COMPARATIVE ASSESSMENT OF PRE- AND POST-EMERGENCE APPLICATIONS OF CASSAVA MILL EFFLUENT FOR WEED MANAGEMENT

Authors

  • O. P. AYODELE Institute of Agricultural Research and Training (IAR&T), Obafemi Awolowo University, PMB 5029, Moor Plantation, Ibadan, Nigeria.
  • J. O. AMOSUN Institute of Agricultural Research and Training (IAR&T), Obafemi Awolowo University, PMB 5029, Moor Plantation, Ibadan, Nigeria.
  • I. J. IMOMOH Department of Crop Science, Faculty of Agriculture, University of Benin, Benin City, Nigeria
  • O. A. ALUKO Institute of Agricultural Research and Training (IAR&T), Obafemi Awolowo University, PMB 5029, Moor Plantation, Ibadan, Nigeria.

Keywords:

Bio-herbicide, cyanogenic compounds, Cassava processing waste, Weed control efficiency

Abstract

Weed management in smallholder and low-input farming systems is constrained by the cost, environmental risks, and declining efficacy of synthetic herbicides. Cassava mill effluent (CME), a cassava-processing by-product rich in cyanogenic compounds, has potential for weed control, but its application strategy and persistence are poorly understood. This study evaluated the efficacy of CME applied as a pre-emergence soil treatment and as a post-emergence foliar spray for weed control. A screen-house experiment was conducted using a Completely Randomised Design with three replicates. CME was applied at rates equivalent to 6, 12, 18, and 24 g CN ha⁻¹, alongside an untreated control, either before weed emergence or after weed establishment. Weed density, species richness, fresh and dry biomass, and weed control efficiency (WCE) were assessed over two successive weed flushes. Pre-emergence soil application of CME showed no significant effects on weed density, biomass, or species richness across both flushes, indicating limited effectiveness under soil-applied conditions. In contrast, post-emergence foliar application significantly reduced weed density from 1188 to 280 plants m2, fresh weight from 3927 to 495 g m2, , and dry weight from 825 to 118 g m2 during the first weed flush. The highest level of weed control was achieved at 24 g CN ha⁻¹ applied post-emergence, with weed control efficiency peaking at 85.9%. No significant weed suppression was observed during the second flush, suggesting limited residual activity of CME. The study concludes that CME functions as a short-lived bioherbicide when applied post-emergence, with effectiveness dependent on direct contact with weed foliage. Its low persistence implies minimal risk to subsequent crops, supporting its suitability for sustainable and integrated weed management systems. Therefore, repeated post-emergence applications of CME at 24 g CN ha⁻¹, or its integration with other weed control methods, are recommended to enhance long-term weed management effectiveness.

 

 

 

References

Aladesanwa, R.D. 2005. Tomato (Lycopersicon esculentum Mill.) crop performance as influenced by aqueous extracts of some tropical plants. Biological Agriculture and Horticulture. 23(2): 125–133.

Batish, D.R., Setia, N., Singh, H.P., Kohli, R.K. 2004. Phytotoxicity of lemon-scented eucalypt oil and its potential use as a bioherbicide. Crop Protection. 23(12): 1209–1214.

Dayan, F.E., Cantrell, C.L., Duke, S.O. 2009. Natural products in crop protection. Bioorganic and Medicinal Chemistry. 17(12): 4022–4034.

Délye, C., Jasieniuk, M., Le Corre, V. 2013. Deciphering the evolution of herbicide resistance in weeds. Trends in Genetics. 29(11): 649–658.

Devine, M.D., Duke, S.O., Fedtke, C. 1993. Physiology of Herbicide Action. PTR Prentice Hall, Englewood Cliffs, New Jersey, USA. 441pp.

Duke, S.O. 2012. Why have no new herbicide modes of action appeared in recent years? Pest Management Science. 68(4): 505–512.

Fayinminnu, O.O., Fadina, O.O., Olabiyi, T.I. 2013. Comparative assessment of three sources of crude cassava water extract as bioherbicide. Journal of Biology, Agriculture and Healthcare. 3(12): 108–114.

Ganyam, M.M., Zikora, A.K., Omeje, N.O., Atsembe, D.M., Nelson, C., Kemmeth, U.C., Samuel, C. 2022. Bioherbicide effect of effluent from processed Manihot esculenta tubers. Asian Journal of Biology. 15(2): 14–21.

Geissdoerfer, M., Savaget, P., Bocken, N.M.P., Hultink, E.J. 2017. The circular economy – a new sustainability paradigm? Journal of Cleaner Production. 143: 757–768.

George, D., Mallery, P. 2016. IBM SPSS Statistics 23 Step by Step: A Simple Guide and Reference. 14th ed. Routledge, New York, USA. 386pp.

Heap, I. 2014. Global perspective of herbicide-resistant weeds. Pest Management Science. 70(9): 1306–1315.

Jaszczak, E., Polkowska, Ż., Narkowicz, S., Namieśnik, J. 2017. Cyanides in the environment—analysis—problems and challenges. Environmental Science and Pollution Research. 24(19): 15929–15948.

Khanh, T.D., Xuan, T.D., Chung, I.M. 2007. Rice allelopathy and the possibility for weed management. Annals of Applied Biology. 151(3): 325–339.

Lawal, N.S., Ogedengbe, K., Oamen, E.C. 2019. Cassava mill wastewater treatment by a combination of physical and nature-based processes: A pilot study. Applied Journal of Environmental Engineering Science. 5(4): 349–356.

Ogundola, A.F., Liasu, M.O. 2007. Herbicidal effects of effluent from processed cassava on growth performances of Chromolaena odorata weed population. African Journal of Biotechnology. 6(6): 685–690.

Osunbitan, J.A. 2012. Short-term effects of cassava processing wastewater on some chemical properties of loamy sand soil in Nigeria. Journal of Soil Science and Environmental Management. 3(7): 164–171.

Patrick, U.A., Egwuonwn, N., Augustine, O.A. 2011. Distribution of cyanide in a cassava-mill-effluent polluted eutric tropofluvent soils of Ohaji Area, south-eastern Nigeria. Journal of Soil Science and Environmental Management. 2(2): 49–57.

Refsgaard, K., Bjarnholt, N., Møller, B.L., Saddik, M.M., Hansen, H.C.B. 2010. Dissipation of cyanogenic glucosides and cyanide in soil amended with white clover (Trifolium repens L.). Soil Biology and Biochemistry. 42(7): 1108–1113.

Soomro, A.M., Laghari, M.Y., Mahar, A.R., Memon, S. 2024. Pre-emergence and post-emergence herbicides: Mechanisms, timing and their role in early weed control in agronomic crops. International Journal of Research in Agronomy. 7(11): 410–413.

Surleva, A., Petkova, Z., Ivanova, I. 2013. Spectrophotometric determination of cyanide using ninhydrin. Bulgarian Chemical Communications. 45(2): 189–193.

Ubalua, A.O. 2010. Cyanogenic glycosides and the fate of cyanide in soil. Australian Journal of Crop Science. 4(4): 223–237.

Velenturf, A.P., Purnell, P. 2021. Principles for a sustainable circular economy. Sustainable Production and Consumption. 27: 1437–1457.

Wang, Y., Zhang, L., Chen, X., Li, H. 2021. Herbicide residues in agroecosystems: Fate, detection, and effect on non-target plants. Research in Agricultural Sciences. 9: 157–165.

Xu, F., Peng, Y., He, Z.-Q., Yu, L.-L. 2023. The role of cyanoalanine synthase and alternative oxidase in promoting salt stress tolerance in Arabidopsis thaliana. BMC Plant Biology. 23: 163.

Zuhra, K., Szabo, C. 2022. The two faces of cyanide: An environmental toxin and a potential novel mammalian gasotransmitter. FEBS Journal. 289(9): 2481–2515.

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Published

2025-07-11

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