Madras Agricultural Journal
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Research Article | Open Access | Peer Review

Effective Utilization of Gypsum-Enriched Water Hyacinth (Pontederia crassipes Mart.) Chunks as Green Manure for Groundnut Fields

A Anto Rashwin ORCID iD , Loganathan Pragadeeshwaran ORCID iD
Volume : 112
Issue: June(4-6)
Pages: 127 - 134
Downloads: 13
Published: August 07, 2025
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Abstract


Water hyacinth (Pontederia crassipes Mart. 1843) is an invasive weed species that poses a significant threat to aquatic ecosystems due to eutrophication caused by natural or anthropogenic effects. The cost of controlling these plants is high. Despite this challenge, water hyacinth offers beneficial and economic advantages, making it a valuable resource for recovery. Due to its invasive nature, water hyacinth causes ecological, social, and economic problems in tropical and subtropical areas. It can be controlled by lowering water levels (drawdown) to "strand" and desiccate the plants on exposed shorelines; however, the time required to dry large mats of the plant can be extended. Additionally, drawdowns and droughts trigger seed germination, rapidly re-establishing water hyacinth when water levels rise. Countries like India, China, Japan, and Vietnam have addressed the problem by utilizing the beneficial aspects of water hyacinth, thus avoiding the high costs of controlling it. This paper discusses one of the beneficial uses of water hyacinth: its application as green manure enriched with gypsum for groundnut fields (Alfisols) in tropical regions. Being an organic source, water hyacinth builds up soil organic matter and enriches the soil's physical, chemical, and biological properties. This approach demonstrates a significant increase in the agronomic growth parameters of groundnut plants.

DOI
Pages
127 - 134
Creative Commons
Copyright
© The Author(s), 2025. Published by Madras Agricultural Students' Union in Madras Agricultural Journal (MAJ). This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 License (https://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution and reproduction in any medium, provided the original work is properly cited by the user.

Keywords


Water hyacinth; Eutrophication; Groundnut; Organic manure; Nutrient recycling

Introduction


Pontederia crassipes, formerly known as Eichhornia crassipes (Mart.) Solms was introduced as an ornamental crop from South America to the botanical gardens in Bengal by 1896, during the British colonial rule. Commonly referred to as Water Hyacinth, it belongs to the Pontederiaceae family. It was once part of the polyphyletic genus Pontederia, named after the Italian botanist and botany professor Giulio Pontedera. This free-floating plant has become one of the world's most notorious aquatic weeds, causing significant problems across tropical and subtropical continents. Water Hyacinth poses various challenges; its dense growth interferes with navigation, creating barriers that impede the movement of boats and waterways. It exhibits an annual growth pattern in temperate regions and persists as a perennial weed in tropical and subtropical climates. Propagation primarily occurs vegetatively through slender horizontal runners known as stolons. Chemical control of water hyacinth using herbicides like 2,4-D Amine has shown some effectiveness; however, such methods pose sustainability concerns and are not environmentally friendly (Hari and Srinivasan, 2023). It can be utilized as green manure, compost, feed for ruminants and non-ruminants, fish feed, and even as a phytoremediator to mitigate heavy metal contamination (Premalatha et al., 2019). Notably, Water Hyacinth can purify wastewater by absorbing dissolved nitrogen, phosphorus, and undesirable minerals, including heavy metals. Anaerobic degradation of water hyacinth has been shown to trigger substantial microbiological activity, contributing to enhanced decomposition and potential nutrient cycling (Rajasekaran, 2023).

Methodology


In this study, Water Hyacinth is utilized as green manure and fortified with gypsum to enhance its efficacy. The research was conducted at the Agricultural College and Research Institute, Vazhavachanur, Tiruvannamalai (12.0728°N, 78.9891°E), situated in a tropical region characterised by Alfisols as the predominant soil class. Groundnut (VRI 10) was chosen as the target crop due to its popularity among the local farmers, though drought is a major limiting factor affecting groundnut yield (Vaithiyalingan, 2016). As we know, Water Hyacinth is an invasive aquatic weed that causes damage to water bodies and the aquatic ecosystem. In the motto of waste to worth and to protect our environment, Water Hyacinth was collected from Avaniyapuram pond near Vellakal, Madurai. The collected plants were shade dried for 4-5 days. Fresh Water Hyacinth contains 90% moisture and 15-20% solid materials. After the fifth day, plant parts are chopped into small pieces to increase the surface area. This research evaluated the utilization of Water Hyacinth as a green manure and its enrichment with gypsum for improved agricultural outcomes, explicitly focusing on conventional groundnut cultivation in Tamil Nadu.

Biology:

Table 1. Scientific classification of Water Hyacinth

Rank

Classification

Kingdom

Plantae

Division

Spermatophyta

Subdivision

Angiospermae

Class

Monocotyledonae

Order

Commelinales

Family

Pontederiaceae

Genus

Pontederia

Species

P. crassipes (Mart.) 1843

Pontederia, a perennial and fast-growing broad-leaved grass weed, proliferates abundantly in water bodies. It is a prime example of invasive and naturalized weeds, firmly establishing itself wherever it invades, such as in India. Pontederia exhibits rapid growth rates. Each inflorescence of Pontederia bears around 20 flowers, each capable of producing 3000-4000 seeds. These seeds sink to the bottom of water bodies and can remain viable for at least 20 years. Water Hyacinth possesses a unique type of parenchyma tissue known as aerenchyma. Aerenchyma is a spongy tissue that contains air spaces or channels, particularly in the hyacinth stem. This structure imparts buoyancy to the stem, enabling Water Hyacinth to float on the water surface.

Chemical Composition of Water Hyacinth

Fresh Water Hyacinth typically contains about 90% water and 15-20% solid materials (Ndimele et al., 2011). Its nutrient composition includes nitrogen (N) at levels ranging from 1.70% to 2.15%, phosphorus (P) ranging from 0.38% to 0.56%, and potassium (K) ranging from 2.68% to 3.45%. The protein content on a dry basis is reported to be between 9.14% and 14.37%. Moreover, Water Hyacinth is recognized as a carrier of heavy metals such as iron, magnesium, and zinc, making it suitable for phytoremediation purposes (Hasani et al., 2021).

Utilizing Water Hyacinth as a Green Manure

               Water Hyacinth proliferates in water bodies due to eutrophication. It was collected from a eutrophied water body and subjected to shade drying. After drying, it was cut into small pieces, less than 3 cm in size, to increase the surface area and facilitate its effective utilization by crops. Various parts of the water hyacinth were used for green manure, which was applied to crops before sowing. Water Hyacinth serves as a rich source of nitrogen (N), phosphorus (P), potassium (K), and micronutrients, providing significant benefits to crops upon application (Canning, 2025). Its utilization has shown promising results, including increased soil microbial populations and enhanced microbial activity. This, in turn, leads to the accumulation of soil organic matter and improved soil aggregation (Begum et al., 2022).

Studies have indicated that the application of water hyacinth results in improved agronomic characteristics for plants. Additionally, it enhances the soil's water holding capacity, with treated soil increasing from 8.21% to 10.16% compared to untreated soil (Khan and Sarwar, 2002). Water hyacinth has been found to contain significant nutrient reserves. When processed through co-composting with cow dung and crop residues, it produces high-quality organic manure with elevated NPK levels (Prithiv Raj et al., 2019).

Enrichment with Gypsum (Fortification)

Shade-dried cut pieces (less than 3 cm) of Water Hyacinth are enriched with calcium sulfate (gypsum) at 1:1. This enriched mixture is applied to the field before sowing and again during earthing up on the 45th day to enhance peg formation. Calcium is essential for strong shell formation and cell wall thickening (middle lamella), while sulfur is essential for increasing the oil content of groundnuts. The porous nature of the small Water Hyacinth pieces helps retain the gypsum, facilitating its slow release to the plants and significantly increasing yield. Gypsum application has long been recognised for improving soil physical properties, particularly in sodic and degraded soils, by enhancing structure and promoting calcium availability (Gashi et al., 2024).

Water hyacinth waste was collected, shade-dried, and cut into small pieces from water bodies. These pieces were then enriched with gypsum. The experiment was conducted using a Completely Randomized Design (CRD) across three trials. The treatments included: T1-Control, T2-Water hyacinth green manure, and T3-Water hyacinth green manure enriched with gypsum. Agronomic growth parameters of the crop were measured at 30, 60, and 90 days, as well as at the time of harvest.

Table 1. Effect on Plant Height and Width

PLANT HEIGHT AND WIDTH

Number of Days After Sowing

T1

T2

T3

Height (cm)

Width (cm)

Height (cm)

Width (cm)

Height (cm)

Width (cm)

30 DAS

10

5

19

9

20

10

60 DAS

13

7

33

12

35

14

90 DAS

15

10

45

14

47

16

At The Time of Harvest (95 DAS)

15

10

46

16

49

18

NUMBER OF FILLED AND UNFILLED PODS

Number of Days After Sowing

T1

T2 

T3

Average Number of pods per plant

Average Number of filled pods/plant

Average Number of pods per plant

Average Number of filled pods/plant

Average Number of pods per plant

Average Number of filled pods/plant

30 DAS

Flower initiation

Nil

Flower initiation

Nil

Flower initiation

Nil

60 DAS

10

Nil

15

Nil

19

Nil

90 DAS

14

9

23

19

25

21

At the time of harvest

19

12

25

20

30

25

 

Results Discussion


Upon observing the soil, it shows aggregation due to decomposition. Water hyacinth releases gum-like substances that aid in binding soil particles together.

From Table 1, agronomical growth parameters were calculated at the 30th, 60th, and 90th days and at the time of harvest. Results show that good plant height and width were achieved in T2 (Fig. 5) and T3 (Fig. 6), while stunted growth (maximum height 15 cm) was observed in the control T1 (Fig. 4). The maximum plant height of 49 cm was observed in T3, and 46 cm was observed in T2. The maximum width of 18 cm was observed in T3, and 16 cm in T2. Applying water hyacinth green manure to the field on the 45th day promotes soil aggregation during the earthing-up process, which helps in more peg formation compared to the control. The application of gypsum-enriched water hyacinth green manure further promotes numerous peg formations. Gypsum prevents soil compaction and loosens the soil, promoting easy peg penetration. Enrichment with water hyacinth promotes soil aggregation by releasing gummy substances, further promoting peg formation and preventing soil erosion due to external factors. Table 2 shows the number of filled and unfilled pods per plant. Results show that the maximum number of good-sized filled pods (25) is achieved in T3. In T2, a maximum number of 20 filled pods is observed, while a lower number of small-sized pods is observed in the control T1. This increment in yield aligns with the study that reported that combined application of organic materials and soil amendments such as gypsum has synergistically improved soil fertility and enhanced crop yield in groundnut systems (Balasubramanian & Palaniappan, 1994).

Conclusion


The results indicate that the agronomic growth and yield parameters of the plants are significantly higher in T3 (Water Hyacinth green manure enriched with gypsum) compared to T2 (Water Hyacinth green manure) and T1 (Control). The growth and yield follow the trend: T1 < T2 < T3. Utilization of Water Hyacinth as green manure, particularly when enriched with gypsum, demonstrates significant improvements in plant growth and yield. This treatment also enhances soil structure and water-holding capacity. It promotes soil aggregation and prevents soil compaction, which paves the way for easy peg penetration and more peg formation. Good agronomical growth parameters are achieved from the experiment. Even though no amount of dry matter is not produced from the Water Hyacinth, due to its invasive nature and rapid multiplication rate, it can be collected large amounts from water bodies. Making Water Hyacinth into green manure and enrichment with gypsum is not laborious and time-consuming. It is the simplest, easiest, and least time-consuming method compared to other composting methods. It is an environment-friendly method that restores the natural balance and creates a healthy habitat for native plants and animals in our waterways by removing. Compared with other conventional methods, it is cost-effective, economical, and eco-friendly for small-scale farmers.

References


Balasubramanian, D., Arunachalam, K., Arunachalam, A., & Das, A. K. (2013). Effect of water hyacinth (Eichhornia crassipes) mulch on soil microbial properties in lowland rainfed rice-based agricultural system in northeast India. Agricultural Research, 2(3), 246–257. https://doi.org/10.1007/s40003-013-0073-7

Begum Rasmiya S.L., Himaya S.M.M.S., Afreen S.M.M.S. (2022). Potential of Water Hyacinth (Eichhornia crassipes) as Compost and its Effect on Soil and Plant Properties: A Review. Agricultural Reviews. 43(1): 20-28. https://doi:10.18805/ag.R-184

Canning, A. (2025). A Review on Harnessing the Invasive Water Hyacinth (Eichhornia crassipes) for Use as an Agricultural Soil Amendment. Land, 14(5), 1116. https://doi.org/10.3390/land14051116

Gashi, N., Szőke, Z., Czakó, A., Fauszt, P., Dávid, P., Mikolás, M., Stündl, L., Gál, F., Remenyik, J., Sándor, Z., & Paholcsek, M. (2024). Gypsum and Tillage Practices for Combating Soil Salinity and Enhancing Crop Productivity. Agriculture, 15(6), 658. https://doi.org/10.3390/agriculture15060658

Hari, M. N., & Srinivasan, K. M. (2023). Observations on the comparative effectiveness of aminotriazole and 2,4-D amine in the control of water hyacinth (Eichhornia crassipes). Madras Agricultural Journal, 53(July), 289–292. https://doi.org/10.29321/MAJ.10.A03801

Hasani, Q., Pratiwi, N. T. M., WardiAtno, Y., Effendi, H., Martin, A. N., Efendi, E., Pirdaus, P., & Wagiran. (2021). Phytoremediation of iron in ex-sand mining waters by water hyacinth (Eichhornia crassipes). Biodiversitas, 22(2), 838–845. https://doi.org/10.13057/biodiv/d220238

Khan, S., & Sarwar, K. S. (2002). Effect of water-hyacinth compost on physical, physico-chemical properties of soil and on rice yield. Journal of Agronomy, 1, 64–65. https://doi.org/10.3923/ja.2002.64.65

Ndimele, P. E., Kumolu-Johnson, C. A., & Anetekhai, M. A. (2011). The invasive aquatic macrophyte, water hyacinth (Eichhornia crassipes (Mart.) Solm-Laubach: Pontedericeae): Problems and prospects. Research Journal of Environmental Sciences, 5(6), 509–520. https://doi.org/10.3923/rjes.2011.509.520

Premalatha, R. P., Parameswari, E., Davamani, V., Malarvizhi, P., & Avudainayagam, S. (2019). Biosorption of Chromium (III) from aqueous solution by water hyacinth biomass. Madras Agricultural Journal, 106(Special Issue), 1-3. https://doi.org/10.29321/MAJ.2019.000215

Prithiv Raj, V., Ilakiya, T., Nivedha, P., Sharmila, A. S., & Parameswari, E. (2019). Assessing the effect of co-composting technique to generate quality manure out of water hyacinth (Eichhornia crassipes). Madras Agricultural Journal, 104, 152–156. https://doi.org/10.29321/MAJ.2019.000213

Rajasekaran, P. (2023). Microbiological changes accompanying degradation of water hyacinth in an anaerobic digester. Madras Agricultural Journal, 67(January), 39–41. https://doi.org/10.29321/MAJ.10.A02799

Vaithiyalingan, M. (2016). Combining ability studies for yield and yield components in groundnut (Arachis hypogaea). Electronic Journal of Plant Breeding, 7(1), 78–85. https://doi.org/10.5958/0975-928X.2016.00011.9

Author Information


Loganathan Pragadeeshwaran


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