Next Article in Journal
Experimental Study on Desorption and Heat Storage Characteristics of Magnesium Sulfate Hydrate in a Moving-Bed Heat Exchange System
Previous Article in Journal
Fortification of a Greek Distilled Spirit by Citrus sinensis Antioxidants Extracted Using Green Recovery via Lecithin-Based Extraction: Optimization of Extraction and Stability
Previous Article in Special Issue
Continuous Fixed Bed Bioreactor for the Degradation of Textile Dyes: Phytotoxicity Assessment
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Biodegradable Menstrual Pads from Hydrophytic Weeds: Sustainability Assessment, Absorption Performance, and Microbial Safety

by
Gayathri Vijayakumar
1,
Swetha Baskar
2,
Sowmiya Raghupathy
2 and
Senthil Kumaran Rangarajulu
3,*
1
Department of Biotechnology, Hindustan Institute of Technology & Science, Chennai 603103, India
2
Department of Biotechnology, Rajalakshmi Engineering College, Chennai 602105, India
3
Department of Biological Engineering, Konkuk University, Seoul 05029, Republic of Korea
*
Author to whom correspondence should be addressed.
Processes 2026, 14(6), 918; https://doi.org/10.3390/pr14060918
Submission received: 3 February 2026 / Revised: 7 March 2026 / Accepted: 11 March 2026 / Published: 13 March 2026

Abstract

Sustainable alternatives to synthetic polymer-based sanitary napkins are essential to reduce the environmental impact and health concerns. This study presents a method for using water hyacinth (Eichhornia crassipes), an invasive aquatic weed, as biomass to produce biodegradable absorbent material for sanitary pads. Water hyacinth fibers were treated with an alkaline solution and incorporated into the absorbent core. Morphological, chemical, structural, functional, microbiological, and biodegradability evaluations were then conducted systematically. Scanning electron microscopy showed that non-cellulosic components were successfully removed, producing a rougher surface topology and enhanced fiber interactions. Fourier-transform infrared spectroscopy confirmed structural changes in cellulose after treatment. Additionally, X-ray diffraction showed that the crystallinity index increased from 53.21% in untreated fibers to 62.56% in treated fibers, indicating improved order and stability. The developed absorbent sanitary pad showed rapid fluid uptake, absorbing 10 mL within three seconds while maintaining a skin-compatible neutral pH of 6.87, as specified in Indian Standard IS 5405:1980. Microbial contamination remained low, with a total bacterial count of 360 CFU/g, no yeast or mold at ≤1 CFU/g, and no presence of Staphylococcus aureus. Soil burial tests showed 70% biodegradability at 40 days and approximately 95% at 60 days, indicating high biodegradability. These findings demonstrate the potential of water hyacinth as an inexpensive and environmentally friendly material for manufacturing hygienic sanitary pads, highlighting the sustainability benefits of valorizing invasive biomass and reducing reliance on synthetic polymers.

Graphical Abstract

1. Introduction

Menstrual protection methods have evolved significantly to meet women’s needs for dependable, discreet, and comfortable hygiene management. Sanitary pads, in particular, offer a variety of forms and features among contemporary disposable feminine care products. Their environmental sustainability and safety, however, continue to be serious concerns [1]. The multilayered architecture of conventional sanitary napkins includes non-biodegradable materials such as polyethylene, polypropylene, superabsorbent polymers, and polymeric films [2]. The widespread use of petroleum-derived polymers has resulted in a substantial carbon footprint. These materials contribute to air pollution and climate change because they remain in the environment for many hundreds of years and when disposed of release harmful pollutants including dioxins and methane [3].
The use of disposable sanitary napkins has expanded significantly in India, as a result of increased health literacy, societal awareness, and government-led menstrual hygiene initiatives. Even if only 10% of Indian women use disposable pads, an estimated 16,180 tons of sanitary waste are produced each month, placing tremendous strain on the country’s existing waste treatment facilities [4]. Disposable sanitary products are vital for women’s health and dignity; however, because of their poor biodegradability and inappropriate disposal methods, their environmental impact has become more apparent.
When exposed to heat, UV light, and mechanical stress, synthetic fibers such as polyester and polypropylene, which are used in traditional sanitary napkins, break down into microplastics and hinder natural degradation processes [5]. Because they are consumed by organisms at various trophic levels, these microplastics pose serious ecological hazards, especially in aquatic habitats, where they can cause oxidative stress, physical harm, and altered metabolism [6]. Additionally, microplastics pose a major threat to public health because they contaminate freshwater and terrestrial ecosystems, damage soil structure, impede plant growth, and enter the human food chain through food products, drinking water, and airborne exposure [7,8].
Recent research has focused on substituting biodegradable, plant-based materials for synthetic absorbents to address these issues. Natural fibers such as bamboo, banana fiber, corn husk, and agricultural residues have shown promising absorbent properties, lower carbon footprints, and improved end-of-life degradation profiles [9,10]. However, many commercially available plant-based sanitary pads emphasize biodegradability and absorbency, whereas active antimicrobial functionality—critical for controlling microbial proliferation, odor generation, and urogenital infections—remains insufficiently explored.
Water hyacinth (Eichhornia crassipes), an invasive aquatic weed, is one of the emerging bioresources that represents both a serious environmental concern and a unique opportunity for sustainable material innovation. Due to its high biomass accumulation and rapid vegetative reproduction, water hyacinth, which is native to the Amazon Basin, has rapidly expanded throughout freshwater bodies worldwide, especially in tropical and subtropical regions [11,12]. Its unchecked growth creates dense floating mats that obstruct waterways, hinder navigation, reduce light penetration, and drastically lower dissolved oxygen levels, thereby disrupting aquatic ecosystems and leading to widespread fish mortality [13,14,15].
Additionally, by trapping sediments and nutrients, water hyacinth infestation accelerates eutrophication, encourages mosquito reproduction, and facilitates the spread of vector-borne diseases, including dengue and malaria [16,17]. From an economic standpoint, infestations result in significant financial burdens due to increased river management expenses, blocked irrigation systems, decreased hydropower generation efficiency, and losses in agriculture and fisheries [18,19]. In India alone, millions of rupees are spent every year on the chemical control and mechanical removal of water hyacinth, with little long-term success [20]. The necessity for sustainable utilization-based management solutions is highlighted by the fact that chemical herbicides exacerbate water contamination and endanger non-target organisms.
Despite these challenges, water hyacinth is a desirable option for value-added applications because of its cellulose-rich fiber structure, high porosity, and rapid renewability. Recent studies have demonstrated its potential in biocomposites, wastewater remediation, natural fiber reinforcement, bioenergy generation, and sustainable polymer systems. Its application has also been extended to phytoremediation for the removal of heavy metals and organic and inorganic pollutants in water bodies [21,22,23]. Notably, the hydrophilic cellulose matrix and porous morphology of water hyacinth fibers enhance liquid absorption and retention, rendering them particularly suitable for absorbent hygiene products.
In this study, sanitary pads were fabricated at a laboratory scale, using processed water hyacinth sheets and finely milled water hyacinth fiber powder as the primary absorbent components. All experimental evaluations were conducted under controlled laboratory conditions to assess the functional performance, pH compatibility, and microbiological safety of the developed sanitary pads.
The principal innovation of this work lies in the dual use of water hyacinth fibers as both an absorbent material and an intrinsically antibacterial component for sanitary napkin production. Water hyacinth reportedly contains bioactive phytochemicals with antibacterial activity against common pathogenic microbes, including phenolics, flavonoids, and alkaloids [24,25]. These characteristics have been effectively utilized in water purification systems, wound dressings, and antimicrobial mats, demonstrating inhibitory activity against Escherichia coli, Staphylococcus aureus, and other clinically significant bacteria [26,27]. By incorporating these naturally occurring antimicrobial fibers into sanitary napkins, user safety can be improved without the need for synthetic chemical additives as bacterial growth, odor development, and the risk of infections during extended use may be reduced.
Furthermore, transforming an environmental liability into a high-value sustainable product through the valorization of water hyacinth for menstrual hygiene applications aligns with the principles of the circular economy and supports the management of invasive species. This approach integrates sustainability, functional antimicrobial performance, and invasive biomass utilization into a single hygiene product platform, in contrast to current biodegradable sanitary pads that primarily emphasize environmental compatibility. Sanitary napkins made from water hyacinth fibers are therefore anticipated to exhibit improved absorbency, biodegradability, and antibacterial activity, providing a practical and environmentally sustainable option for menstrual hygiene management.

2. Materials and Methods

2.1. Preparation of Absorbent Layers of the Napkin

The raw material used to create the absorbent layers of sanitary napkins was water hyacinth (Eichhornia crassipes) (Figure 1), an invasive freshwater macrophyte rich in lignocellulosic biomass. The collected biomass was processed as illustrated in Figure 2.
Mature plants were collected (Figure 1) from Chembarambakkam Lake in Chennai, Tamil Nadu, India, where eutrophication frequently causes excessive growth [28,29]. Fully developed petioles were selected from among several plant components because of their superior fiber structure and higher cellulose content compared with leaves and roots [30]. To eliminate lignin and hemicellulose and release cellulose fibers, the petioles were thoroughly cleaned, cut into 1–3 inch segments, and then subjected to alkaline pulping using 2–5% (w/v) sodium hydroxide at 90 °C for 60 min [3].
After cooling, the fibers were filtered, repeatedly washed, and neutralized using diluted acetic acid to achieve a near-neutral pH and ensure fiber stability and suitability for hygienic applications [11]. The treated fibers were mechanically ground into a homogeneous pulp, and paper sheets were prepared using a traditional handsheet formation method. The sheets were dried naturally without the use of bleaching agents or artificial additives to produce eco-friendly, cellulose-rich absorbent layers [3,30].

2.2. Evaluation of Biodegradable Napkins

To evaluate the physical properties of the water hyacinth menstrual pads, a comparative analysis including two other types of pads was conducted. The menstrual pads selected for the study were a cloth pad (made of cotton), a commercial pad, and a water hyacinth pad, all of which were of the same size. The goal of the study was to assess several properties of the pads, including absorbency, leak protection, and pH levels [31]. Additionally, antimicrobial testing, bioburden analysis, and a skin irritation test were conducted specifically for the water hyacinth pad to ensure its safety and efficacy. During these tests, eight pads per test were used.

2.2.1. Absorbency Test

The absorbency performance of the developed water hyacinth-based sanitary pads was evaluated and compared with commercially available disposable sanitary pads and reusable cloth pads using a standardized liquid uptake test [13].
Each sanitary pad was placed horizontally on a flat, non-absorbent surface under ambient laboratory conditions (25 ± 2 °C). A fixed volume (10 mL) of an aqueous coloring solution (0.1% w/v methylene blue in distilled water) was drawn into a sterile syringe and injected vertically into the center of the pad’s absorbent core. The volume of liquid introduced was maintained constant across all samples to ensure reproducibility.
The time required for the complete disappearance of liquid from the pad surface was recorded using a digital stopwatch and expressed as the absorption time (s). Absorption was considered complete when no visible liquid remained on the surface. Each test was performed in triplicate for each pad type, and the mean absorption time was calculated.
To confirm repeatability and minimize experimental variability arising from pad positioning or liquid distribution, the absorbency test was repeated after a 10 min interval under identical conditions. The absorbency performance was evaluated based on the rate of liquid uptake and liquid retention efficiency [13,15].

2.2.2. pH Test

The pH of the developed sanitary pads was measured to assess their compatibility with the skin environment and compliance with recommended hygienic product standards [32]. A representative section of the water hyacinth sanitary pad (approximately 1 g) was aseptically cut into small pieces and immersed in 50 mL of distilled water. The mixture was gently agitated for 30 min at room temperature (25 ± 2 °C) to allow soluble components to equilibrate with the aqueous phase. The resulting suspension was then filtered through Whatman No. 1 filter paper to remove insoluble fibers and particulate matter.
The pH of the filtrate was measured using a calibrated digital pH meter (±0.01 accuracy). The instrument was calibrated prior to measurement using standard buffer solutions of pH 4.0, 7.0, and 9.2. Each sample was analyzed in triplicate, and the mean pH value was calculated. The measured pH values were compared with the recommended limits for sanitary napkins to evaluate skin safety and user comfort [32,33].

2.2.3. Bioburden Test

Bioburden testing was performed to determine the total viable microbial load present on the laboratory-developed sanitary pads fabricated from water hyacinth sheets and fiber powder. The test was conducted in accordance with standard microbiological evaluation protocols for hygiene and absorbent products [34,35]. All microbiological analyses were conducted in triplicate to ensure reproducibility and statistical reliability.
A representative portion (5 g) of each sanitary pad sample was aseptically cut using sterile scissors and transferred into a sterile conical flask containing 100 mL of sterile 0.1% (w/v) peptone water (HiMedia, Mumbai, India). The suspension was homogenized by gentle shaking for 15 min to facilitate the release of surface-associated microorganisms into the diluent. This initial suspension served as the stock solution (100 dilution). Serial decimal dilutions (10−1–10−3) were prepared using sterile 0.1% peptone water [36].
The total aerobic bacterial load was determined using the aerobic plate count method. Aliquots (1 mL) from appropriate dilutions were aseptically transferred into sterile Petri plates, followed by the addition of molten Plate Count Agar (PCA) maintained at 45 ± 1 °C. The plates were gently rotated to ensure uniform distribution of the inoculum and allowed to solidify.
The inoculated plates were incubated at 30 ± 2 °C for 48 ± 2 h under aerobic conditions. After incubation, plates containing 30–300 colonies were selected for enumeration. Results were expressed as colony-forming units per gram of sample (CFU/g) using the standard colony count calculation formula [35,37].
The presence of Staphylococcus aureus was evaluated using a selective enrichment and differential plating method following established microbiological standards for hygiene products [30]. A 5 g sanitary pad sample was immersed in 100 mL of sterile 0.1% peptone water and incubated at 37 °C for 18–24 h for pre-enrichment. Subsequently, 10 mL of the enriched suspension was transferred into 90 mL of Staphylococcus Chromogenic Differential Medium (SCDM) and incubated at 30–35 °C for 18–24 h.
A positive control containing Staphylococcus aureus ATCC 6538 and a negative control consisting of uninoculated SCDM were incubated simultaneously to validate the selectivity of the medium. After incubation, a loopful of the enriched culture was streaked onto Mannitol Salt Agar (MSA) plates. The plates were incubated at 30–35 °C for 24–72 h. Yellow colonies surrounded by yellow zones were considered presumptively positive for Staphylococcus aureus due to mannitol fermentation. Confirmation was performed based on colony morphology and selective growth characteristics [38,39].
Fungal contamination was assessed using Yeast Extract Glucose Chloramphenicol Agar (YGC agar). From selected serial dilutions, 0.1 mL of the suspension was spread evenly onto the surface of pre-solidified YGC agar plates using a sterile L-shaped spreader. A positive control inoculated with Candida albicans ATCC 10231 and a negative control consisting of sterile diluent were included. The plates were incubated at 25 ± 2 °C for 3–5 days. Distinct yeast and mold colonies were counted, and the results were expressed as CFU g−1 of the sanitary pad sample [40].

2.2.4. Skin Irritation Test

The skin irritation potential of the developed sanitary pads was evaluated to assess dermal compatibility and user safety. The test was conducted in accordance with standard skin irritation assessment guidelines for absorbent hygiene products [11]. All evaluations were performed in triplicate to ensure consistency of the observations.
The sanitary pad samples were applied to intact skin under controlled conditions for a specified exposure period. A negative control (medical-grade cotton gauze) and a positive control (0.8% sodium lauryl sulfate solution, a known skin irritant) were applied to separate test sites under identical conditions to validate the sensitivity of the test system.
The test area was examined for visible signs of erythema, edema, itching, or swelling immediately after exposure and after the defined observation period. The irritation response was scored using a standardized grading scale. Samples exhibiting no observable adverse skin reactions comparable to those of the negative control were classified as nonirritant and suitable for prolonged skin contact [41,42].

2.3. Chareterization of Water Hyacinth Fibrous Polymer

The fiber polymer isolated from water hyacinth was subjected to scanning electron microscopy (SEM) analysis to examine the morphology and surface cross-sections of the water hyacinth fiber composite. This analysis was performed using a desktop scanning electron microscope (Hitachi TM 3000, Tokyo, Japan). The samples were prepared by drying in an air oven at 70 °C for 2 h and then used for analysis [43]. Fourier-transform infrared (FTIR) analysis was performed using a double-beam FTIR spectrophotometer equipped with an attenuated total reflectance accessory (PerkinElmer Spectrum Two, C100599 instrument, Waltham, MA, USA). Transmittance spectra were recorded over the range of 400–4000 cm−1. X-ray diffraction (XRD) analysis was performed using a Rigaku MiniFlex 600 X-ray diffractometer (Tokyo, Japan) operating at an accelerating voltage of 40 kV and a current of 15 mA [44]. The Segal crystallinity index of the samples (CrI%) was determined from the XRD spectra, where I002 represents the maximum diffraction intensity and Iam represents the amorphous diffraction intensity, using Equation (1).
C r I % = I 002 I a m I 002 × 100 %
In this method, I002 represents the maximum intensity of the (200) crystalline plane at approximately 2θ ≈ 22°, while Iam corresponds to the intensity of the amorphous region measured at approximately 2θ ≈ 18°, which is characteristic for cellulose I.

2.4. Biodegradability Analysis

The soil burial test was used to evaluate the biodegradability of the developed pad by analyzing the degradation of the pad components under natural environmental conditions. The samples were buried in 10 cm of biologically active soil and maintained at room temperature for 90 days. At regular intervals, the samples were carefully exhumed, cleaned, and dried to determine the percentage of weight loss [45].

2.5. Statistical Analysis

The results were reported as mean ± standard deviation (SD). Data were analyzed using one-way ANOVA followed by Tukey’s post hoc test, with p < 0.05 considered statistically significant.

3. Results and Discussion

Different materials are used in the manufacture of sanitary napkins to achieve optimal absorbency and comfort. Conventional materials such as cotton are valued for their soft texture and high absorbent capacity, making them comfortable for prolonged wear. Biodegradable materials, including water hyacinth paper and fibers, have recently emerged as environmentally friendly alternatives to plastic absorbent cores. Combining cotton with these biodegradable materials enables the production of high-quality sanitary napkins that provide reliable menstrual protection. This combination offers period hygiene products that are safe, efficient, and environmentally sustainable.
The biodegradable sanitary pad developed in this study was designed with a multilayer configuration consisting of a top sheet, an absorbent core, and a barrier layer. The top sheet functions to rapidly absorb menstrual fluid and transfer it to the underlying layers. Commercial sanitary pads predominantly use polypropylene-based nonwoven fabrics; however, such materials are non-biodegradable and environmentally persistent. In this study, a water hyacinth fiber-based nonwoven material was used as a sustainable alternative because of its softness, breathability, skin compatibility, and biodegradability [4,28].
The petiole region of Eichhornia crassipes was chosen as the primary raw material for the production of sanitary pads because of its favorable fiber structure and relatively higher cellulose content compared with leaves and roots [29,30]. Since each plant normally produces 7–12 petioles, 5–6 fully developed petioles were consistently selected to ensure consistency and repeatability of the absorbent material (Figure 3a). Mature petioles were selected to optimize fiber strength, hydrophilicity, and processing consistency, all of which are critical for hygienic applications.
After being carefully cleaned to remove attached contaminants, the collected petioles were cut into sections approximately 1–3 inches long (Figure 3b). As documented for other natural lignocellulosic fibers, this size reduction improved chemical penetration during pulping and enabled efficient fiber liberation during subsequent processing steps [3,30]. Chemical pulping was performed using sodium hydroxide (2–5% w/v) for 60 min at 90 °C. The alkali treatment effectively disrupted the lignin and hemicellulose matrix, producing cellulose-rich fibers suitable for absorbent applications [11,31]. After cooling, repeated washing followed by pH neutralization with diluted acetic acid ensured the removal of residual alkali and restored a near-neutral pH, which is essential for material safety in menstrual hygiene products (Figure 3c).
To create a uniform pulp, the fibers were mechanically ground after neutralization (Figure 4a). The pulp’s soft texture and uniform dispersion enabled effective sheet formation without the addition of bleaching agents, binders, or synthetic additives. Naturally colored paper sheets were produced through handsheet formation and subsequently dried in sunlight (Figure 4b,c). The high cellulose content of water hyacinth petioles provided the sheets with sufficient mechanical integrity and absorbency, indicating their suitability as biodegradable absorbent components [19,20,21].
To improve absorbent performance, alkali-treated water hyacinth fibers were further processed into a fine powder in addition to sheet formation (Figure 4d). The enlarged surface area and relatively short fiber length of the powder enhanced capillary action and packing density, thereby increasing the liquid absorption capacity. Previous studies have shown that alkali-treated water hyacinth fibers exhibit absorption capacities ranging from 5 to 11 times their dry weight, indicating their effectiveness in absorbent hygiene applications [11,46].
The multilayer design of the biodegradable sanitary pad created in this study included a top sheet, an absorbent core, and a barrier layer. Water hyacinth fiber-based nonwoven material, a sustainable substitute for conventional polypropylene nonwovens, was used to fabricate the top sheet. The softness, breathability, skin compatibility, and biodegradability of this layer addressed the environmental and comfort concerns associated with synthetic polymers [4,28]. The absorbent core consisted of cotton (approximately 8 g), fiber powder, and water hyacinth paper. The addition of water hyacinth fibers substantially improved fluid uptake, retention capacity, and antibacterial performance because of their hydrophilic cellulose matrix and intrinsic bioactive properties, whereas cotton provided softness and baseline absorbency [3,11,25,30].
In place of traditional polyethylene or polyurethane films, a biodegradable cornstarch-based sheet was used as the barrier layer to prevent leakage. Canvas paper was incorporated as a supporting layer to enhance structural stability while maintaining overall biodegradability [47]. After aligning the top sheet, absorbent core, and barrier layer, the three layers were assembled through localized heat sealing at the margins. This assembly technique maintained the eco-friendly characteristics of the product while eliminating the need for synthetic adhesives [9]. Figure 5 illustrates the completed biodegradable sanitary napkin.
Overall, the findings show that water hyacinth-based materials can successfully replace synthetic components in sanitary napkins while still providing sufficient absorbency, comfort, and hygienic performance. By reducing dependence on petroleum-based polymers and increasing the value of invasive biomass, this strategy offers dual sustainability benefits.

3.1. Absorbance Examination

Absorbency is a critical feature of menstrual pads and is essential for ensuring comfort and security during use. Effective absorbency ensures that menstrual flow is managed quickly and efficiently. To measure this property, an absorbency test is performed. During this test, a specified volume of aqueous coloring solution (dye) is applied to the surface of the pad, and the time required for the fluid to be completely absorbed is recorded [31]. This procedure evaluates the pad’s ability to manage menstrual flow promptly and effectively.
In the present study, absorbency tests were performed on different types of menstrual pads, including water hyacinth-based pads, cloth (cotton) pads, and commercial sanitary pads (Figure 6). The comparative results are presented in Table 1.
The data indicate that both the cotton and water hyacinth pads absorbed a larger volume of liquid compared with the commercial product, which absorbed only 71 mL. In contrast, the cotton and water hyacinth pads each absorbed 111 mL under the same test conditions. These findings suggest that the absorbent capacity of these natural materials may exceed that of some commercial sanitary pads, likely because of the high water affinity of cellulose-rich fibers [31].
The absorbent performance of natural fibers has been well documented in previous studies. For example, cotton fibers have a hydrophilic structure and high cellulose content, enabling them to absorb 24–27 times their own weight in water, although this capacity can vary with weave and fabric form [24,48]. Similarly, studies on natural and eco-friendly menstrual pad materials have shown that plant-derived fibers such as bamboo can outperform conventional cotton in fluid uptake, with absorbency several times greater than that of commercial pads in controlled tests [49].
Earlier research specifically addressing water hyacinth fiber highlights its excellent moisture absorbency. Water hyacinth (Eichhornia crassipes) is a cellulose-rich aquatic plant whose fibers exhibit significant water uptake capability, often comparable to or exceeding that of untreated cotton fibers after appropriate processing [50]. This high absorbency performance is attributed to the hydrophilic nature of cellulose chains and the porous structure of the fibers, which facilitates fluid penetration and retention. In this context, the absorbent properties of water hyacinth fibers have attracted attention as sustainable alternatives for absorbent core materials in hygiene products. The current experimental results align with these observations, showing that the combination of water hyacinth fiber with cotton not only preserves but may also enhance liquid retention capacity relative to conventional commercial pads. This effect likely arises from the complementary absorbent characteristics of cotton and water hyacinth fibers, with cotton providing established comfort and wicking properties and water hyacinth contributing additional hydrophilic sites and structural porosity.
Additionally, previous studies emphasize the importance of material selection and treatment in determining overall absorbency performance. For instance, surface treatments, fiber processing methods, and composite configurations play a significant role in optimizing water uptake and retention in natural fibers, which directly affect their suitability as absorbent media in sanitary products [51].
These findings and the supporting literature indicate that natural plant fibers such as cotton and water hyacinth can provide competitive or improved absorbency compared with conventional commercial products while also offering ecological benefits such as biodegradability and sustainability.

3.2. pH Assessment: Considerations for Sanitary Pads and Implications for Vaginal Health

The pH of sanitary pads is a critical parameter influencing vaginal health, comfort, and microbiological balance. The healthy human vagina maintains a naturally acidic environment, typically within a pH range of 3.5–4.5. This condition is primarily due to the dominance of Lactobacillus species, which produce lactic acid as a metabolic byproduct. This acidic environment plays a protective role by inhibiting the growth of pathogenic microorganisms that thrive in neutral or alkaline conditions, thereby reducing the risk of infections such as bacterial vaginosis and vulvovaginal candidiasis [52,53].
Sanitary pads come into prolonged contact with the vulvar region during menstruation, and the materials used in their construction can influence the local pH microenvironment. Prolonged exposure to products with unsuitable pH levels may disrupt the natural acidic barrier, potentially leading to irritation, itching, dermatitis, or increased susceptibility to microbial infections [54]. Previous studies have shown that sanitary products manufactured from natural fibers such as cotton, cellulose, or other plant-based materials generally exhibit pH values closer to physiological compatibility compared with pads containing predominantly synthetic polymers such as polypropylene or polyethylene [7,11]. This material-dependent pH variation directly influences wearer comfort and overall genital health.
In India, the safety and quality of sanitary napkins are regulated by IS 5405:2019 [55], which specifies that the pH of aqueous extracts of sanitary napkins should fall within the range of 6.0–8.5. This range is considered acceptable for minimizing toxicological risks, including skin irritation, allergic reactions, and microbial growth during extended use [34]. Although this standard pH range is higher than the native vaginal pH, it is intended to ensure dermal safety at the vulvar interface rather than directly replicating the vaginal environment.
In the present study, the pH values obtained for the aqueous extracts of the developed water hyacinth-based sanitary pad are summarized in Table 2.
Statistical analysis revealed minimal variation among triplicate measurements (SD < 0.05), indicating good reproducibility and uniformity of the pad material. The measured pH value of 6.87 lies well within the permissible range specified by IS 5405:1980 [32], confirming dermal safety for sanitary napkin applications.
The developed water hyacinth-based sanitary pad is classified as compliant because the measured pH value (6.87 ± 0.04) lies well within the acceptable range of 6.0–8.5 specified by IS 5405:1980 for sanitary napkins. This range is prescribed to ensure dermal safety and minimize the risk of skin irritation, allergic reactions, or adverse dermatological effects during prolonged contact with the vulvar area. The low standard deviation indicates consistent pH values across replicates, confirming material uniformity. Since the pH does not exceed the upper safety limit or fall below the minimum specified value, the product meets the regulatory requirements and is considered safe and suitable for hygienic use.
Although the physiological vaginal pH is acidic (3.5–4.5), sanitary pads are primarily intended for contact with the vulvar skin, where a near-neutral pH is desirable to prevent irritation and dermatitis. Pads with an excessively alkaline pH have been associated with skin barrier disruption and increased susceptibility to microbial infections [52,54]. The observed pH value suggests that the lignocellulosic composition of Eichhornia crassipes fibers helps maintains a skin-compatible microenvironment.
Recent investigations into biodegradable and reusable sanitary products have highlighted the importance of optimizing pH alongside absorbency and mechanical performance. For instance, a reusable cloth pad fabricated from corn husk fibers exhibited a pH value of 7.45, which lies toward the upper limit of the recommended IS standard but remains within the permissible safety range [56]. Similarly, studies evaluating natural fiber–based sanitary napkins have reported that plant-derived cellulose materials tend to maintain neutral to mildly acidic pH levels, thereby reducing the likelihood of irritation during prolonged wear [19,26]. The pH result obtained in this study is comparable to those reported for reusable cloth pads (pH 7.2–7.5) and remains significantly below the upper safety threshold (8.5), suggesting a reduced risk of irritation during prolonged menstrual use.
In general, preserving vulvovaginal health requires sanitary pad materials to be pH-compatible, especially when biodegradable and plant-based substitutes are developed as sustainable alternatives to petroleum-derived polymers. The results of this study suggest that water hyacinth-based sanitary pads meet established safety criteria and offer a promising eco-friendly alternative without compromising pH-related user safety.

3.3. Bioburden Assessment

Bioburden testing is a critical microbiological quality control parameter for sanitary products, as it evaluates the total viable microbial load present on a product prior to use. Excessive microbial contamination may lead to skin irritation, allergic reactions, and an increased risk of urogenital infections, particularly during prolonged contact with sensitive skin areas. Therefore, maintaining a low microbial bioburden is essential to ensure product safety, hygienic integrity, and user comfort [57,58].
According to IS 5405:2019 [55] and ISO 11737-1:2018 [34] (Amd.1:2021), sanitary napkins are required to meet stringent microbiological limits. A product is considered microbiologically safe when the total bacterial count does not exceed 1000 CFU/g and the total yeast and mold count remains below 10 CFU/g [34]. These limits are established to minimize the risk of microbial growth during storage and use, thereby ensuring consumer safety.
The bioburden results obtained for the developed water hyacinth-based sanitary pad are presented in Table 3. The total bacterial count was found to be 360 CFU/g, while the total yeast and mold count was <1 CFU/g, both of which fall well within the permissible limits specified by the standards. Therefore, the sample complied with the established bioburden requirements.
The total aerobic bacterial load was 360 CFU/g, which is significantly lower than the maximum permissible limit of 1000 CFU/g. Yeast and mold counts were below the detectable limit (<1 CFU/g). One-way ANOVA confirmed no statistically significant variation among replicate samples (p > 0.05), demonstrating microbiological consistency of the fabricated pads.
The developed water hyacinth-based sanitary pad meets the bioburden requirements because the observed microbial counts are well below the maximum permissible limits specified by the relevant standards. The total bacterial count of 360 ± 22 CFU/g is substantially lower than the allowable limit of ≤1000 CFU/g prescribed under IS 5405:2019 (Clause 7.3.1), indicating effective hygienic processing and minimal microbial contamination. Similarly, the total yeast and mold count was below the detectable limit (<1 CFU/g), which is far lower than the specified maximum of ≤10 CFU/g as defined in ISO 11737-1:2018 (Amd.1:2021) [34]. These results confirm that the product meets microbiological safety criteria, poses minimal risk of infection or irritation, and is suitable for safe hygienic use, thereby justifying the Pass compliance status.
The microbiological assessment is further illustrated in Figure 7 and Figure 8, depicting the total bacterial count and total yeast and mold count, respectively. In both cases, the developed sanitary pad sample showed negligible microbial growth compared with the positive control, while the results were comparable to those of the negative control, confirming satisfactory microbiological quality.
Low bioburden levels are particularly important for maintaining vaginal and perineal health, as microbial imbalance in sanitary materials may contribute to infections and discomfort [54]. The results of the present study demonstrate that the water hyacinth sanitary pad is microbiologically safe and suitable for hygienic use.
Comparative studies on natural fiber-based sanitary napkins have reported higher microbial loads in certain formulations. For instance, sanitary pads developed using 50% corn husk fiber exhibited fungal bioburden levels of approximately 400 CFU/mL and bacterial loads of 510 CFU/mL, indicating relatively higher microbial presence [59]. Similarly, pads incorporated with neem extract showed a markedly elevated bacterial count of 12 × 103 CFU/mL, possibly due to processing- or storage-related factors despite neem’s known antimicrobial properties [57]. In contrast, the water hyacinth-based pad developed in this study demonstrated substantially lower microbial counts, highlighting its superior microbiological safety profile.
Overall, the low bacterial and fungal counts observed in the present investigation confirm that the developed sanitary pad meets international and national microbiological safety standards, thereby ensuring reduced infection risk and improved user safety.

3.4. Skin Irritation Assessment

Skin irritation and microbiological safety are critical parameters in evaluating sanitary napkins, as prolonged skin contact under moist conditions can promote microbial growth and lead to infections. Skin irritation tests are routinely performed to assess the presence of pathogenic microorganisms that may compromise dermal and vaginal health. Among these, Staphylococcus aureus is of particular concern because of its role in skin and soft tissue infections, bacteremia, endocarditis, and toxin-mediated diseases such as toxic shock syndrome (TSS) [54]. This bacterium is also frequently associated with irritation, inflammation, and secondary infections in users of contaminated hygiene products.
Previous studies have established that S. aureus colonization in menstrual hygiene products can disrupt the normal skin microflora and increase susceptibility to infections, particularly among adolescent and reproductive-age women [60]. Consequently, regulatory standards emphasize the complete absence of specified pathogens in sanitary products. According to ISO 11737-1:2018 (Amd.1:2021) and IS 5405:2019 [34,40], sanitary napkins must be free from Staphylococcus aureus to ensure consumer safety and hygienic acceptability.
In the present study, the developed water hyacinth-based sanitary pads were evaluated for the presence of Staphylococcus aureus using standard microbiological test methods (Table 4). The results demonstrated the complete absence of S. aureus in the tested samples, indicating excellent microbiological safety. The sample successfully met the specified requirement of “absence per gram,” thereby fulfilling the skin irritation and pathogen safety criteria.
No detectable growth of Staphylococcus aureus was observed in the developed sanitary pad sample. The absence of this pathogen satisfies mandatory regulatory requirements and confirms excellent microbiological safety.
The developed water hyacinth-based sanitary pad is rated as Pass for pathogen safety because Staphylococcus aureus was not detected in the sample. According to IS 5405:2019 and ISO 11737-1:2018 (Amd.1:2021), sanitary napkins must be completely free from specified pathogenic microorganisms, including Staphylococcus aureus, to ensure user safety. The absence of this pathogen per gram of the product indicates that the sanitary pad does not pose a risk of skin irritation, infection, or toxin-mediated conditions such as TSS. Therefore, the product fully complies with the regulatory microbiological safety requirements, thereby justifying the Pass compliance status.
These findings were further confirmed by Figure 9, showing no detectable microbial growth in the developed sanitary pad sample compared with the positive and negative controls. The absence of S. aureus strongly suggests that the water hyacinth-based material does not promote pathogenic bacterial colonization and is suitable for prolonged skin contact.
The use of natural and sustainable fibers in hygiene products has gained increasing attention because of their favorable antimicrobial properties, breathability, and reduced risk of irritation [26]. Several studies have reported similar outcomes in sanitary pads fabricated using plant-based fibers such as corn husk, banana fiber, and other lignocellulosic materials, where no Staphylococcus aureus growth was detected [4,39]. In another study, sanitary pads incorporating 50% corn husk fibers were also found to be free from S. aureus, supporting the antimicrobial suitability of agro-waste-derived fibers [61,62].
Overall, the absence of Staphylococcus aureus in the developed water hyacinth sanitary pads highlights their potential as a safe, hygienic, and eco-friendly alternative to conventional synthetic products. These findings reinforce the suitability of water hyacinth fibers for sustainable menstrual hygiene applications, with minimal risk of skin irritation or bacterial infection.

3.5. Characterization of Water Hyacinth Fibrous Polymer

3.5.1. SEM Analysis

The surface morphology of water hyacinth fibers before and after pretreatment was examined using SEM. In the untreated fiber sample, the surface features are not clearly distinguishable in the SEM micrograph (Figure 10a). The arrangement of individual fibers is also unclear, as the fiber surfaces and inter-fiber spaces are largely covered by components such as lignin, pectin, hemicellulose, and other soluble substances. In contrast, SEM analysis of the treated water hyacinth fibers agrees with observations reported in earlier studies [63]. As shown in Figure 10b, the fiber surface becomes noticeably rougher after treatment, which can be attributed to the removal of surface-coating components by the NaOH solution.
The micrographs indicate that impurities were successfully removed after treatment. The results of chemical composition analysis further demonstrate that the percentages of lignin and hemicellulose decreased following treatment. The removal of the lignin layer results in a rougher fiber surface, which may enhance inter-fiber interactions [63].

3.5.2. FTIR Spectroscopy

To determine the functional groups, present and evaluate how effectively bleaching removed non-cellulosic components such as hemicellulose and lignin, the FTIR spectrum of bleached water hyacinth cellulose was examined (Figure 11).
O–H stretching vibrations of hydroxyl groups, which are typical of cellulose and arise from significant intra- and intermolecular hydrogen bonding, are responsible for the broad and strong absorption band observed at 3339.7 cm−1 [64].
Polysaccharide-rich materials frequently exhibit overtone or combination vibrations, which are represented by the weak band at 2102.8 cm−1. Aromatic skeletal vibrations associated with residual lignin structures and/or H–O–H bending vibrations of adsorbed moisture are attributed to the absorption peak at 1638.3 cm [65].
A clearly defined cellulosic backbone is indicated by the band at 1420.1 cm−1, which is attributed to CH2 bending vibrations. The signal detected at 1241.2 cm−1 indicates trace levels of lignin or hemicellulose and is associated with C–O stretching vibrations. The prominent band at 1032.5 cm−1 corresponds to C–O–C stretching vibrations of polysaccharides, a characteristic feature of cellulose [66].
The FTIR results confirm the lignocellulosic nature of the water hyacinth fibers and indicate that bleaching successfully increased the cellulose content while substantially reducing hemicellulose and lignin impurities, thereby preparing the material for use in biodegradable and sustainable products.

3.5.3. X-Ray Diffraction Analysis

CrI% was calculated from the XRD spectra, as shown in Figure 12. Both samples exhibited distinctive diffraction peaks indicative of the crystalline structure of cellulose I. With respect to the (200) and (110) crystallographic planes of native cellulose, the untreated water hyacinth showed a prominent diffraction peak centered around 2θ = 22° and a less intense peak near 2θ ≈ 16°. However, the peaks appeared broader and less intense, indicating the presence of amorphous components such as hemicellulose and lignin within the lignocellulosic matrix.
In contrast, the cellulose isolated from water hyacinth showed stronger and sharper diffraction peaks at similar 2θ positions, indicating that crystalline cellulose domains were enriched following chemical treatment. In the extracted cellulose, CrI increased from 53.21% in raw water hyacinth to 62.56%. This increase in crystallinity is attributed to the removal of amorphous components, particularly hemicellulose and lignin, during alkali and bleaching treatments. Alkali treatment breaks ester bonds and solubilizes non-cellulosic fractions, thereby improving the ordering of cellulose chains. Similar increases in crystallinity following chemical purification of lignocellulosic biomass have been extensively documented in the literature [67,68,69].
The crystallinity index (CrI%) was calculated from the XRD patterns using the Segal method, where the maximum intensity of the crystalline peak at 2θ ≈ 22° (I002) and the amorphous intensity at 2θ ≈ 18° (Iam) were used. Both samples exhibited characteristic diffraction peaks corresponding to cellulose I, with peaks near 16° and 22° representing the (110) and (200) planes. The untreated water hyacinth showed broader and less intense peaks due to the presence of amorphous components such as hemicellulose and lignin. After chemical treatment, the extracted cellulose displayed sharper diffraction peaks, indicating improved crystalline ordering. Consequently, the crystallinity index increased from 53.21% to 62.56%, confirming the removal of amorphous constituents during alkali and bleaching treatments.
Stronger intermolecular hydrogen bonding and improved structural order within the cellulose microfibrils are suggested by the increased crystallinity of the isolated cellulose. Increased crystallinity is typically associated with improved mechanical strength, enhanced thermal stability, and reduced water solubility in biodegradable absorbent materials [70]. The CrI value of 62.56% obtained in this study is consistent with previously reported crystallinity indices for cellulose derived from aquatic and agricultural biomass sources, which often range between 55% and 70% depending on extraction conditions [68,71].
The relatively lower crystallinity index of raw water hyacinth (53.21%) reflects the composite nature of the lignocellulosic structure, in which amorphous lignin and hemicellulose hinder the regular packing of cellulose chains. The observed increase in peak sharpness and intensity after treatment confirms the effectiveness of the extraction protocol in isolating cellulose-rich fractions suitable for biodegradable product development.

3.6. Biodegradability Test

The biodegradation profile of the sanitary pad made from water hyacinth was determined over a 60-day period. The results indicated that degradation occurred progressively over time, with clear visual evidence of structural breakdown caused by natural environmental factors (Figure 13 and Figure 14).
The data revealed that by Day 10 of the study, approximately 15% degradation had already occurred, suggesting rapid microbial colonization and enzymatic activity on the hydrophilic polysaccharide matrix of water hyacinth. During this phase, cellulose and hemicellulose were degraded as a result of microbial colonization and enzymatic activity, thereby significantly reducing their contribution to the structural integrity of the sanitary pad [72,73]. Between Days 20 and 30, the degree of degradation increased significantly to between 35% and 55%. This increase corresponds to accelerated polymer breakdown caused by an increase in the surface area and porosity of the fiber matrix, which enhances microbial access to the material and improves water retention. Similar patterns have been reported in previous studies examining the degradation of lignocellulosic fibrous waste materials used in biodegradable absorbent products [60,74].
The degradation percentages of the water hyacinth-based pad increased steadily over 40 days, reaching nearly 70% degradation at the end of this period and approximately 95% degradation after a total of 60 days. This result reflects the predominance of cellulose and hemicellulose, which are compostable components, over lignin in the pretreated water hyacinth fiber and explains the high biodegradation observed compared with other studies on green composites and natural fiber-based hygiene products that reported over 80% biodegradation within 2–3 months [72,75]. Commercial sanitary pads commonly available in the market do not readily biodegrade in the environment and are known to persist in landfills for hundreds of years, with only minimal degradation (<15% after several months) [60]. The significantly faster biodegradation rate of the water hyacinth-based product demonstrates its superior environmental performance compared with conventional products and highlights its suitability as a sustainable alternative sanitary pad. In addition, as an aquatic invasive species, the use of Eichhornia crassipes provides an environmental benefit by converting problematic biomass into an eco-friendly value-added product. These advantages align with the principles of sustainable waste management strategies and the circular bioeconomy model and confirm that water hyacinth fibers have strong potential as a raw material for manufacturing biodegradable menstrual products [72,74].

3.7. Statistical Study

Statistical evaluation (mean ± SD; one-way ANOVA, p < 0.05) confirmed that the developed water hyacinth-based sanitary pad demonstrated skin-compatible pH, very low bioburden levels, complete absence of pathogenic bacteria, and compliance with IS and ISO safety standards.
These findings collectively establish the hygienic safety, dermal compatibility, and suitability of Eichhornia crassipes fibers for sustainable menstrual hygiene applications. The results strongly support the potential of water hyacinth-based products as an eco-friendly alternative to petroleum-derived sanitary products without compromising user safety.

4. Conclusions

This study demonstrates the strong potential of water hyacinth (Eichhornia crassipes) fibers as a sustainable, biodegradable, and environmentally responsible alternative material for sanitary napkin core development. The findings suggest that the use of natural lignocellulosic fibers in menstrual hygiene products can help alleviate user safety concerns and reduce the growing environmental burden associated with traditional sanitary pads. Commercial sanitary pads are primarily composed of non-biodegradable materials such as polyethylene and polymeric films. Large quantities of these products contribute to solid waste accumulation, microplastic pollution, and hazardous by-products during disposal, whereas water hyacinth fibers, as a renewable natural material, could significantly reduce the overall environmental impact of menstrual hygiene products.
Comprehensive material characterization demonstrated that water hyacinth fibers are suitable for use in absorbent hygiene products. Alkali treatment of the fibers, as observed through SEM analysis, resulted in the removal of surface contaminants (i.e., lignin, hemicellulose, and pectin) and produced a rougher and more exposed fiber surface. These morphological changes improved fiber–fiber bonding and liquid absorption capacity, which are essential properties for hygienic performance. The removal of non-cellulosic components was further confirmed by FTIR spectroscopy through the identification of characteristic cellulose peaks, indicating that chemical treatment increased the cellulose content of the extracted fibers. The crystallinity index of the raw and treated fibers was determined using XRD, increasing from 53.21% in raw fibers to 62.56% in extracted cellulose. This increase indicates the improved structural ordering, stronger intermolecular hydrogen bonding, and enhanced mechanical strength and thermal stability of the material—properties that are desirable for biodegradable absorbent applications.
Performance evaluation of the handmade sanitary napkin indicated that combining cotton with water hyacinth fibers improved liquid absorption and distribution, thereby enhancing comfort and protection. The measured pH value of 6.87 falls within the acceptable limit specified by the Indian Standard IS 5405:1980, indicating good skin compatibility and a low risk of irritation or disruption of the natural vulvovaginal flora. The bioburden level was low at the time of analysis and Staphylococcus aureus was absent, indicating a minimal risk of infection during use.
In the biodegradability testing, the sanitary pads demonstrated significant environmental benefits. Soil burial testing showed that approximately 70% degradation occurred after 40 days and nearly 95% degradation after 60 days, whereas traditional sanitary napkins show little or no measurable biodegradation even after several months. The biodegradability of the treated fibers was attributed to the high proportion of cellulose and hemicellulose in the material and the successful removal of lignin. Furthermore, since water hyacinth is an aquatic invasive weed, converting its biomass into useful products provides an additional environmental benefit by supporting circular bioeconomy principles and sustainable waste management.
This study has shown that sanitary napkins made from water hyacinth have strong potential as a next-generation solution that balances performance, safety, and sustainability. Future research should emphasize improving fiber processing techniques to enhance pad performance, exploring alternative constructions using advanced layering strategies or bio-based superabsorbents, and incorporating natural antimicrobial or odor-control agents into the pads. To ensure that the production of water hyacinth-based sanitary napkins can be implemented at an industrial scale while delivering environmental benefits, further scale-up studies, long-term field assessments, life-cycle assessments, and techno-economic analyses are required before commercial deployment. These findings further support the transition of the hygiene products market toward technologies that are safer, greener, and more socially responsible.

Author Contributions

Conceptualization, G.V. and S.K.R.; methodology, S.B.; software, S.R.; validation, S.B. and S.R.; formal analysis, G.V.; investigation, S.B. and S.R.; resources, S.K.R.; data curation, S.B. and S.R.; writing—original draft preparation, G.V.; writing—review and editing, S.K.R.; supervision, S.K.R.; project administration, S.K.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Blignaut, J.; Visser, H.G.; Erasmus, E.; Smith, M.S. Sanitary pads—Composition, regulation, and ongoing research to address associated challenges. J. Mater. Sci. 2025, 60, 13109–13155. [Google Scholar] [CrossRef]
  2. Pawar, S.; Farshi, R.; Gowda Karegowda, A.; Bhat, P.; Pragathi, M.S. Affordable, biodegradable, and environmentally friendly sanitary napkins for rural women, with a focus on degradation study. Results Eng. 2024, 24, 102988. [Google Scholar] [CrossRef]
  3. Reddy, N.; Yang, Y. Biofibers from agricultural byproducts for industrial applications. Trends Biotechnol. 2005, 23, 22–27. [Google Scholar] [CrossRef]
  4. van Eijk, A.M.; Sivakami, M.; Thakkar, M.B.; Bauman, A.; Laserson, K.F.; Coates, S.; Phillips-Howard, P.A. Menstrual hygiene management among adolescent girls in India: A systematic review and meta-analysis. BMJ Open 2016, 6, e010290. [Google Scholar] [CrossRef] [PubMed]
  5. Suvagiya, K.; Mehta, M.; Shah, G.; Vora, J. Reducing the bioburden on organic sanitary napkins and attempt to solve the sterility issue. Environ. Sci. Pollut. Res. 2023, 31, 57346–57353. [Google Scholar] [CrossRef]
  6. Malik, A. Environmental challenge vis à vis opportunity: The case of water hyacinth. Environ. Int. 2007, 33, 122–138. [Google Scholar] [CrossRef]
  7. George, S.; Thomas, S.; Nedumpillil, N.N.; Jose, S. Extraction and characterization of fibers from water hyacinth stem using a custom-made decorticator. J. Nat. Fibers 2023, 20, 2212927. [Google Scholar] [CrossRef]
  8. Hubbe, M.A.; Ayoub, A.; Daystar, J.S.; Venditti, R.A.; Pawlak, J.J. Enhanced absorbent products incorporating cellulose and its derivatives: A review. BioResources 2013, 8, 6556–6629. [Google Scholar] [CrossRef]
  9. Barman, A.; Katkar, P.M.; Asagekar, S.D. Natural and sustainable raw materials for sanitary napkin. J. Text. Sci. Eng. 2017, 7, 308. [Google Scholar] [CrossRef]
  10. Lu, D.; Xiao, C.; Xu, S.J. Starch-based completely biodegradable polymer materials. Express Polym. Lett. 2009, 3, 366–375. [Google Scholar] [CrossRef]
  11. Samanta, K.K.; Chattopadhyay, S.N.; Shakyawar, D.B.; Debnath, T.B.; Bhowmick, S.; Bhattacharya, S. Potential of natural fibres in sanitary napkin. Int. J. Bioresour. Sci. 2023, 10, 89–98. [Google Scholar] [CrossRef]
  12. Mei, G.; Kumar, H.; Huang, H.; Cai, W.; Reddy, N.G.; Chen, P.; Garg, A.; Ganeshan, S.P. Desiccation cracks mitigation using biomass-derived carbon produced from aquatic species in South China Sea. Waste Biomass Valorization 2021, 12, 1493–1505. [Google Scholar] [CrossRef]
  13. Jeyakanthan, D.M.; Schuster, J.; Shaik, Y.P. Development of ecological absorbent core sanitary pads in combination of kenaf and chitosan fibers. Mater. Sci. Appl. 2023, 14, 429–444. [Google Scholar] [CrossRef]
  14. Sannino, A.; Demitri, C.; Madaghiele, M. Biodegradable cellulose-based hydrogels: Design and application. Materials 2009, 2, 353–357. [Google Scholar] [CrossRef]
  15. Anbalagan, S.; Mekala, M. An overview of the plant fibres in the development of ecologically sustainable sanitary napkins for the green economy. J. Univ. Shanghai Sci. Technol. 2021, 23, 161–172. [Google Scholar] [CrossRef]
  16. Namitha, V.V.; Pavithra, T.V.; Ramanathan, H.N. The socio-economic and ecological impacts of water hyacinth proliferation in water bodies: A case from Greater Kochi area in South India. J. Vijnana Bharathi 2010, 10, 13–24. [Google Scholar] [CrossRef]
  17. Coetzee, J.A.; Jones, R.W.; Hill, M.P. Water hyacinth (Eichhornia crassipes) reduces benthic macroinvertebrate diversity in a protected subtropical lake in South Africa. Biodivers. Conserv. 2014, 23, 1319–1330. [Google Scholar] [CrossRef]
  18. Getenet, B.; Assefa, W.W.; Gezie, A. Socioeconomic effects of water hyacinth (Eichhornia crassipes) in Lake Tana, North Western Ethiopia. PLoS ONE 2020, 15, e0237668. [Google Scholar] [CrossRef]
  19. Mailu, A.M. Preliminary assessment of the social, economic and environmental impacts of water hyacinth in the Lake Victoria basin and the status of control. In Biological and Integrated Control of Water Hyacinth; ACIAR Proceedings No. 102; Australian Centre for International Agricultural Research: Canberra, Australia, 2001; pp. 130–139. Available online: http://www.bio-nica.info/biblioteca/Mailu2001Eischhornia.pdf (accessed on 20 January 2026).
  20. Pendse, D.S.; Deshmukh, M.P. A comprehensive study on an integrated approach for water hyacinth management to conserve natural water resources in India. Mater. Today Proc. 2024, in press. [Google Scholar] [CrossRef]
  21. Rezania, S.; Ponraj, M.; Talaiekhozani, A.; Mohamad, S.E.; Din, M.F.M.; Taib, S.M.; Sabbagh, F.; Sairan, F.M. Perspectives of phytoremediation using water hyacinth for removal of heavy metals, organic and inorganic pollutants in wastewater. J. Environ. Manag. 2015, 163, 125–133. [Google Scholar] [CrossRef]
  22. Sonu, K.; Sogani, M.; Sen, H.; Maheshwari, K.; Tiwari, M.K. Water hyacinth-assisted microbial fuel cells: A review on prospects for bioenergy and wastewater treatment. Environ. Prog. Sustain. Energy 2025, e70240. [Google Scholar] [CrossRef]
  23. Del Angel, G.G.; Cabrera, R.; Rolon, J.; Pichardo, R. Recycling water hyacinth as supplementary cementitious material, admixture, and fiber in mortar and concrete: Current trends and research gaps. Recycling 2025, 10, 18. [Google Scholar] [CrossRef]
  24. Rafin, M.D.; Ohe, A.G.; Arpita, N.; Mumit, S.H. Innovating eco-friendly and sustainable diapers and pads from water hyacinth and coconut coir. Preprints 2024. [Google Scholar] [CrossRef]
  25. Islami, L.N.; Oktiani, B.W.; Wasiaturrahmah, Y. Antibacterial effectiveness of water hyacinth (Eichhornia crassipes) leaf extract on the growth of Porphyromonas gingivalis. Dentin 2023, 7, 85–90. [Google Scholar] [CrossRef]
  26. Fanani, A.Z.; Triastuti, R.; Sulmartiwi, L. Identification and antimicrobial activity test of endophytic fungi from water hyacinth petiole (Eichhornia crassipes) against Escherichia coli and Staphylococcus aureus. IOP Conf. Ser. Earth Environ. Sci. 2021, 718, 012012. [Google Scholar] [CrossRef]
  27. Febriani, A.; Manalu, R.T.; Damanik, N.D. Exploring the antibacterial potential of water hyacinth (Eichhornia crassipes) against Staphylococcus epidermidis and Propionibacterium acnes. In Proceedings of the BRIN International Conference for Health Research (ICHR), Cibinong, Indonesia, 28–29 August 2024. [Google Scholar] [CrossRef]
  28. Khan, H.; Uslu, Ö.S.; Gul, B. Management and Utilization of Water Hyacinth (Eichhornia crassipes Mart.). In A Look into Some Recent Advances in Biology, Ecology and Agricultural Practices; Toncer, Ö., Gunes, Z., Eds.; IKSAD Publishing House: Ankara, Turkey, 2022; pp. 73–96. Available online: https://iksadyayinevi.com/wp-content/uploads/2022/12/A-Look-Into-Some-Recent-Advances-in-Biology-Ecology-and-Agricultural-Practices.pdf (accessed on 21 January 2026).
  29. Vaidyanathan, J. Water hyacinth: Environment challenge vis-à-vis opportunity. In Proceedings of the International Conference on Environment Challenges and Solutions, Faridabad, India, 31 January–2 February 2020; National Institute of Advanced Studies: Faridabad, India, 2020; Available online: https://www.researchgate.net/publication/348729807_Water_hyacinth_Environment_challenge_Vis-a_vis_Opportunity (accessed on 20 January 2026).
  30. Chen, W.-Y.; Azanaw, A.; Ketema, A.; Chang, L.-C. Extraction and Characterization of Sustainable Cellulosic Fibers from Urera hypselodendron Plant. J. Nat. Fibers 2025, 22, 2528103. [Google Scholar] [CrossRef]
  31. Shibly, M.M.H.; Hossain, M.A.; Hossain, M.F.; Nur, M.G.; Hossain, M.B. Development of Biopolymer-Based Menstrual Pad and Quality Analysis against Commercial Merchandise. Bull. Natl. Res. Cent. 2021, 45, 50. [Google Scholar] [CrossRef]
  32. IS 5405:1980; Specification for Disposable Sanitary Napkins. Bureau of Indian Standards: New Delhi, India, 1980.
  33. Sumithra, M. Safety evaluation of biodegerable sanitary napkin. Int. J. Adv. Eng. Manag. 2023, 5, 25–27. [Google Scholar] [CrossRef]
  34. ISO 11737-1:2018; Sterilization of Health Care Products—Microbiological Methods—Part 1: Determination of a Population of Microorganisms on Products. International Organization for Standardization: Geneva, Switzerland, 2018. Available online: https://www.iso.org/standard/66451.html (accessed on 21 January 2026).
  35. Bae, J.; Kwon, H.; Kim, J. Safety Evaluation of Absorbent Hygiene Pads: A Review on Assessment Framework and Test Methods. Sustainability 2018, 10, 4146. [Google Scholar] [CrossRef]
  36. Cappuccino, J.G.; Sherman, N. Microbiology: A Laboratory Manual, 10th ed.; Pearson Education: New York, NY, USA, 2014; Available online: https://cuvas.edu.pk/cuvas_libraries/ebooks/microbiology-a-laboratory-manual-pearson-education-2014.pdf (accessed on 22 January 2026).
  37. ISO 4833-1:2013; Microbiology of the Food Chain—Horizontal Method for the Enumeration of Microorganisms—Part 1: Colony Count at 30 °C. ISO: Geneva, Switzerland, 2013. Available online: https://www.iso.org/standard/53728.html (accessed on 20 January 2026).
  38. ISO 21527-1:2008; Microbiology of Food and Animal Feeding Stuffs—Horizontal Method for the Enumeration of Yeasts and Molds. ISO: Geneva, Switzerland, 2008. Available online: https://www.iso.org/standard/38275.html (accessed on 21 January 2026).
  39. ISO 6888-1:2021; Microbiology of the Food Chain—Horizontal Method for the Enumeration of Coagulase-Positive Staphylococci (Staphylococcus aureus). ISO: Geneva, Switzerland, 2021. Available online: https://www.iso.org/standard/76672.html (accessed on 21 January 2026).
  40. Baird, R.M.; Hodges, N.A.; Denyer, S.P. Handbook of Microbiological Quality Control: Pharmaceuticals and Medical Devices; CRC Press: Boca Raton, FL, USA, 2000. [Google Scholar] [CrossRef]
  41. ISO 10993-10:2021; Biological Evaluation of Medical Devices—Part 10: Tests for Irritation and Skin Sensitization. ISO: Geneva, Switzerland, 2021. Available online: https://www.iso.org/standard/75279.html (accessed on 21 January 2026).
  42. OECD. Test No. 404: Acute Dermal Irritation/Corrosion; OECD Publishing: Paris, France, 2015; Available online: https://www.oecd.org/en/publications/2015/07/test-no-404-acute-dermal-irritation-corrosion_g1g59b23.html (accessed on 21 January 2026).
  43. Chonsakorn, S.; Srivorradatpaisan, S.; Mongkholrattanasit, R. Effects of different extraction methods on some properties of water hyacinth fiber. J. Nat. Fibers 2019, 16, 1015–1025. [Google Scholar] [CrossRef]
  44. Guru, R.; Fangueiro, R. Physical, chemical, thermal, and surface morphological properties of stem fibers extracted from the plant Cayratia trifolia L. Text. Res. J. 2026, 00405175251403947. [Google Scholar] [CrossRef]
  45. Rumi, S.S.; Liyanage, S.; Abidi, N. Soil burial-induced degradation of cellulose films in a moisture-controlled environment. Sci. Rep. 2024, 14, 6921. [Google Scholar] [CrossRef]
  46. Suwanniroj, A.; Suppakarn, N. Water hyacinth fiber as a bio-based carbon source for intumescent flame-retardant poly (butylene succinate) composites. Polymers 2023, 15, 4211. [Google Scholar] [CrossRef]
  47. Saha, P.; Roy, D.; Manna, S. Starch-based biodegradable polymeric materials. Polym. Degrad. Stab. 2018, 147, 82–90. [Google Scholar] [CrossRef]
  48. Soocheta, V.; Jadheea, J.; Nerurkar, M. Evaluation of antibacterial and antifungal susceptibility of water hyacinth. Int. J. Innov. Sci. Res. Technol. 2022, 7, 563–567. [Google Scholar] [CrossRef]
  49. Foster, J.; Montgomery, P. A Study of Environmentally Friendly Menstrual Absorbents in the Context of Social Change for Adolescent Girls in Low- and Middle-Income Countries. Int. J. Environ. Res. Public Health 2021, 18, 9766. [Google Scholar] [CrossRef]
  50. Punitha, S.; Sangeetha, K.; Bhuvaneshwari, M. Processing of water hyacinth fiber to improve its absorbency. Int. J. Adv. Res. 2015, 3, 290–294. [Google Scholar]
  51. Abdel-Fattah, A.F.; Abdel-Naby, M.A. Pretreatment and enzymic saccharification of water hyacinth cellulose. Carbohydr. Polym. 2012, 87, 2109–2113. [Google Scholar] [CrossRef]
  52. O’Hanlon, D.E.; Moench, T.R.; Cone, R.A. Vaginal pH and microbicidal lactic acid when Lactobacillus dominates the microbiota. PLoS ONE 2013, 8, e80074. [Google Scholar] [CrossRef]
  53. Linhares, I.M.; Summers, P.R.; Larsen, B.; Giraldo, P.C.; Witkin, S.S. Contemporary perspectives on vaginal pH and Lactobacillus dominance. Am. J. Obstet. Gynecol. 2011, 204, 120.e1–120.e5. [Google Scholar] [CrossRef]
  54. Ravel, J.; Gajer, P.; Abdo, Z.; Forney, L.J. Vaginal microbiome of reproductive-age women. Proc. Natl. Acad. Sci. USA 2011, 108, 4680–4687. [Google Scholar] [CrossRef]
  55. IS 5405:2019; Sanitary Napkins-Specification. Bureau of Indian Standards: New Delhi, India, 2020. Available online: https://archive.org/details/gov.in.is.5405.2019/IS5405%3A2019/page/n9/mode/2up (accessed on 21 January 2026).
  56. Kumar, V.; Chakraborty, P.; Janghu, P.; Umesh, M.; Sarojini, S.; Pasrija, R.; Kaur, K.; Lakkaboyana, S.K.; Sugumar, V.; Nandhagopal, M.; et al. Potential of banana-based cellulose materials for advanced applications: A review on properties and technical challenges. Carbohydr. Polym. Technol. Appl. 2023, 6, 100366. [Google Scholar] [CrossRef]
  57. Das, P.; Pal, S.; Roy, S. Hygiene and safety considerations in feminine sanitary products: A review. Polymers 2021, 13, 2418. [Google Scholar] [CrossRef]
  58. Hennegan, J.; Montgomery, P. Do menstrual hygiene management interventions improve health outcomes? A systematic review. PLoS ONE 2016, 11, e0146985. [Google Scholar] [CrossRef]
  59. Rastogi, D.; Jain, A.; Chanana, B. Development of sanitary napkins using corn husk fibres in absorbent layer—An exploratory study. J. Ind. Text. 2022, 51, 2267S–2282S. [Google Scholar] [CrossRef]
  60. Kaur, R.; Kaur, K.; Gupta, R. Menstrual hygiene, management, and waste disposal: Practices and challenges faced by girls/women of developing countries. J. Environ. Public Health 2018, 2018, 1730964. [Google Scholar] [CrossRef]
  61. Achuthan, K.; Muthupalani, S.; Kolil, V.K. A novel banana fiber pad for menstrual hygiene in India: A feasibility and acceptability study. BMC Women’s Health 2021, 21, 129. [Google Scholar] [CrossRef] [PubMed]
  62. Wilkins, A.L.; Steer, A.C.; Smeesters, P.R.; Curtis, N. Toxic Shock Syndrome—The Seven Rs of Management and Treatment. J. Infect. 2017, 74, S147–S152. [Google Scholar] [CrossRef]
  63. Hassan, A.; Mohd Isa, M.R.; Mohd Ishak, Z.A.; Ishak, N.A.; Rahman, N.A.; Md Salleh, F. Characterization of sodium hydroxide-treated kenaf fibres for biodegradable composite application. High Perform. Polym. 2018, 30, 890–899. [Google Scholar] [CrossRef]
  64. Pandey, R.; Patel, S.; Pandit, P.; Nachimuthu, S.; Jose, S. Colouration of textiles using roasted peanut skin-an agro processing residue. J. Clean. Prod. 2018, 172, 1319–1326. [Google Scholar] [CrossRef]
  65. Basu, G.; Mishra, L.; Jose, S.; Samanta, A.K. Accelerated retting cum softening of coconut fiber. Ind. Crops Prod. 2015, 77, 66–73. [Google Scholar] [CrossRef]
  66. Hazarika, D.; Gogoi, N.; Jose, S.; Das, R.; Basu, G. Exploration of future prospects of Indian pineapple leaf, an agro waste for textile application. J. Clean. Prod. 2017, 141, 580–586. [Google Scholar] [CrossRef]
  67. Segal, L.; Creely, J.J.; Martin, A.E.; Conrad, C.M. An empirical method for estimating the degree of crystallinity of native cellulose using the X-ray diffractometer. Text. Res. J. 1959, 29, 786–794. [Google Scholar] [CrossRef]
  68. French, A.D.; Santiago Cintrón, M. Cellulose polymorphy, crystallite size, and the Segal crystallinity index. Cellulose 2013, 20, 583–588. [Google Scholar] [CrossRef]
  69. Sun, Y.; Cheng, J. Hydrolysis of lignocellulosic materials for ethanol production: A review. Bioresour. Technol. 2002, 83, 1–11. [Google Scholar] [CrossRef]
  70. Kabir, M.M.; Wang, H.; Lau, K.T.; Cardona, F. Chemical treatments on plant-based natural fibre reinforced polymer composites: An overview. Compos. Part B Eng. 2012, 43, 2883–2892. [Google Scholar] [CrossRef]
  71. Johar, N.; Ahmad, I.; Dufresne, A. Extraction, preparation and characterization of cellulose fibres and nanocrystals from rice husk. Ind. Crops Prod. 2012, 37, 93–99. [Google Scholar] [CrossRef]
  72. Guna, V.; Ilangovan, M.; Anantha Prasad, M.G.; Reddy, N. Water Hyacinth: A Unique Source for Sustainable Materials and Products. ACS Sustain. Chem. Eng. 2017, 5, 4478–4490. [Google Scholar] [CrossRef]
  73. Datta, R. Enzymatic degradation of cellulose in soil: A review. Heliyon 2024, 10, e24022. [Google Scholar] [CrossRef]
  74. Paul, S.C.; Islam, M.S.; Kaikobad, M.; Sadman, M.S.; Emon, M.H.; Zaman, B.; Islam, M.B.; Hossen, M.S.; Sarker, M.E.; Mamun, M.A.A. Exploring biodegradable fibers as sustainable alternatives for sanitary napkin: A comprehensive review. Environ. Technol. Innov. 2026, 41, 104735. [Google Scholar] [CrossRef]
  75. Rajeshkumar, L.; Sathish Kumar, P.; Ramesh, M.; Sanjay, M.R.; Siengchin, S. Assessment of biodegradation of lignocellulosic fiber-based composites—A systematic review. Int. J. Biol. Macromol. 2023, 253, 127237. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Collection of water hyacinth (Eichhornia crassipes) from a freshwater body for use as a lignocellulosic raw material.
Figure 1. Collection of water hyacinth (Eichhornia crassipes) from a freshwater body for use as a lignocellulosic raw material.
Processes 14 00918 g001
Figure 2. Fabrication process of water hyacinth-based sanitary napkins. The figure illustrates the sequential steps, including collection of the Eichhornia crassipes, fiber extraction and alkaline pretreatment (washing and neutralization), pulping and cellulose sheet formation, and polymer-based-layer assembly. The final multilayer structure consists of a water hyacinth fiber sheet as the top layer, a cellulose–cotton composite absorbent core, and a cornstarch-based biodegradable polymer film as the barrier layer.
Figure 2. Fabrication process of water hyacinth-based sanitary napkins. The figure illustrates the sequential steps, including collection of the Eichhornia crassipes, fiber extraction and alkaline pretreatment (washing and neutralization), pulping and cellulose sheet formation, and polymer-based-layer assembly. The final multilayer structure consists of a water hyacinth fiber sheet as the top layer, a cellulose–cotton composite absorbent core, and a cornstarch-based biodegradable polymer film as the barrier layer.
Processes 14 00918 g002
Figure 3. (a) Petioles of water hyacinth selected for fiber extraction because of their high cellulose content; (b) Petioles of water hyacinth cut into small segments prior to chemical pulping; (c) Water hyacinth fibers after alkali treatment and pH neutralization.
Figure 3. (a) Petioles of water hyacinth selected for fiber extraction because of their high cellulose content; (b) Petioles of water hyacinth cut into small segments prior to chemical pulping; (c) Water hyacinth fibers after alkali treatment and pH neutralization.
Processes 14 00918 g003
Figure 4. (a) Homogeneous water hyacinth pulp obtained after mechanical grinding shows a swollen paste-like mass with a soft and moist texture; (b) Drying of water hyacinth-based paper sheets after sheet formation; (c) Finished paper produced from water hyacinth fibers without the addition of synthetic chemicals; (d) Water hyacinth fiber powder prepared after alkali treatment, drying, and mechanical grinding.
Figure 4. (a) Homogeneous water hyacinth pulp obtained after mechanical grinding shows a swollen paste-like mass with a soft and moist texture; (b) Drying of water hyacinth-based paper sheets after sheet formation; (c) Finished paper produced from water hyacinth fibers without the addition of synthetic chemicals; (d) Water hyacinth fiber powder prepared after alkali treatment, drying, and mechanical grinding.
Processes 14 00918 g004
Figure 5. (a) Fully assembled biodegradable sanitary napkin fabricated using water hyacinth-based materials; (b) The multilayer sanitary pad consists of a moisture-wicking top layer for rapid fluid uptake and skin dryness, an absorbent core responsible for fluid absorption and retention, a leak-proof barrier layer that prevents fluid backflow and leakage, and an outer breathable layer that provides structural support and wearer comfort.
Figure 5. (a) Fully assembled biodegradable sanitary napkin fabricated using water hyacinth-based materials; (b) The multilayer sanitary pad consists of a moisture-wicking top layer for rapid fluid uptake and skin dryness, an absorbent core responsible for fluid absorption and retention, a leak-proof barrier layer that prevents fluid backflow and leakage, and an outer breathable layer that provides structural support and wearer comfort.
Processes 14 00918 g005
Figure 6. Absorbency performance of different sanitary napkins evaluated using the dye-injection method. Images show liquid absorption and spreading patterns in (a) water hyacinth-based pad; (b) reusable cloth (cotton) pad, and (c) commercial sanitary pad after injection of a fixed volume of colored dye simulating menstrual fluid. The water hyacinth-based pad (a) exhibits rapid uptake with relatively uniform spreading, indicating effective wicking by cellulose-rich fibers. The cloth pad (b) shows moderate absorption with less uniform distribution, influenced by the fabric structure. The commercial pad (c) displays localized absorption with dye concentrated in the central region, characteristic of synthetic absorbent cores.
Figure 6. Absorbency performance of different sanitary napkins evaluated using the dye-injection method. Images show liquid absorption and spreading patterns in (a) water hyacinth-based pad; (b) reusable cloth (cotton) pad, and (c) commercial sanitary pad after injection of a fixed volume of colored dye simulating menstrual fluid. The water hyacinth-based pad (a) exhibits rapid uptake with relatively uniform spreading, indicating effective wicking by cellulose-rich fibers. The cloth pad (b) shows moderate absorption with less uniform distribution, influenced by the fabric structure. The commercial pad (c) displays localized absorption with dye concentrated in the central region, characteristic of synthetic absorbent cores.
Processes 14 00918 g006
Figure 7. Bioburden testing for total bacterial count using the aerobic plate count method. (a) Developed water hyacinth-based sanitary pad sample showing bacterial colonies after incubation on Plate Count Agar (PCA); (b) Positive control consisting of PCA inoculated with a known bacterial suspension (e.g., Escherichia coli ATCC 25922 or mixed aerobic flora) demonstrates expected colony growth and validates the suitability of the culture medium and incubation conditions; (c) Negative control comprising sterile PCA plates prepared with sterile 0.1% peptone water without sample inoculation shows no colony formation and confirms the absence of external contamination during the assay.
Figure 7. Bioburden testing for total bacterial count using the aerobic plate count method. (a) Developed water hyacinth-based sanitary pad sample showing bacterial colonies after incubation on Plate Count Agar (PCA); (b) Positive control consisting of PCA inoculated with a known bacterial suspension (e.g., Escherichia coli ATCC 25922 or mixed aerobic flora) demonstrates expected colony growth and validates the suitability of the culture medium and incubation conditions; (c) Negative control comprising sterile PCA plates prepared with sterile 0.1% peptone water without sample inoculation shows no colony formation and confirms the absence of external contamination during the assay.
Processes 14 00918 g007
Figure 8. Bioburden testing for total yeast and mold count on YGC agar. (a) Developed water hyacinth-based sanitary pad sample plated on Yeast Extract Glucose Chloramphenicol (YGC) agar, showing negligible or no fungal growth after incubation; (b) Positive control consisting of YGC agar inoculated with a known fungal strain (e.g., Candida albicans ATCC 10231), exhibiting characteristic yeast or mold colonies and confirming the effectiveness of the medium and incubation conditions; (c) Negative control consisting of a YGC agar plate spread with sterile diluent only, showing no microbial growth and validating aseptic handling and media sterility.
Figure 8. Bioburden testing for total yeast and mold count on YGC agar. (a) Developed water hyacinth-based sanitary pad sample plated on Yeast Extract Glucose Chloramphenicol (YGC) agar, showing negligible or no fungal growth after incubation; (b) Positive control consisting of YGC agar inoculated with a known fungal strain (e.g., Candida albicans ATCC 10231), exhibiting characteristic yeast or mold colonies and confirming the effectiveness of the medium and incubation conditions; (c) Negative control consisting of a YGC agar plate spread with sterile diluent only, showing no microbial growth and validating aseptic handling and media sterility.
Processes 14 00918 g008
Figure 9. Evaluation of Staphylococcus aureus in the developed water hyacinth-based sanitary pad. (a) Sample from the developed sanitary pad after selective enrichment and plating on Mannitol Salt Agar (MSA) showing no yellow colonies or mannitol fermentation; (b) Positive control consisting of an MSA plate inoculated with Staphylococcus aureus ATCC 6538 displaying characteristic yellow colonies surrounded by yellow zones due to mannitol fermentation, confirming test sensitivity and selectivity; (c) Negative control consisting of an MSA plate inoculated with sterile diluent or non-Staphylococcus flora, showing no characteristic growth and confirming media specificity and absence of cross-contamination.
Figure 9. Evaluation of Staphylococcus aureus in the developed water hyacinth-based sanitary pad. (a) Sample from the developed sanitary pad after selective enrichment and plating on Mannitol Salt Agar (MSA) showing no yellow colonies or mannitol fermentation; (b) Positive control consisting of an MSA plate inoculated with Staphylococcus aureus ATCC 6538 displaying characteristic yellow colonies surrounded by yellow zones due to mannitol fermentation, confirming test sensitivity and selectivity; (c) Negative control consisting of an MSA plate inoculated with sterile diluent or non-Staphylococcus flora, showing no characteristic growth and confirming media specificity and absence of cross-contamination.
Processes 14 00918 g009
Figure 10. SEM micrographs of water hyacinth fibers at 500× magnification: (a) Untreated fiber showing a relatively smooth surface with indistinct structural features due to the presence of lignin, hemicellulose, pectin, and other surface impurities covering the fibers; (b) NaOH-treated fiber exhibiting a rougher and more exposed surface morphology resulting from the removal of surface-coating components during alkali pretreatment.
Figure 10. SEM micrographs of water hyacinth fibers at 500× magnification: (a) Untreated fiber showing a relatively smooth surface with indistinct structural features due to the presence of lignin, hemicellulose, pectin, and other surface impurities covering the fibers; (b) NaOH-treated fiber exhibiting a rougher and more exposed surface morphology resulting from the removal of surface-coating components during alkali pretreatment.
Processes 14 00918 g010
Figure 11. FTIR spectrum of water hyacinth fiber extract (4000–650 cm−1) showing characteristic O–H stretching (~3339 cm−1), aromatic/H–O–H bending (~1638 cm−1), CH2 bending (~1420 cm−1), and C–O–C stretching (~1032 cm−1), confirming the lignocellulosic nature of the material.
Figure 11. FTIR spectrum of water hyacinth fiber extract (4000–650 cm−1) showing characteristic O–H stretching (~3339 cm−1), aromatic/H–O–H bending (~1638 cm−1), CH2 bending (~1420 cm−1), and C–O–C stretching (~1032 cm−1), confirming the lignocellulosic nature of the material.
Processes 14 00918 g011
Figure 12. X-ray diffraction (XRD) patterns of raw water hyacinth and water hyacinth cellulose fiber, showing the characteristic cellulose I diffraction peaks and the corresponding crystallinity index (CrI%).
Figure 12. X-ray diffraction (XRD) patterns of raw water hyacinth and water hyacinth cellulose fiber, showing the characteristic cellulose I diffraction peaks and the corresponding crystallinity index (CrI%).
Processes 14 00918 g012
Figure 13. Visual representation of the biodegradation of the water hyacinth-based sanitary pad over a 60-day soil burial period. Photographic images show progressive structural disintegration and surface morphological changes recorded at Day 0, Day 10, Day 20, Day 40, and Day 60. Initial integrity observed at Day 0 gradually decreased, with visible fiber disruption by Day 10, increased porosity and fragmentation by Day 20, pronounced structural breakdown by Day 40, and near-complete degradation by Day 60.
Figure 13. Visual representation of the biodegradation of the water hyacinth-based sanitary pad over a 60-day soil burial period. Photographic images show progressive structural disintegration and surface morphological changes recorded at Day 0, Day 10, Day 20, Day 40, and Day 60. Initial integrity observed at Day 0 gradually decreased, with visible fiber disruption by Day 10, increased porosity and fragmentation by Day 20, pronounced structural breakdown by Day 40, and near-complete degradation by Day 60.
Processes 14 00918 g013
Figure 14. Biodegradation profile of the water hyacinth-based sanitary pad over a period of 60 days, showing a progressive increase in degradation percentage with time under natural environmental conditions.
Figure 14. Biodegradation profile of the water hyacinth-based sanitary pad over a period of 60 days, showing a progressive increase in degradation percentage with time under natural environmental conditions.
Processes 14 00918 g014
Table 1. Comparative absorbency performance of water hyacinth-based, cloth, and commercial sanitary napkins evaluated using the absorbency test.
Table 1. Comparative absorbency performance of water hyacinth-based, cloth, and commercial sanitary napkins evaluated using the absorbency test.
ParametersAbsorbency Performance
Water Hyacinth PadCloth Pad (Cotton)Commercial Pad
Total volume (mL)11111171
Total time (s)12510534
Table 2. pH values of the developed water hyacinth-based sanitary pad (n = 3).
Table 2. pH values of the developed water hyacinth-based sanitary pad (n = 3).
SamplepH Value (Mean ± SD)IS 5405:1980 [32] Acceptable RangeCompliance Status
Water hyacinth-based sanitary pad6.87 ± 0.046.0–8.5Compliant
Table 3. Bioburden test results of the developed water hyacinth-based sanitary pad evaluated according to IS 5405:2019 and ISO 11737-1:2018 (Amd.1:2021), showing the total bacterial count and total yeast and mold count in comparison with the specified microbiological limits.
Table 3. Bioburden test results of the developed water hyacinth-based sanitary pad evaluated according to IS 5405:2019 and ISO 11737-1:2018 (Amd.1:2021), showing the total bacterial count and total yeast and mold count in comparison with the specified microbiological limits.
Test ParameterTest MethodSpecification LimitResults
(Mean ± SD)
Compliance Status
Total bacterial countIS 5405:2019, Clause 7.3.1≤1000 CFU/g360 ± 22 CFU/gPass
Total yeast and mold countISO 11737-1:2018 (Amd.1:2021)≤10 CFU/g<1 CFU/gPass
Table 4. Skin irritation test results of the developed water hyacinth-based sanitary pad evaluated for the presence of Staphylococcus aureus according to IS 5405:2019 and ISO 11737-1:2018 (Amd.1:2021).
Table 4. Skin irritation test results of the developed water hyacinth-based sanitary pad evaluated for the presence of Staphylococcus aureus according to IS 5405:2019 and ISO 11737-1:2018 (Amd.1:2021).
Test ParameterTest MethodSpecification LimitResultCompliance Status
Staphylococcus aureusIS 5405:2019; ISO 11737-1:2018 (Amd.1:2021)Absent/gAbsentPass
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Vijayakumar, G.; Baskar, S.; Raghupathy, S.; Rangarajulu, S.K. Biodegradable Menstrual Pads from Hydrophytic Weeds: Sustainability Assessment, Absorption Performance, and Microbial Safety. Processes 2026, 14, 918. https://doi.org/10.3390/pr14060918

AMA Style

Vijayakumar G, Baskar S, Raghupathy S, Rangarajulu SK. Biodegradable Menstrual Pads from Hydrophytic Weeds: Sustainability Assessment, Absorption Performance, and Microbial Safety. Processes. 2026; 14(6):918. https://doi.org/10.3390/pr14060918

Chicago/Turabian Style

Vijayakumar, Gayathri, Swetha Baskar, Sowmiya Raghupathy, and Senthil Kumaran Rangarajulu. 2026. "Biodegradable Menstrual Pads from Hydrophytic Weeds: Sustainability Assessment, Absorption Performance, and Microbial Safety" Processes 14, no. 6: 918. https://doi.org/10.3390/pr14060918

APA Style

Vijayakumar, G., Baskar, S., Raghupathy, S., & Rangarajulu, S. K. (2026). Biodegradable Menstrual Pads from Hydrophytic Weeds: Sustainability Assessment, Absorption Performance, and Microbial Safety. Processes, 14(6), 918. https://doi.org/10.3390/pr14060918

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop