Authors :
Ali Khan Kanani
Volume/Issue :
Volume 11 - 2026, Issue 7 - July
Google Scholar :
https://tinyurl.com/bddshhkh
Scribd :
https://tinyurl.com/3444dttk
DOI :
https://doi.org/10.38124/ijisrt/26jul273
Note : A published paper may take 4-5
working days from the publication date to appear in PlumX Metrics, Semantic Scholar, and
ResearchGate.
Abstract :
Soil acidification is one of the most critical and underaddressed threats to global agriculture, currently affecting
an estimated 50% of the world's arable land. Driven primarily by atmospheric deposition of sulfur dioxide and nitrogen
oxides, excessive nitrogen fertilization, and the natural leaching of base cations, soil acidification disrupts the chemical
equilibrium of the rhizosphere, diminishing nutrient bioavailability and increasing the concentration of phytotoxic elements
such as aluminum (Al³⁺) and manganese (Mn²⁺). This research investigates the impact of two soil contaminants —
hydrochloric acid (HCl) and lead nitrate [Pb(NO₃)₂] — at three concentration levels each (0.5 mol/L, 1.0 mol/L, and 2.0
mol/L) on the germination rate and early shoot development of Vigna radiata (mung bean) under controlled laboratory
conditions. The results were unambiguous: only the untreated control group (pH ≈ 7.0, distilled water) achieved successful
germination, producing shoots averaging 3.2 cm at Day 7. All six treatment groups — spanning pH values from
approximately 1.9 to 5.2 — recorded either negligible or zero germination, confirming that even moderate soil acidification
produces conditions lethal to seed germination in acid-sensitive legume species. These findings corroborate the hypothesis
that soil pH deviations beyond the tolerance range of a given species produce dose-dependent inhibition of germination and
growth. The paper contextualizes these experimental results within the broader literature on soil acidification mechanisms,
discusses real-world agricultural implications particularly for smallholder farmers in South Asia, and proposes sustainable
mitigation strategies including biochar application, composting, and integrated soil management systems.
References :
- Agegnehu, G., Bass, A. M., Nelson, P. N., & Bird, M. I. (2016). Benefits of biochar, compost and biochar–compost for soil quality, maize yield and greenhouse gas emissions in a tropical agricultural soil. Science of the Total Environment, 543, 295–306.
- Amlinger, F., Peyr, S., & Cuhls, C. (2007). Greenhouse gas emissions from composting and mechanical biological treatment. Waste Management & Research, 26(1), 47–60.
- Barrios, E., Sileshi, G. W., Shepherd, K., & Sinclair, F. (2012). Agroforestry and soil health: Linking trees, soil biota and ecosystem services. In D. H. Wall et al. (Eds.), Soil Ecology and Ecosystem Services. Oxford University Press.
- Brady, N. C., & Weil, R. R. (2016). The Nature and Properties of Soils (15th ed.). Pearson.
- Edmeades, D. C. (2003). Lime responses in pastures and crops in New Zealand soils: A review. New Zealand Journal of Agricultural Research, 46(1), 17–28.
- Evans, C. D., Monteith, D. T., Reynolds, B., & Clark, J. M. (2014). Long-term decreases in dissolved organic carbon levels in upland soils and waters in the UK. European Journal of Soil Science, 65(6), 713–720.
- Fageria, N. K., & Baligar, V. C. (2008). Ameliorating soil acidity of tropical Oxisols by liming for sustainable crop production. Advances in Agronomy, 99, 345–431.
- Food and Agriculture Organization of the United Nations. (2019). Soil degradation. FAO. https://www.fao.org/soils-portal/soil-degradation-restoration
- Goulding, K. W. T. (2016). Soil acidification and the importance of liming agricultural soils with particular reference to the United Kingdom. Soil Use and Management, 32(3), 390–399.
- Guo, J. H., Liu, X. J., Zhang, Y., Shen, J. L., Han, W. X., Zhang, W. F., Christie, P., Goulding, K. W. T., Vitousek, P. M., & Zhang, F. S. (2010). Significant acidification in major Chinese croplands. Science, 327(5968), 1008–1010.
- Lehmann, J., Rillig, M. C., Thies, J., Masiello, C. A., Hockaday, W. C., & Crowley, D. (2011). Biochar effects on soil biota – A review. Soil Biology and Biochemistry, 43(9), 1812–1836.
- Likens, G. E., Driscoll, C. T., & Buso, D. C. (1996). Long-term effects of acid rain: Response and recovery of a forest ecosystem. Science, 272(5259), 244–246.
- Menz, F. C., & Seip, H. M. (2004). Acid rain in Europe and the United States: An update. Environmental Science & Policy, 7(4), 253–265.
- Odén, S. (1968). The acidification of air and precipitation and its consequences in the natural environment. Ecology Committee Bulletin, 1, Swedish National Science Research Council.
- Reddy, P. P. (2020). Smallholder farming in India: Challenges and strategies. Springer Nature.
- Rengel, Z. (2011). Soil pH, soil health and climate change. In B. P. Singh, A. L. Cowie, & K. Y. Chan (Eds.), Soil Health and Climate Change (pp. 139–159). Springer.
- Siddiqui, M. H., Al-Whaibi, M. H., & Mohammad, F. (2011). Heavy metals and plant physiology. In M. H. Siddiqui et al. (Eds.), Bioinorganic Chemistry and Applications. Hindawi.
- Singh, A., & Agrawal, M. (2012). Effects of waste water irrigation on physical and biochemical characteristics of soil and metal partitioning in Beta vulgaris L. Agricultural Water Management, 98, 1857–1865.
- Van Breemen, N., Mulder, J., & Driscoll, C. T. (1998). Acidification and alkalinization of soils. Plant and Soil, 75(3), 283–308.
- Young, A. (1997). Agroforestry for Soil Management (2nd ed.). CABI Publishing.
Soil acidification is one of the most critical and underaddressed threats to global agriculture, currently affecting
an estimated 50% of the world's arable land. Driven primarily by atmospheric deposition of sulfur dioxide and nitrogen
oxides, excessive nitrogen fertilization, and the natural leaching of base cations, soil acidification disrupts the chemical
equilibrium of the rhizosphere, diminishing nutrient bioavailability and increasing the concentration of phytotoxic elements
such as aluminum (Al³⁺) and manganese (Mn²⁺). This research investigates the impact of two soil contaminants —
hydrochloric acid (HCl) and lead nitrate [Pb(NO₃)₂] — at three concentration levels each (0.5 mol/L, 1.0 mol/L, and 2.0
mol/L) on the germination rate and early shoot development of Vigna radiata (mung bean) under controlled laboratory
conditions. The results were unambiguous: only the untreated control group (pH ≈ 7.0, distilled water) achieved successful
germination, producing shoots averaging 3.2 cm at Day 7. All six treatment groups — spanning pH values from
approximately 1.9 to 5.2 — recorded either negligible or zero germination, confirming that even moderate soil acidification
produces conditions lethal to seed germination in acid-sensitive legume species. These findings corroborate the hypothesis
that soil pH deviations beyond the tolerance range of a given species produce dose-dependent inhibition of germination and
growth. The paper contextualizes these experimental results within the broader literature on soil acidification mechanisms,
discusses real-world agricultural implications particularly for smallholder farmers in South Asia, and proposes sustainable
mitigation strategies including biochar application, composting, and integrated soil management systems.