the right form is what separates a profitable field from a wasteful one. Globally, urea remains the dominant N source for cotton. It is cheap, widely available, and fast-actingqualities that also make it prone to volatilisation and leaching when applied in excess [2] . Organic alternatives such as composted manure release nitrogen more slowly, matching the crop's extended uptake window better in theory, but often delivering less total available N per unit applied [3] . The trade-off between immediate N supply and longer-term soil health benefits is at the heart of the organic-versus-inorganic debate in cotton nutrition [4] . Iran's Fars Province grows about 18% of the country's cotton on calcareous soils with high pH and low organic matterconditions that amplify ammonia volatilisation from surfaceapplied urea [5] . Despite this, most local growers rely exclusively on mineral fertilisers. Fieldlevel N balances that could guide more nuanced recommendations are nearly absent from the regional literature. This research was set up to compare the nitrogen dynamics, crop uptake, and post-season balance of organic and inorganic N sources across a range of application rates in irrigated cotton at Shiraz. The aim was to identify a management strategy that sustains yield while minimising residual mineral N left vulnerable to off-season losses.

Climatic and Environmental Conditions

During the 2023 growing season, mean monthly temperatures ranged from 24.1 °C in May to 33.6 °C in July, with a seasonal average of 29.3 °C. Relative humidity remained between 18% and 34%. No rainfall was recorded between mid-May and late September. Cumulative reference evapotranspiration (ET₀) during the crop cycle was 1,087 mm. These hot, dry conditions are representative of arid-zone cotton environments and strongly influence nitrogen transformation rates in soil [6] .

Material and Methods

Material and Methods

Material

The trial used a randomised complete block design with two N source treatments (composted cattle manure, 1.8% N; and urea, 46% N) each at five rates (0, 40, 80, 120, 160 kg N ha⁻¹), giving ten treatment combinations replicated four times. Cotton cultivar Varamin-76, a medium-staple upland type, was sown on 8 May 2023 at 80 × 20 cm spacing in plots of 6 m × 4 m. Manure was incorporated one week before sowing; urea was split 50% at sowing and 50% at first-square stage. Phosphorus (90 kg P₂O₅ ha⁻¹ as triple super phosphate) and potassium (60 kg K₂O ha⁻¹ as potassium sulphate) were applied uniformly.

Methods

Soil mineral N (NH₄⁺-N + NO₃⁻-N) was measured at 0-30 cm depth at sowing, peak bloom, and harvest using 2M KCl extraction and a continuous-flow analyser [7] . Plant N uptake was determined by Kjeldahl digestion of seed cotton and vegetative biomass at final harvest [8] . The N balance for each plot was calculated as: N balance = (N applied + initial soil mineral N) -(crop N uptake + residual soil mineral N + estimated gaseous losses). Gaseous losses were estimated using the emission-factor approach of the IPCC Tier 1 methodology (1% of applied N as N₂O-N; 10% of urea-N as NH₃-N) [9] . All data were analysed by two-way ANOVA with Fisher's LSD at p = 0.05.

Results

Results

Comprehensive Interpretation

Inorganic urea delivered higher N uptake at every application rate, but the margin of superiority shrank progressively -from 17.8% at 40 kg N ha⁻¹ to 26.6% at 160 kg N ha⁻¹ for uptake, though apparent recovery fell in both sources as rate increased. Residual mineral N accumulated faster under urea, reaching 68.9 kg ha⁻¹ at the highest rate versus 43.6 kg ha⁻¹ for organic, indicating a larger pool of unused mineral N vulnerable to post-season leaching.

Discussion

The lower apparent recovery of organic N (27-39%) compared to inorganic N (38-49%) reflects the slower mineralisation kinetics of composted manure in calcareous soils [3] . With soil pH near 8.0 and CaCO₃ above 23%, a fraction of the urea-N is also lost to ammonia volatilisation, but the rapid hydrolysis of urea still delivers a quick pulse of plant-available N that cotton captures during the square-tobloom period [10] . Organic sources, by contrast, release N gradually -some of it after the crop's peak demand has passed.

The high residual mineral N in urea plots at harvest is cause for concern. In the semi-arid Fars environment, the first autumn rains can move this leftover nitrate below the root zone before the next crop is sown [5] . Over several seasons, this pattern degrades groundwater quality and wastes purchased nitrogen. Organic-treated plots left less residual mineral N because a larger share of the applied N remained immobilised in soil organic matter, where it mineralises slowly across subsequent years [11] . A blended strategy -say, 80 kg N ha⁻¹ from compost topped up with 40 kg inorganic N at first squarecould capture the best of both worlds: a slow organic base that feeds the soil's long-term N pool, plus a targeted mineral supplement during peak demand.

Conclusion

Inorganic urea produced higher immediate N uptake and seed-cotton yield than composted manure at equivalent rates, but it also left substantially more mineral N in the soil after harvesta surplus susceptible to leaching losses. Organic management retained more nitrogen within the soil organic pool, offering a slower but steadier N supply. Neither source alone optimised both short-term yield and long-term N conservation.

Combining a moderate organic base with a small inorganic supplement at peak demand appears to be the most balanced approach for irrigated cotton on calcareous soils in arid regions. Further trials over multiple seasons would clarify whether this integrated strategy sustains soil organic N stocks without sacrificing fibre quality or economic returns.

Figures and tables from the paper

Table 1. Nitrogen uptake, apparent N recovery, and residual soil
N Rate (kg ha⁻¹)SourceTotal N UptakeApparent Recovery %Residual Mineral NSeed Cotton (kg ha⁻¹)
0Control18.2—24.31087
40Organic32.636.027.81463
40Inorganic38.450.531.61612
80Organic48.938.434.21884
80Inorganic56.748.141.72156
120Organic57.332.638.12247
120Inorganic71.244.252.42583
160Organic62.127.443.62391
160Inorganic78.637.868.92774

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

View original table image
Nitrogen uptake, apparent N recovery, and residual soil↗ Enlarge
Table 1
Nitrogen uptake, apparent N recovery, and residual soil

Nitrogen uptake, apparent N recovery, and residual soil

Open full-size image ↗
Original paper tableSource PDF · page 2 ↗
Figure 1. Relationship between nitrogen applied and total N uptake for organic (circles, dashed) and inorganic (triangles, solid) sources in
Relationship between nitrogen applied and total N uptake for organic (circles, dashed) and inorganic (triangles, solid) sources in↗ Enlarge
Figure 1
Relationship between nitrogen applied and total N uptake for organic (circles, dashed) and inorganic (triangles, solid) sources in

Relationship between nitrogen applied and total N uptake for organic (circles, dashed) and inorganic (triangles, solid) sources in

Open full-size image ↗
Original paper figureSource PDF · page 2 ↗
Figure 2. Schematic representation of the nitrogen balance components under organic and inorganic nutrient management in cotton.
Schematic representation of the nitrogen balance components under organic and inorganic nutrient management in cotton.↗ Enlarge
Figure 2
Schematic representation of the nitrogen balance components under organic and inorganic nutrient management in cotton.

Schematic representation of the nitrogen balance components under organic and inorganic nutrient management in cotton.

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗

References

14 in the original paper
  1. Rochester IJ. Nutrient uptake and export from an Australian cotton field. Nutr Cycl Agroecosyst. 2007;77(3):213-223.
  2. Freney JR, Denmead OT, Simpson JR. Nitrous oxide emission from soils at low moisture contents. Soil Biol Biochem. 1979;11(2):167-173.
  3. Gaskell M, Smith R. Nitrogen sources for organic vegetable crops. HortTechnology. 2007;17(4):431-441.
  4. Watson CA, Atkinson D, Gosling P, Jackson LR, Rayns FW. Managing soil fertility in organic farming systems. Soil Use Manag. 2002;18(S1):239-247.
  5. Jalali M. Nitrates leaching from agricultural land in Hamadan, western Iran. Agric Ecosyst Environ. 2005;110(3-4):210-218.
  6. Ghosh PK, Dayal D, Bandyopadhyay KK, Mohanty M. Evaluation of straw and polythene mulch for enhancing productivity of irrigated summer groundnut. Field Crops Res. 2006;99(2-3):76-86.
  7. Mulvaney RL. Nitrogen-inorganic forms. In: Sparks DL, editor. Methods of soil analysis. Part 3. Madison: SSSA; 1996. p. 1123-1184.
  8. Bremner JM. Nitrogen-total. In: Sparks DL, editor. Methods of soil analysis. Part 3. Madison: SSSA; 1996. p. 1085-1121.
  9. IPCC. 2006 IPCC guidelines for national greenhouse gas inventories. Hayama: Institute for Global Environmental Strategies; 2006. p. 4.1-4.54.
  10. Suter HC, Sultana H, Turner D, Davies R, Walker C, Chen DL. Influence of urea fertiliser formulation, soil pH and rainfall on emissions of nitrous oxide. Soil Res. 2013;51(3):220-227.
  11. Gaskell M, Smith R, Mitchell J, Koike ST, Fouche C, Hartz TK, et al. Soil fertility management for organic crops. University of California ANR Publication 7249; 2006. p. 1-8.
  12. Constable GA, Rochester IJ. Nitrogen application to cotton on clay soil: timing, soil testing and simulation. Agron J. 1988;80(3):498-502.
  13. Halvorson AD, Wienhold BJ, Black AL. Tillage, nitrogen, and cropping system effects on soil carbon sequestration. Soil Sci Soc Am J. 2002;66(3):906-912.
  14. Bronson KF, Booker JD, Keeling JW, Boman RK, Wheeler TA, Lascano RJ, et al. Cotton canopy reflectance at landscape scale as affected by nitrogen fertilization. Agron J. 2005;97(3):654-660.