Many menstruators around the world have limited access to education about menstruation and to sanitary methods for managing menstruation. The use of sanitary products is influenced by economic status, proximity to resources, education, and cultural beliefs. Improper use of sanitary products or lack thereof can lead to major health issues. Plastic-based, commercial pads take decades to degrade and cause harm to the environment and pose health risks to menstruators. To combat the lack of education and accessibility to menstrual products, there is a need to develop inexpensive, environmentally friendly, and culturally acceptable menstrual hygiene pads. Organic sanitary pads have been developed with locally available materials, such as water hyacinth, banana stems, bamboo, papyrus, hemp, and cotton. These sanitary pads have the potential to create better health and economic outcomes for menstruators across the globe and reduce the environmental footprint.

  • Proper MHM is an important factor in menstrual health.

  • Plastic-based menstrual pads can cause health and environmental problems.

  • More eco- and user-friendly, frugal alternatives can be organic, plant-based pads.

Graphical Abstract

Graphical Abstract
Graphical Abstract

Menstruation is defined as the cyclical bleeding process that occurs between menarche and menopause, which typically begins between 12 and 13 years of age (Kaur et al. 2018; Critchley et al. 2020). In binary gender terms, women comprise 49.5% of the world's population (The World Bank 2021). As such, at any given moment about 10% of the world's population is menstruating (Bull et al. 2019; Barrington et al. 2021). Menstruation is not defined by gender as transgender men, intersex and non-binary persons may menstruate and should therefore not be disregarded in menstrual health services (Bobel 2010; Frank 2020; Barrington et al. 2021). It is estimated that between 0.1% and 2% of the global population do not identify as cisgender (Spizzirri et al. 2021). Although menstruators understand how to manage menstruation sanitarily, which reduces the number of infections caused by poor Menstrual hygiene management (MHM) (Freidenfelds 2009), research shows that approximately 4.5 million American menstruators still suffer from menstrual health problems each year and that menstruation significantly disrupts their physical, mental, and social well-being of tens of millions of menstruators around the world (Critchley et al. 2020). It should be, however, noted that not all menstruators know how to manage their periods sanitarily. There are big gaps in knowledge when it is not taught in schools or by family members due to its taboo nature.

MHM differs drastically across the spatial landscape as the menstruating experience is influenced by culture, socioeconomic status, and individual health. For example, some cultures perceive menstruation as a natural, healthy process to be celebrated (Leena 2016; Chebii 2018) while others associate shame and impurity with the process (Sommer et al. 2015). Menstrual health, which includes the accessibility of menstrual products, accurate information on menstruation, and access to safe, hygienic bathroom facilities, is integral to MHM (Medina-Perucha et al. 2020). It should be noted that access to MH materials is a global problem and that inequalities exist between and within countries. Approximately 130-million menstruating minors are out of school due to inadequate MHM and approximately 500 million menstruators globally lack access to adequate facilities for MHM (The World Bank 2018; PMNCH 2020). In a study in an urban metropolitan city in Missouri, USA, 17% of high school students missed at least one day at school due to an inadequate supply of menstrual products, with significantly more 9th graders (33.3%) than 10th–12th graders (6.1%) (Kuhmann et al. 2020).

MHM may be overlooked as a health concern because of the seemingly accessible sanitary products and bathroom facilities. However, for a large number of menstruators in some low-income countries, the use of a pad or proper sanitary products is considered a luxury and is not common. Menstruators often resort to using available household items, like towels, clothing, or in some cases, plant materials. This lack of accessibility to sanitary products is termed ‘period poverty’ (Tull 2019; PMNCH 2020). Period poverty is linked with poor health outcomes. For example, one study found that in menstruators aged 15–24 years, more than one-third use unhygienic menstrual management such as clothes and anything else other than sanitary pads, locally prepared napkins, and tampons. These menstruators had significantly more symptoms of reproductive tract infections such as genital sore/ulcer (1.59 times more) and abnormal vaginal discharge (1.37 times more) than those who use hygienic methods during menstruation (Vishwakarma et al. 2021). Another study showed that 14.2% of college-attending menstruators in the US experienced period poverty with menstrual health products to meet their monthly needs and they reported severe mental depression (Cardoso et al. 2021). As such, the use of sanitary products is dependent on one's economic status and improper use of sanitary products or lack thereof can lead to major health issues (Das et al. 2015). To combat the lack of education and accessibility to menstrual products, there is a need for inexpensive, environmentally friendly, locally sourced, and culturally acceptable interventions. Economical menstrual pads made of locally available and ecological materials, such as banana, bamboo, aloe vera, papyrus, and water hyacinth fibers have been explored (Lee 2012; Kathirvel & Ramachandran 2014; Musaazi et al. 2015; Krishna et al. 2018).

We seek to explore and synthesize the current frugal methods to develop menstrual hygiene products with plant materials that are inexpensive, environmentally friendly, and easily accessible compared to plastic-based, commercial pads. The goal of this paper is to acknowledge unhygienic methods used to manage menstruation and explore the alternatives to reduce the environmental impact and health issues involved with the use of plastic-based menstrual products. In doing so, we aim to move the conversation of menstruation into the sustainability sector as menstruation is at the nexus of the three spheres of sustainability: economic, social, and environmental. For more technical aspects of the production and waste management of biodegradable, organic menstrual products, we recommend the readers review previous studies reported by Luchese et al. (2021) and Velasco Perez et al. (2021).

Commercial menstrual hygiene products, such as pads and tampons, are produced using methods from the 20th century. While these products have evolved to be flexible and absorptive for the active, modern-day menstruators, the ingredients of these products are likely hazardous for the human and environmental health (Soni et al. 2019). Menstrual products are classified in the US as medical devices, meaning that the ingredients of these products do not need to be disclosed to the public (WVE 2014). The proprietary nature of ingredients is highly problematic as the female reproductive system is extremely absorptive and sensitive, which allows for the chemicals to be quickly distributed to the blood stream and throughout the rest of the body (Scranton 2013; Lin et al. 2020). Research has been conducted on the link between endometriosis, cancer, reproductive organ damage, and pregnancy complications with plasticizers, volatile organic compounds, dioxins, furans, and synthetic fibers that are found in plastic-based menstrual pads (Table 1) (Weuve et al. 2010; Scranton 2013; Ferguson et al. 2019).

Table 1

Environmental and health effects of chemicals found in plastic-based menstrual hygiene products

Chemical Name (CAS #) [molecular weight]Chemical formula & structureHealth effectsaEnvironmental fateaToxicity (LD50)a,b
Chloroform (67-66-3) [119.37]  
  • Serious irritation

  • Suspected of causing cancer

  • Suspected of damaging an unborn child

  • Causes damage to organs through prolonged or repeated exposure

 
  • Moderate soil mobility

  • Non-biodegradable in soil

 
  • Oral, guinea pig; LD50 = 820 mg/kg

  • Skin, rabbit; LD50 > 20 g/kg

  • Oral, mouse; LD50 = 36 mg/kg

 
Chloromethane (74-87-3) [50.49]  
  • Suspected of causing cancer

  • Causes damage to organs through prolonged or repeated exposure

 
  • Not susceptible to photolysis

  • Very high soil mobility

  • Not readily biodegradable

 
  • Oral, rat; LD50 = 1800 mg/kg

 
Benzene (71-43-2) [78.11]  
  • Serious eye and skin irritation

  • May cause genetic defects

  • May cause cancer

  • Causes damage to organs through repeated or prolonged exposure

 
  • Very water soluble

  • High soil mobility

 
  • Skin, guinea pig; LD50 > 9400 μL/kg

  • Skin, mouse; LD50 = 4700 mg/kg

  • Oral, rat; LD50 = 930 mg/kg

 
1,4-Dioxane (123-91-1) [88.11]  
  • Serious irritation

  • Respiratory irritation

  • Suspected of causing cancer

 
  • Very high soil mobility

  • Non-biodegradable

 
  • Oral, guinea pig; LD50 = 3150 mg/kg

  • Oral, rabbit; LD50 = 2 g/kg

  • Skin, rabbit; LD50 = 7600 μL/kg

 
Styrene (100-42-5) [104.15]  
  • Causes serious skin and eye irritation

  • Harmful if inhaled

  • Suspected of damaging an unborn child

  • Causes damage to organs after prolonged or repeated exposure

 
  • Not susceptible to photolysis

  • Low soil mobility

 
  • Oral, mouse; LD50 = 316 mg/kg

  • Oral, rat; LD50 = 2650 mg/kg

  • Oral, mammal (species unspecified); LD50 > 1500 mg/kg

 
Di(2-ethylhexyl) Phthalate (117-81-7) [390.6]  
  • May damage fertility

  • May damage unborn child

 
  • No soil mobility rate

 
  • Skin, guinea pig; LD50 = 10 g/kg

  • Oral, mouse; LD50 = 1500 mg/kg

  • Skin, rabbit; LD50 = 25 g/kg

 
Di-n-butyl Phthalate (84-74-2) [278.34]  
  • Suspected to cause damage to unborn child

  • Suspected of damaging fertility

 
  • Low soil mobility rate

  • Very toxic to aquatic life

 
  • Skin, rabbit; LD50 > 20 mL/kg

  • Oral, guinea pig; LD50 = 10 g/kg

  • Oral, mouse; LD50 = 3474 mg/kg

 
Tetrachlorodibenzo-p-dioxin (1746-01-6) [322.0]  
  • • Fatal if swallowed

  • • Cause serious eye irritation

 
  • No soil mobility rate

  • Very high bioconcentration in aquatic organisms

  • Prolonged environmental effects

 
  • Skin, rabbit; LD50 = 275 μg/kg

  • Oral, rat; LD50 = 20 μg/kg

  • Oral, mouse; LD50 = 114 μg/kg

 
Tetrachlorodibenzofuran (24478-72-6) [306.0]  
  • Fatal if swallowed

  • Fatal if in contact with skin

  • Fatal if inhaled

  • Suspected of damaging fertility or an unborn child

 
  • Very toxic to aquatic life

  • Prolonged environmental effects

 
  • Oral, guinea pig; LD50 > 0.005 mg/kg

  • Oral, rat; LD50 > 1.00 mg/kg

  • Oral, mouse; LD50 > 6.00 mg/kg

 
Chemical Name (CAS #) [molecular weight]Chemical formula & structureHealth effectsaEnvironmental fateaToxicity (LD50)a,b
Chloroform (67-66-3) [119.37]  
  • Serious irritation

  • Suspected of causing cancer

  • Suspected of damaging an unborn child

  • Causes damage to organs through prolonged or repeated exposure

 
  • Moderate soil mobility

  • Non-biodegradable in soil

 
  • Oral, guinea pig; LD50 = 820 mg/kg

  • Skin, rabbit; LD50 > 20 g/kg

  • Oral, mouse; LD50 = 36 mg/kg

 
Chloromethane (74-87-3) [50.49]  
  • Suspected of causing cancer

  • Causes damage to organs through prolonged or repeated exposure

 
  • Not susceptible to photolysis

  • Very high soil mobility

  • Not readily biodegradable

 
  • Oral, rat; LD50 = 1800 mg/kg

 
Benzene (71-43-2) [78.11]  
  • Serious eye and skin irritation

  • May cause genetic defects

  • May cause cancer

  • Causes damage to organs through repeated or prolonged exposure

 
  • Very water soluble

  • High soil mobility

 
  • Skin, guinea pig; LD50 > 9400 μL/kg

  • Skin, mouse; LD50 = 4700 mg/kg

  • Oral, rat; LD50 = 930 mg/kg

 
1,4-Dioxane (123-91-1) [88.11]  
  • Serious irritation

  • Respiratory irritation

  • Suspected of causing cancer

 
  • Very high soil mobility

  • Non-biodegradable

 
  • Oral, guinea pig; LD50 = 3150 mg/kg

  • Oral, rabbit; LD50 = 2 g/kg

  • Skin, rabbit; LD50 = 7600 μL/kg

 
Styrene (100-42-5) [104.15]  
  • Causes serious skin and eye irritation

  • Harmful if inhaled

  • Suspected of damaging an unborn child

  • Causes damage to organs after prolonged or repeated exposure

 
  • Not susceptible to photolysis

  • Low soil mobility

 
  • Oral, mouse; LD50 = 316 mg/kg

  • Oral, rat; LD50 = 2650 mg/kg

  • Oral, mammal (species unspecified); LD50 > 1500 mg/kg

 
Di(2-ethylhexyl) Phthalate (117-81-7) [390.6]  
  • May damage fertility

  • May damage unborn child

 
  • No soil mobility rate

 
  • Skin, guinea pig; LD50 = 10 g/kg

  • Oral, mouse; LD50 = 1500 mg/kg

  • Skin, rabbit; LD50 = 25 g/kg

 
Di-n-butyl Phthalate (84-74-2) [278.34]  
  • Suspected to cause damage to unborn child

  • Suspected of damaging fertility

 
  • Low soil mobility rate

  • Very toxic to aquatic life

 
  • Skin, rabbit; LD50 > 20 mL/kg

  • Oral, guinea pig; LD50 = 10 g/kg

  • Oral, mouse; LD50 = 3474 mg/kg

 
Tetrachlorodibenzo-p-dioxin (1746-01-6) [322.0]  
  • • Fatal if swallowed

  • • Cause serious eye irritation

 
  • No soil mobility rate

  • Very high bioconcentration in aquatic organisms

  • Prolonged environmental effects

 
  • Skin, rabbit; LD50 = 275 μg/kg

  • Oral, rat; LD50 = 20 μg/kg

  • Oral, mouse; LD50 = 114 μg/kg

 
Tetrachlorodibenzofuran (24478-72-6) [306.0]  
  • Fatal if swallowed

  • Fatal if in contact with skin

  • Fatal if inhaled

  • Suspected of damaging fertility or an unborn child

 
  • Very toxic to aquatic life

  • Prolonged environmental effects

 
  • Oral, guinea pig; LD50 > 0.005 mg/kg

  • Oral, rat; LD50 > 1.00 mg/kg

  • Oral, mouse; LD50 > 6.00 mg/kg

 

aInformation on health effects, environmental fate and toxicity (LD50) were from NIH (2021), except for toxicity (LD50) values of tetrachlorodibenzofuran which are from CDC (2021).

bLD50: the median lethal dose that is the amount of a test substance, given all at once, which causes the death of 50% of a group of test animals.

Plasticizer

Menstrual hygiene products made from polyethylene and polypropylene contain plasticizers, such as phthalates, to enhance the pliability of the product. During menstruation, the reproductive organ comes in direct contact with phthalate-containing pads and tampons. Therefore, significant absorption of phthalates (e.g., Di(2-ethylhexyl) Phthalate and Di-n-butyl Phthalate) into the female reproductive system is highly possible. In fact, many endocrine-disrupting health complications are associated with elevated exposure to phthalates, for example, precocious puberty (Kim et al. 2019), ovulation disorders (Weuve et al. 2010), and preterm birth (Ferguson et al. 2019).

Volatile organic compounds

Since menstrual products are not regulated, the high rates of volatile organic compounds (VOCs) detected in these products are very alarming (Kim et al. 2020). VOCs such as benzene, 1,4-dioxane, styrene, chloromethane, and chloroform have been detected in menstrual hygiene pads (WVE 2014). Specifically in menstrual pads, VOCs are typically added as adhesives, binders, and fragrances. Other products using VOCs include the manufacturing of car tires, the refining of petroleum, and nail polish remover (WVE 2014). Exposure to VOCs via dermal permeation during menstrual periods is of concern as multiple VOCs are known for reproductive effects, carcinogenicity, and damage to the liver and kidney (Lin et al. 2020).

Dioxins and furans

The dioxins and furans such as tetrachlorodibenzo-p-dioxin (TCDDs) and tetrachlorodibenzofuran (TCDFs) are found in products that use chlorine-bleached materials (Shin & Ahn 2007). Since plastic-based pads contain these materials, exposure can cause the growth of uterine tissue on the outer areas of the uterus (i.e., endometriosis), cancer of the female reproductive system (i.e., endometrial cancer), and the abnormal growth of cells within or around the uterus muscle (i.e., uterine leiomyomata) (Shin & Ahn 2007; Weuve et al. 2010).

Synthetic fibers

A synthetic fiber used in the production of plastic-based menstrual products to promote super absorbance is viscose rayon. Viscose rayon is made from wood pulp, which categorizes it as a natural regenerated polymer while still being a synthetic fiber because the wood pulp is treated with carbon disulfide to start the production of viscose (Shaikh et al. 2012). Viscose rayon is often mixed with cotton to produce a high level of absorbance. Viscose rayon was one of four synthetic fibers that were used in menstrual products. When companies started using these synthetic ingredients in pads, cases of menstrual toxic shock syndrome (MTSS) increased significantly and the use of these synthetic ingredients was banned, except for the use of viscose rayon (Nicole 2013). MTSS is known to be caused by a poison produced by Staphylococcus aureus bacteria. S. aureus are normally present without causing any harm in the vagina. However, when S. aureus are in an environment supportive of their rapid growth, they release superantigenic exotoxins that enter the bloodstream affecting the reproductive system, digestive system, muscular system, and the nervous system (Vostral 2018). The longer use of tampons or other intra-vaginal menstrual devices, the higher the risk of MTSS is (Billon et al. 2020), and synthetic fibers (e.g., polyester) provide a better environment for the growth of S. aureus than natural fibers (e.g., cotton). Furthermore, female workers in the viscose rayon industry have reported health issues regarding the female reproductive system such as menstruation disorders and spontaneous abortions (Koh & Chia 1994; Takebayashi et al. 1998; Wong et al. 2009; Sieja et al. 2018). What is more, the factory workers were exposed via dermal contact, i.e., the product was not on or near the reproductive area. Future research should examine the relations between the presence of viscose rayon in menstrual products and the harmful effects of some menstrual products throughout the duration of one's menstruating life cycle.

While we are not aware of any research stating that the level of these phthalates, VOCs, dioxins or furans, or viscose rayon are over the toxic health guidelines, the continuous exposure to these toxins can lead to many health issues and even result in death (Scranton 2013). Many menstruators across North America are becoming aware of the health hazards and demanding that menstrual products are no longer considered medical devices so that all the ingredients of these products are explicitly stated on their packaging (WVE 2014). The harmful ingredients detected in plastic-based pads and the associated health issues affect not only the human body but also the environment.

Waste produced from menstrual hygiene products

One of the major impacts that plastic-based pads have on the environment is the residual waste resulting from the disposal of the product. For example, about 12,000 single-use products are used throughout one individual's reproductive years; each product may take up to 800 years to biodegrade (Soni et al. 2019). In other words, on average, menstruation occurs for about 40 years in a lifetime, bleeding for 3–7 days a month or about 6.5 years of period. A single menstruator is estimated to use between 5,000 and 15,000 pads and tampons in their menstrual life cycle (Borunda 2019). In the US alone, approximately 12 billion pads and 7 million tampons are discarded annually (Dillon 2017). As are other solid wastes, most used pads and tampons are disposed of in trash receptacles and end up in landfills, while others find their way to reach the marine environment. Plastic-based pads are composed of up to 90% plastic or non-degradable materials, such as pad wrappers, adhesive strips, and so on, so that they take up to 500 years to fully break down in a landfill (Barr 2018). By replacing plastic-based commercial pads with a biodegradable alternative, the 500 years it takes for plastic-based pads to degrade could be reduced to 5 weeks. Other negative impacts that plastic-based pads have on the environment are petroleum-derived synthetic materials in the production of the pads and emissions during material acquisition, processing, packaging, and distribution (Hait & Powers 2019).

Used menstrual pads are disposed of in several different ways depending on sociocultural norms and taboos related to menstruation (Elledge et al. 2018). The less biodegradable waste generated from single-use feminine hygiene products (FHPs) is sent to landfills, clogs sewage pipes, and/or is thrown out into open fields every day (Kaur et al. 2018; Soni et al. 2019). As plastic-based pads degrade, the microplastics, fragmentation, and degradation of plastic materials, within the product enter the environment during landfill disposal or can infiltrate water streams if single-use FHPs are not disposed of properly. After the disposal of plastic-based pads in either the marine environment or a landfill, they begin to degrade into microplastics. The occurrence of microplastics (<5 mm) in the water is a significant threat to human health (Rahman et al. 2021) and aquatic ecosystems (Rezania et al. 2018). The occurrence that humans have with microplastics is larger than one might expect. Humans are typically exposed to microplastics through ingestion, inhalation, and dermal contact which may cause oxidative stress, cytotoxicity, altering metabolism, immunity disruption, translocation to distant organs, neurotoxicity, reproductive toxicity, and carcinogenicity (Rahman et al. 2021). The ingested microplastics bioaccumulate in aquatic biota and may cause negative impacts on growth and development (Rezania et al. 2018). For example, larval and juvenile sea snail showed a delayed growth due to exposure to high microplastic concentrations, although an insignificant effect was found at environmental concentrations (Lo & Chan 2018). Ingested microplastics have shown lethal or sublethal effects on marine organisms as they can serve as a vector of toxic chemicals (Rodrigues et al. 2018). These products pollute the environment, thereby indirectly impacting human and nonhuman health (Grose & Grabe 2014) and a fully biodegradable alternative could ameliorate these issues (Tudu 2019; Achuthan et al. 2021).

The biodegradation of organic products takes less time than plastic-based products, making organic products a more ecologically sound option (Kaur et al. 2018). A biodegradable sanitary pad disposed through a green waste stream would be composted. Composting, the breaking down of organic matter into a usable and commodifiable product, is an important part of circular waste management (Rynk et al. 1992) that can eliminate harmful pathogens while simultaneously generating a highly useful product for agricultural use (Sikora 1998).

Waste management, sanitation, and sociocultural barriers

The Water, Sanitation, and Hygiene (WASH) sector focuses on Sustainable Development Goal 6 which aims to provide clean water, proper hygienic methods (including MHM), and sanitary areas for civilians to clean themselves (United Nations 2021). As waste management facilities are not readily available globally, the structure of one's built environment influences the menstruation experience. Shoemaker (2008) described how rural people living in the riparian environments often toss menstrual waste directly into streams, which contaminate them with pathogenic microbes. Those experiencing homelessness in urban centers like New York City, USA, lack sanitary disposal access (Sommer et al. 2020; Barrington et al. 2021). Chebii (2018) and Ngugi & Nyaura (2014) detailed the indelible and complex relationship between the built environment and menstruation experiences in a Kenyan case study. As economic inequality produced a slum and squatter settlement, the lack of sanitation disproportionally affected young girls. As their families struggle to attain basic needs, menstrual products and privacy are non-existent. Alternatively, the at-home living environment may offer a respite to some young girls in South Asia who often missed school as their educational facilities lacked disposal systems, proper privacy measures, and water supply (Mahon & Fernandes 2010).

The aforementioned examples deal with the infrastructural failures of society, but culture folklore also produces tangible social and environmental consequences. Menstruation has been associated with ‘black magic’ as well as witchcraft (Sommer et al. 2013). A striking example is reported by Umeora & Egwuatu (2008). In rural Nigeria, according to the folklore, if menstrual waste is not buried, witches would seek out the blood. And if blood is found, the woman would become infertile and therefore deemed ‘destroyed’. The folklore can affect the environment depending as any menstrual products containing synthetic fiber rayon or organochlorines will disturb the soil microflora when buried (Kroesa 1990). Furthermore, human health is at risk if the disposer was infected with a virus like hepatitis or HIV; these viruses retain infectivity and may live up to 6 months in soil (Shoemaker 2008). To that end, improved waste management techniques would also require addressing sociocultural misconceptions. Until then, providing a biodegradable alternative to single-use menstrual pads will decrease the amount of solid waste generated and will also give menstruators a cheaper alternative to expensive FHPs on the market.

Plastic-based pads have been used for decades and their disposal has caused great environmental harm and created a market for more eco-friendly options. Not only do organic menstrual pads help with environmental conservation, they also are more easily accessible in rural areas and low-income countries. As such, plant-based products with locally sourced materials help alleviate some of the health issues involved with unsanitary methods often used due to the price, inaccessibility, and sociocultural barriers to MHM. We define plastic-based menstrual products as menstrual products that are not made with organic products and/or contain chemicals to make the product more esthetic, comfortable, or to lower production/manufacturing costs. We acknowledge that plant-based pads as opposed to plastic-based pads also have plastic components, such as wrappers, backing, adhesive strips, and so on, even though the main absorbance layer is made of natural materials.

Table 2 offers examples of organic pads. While the plant-based, organic pad products presented here are not meant to be exhaustive, we seek to explore suitable plant materials that can be locally harvested and manufactured at a low cost. We explore water hyacinth, bamboo, banana stems, papyrus, cotton, and hemp. Natural plant fibers are cellulose-based and attract liquids which make them highly absorbent (Table 3). For example, cotton fibers can hold water about 25 times their own weight (Dochia et al. 2012). Each organic pad has a different focus depending on the salient issue(s) companies seek to address. The intentions of the product can vary between emphasis on addressing social issues, such as absenteeism from work and school, environmental issues, due to the large number of disposable pads that take decades to degrade, or economic issues, with the inaccessibility to use hygienic menstrual methods because of how expensive plastic-based pads are in their area. As these issues are interconnected and non-mutually exclusive, all companies work towards a common goal: an affordable, sanitary, eco-friendly alternative to plastic-based pads.

Table 2

Detailed information on organic menstrual hygiene pads

Pad nameCountry of originDeveloper/FounderMain plantOther componentsSource
LilyPad Uganda Team 60 Water hyacinth Straw, wood & bamboo Lockley et al. (2014)  
JaniPad Kenya Chalmers Univ. of Technology, Sweden Water hyacinth Unknown MAPPINGDW (2013)  
Saathi Pad India Kagetsu, K., Bothra, T. & Kane, G. Bamboo & banana stem Unknown Saathipads.com 
Safe Pad India Agarwal, A. & Sehrawat, H. Banana stem Unknown Barrett (2019)  
Go! Pad Rwanda Scharpf, E. Banana stem Unknown Sheinnovates.com 
BanaPads Uganda Bbaale, R. Banana stem Unknown Roddenberryfoundation.org 
MakaPads Uganda Makerere Univ., Uganda Papyrus Recycled paper Musaazi et al. (2015)  
Aisle Pads (Lunapads) Canada Siemens, S. & Shaw, M. Cotton Wood, polyester, polyurethane Periodaisle.com 
PadBack South Korea Akarsu, C. Papyrus, cotton & hemp Unknown Cansuakarsu.com 
Pad nameCountry of originDeveloper/FounderMain plantOther componentsSource
LilyPad Uganda Team 60 Water hyacinth Straw, wood & bamboo Lockley et al. (2014)  
JaniPad Kenya Chalmers Univ. of Technology, Sweden Water hyacinth Unknown MAPPINGDW (2013)  
Saathi Pad India Kagetsu, K., Bothra, T. & Kane, G. Bamboo & banana stem Unknown Saathipads.com 
Safe Pad India Agarwal, A. & Sehrawat, H. Banana stem Unknown Barrett (2019)  
Go! Pad Rwanda Scharpf, E. Banana stem Unknown Sheinnovates.com 
BanaPads Uganda Bbaale, R. Banana stem Unknown Roddenberryfoundation.org 
MakaPads Uganda Makerere Univ., Uganda Papyrus Recycled paper Musaazi et al. (2015)  
Aisle Pads (Lunapads) Canada Siemens, S. & Shaw, M. Cotton Wood, polyester, polyurethane Periodaisle.com 
PadBack South Korea Akarsu, C. Papyrus, cotton & hemp Unknown Cansuakarsu.com 
Table 3

The amount of cellulose, hemicellulose, and lignin in the plants used for the production of organic menstrual hygiene pads

PlantCellulose (wt. %)Hemicellulos (wt. %)Lignin (wt. %)Reference
Water hyacinth 18.2 48.7 3.5 Nigam (2002)  
27.6 39.8 15.0 Pattra & Sittijunda (2015)  
57 25.6 4.1 Tanpichai et al. (2019)  
34.2 17.7 12.2 Ahn et al. (2012)  
Bamboo 57–66 20–25 20–30 Yang et al. (2008)  
33.1 22.8 9.7 Wijaya et al. (2019)  
45.8 26.6 23.4 Li et al. (2021)  
54.6 11.4 21.7 Dorez et al. (2014)  
Banana stems 32 32 19 Shrestha et al. (2021)  
63–64 – 15 Subash & Muthiah (2021)  
Papyrus 53.3–62.0 – 22.8–32.8 Weidemann & Bayer (1983)  
Cotton 89.7 2.7 Dorez et al. (2014)  
85–90 – 0.4–1.0 Subash & Muthiah (2021)  
Hemp 46.1 21.5 8.5 Arufe et al. (2021)  
74.1 7.6 2.2 Dorez et al. (2014)  
PlantCellulose (wt. %)Hemicellulos (wt. %)Lignin (wt. %)Reference
Water hyacinth 18.2 48.7 3.5 Nigam (2002)  
27.6 39.8 15.0 Pattra & Sittijunda (2015)  
57 25.6 4.1 Tanpichai et al. (2019)  
34.2 17.7 12.2 Ahn et al. (2012)  
Bamboo 57–66 20–25 20–30 Yang et al. (2008)  
33.1 22.8 9.7 Wijaya et al. (2019)  
45.8 26.6 23.4 Li et al. (2021)  
54.6 11.4 21.7 Dorez et al. (2014)  
Banana stems 32 32 19 Shrestha et al. (2021)  
63–64 – 15 Subash & Muthiah (2021)  
Papyrus 53.3–62.0 – 22.8–32.8 Weidemann & Bayer (1983)  
Cotton 89.7 2.7 Dorez et al. (2014)  
85–90 – 0.4–1.0 Subash & Muthiah (2021)  
Hemp 46.1 21.5 8.5 Arufe et al. (2021)  
74.1 7.6 2.2 Dorez et al. (2014)  

Water hyacinth

Water hyacinth is a floating aquatic plant that is invasive to many regions. This plant grows very quickly, with a doubling period of approximately 2 weeks, and reproduces asexually, generating daughter plants, where the root systems are connected through stolons. As such, water hyacinth can create floating barricades in the water that inhibit the environment they are growing in. The water hyacinth, when grown in multitudes, can disrupt aquatic life by reducing oxygen levels in the water and taking over the native plant species' habitat. Not only does the water hyacinth disrupt aquatic life, but it also limits, if not eliminates, the recreational use of the body of water (McVea & Boyd 1975; Masifwa et al. 2001; Toft et al. 2003).

Water hyacinth fibers have been utilized in the production of polymer composites (Abral et al. 2014), livestock feed (Lu et al. 2008), wastewater treatment (Qin et al. 2020), and sanitary applications (Musaazi et al. 2015). Water hyacinth is a suitable alternative to plastic-based pads because it is cellulose-based, biodegradable, and does not harm the human body. In addition, it is a fast-growing invasive species that causes environmental problems if not managed properly.

Bamboo

Bamboo is native to many Asian countries and its adaptability allows growth in many different climates. Bamboo is used in many different industries of textiles, erosion control, and construction because of its rapid growth rate of 3–4 years (Erdumlu & Ozipek 2008). With rapid growth, bamboo can become invasive and cause damage to the native fauna and flora. As a result of this, the health of native species declines due to the lack of nutrients they are receiving.

The high absorption rate, antibacterial properties, and biodegradability make bamboo a healthy and environmentally friendly alternative to plastic-based, commercial pads (Rathod & Kolhatkar 2014). By utilizing bamboo in the production of organic pads, it decreases the cost of materials and is less harmful to the environment than plastic-based commercial pads.

Banana stems

Banana trees are native to the tropical areas in the eastern hemisphere. In Sri Lanka, over 123,000 acres of land is devoted to the cultivation of bananas and the annual production rate is approximately 20 tons per acre (Kudagamage et al. 2002). With high banana production rates, the disposal of the stems after cultivation is challenging. As such, companies like BanaPads (Table 2) have endeavored to create a ‘frugal development’ that manages banana tree waste by making organic pads.

Papyrus

Papyrus is an aquatic plant that is also known as paper reed, which is native to Africa. The plant and its cellulosic fiber have been used for centuries in different applications, such as ancient Grecian documents, wastewater treatment, shoe soles, menstrual products, and constructed wetlands (Alexopoulou et al. 2013; Mburu et al. 2015; Musaazi et al. 2015; Abou-Elela et al. 2017; Bemerw et al. 2021). In fact, Egyptian menstruators used tampons made of papyrus in the 15th century B.C. (Weissfeld 2010). Furthermore, papyrus has been utilized as a component for menstrual pads in rural Africa where the plant grows abundantly and accessibility to menstrual products is limited.

Cotton

Cotton is native to tropical and subtropical parts of the world and is now cultivated in various regions around the world. Cotton has been used in many industries, most notably in the textile industry. Cotton fibers are absorbent, durable, and soft, which makes them the prime material used for items, such as towels, hygiene products, and many household items. Because of the high absorbency and successful cultivation, cotton is easily accessible and highly diverse. Using pure, organic cotton for menstrual products is likely to not cause health issues and allows the menstrual pad to be more biodegradable compared to plastic-based pads.

The global organic sanitary pads market is expected to increase by USD 901.71 million from 2021 to 2026 (Technavio 2022). This increase is mainly attributed to a growing population of working women, growing awareness about female hygiene and environmental impact, and increasing health issues related to plastic-based pads (Peberdy et al. 2019; IMARC 2021). This section details products that are made predominately with plant materials and offers brief examples of how companies are working at the nexus of sustainability and menstruation.

Predominate plant material: water hyacinth

The Lilypad and Janipad are examples of organic menstrual products using predominately water hyacinth. The Lilypad is a menstrual pad that is made from water hyacinth and agricultural waste such as wood and bamboo (Lockley et al. 2014). With origins in Uganda, this biodegradable pad was created to address the lack of education and sanitary practices. As water hyacinth grows in abundance and is therefore easily accessible in this region, the manufacturing costs of this pad are very low. Lilypad sells in Uganda for the market price of $1 USD for a pack of 10 pads. Demand for products results in a demand for workers. As the popularity of products such as Lilypad rises, more workers will need to be employed to keep pace with product demand. Increased demand for handmade products has allowed women in the area to become employed in an industry that expands economic opportunities for women.

Created from water hyacinths in Kenya, the Janipad decomposes within months (MAPPINGDW 2013). Lake Victoria has a plethora of water hyacinths that have hindered the recreational use of some parts of the lake and disrupted the native flora and fauna. Therefore, creating a sanitary pad from an abundant material minimizes the cost of products needed to create the pad and benefits the habitat by allowing the native species to grow instead of the water hyacinth. Janipad addresses the social and environmental issues that pertain to menstruation, namely school absenteeism and generation of plastic waste. On average, over half of young menstruators miss school for the duration of their cycle (BRIDGE 2015) and reducing the number of missed school days is of the utmost importance for young menstruators' long-term well-being. Research shows an accumulation of missed school days often results in girls completely abandoning their education, which increases the likelihood of child brides (BRIDGE 2015; Yilmaz et al. 2021).

Predominate plant material: banana stems

Banana stems from banana trees are widely available as agricultural waste. Multiple companies recognized an opportunity to recover the perceived waste and produce a sustainable solution to menstruation in low-income countries. For example, the Go! Pad, created by Sustainable Earth Enterprises (SHE) utilizes locally sourced banana plants to lower production costs and increase accessibility. Since banana fibers have such high absorbency qualities, SHE taught local banana farmers to properly cultivate the stems and unwanted materials from the plant for SHE to purchase for use in the production of the Go! Pads. Moreover, SHE works to increase the accessibility of menstrual hygiene products to menstruators in Rwanda where many young menstruators must miss school and work because they do not have the means to properly address menstruation (SHE 2021). The lack of employment for women in this region is caused by their absence from work due to menstruation. SHE offers jobs to women, giving them an opportunity to work and learn about proper hygienic menstruation methods, and access to affordable, safe methods for managing menstruation.

BanaPads is a company that was founded in Uganda with the purpose of improving menstrual hygiene methods in the country (Roddenberry Foundation 2022). By tackling this social issue, this company also wanted to create an environmentally friendly, biodegradable pad that utilized the excess waste material from banana plants. The banana fibers are dried and combined with paper materials and an enzyme, which creates an absorbent pad. This company helps menstruators to become more educated on healthy MHM. Furthermore, BanaPads offers menstruators an opportunity to individually practice safer MHM while also enabling them to generate a form of secondary income. Since these pads are sold by menstruators and to people that they know, a network marketing business model helps expand accessibility to menstrual products and increase menstruation knowledge.

Saathi, creators of the Saathi Pad, uses locally sourced banana and bamboo fibers (Saathi 2021). While this pad was created in Gujarat, India, it is available to menstruators around the world to purchase. Because the sole components of these pads are plant-based, they are biodegradable and chemical free, which mitigates the environmental and health issues that plastic-based pads pose. The Saathi Pad not only increases the availability of pads for menstruators in India but also creates an environment of menstrual education for those who purchase a Saathi pad. Saathi also employs women to increase gender equality, which induces a social and economic change in the culture of this region. By purchasing materials from local farmers and selling pads at $1.62 USD, Saathi strengthens the local economy and makes affordable sanitary pads available in the region.

Finally, the Safe Pad is a reusable, biodegradable pad that was created by Sanfe to address the social and environmental issues regarding menstruation and proper menstrual hygiene (Barrett 2019). Created from banana fibers, polyester piling, and cotton polyurethane laminate, the reusable pad helps menstruators in India use proper sanitary methods. The use of banana fibers in the production of the Safe Pad helps to lower the production and market cost of the pads ($2.68 USD), making the pad more affordable for menstruators in India. However, it should be noted that polyester (polyethylene terephthalate) used in the Safe Pad is a petroleum-derived artificial polymer.

Other combination of organic pad products

Papyrus, cotton, and hemp are utilized to create cleaner and safer menstruation products. One example is the MakaPads, produced from papyrus and wastepaper. Developed in Uganda, the MakaPads emerged in a region where many menstruators cannot or do not attend school due to unhygienic or improper menstrual management (Musaazi et al. 2015) as they do not have the accessibility to inexpensive, sanitary methods to manage their menstruation. In Uganda, papyrus is a native plant and is abundant. This pad is often provided free of charge or sold at a very low price ($0.60–0.68 USD for 10 pads) to increase accessibility. By doing so, the MakaPads have addressed the economic issue that is a major factor in menstrual hygiene in the region.

Aisle, previously called Lunapads, is a Canadian company that creates reusable menstrual undergarments and the Aisle Pads (Aisle 2021). The company aims to offer menstruators a way to use menstrual products hygienically while minimizing the waste produced from disposable menstrual products. The pads are made from various plant materials that include: (1) Tencel, a fiber from wood sources that helps develop the yarn for absorbency in these pads and undergarments; (2) Organic cotton grown without any chemicals to decrease exposure to harmful chemicals that are often in menstrual products; and (3) Technical cotton created from absorbent and water repelling yarn to improve the performance of pads (Aisle 2021). These pads range from $16 to $22 USD, dependent on the absorbency of the reusable pad.

PadBack is a company originating in South Korea that created a biodegradable box that contains materials to make pads in a user-friendly manner (Arkarsu 2013). PadBack aims to overcome social issues associated with menstruators who do not have accessibility to feminine products made of agricultural fibers like papyrus, cotton, and hemp. Once used, a PadBack can be disposed of in soil where it can serve as a fertilizer to help the plants grow.

Menstruation is a biological process that nearly half of the global population experiences, which is steeped with misconceptions about cleanliness, causing alienation and health risks. What is more, menstruation could be addressed at the crux of the sustainability movement. The social, economic, and environmental constraints offer opportunities to improve sustainability practice on multiple fronts, including equity. Here, we offer an overview of alternative organic menstrual products that alleviate health issues, social sigma, and economic inequality. Due to the health and environmental effects of plastic-based products, the use of organic products should be more commonplace in our global society. The Lilypad, Janipad, Saathi Pad, Safe Pad, Go! pad, BanaPads, MakaPad, Aisle Pads, and PadBack are some of the organic menstrual products that have been proven to work and satisfy the needs regarding MHM. These brands of pads demonstrate how the production of organic pads can play a potential role in environmental conservation and allow menstrual products to be more accessible to menstruators who have challenges practicing sanitary methods. Unfortunately, the ingredients in most plastic-based products are not disclosed, although the consequences for health have been demonstrated through research. While some negative health effects can be attributed to the misuse of menstrual products, other effects are solely due to the chemicals used in the products that the menstruators place in sensitive, absorbent parts of their bodies. An affordable, accessible, and chemical-free menstrual product is a necessity for gender equity and the global sustainability movement. Since menstrual products are commonly used every month by menstruators including women from early teens to around 50 years old, the amount of used menstrual products sent to landfills is of concern. Biodegradable, organic products have the potential to create better health and economic outcomes for menstruators across the globe and reduce the environmental footprint.

This study was financially supported, in part, by the Texas State Houston-Louis Stokes STEM Pathways and Research Alliance (H-LSAMP) scholarship (Grant #: 1911310) awarded to Jamie Hand and by the start-up fund from the Texas State University to Sangchul Hwang. The authors would also like to thank the National Science Foundation (Grant #: 1829144) for funding.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

Abou-Elela
S. I.
,
Elekhnawy
M. A.
,
Khalil
M. T.
&
Hellal
M. S.
2017
Factors affecting the performance of horizontal flow constructed treatment wetland vegetated with Cyperus papyrus for municipal wastewater treatment
.
International Journal of Phytoremediation
19
,
1023
1028
.
https://doi.org/10.1080/15226514.2017.1319327.
Abral
H.
,
Kadriadi
D.
,
Rodianus
A.
,
Mastariyanto
P.
,
Ilhamdi
S.
,
Arief
S.
,
Sapuan
S. M.
&
Ishak
M. R.
2014
Mechanical properties of water hyacinth fibers – polyester composites before and after immersion in water
.
Materials and Design
58
,
125
129
.
https://doi.org/10.1016/j.matdes.2014.01.043
.
Achuthan
K.
,
Muthupalani
S.
,
Kolil
V. K.
,
Bist
A.
,
Sreesuthan
K.
&
Sreedevi
A.
2021
A novel banana fiber pad for menstrual hygiene in India: a feasibility and acceptability study
.
BMC Women's Health
21
,
129
.
https://doi.org/10.1186/s12905-021-01265-w
.
Ahn
D. J.
,
Kim
S. K.
&
Yun
H. S.
2012
Optimization of pretreatment and saccharification for the production of bioethanol from water hyacinth by Saccharomyces cerevisiae
.
Bioprocess and Biosystem Engineering
35
,
35
41
.
https://doi.org/10.1007/s00449-011-0600-5
Aisle
2021
Our Tech
.
Available from: https://periodaisle.com (accessed 4 September 2021)
.
Alexopoulou
A. A.
,
Kaminari
A. A.
,
Panagopoulous
A.
&
Pöhlmann
E.
2013
Multispectral documentation and image processing analysis of the papyrus of tomb II at Daphne, Greece
.
Journal of Archaeological Science
40
,
1242
1249
.
https://doi.org/10.1016/j.jas.2012.09.013
.
Arkarsu
C.
2013
PadBack
.
Available from: https://www.cansuakarsu.com/padback (accessed 20 August, 2021)
.
Arufe
S.
,
de Menibus
A. H.
,
Leblanc
N.
&
Lenormand
H.
2021
Effect of retting on hemp shiv physicochemical properties
.
Industrial Crops & Products
171
,
113911
.
https://doi.org/10.1016/j.indcrop.2021.113911
.
Barr
S.
2018
Flushing Plastic Period Products Down the Toilet Pollutes Ocean, Research Warns
.
Independent
. .
Barrett
A.
2019
Reusable, Biodegradable, Sanitary Napkin Made of Banana Fibre. Bioplastics NEWS. Available from: https://bioplasticsnews.com/2019/09/01/reusable-biodegradable-sanitary-napkin-banana-fibre/ (accessed 31 August 2021)
.
Barrington
D. J.
,
Robinson
H. J.
,
Wilson
E.
&
Hennegan
J.
2021
Experiences of menstruation in high income countries: a systematic review, qualitative evidence synthesis and comparison to low-and middle-income countries
.
PLOS ONE
16
,
e0255001
.
https://doi.org/10.1371/journal.pone.0255001
.
Bemerw
B.
,
Teshome
B.
,
Gibril
M.
&
Kong
F.
2021
Development of Papyrus fiber reinforced natural rubber composite for shoe sole
.
Journal of Natural Fibers
.
Article-in-Press. https://doi.org/10.1080/15440478.2021.1875375
.
Billon
A.
,
Gustin
M.-P.
,
Tristan
A.
,
Bénet
T.
,
Berthiller
J.
,
Gustave
C. A.
,
Vanhems
P.
&
Lina
G.
2020
Association of characteristics of tampon use with menstrual toxic shock syndrome in France
.
EClinicalMedicine
21
,
100308
.
https://doi.org/10.1016/j.eclinm.2020.100308
.
Bobel
C.
2010
New Blood: Third-Wave Feminism and the Politics of Menstruation
.
Rutgers University Press
,
New Brunswick, NJ
.
Borunda
A.
2019
How Tampons and Pads Became so Unsustainable
.
National Geographic
. .
BRIDGE
2015
Gender Update: Gender and Menstrual Hygiene Management (MHM)
. .
Bull
J. R.
,
Rowland
S. P.
,
Scherwitzl
E. B.
,
Scherwitzl
R.
,
Danielsson
K. G.
&
Harper
J.
2019
Real-world menstrual cycle characteristics of more than 600,000 menstrual cycles
.
NPJ Digital Medicine
2
,
1
8
.
https://doi.org/10.1038/s41746-019-0152-7
.
Cardoso
L. F.
,
Scolese
A. M.
,
Hamidaddin
A.
&
Gupta
J.
2021
Period poverty and mental health implications among college-aged women in the United States
.
BMC Women's Health
21
,
14
.
https://doi.org/10.1186/s12905-020-01149-5
.
CDC
2021
Polychlorinated Biphenyls (PCB's)
.
Current Intelligence Bulletin 45. Centers for Disease Control and Prevention
.
Available from: https://www.cdc.gov/niosh/docs/86-111/default.html (accessed 2 November 2021)
.
Chebii
S. J.
2018
Menstrual issues: how adolescent schoolgirls in the Kibera slums of Kenya negotiate their experiences with menstruation
.
Women's Reproductive Health
5
,
204
215
.
https://doi.org/10.1080/23293691.2018.1490534
.
Critchley
H. O. D.
,
Babayev
E.
,
Bulun
S. E.
,
Clark
S.
,
Garcia-Grau
I.
,
Gregersen
P. K.
,
Kilcoyne
A.
,
Kim
J.-Y. J.
,
Lavender
M.
,
Marsh
E. E.
,
Matteson
K. A.
,
Maybin
J. A.
,
Metz
C. N.
,
Moreno
I.
,
Silk
K.
,
Sommer
M.
,
Simon
C.
,
Tariyal
R.
,
Taylor
H. S.
,
Wagner
G. P.
&
Griffith
L. G.
2020
Menstruation: science and society
.
American Journal of Obstetrics and Gynecology
223
,
624
664
.
https://doi.org/10.1016/j.ajog.2020.06.004
.
Das
P.
,
Baker
K. K.
,
Dutta
A.
,
Swain
T.
,
Sahoo
S.
,
Das
B. S.
,
Panda
B.
,
Nayak
A.
,
Bara
M.
,
Bilung
B.
,
Mishra
P. R.
,
Panigrahi
P.
,
Cairncross
S.
&
Torondel
B.
2015
Menstrual hygiene practices, wash access and the risk of urogenital infection in women from Odisha, India
.
PLoS ONE
10
,
e0130777
.
https://doi.org/10.1371/journal.pone.0130777
.
Dillon
A.
,
2017
Planet-friendly periods
. In:
Stanford Magazine
(
Black
H.
ed.).
Available from: https://stanfordmag.org/contents/planet-friendly-periods (accessed 30 June 2021)
.
Dochia
M.
,
Sirghie
C.
,
Kozlowsky
R. M.
&
Roskwitalski
Z.
,
2012
Cotton fibres
. In:
Handbook of Natural Fibres
(
Kozlowski
R. M.
ed.).
Woodhead Publishing Series in Textiles
.
https://doi.org/10.1533/9780857095503.1.9
.
Dorez
G.
,
Ferry
L.
,
Sonnier
R.
,
Taguet
A.
&
Lopez-Cuesta
J.-M.
2014
Effect of cellulose, hemicellulose and lignin contents on pyrolysis and combustion of natural fibers
.
Journal of Analytical and Applied Pyrolysis
107
,
323
331
.
https://doi.org/10.1016/j.jaap.2014.03.017
.
Elledge
M. F.
,
Muralidharan
A.
,
Parker
A.
,
Ravndal
K. T.
,
Siddiqui
M.
,
Toolaram
A. P.
&
Woodward
K. P.
2018
Menstrual hygiene management and waste disposal in low and middle income countries – A review of the literature
.
International Journal Environmental Research and Public Health
15
,
2562
.
Erdumlu
N.
&
Ozipek
B.
2008
Investigation of regenerated bamboo fibre and yarn characteristics
.
FIBRES & TEXTILES in Eastern Europe
16
,
43
47
.
Ferguson
K. K.
,
Rosen
E. M.
,
Rosario
Z.
,
Feric
Z.
,
Calafat
A. M.
,
McElrath
T. F.
,
Vélez Vega
C.
,
Cordero
J. F.
,
Alshawabkeh
A.
&
Meeker
J. D.
2019
Environmental phthalate exposure and preterm birth in the PROTECT birth cohort
.
Environment International
132
,
105099
.
https://doi.org/10.1016/j.envint.2019.105099
.
Frank
S. E.
2020
Queering menstruation: trans and non-binary identity and body politics
.
Sociological Inquiry
90
,
371
404
.
https://doi.org/10.1111/soin.12355
.
Freidenfelds
L.
2009
The Modern Period: Menstruation in Twentieth-Century America
.
JHU Press
,
Baltimore, MD
.
Grose
R. G.
&
Grabe
S.
2014
Sociocultural attitudes surrounding menstruation and alternative menstrual products: the explanatory role of self-objectification
.
Health Care for Women International
35
,
677
694
.
https://doi.org/10.1080/07399332.2014.888721
.
Hait
A.
&
Powers
S. E.
2019
The value of reusable feminine hygiene products evaluated by comparative environmental life cycle assessment
.
Resources, Conservation & Recycling
150
,
104422
.
https://doi.org/10.1016/j.resconrec.2019.104422
.
IMARC
2021
Biodegradable Sanitary Napkins Market: Global Industry Trends, Share, Size, Growth, Opportunity and Forecast 2021–2026
.
Available from: https://www.imarcgroup.com/biodegradable-sanitary-napkins-market (accessed 14 December 2021)
.
Kathirvel
K. P.
&
Ramachandran
T.
2014
Development of antimicrobial feminine hygiene products using bamboo and aloevera fibers
.
Journal of Natural Fibers
11
,
242
255
.
https://doi.org/10.1080/15440478.2013.879548
.
Kaur
R.
,
Kaur
K.
&
Kaur
R.
2018
Menstrual hygiene, management, and waste disposal: practices and challenges faced by girls/women of developing countries
.
Journal of Environmental and Public Health
2018
,
1730964
.
https://doi.org/10.1155/2018/1730964
.
Kim
Y. J.
,
Kwon
A.
,
Jung
M. K.
,
Kim
K. E.
,
Suh
J.
,
Chae
H. W.
,
Kim
D. H.
,
Ha
S.
,
Seo
G. H.
&
Kim
H.-S.
2019
Incidence and prevalence of central precocious puberty in Korea: an epidemiology study based on a national database
.
The Journal of Pediatrics
208
,
221
228
.
https://doi.org/10.1016/j.jpeds.2018.12.022
.
Koh
D.
,
Chia
S. E.
,
1994
Health Concerns of Women at Work
. In:
Occupational Health in National Development
(
Jeyaratnam
J.
&
Chia
K. S.
eds.).
World Scientific Publishing Co
,
Singapore
, pp.
74
101
.
Krishna
A. B.
,
Harikrishnan
K. R.
,
Sreerag
S. R.
&
Sivaselvi
K.
2018
Design and Structural analysis of supporting structure for Banana fibre caking machine in sanitary pads manufacturing
.
Materials Today: Proceedings
5
,
18268
18274
.
https://doi.org/10.1016/j.matpr.2018.06.164
.
Kroesa
R.
1990
The Greenpeace Guide to Paper
.
Greenpeace
,
Vancouver
,
Canada
.
Kudagamage
C.
,
Chandrasisri
G. W. J.
&
Razmy
A. M. Z.
2002
Analysis of long-term trend in the banana sector of Sri Lanka
.
Annals of the Sri Lanka Department of Agriculture
4
,
21
32
.
Kuhmann
A. S.
,
Key
R.
,
Billingsley
C.
,
Shato
T.
,
Scroggins
S.
&
Teni
M.
2020
Students’ menstrual hygiene needs and school attendance in an Urban St. Louis, Missouri District
.
Journal of Adolescent Health
67
,
444
446
.
https://doi.org/10.1016/j.jadohealth.2020.05.040
.
Lee
A.
2012
Innovations in Sanitary Pads From Water Hyacinths
. .
Leena
S.
2016
A descriptive study on cultural practices about menarche and menstruation
.
Journal of Health and Allied Sciences NU
6
,
010
013
.
https://doi.org/10.1055/s-0040-1708631
.
Li
J.
,
Liu
Z.
,
Feng
C.
,
Liu
X.
,
Qin
F.
,
Liang
C.
,
Bian
H.
,
Qin
C.
&
Yao
S.
2021
Green, efficient extraction of bamboo hemicellulose using freeze-thaw assisted alkali treatment
.
Bioresource Technology
333
,
125107
.
https://doi.org/10.1016/j.biortech.2021.125107
.
Lin
N.
,
Ding
N.
,
Meza-Wilson
E.
,
Devasurendra
A. M.
,
Godwin
C.
,
Park
S. K.
&
Batterman
S.
2020
Volatile organic compounds in feminine hygiene products sold in the US market: a survey of products and health risks
.
Environment International
144
,
105740
.
https://doi.org/10.1016/j.envint.2020.105740
.
Lo
H. K. A.
&
Chan
K. Y. K.
2018
Negative effects of microplastic exposure on growth and development of Crepidula onyx
.
Environmental Pollution
233
,
588
595
.
https://doi.org/10.1016/j.envpol.2017.10.095
.
Lockley
G.
,
Kass
P.
,
Duque
N.
,
Chi
L.
,
Lee
L.
,
Lin
I.
,
Li
G.
&
Primavera
C.
2014
Enhancing the Lives of Young Girls
.
Team 60
.
Lilypads Global Enterprise Experience 2014
.
Luchese
C. L.
,
Engel
J. B.
&
Tessaro
I. C.
,
2021
Disposal, reusable and biodegradable hygiene products
. In:
Antimicrobial Textiles From Natural Resources
(
Mondal
I. H.
ed.).
Woodhead Publishing, Elsevier Ltd
,
Sawston, UK
.
Mahon
T.
&
Fernandes
M.
2010
Menstrual hygiene in South Asia: a neglected issue for WASH (water, sanitation and hygiene) programmes
.
Gender and Development
18
,
99
113
.
https://doi.org/10.1080/13552071003600083
.
MAPPINGDW
2013
KENYA/SWEDEN KARIN LISMAN ao: Janipad (2009-ONGOING)
. .
Mburu
N.
,
Rousseau
D. P. L.
,
van Bruggen
J. J. A.
&
Lens
P. N. L.
,
2015
Use of the Macrophyte Cyperus papyrus in Wastewater Treatment
. In:
The Role of Natural and Constructed Wetlands in Nutrient Cycling and Retention on the Landscape
(
Vymazal
J.
ed.).
Springer
.
https://doi.org/10.1007/978-3-319-08177-9_20
.
McVea
C.
&
Boyd
C. E.
1975
Effects of waterhyacinth cover on water chemistry, phytoplankton, and fish in ponds
.
Journal of Environmental Quality
4
,
375
378
.
https://doi.org/10.2134/jeq1975.00472425000400030020x
.
Medina-Perucha
L.
,
Jacques-Aviñó
C.
,
Valls-Llobet
C.
,
Turbau-Valls
R.
,
Pinzón
D.
,
Hernández
L.
,
Canseco
P. B.
,
López-Jiménez
T.
,
Lizarza
E. S.
,
Feliu
J. M.
&
Berenguera
A.
2020
Menstrual health and period poverty among young people who menstruate in the Barcelona metropolitan area (Spain): protocol of a mixed-methods study
.
BMJ Open
10
,
e035914
.
https://doi.org/10.1136/bmjopen-2019-035914
.
Musaazi
M. K.
,
Mechtenberg
A. R.
,
Nakibuule
J.
,
Sensenig
R.
,
Miyingo
E.
,
Makanda
J. V.
,
Hakimian
A.
&
Eckelman
M. J.
2015
Quantification of social equity in life cycle assessment for increased sustainable production of sanitary products in Uganda
.
Journal of Cleaner Production
96
,
569
579
.
https://doi.org/10.1016/j.jclepro.2013.10.026
.
Ngugi
M. N.
&
Nyaura
J. E.
2014
Demystifying the menstruation process among the Kenyan girl-child ‘A period of shame’: a socio-cultural perspective
.
International Journal of Science and Research
3
,
1077
1083
.
Nicole
W.
2013
A question for women's health: chemicals in feminine hygiene products and personal lubricants
.
Environmental Health Perspectives
122
,
A70
A75
.
https://doi.org/10.1289/ehp.122-A70
.
NIH
2021
National Center for Biotechnology Information
.
National Institute of Health
.
Available from: https://www.ncbi.nlm.nih.gov/ (accessed 2 November 2021)
.
Pattra
S.
&
Sittijunda
S.
2015
Optimization of factors affecting acid hydrolysis of water hyacinth stem (Eichhornia crassipes) for bio-hydrogen production
.
Energy Procedia
79
,
833
837
.
https://doi:10.1016/j.egypro.2015.11.574
.
Peberdy
E.
,
Jones
A.
&
Green
D.
2019
A study into public awareness of the environmental impact of menstrual products and product choice
.
Sustainability
11
,
473
.
https://doi.org/10.3390/su11020473
.
PMNCH
2020
Menstrual Hygiene and Health – A Call for Dignity, Rights and Empowerment
.
The Partnership for Maternal, Newborn & Child Health, World Health Organization
. .
Qin
H.
,
Diao
M.
,
Zhang
Z.
,
Visser
P. M.
,
Zhang
Y.
,
Wang
Y.
&
Yan
S.
2020
Responses of phytoremediation in urban wastewater with water hyacinths to extreme precipitation
.
Journal of Environmental Management
271
,
110948
.
https://doi.org/10.1016/j.jenvman.2020.110948
.
Rahman
A.
,
Sarkar
A.
,
Yadav
O. P.
,
Achari
G.
&
Slobodnik
J.
2021
Potential human health risks due to environmental exposure to nano and microplastics and knowledge gaps: a scoping review
.
Science of the Total Environment
757
,
143872
.
https://doi.org/10.1016/j.scitotenv.2020.143872
.
Rathod
A.
&
Kolhatkar
A.
2014
Analysis of physical characteristics of bamboo
.
International Journal of Research in Engineering and Technology
3
,
21
25
.
Rezania
S.
,
Park
J.
,
Din
M. F. M.
,
Taib
S. M.
,
Talaiekhozani
A.
,
Yadav
K. K.
&
Kamyab
H.
2018
Microplastics pollution in different aquatic environments and biota: a review of recent studies
.
Marine Pollution Bulletin
133
,
191
208
.
https://doi.org/10.1016/j.marpolbul.2018.05.022
.
Roddenberry Foundation
2022
About BabaPads
.
Available from: https://roddenberryfoundation.org/blog/awardee/banapads/ (accessed 9 September 2022)
.
Rodrigues
J. P.
,
Duarte
A. C.
,
Santos-Echeandía
J.
&
Rocha-Santos
T.
2018
Significance of interactions between microplastics and POPs in the marine environment: a critical overview
.
TrAC Trends in Analytical Chemistry
111
,
252
260
.
https://doi.org/10.1016/j.trac.2018.11.038
.
Rynk
R.
,
van de Kamp
M.
,
Wilson
G. B.
,
Singley
M. E.
,
Richard
T. L.
,
Kolega
J. J.
,
Gouin
F. R.
,
Laliberty
L.
, Jr.
,
Kay
D.
,
Murphy
D. W.
,
Hoitink
H. A. J.
&
Brinton
W. F.
1992
On-Farm Composting Handbook, NRAES-54
.
Northeast Regional Agricultural Engineering Service (NRAES)
,
Ithaca, NY
.
Saathi
2021
Eco-Friendly, Period
.
Available from: https://saathipads.com/ (accessed 1 August 2021)
.
Scranton
A.
2013
Chem Fatale: Potential Health Effects of Toxic Chemicals in Feminine Care Products
.
Women's Voices for the Earth
. .
Shaikh
T.
,
Chaudhari
S.
&
Varma
A.
2012
Viscose rayon: a legendary development in the manmade textile
.
International Journal of Engineering Research and Application
2
,
675
680
.
SHE
2021
Sustainable Health Enterprises
.
Available from: https://sheinnovates.com/ (accessed 1 August 2021)
.
Shin
J. H.
&
Ahn
Y. G.
2007
Analysis of polychlorinated dibenzo-p-dioxins and dibenzo-furans in sanitary products of women
.
Textile Research Journal
77
,
597
603
.
https://doi.org/10.1177%2F0040517507078786
.
Shoemaker
D.
2008
Proper procedure for sanitary napkin disposal
.
Cleaning and Maintenance Management
45
,
33
37
.
Shrestha
P.
,
Sadiq
M. B.
&
Anal
A. K.
2021
Development of antibacterial biocomposites reinforced with cellulose nanocrystals derived from banana pseudostem
.
Carbohydrate Polymer Technologies and Applications
2
,
100112
.
https://doi.org/10.1016/j.carpta.2021.100112
.
Sieja
K.
,
von Mach-Szczypiniski
J. V.
&
von Mach-Szczypinski
J. V.
2018
Health effect of chronic exposure to carbon disulfide (CS2) on women employed in viscose industry
.
Medycyna Pracy
69
,
329
335
.
https://doi.org/10.13075/mp.5893.00600
.
Sikora
L.
1998
Benefits and drawbacks to composting organic by-products
. In:
Beneficial Co-Utilization of Agricultural, Municipal and Industrial By-Products
(S. Brown, J. S. Angle & L. Jacobs, eds).
Kluwer Academic Publishers
,
Environmental Science
. pp.
69
77
.
https://doi.org/10.1007/978-94-011-5068-2_6.
Sommer
M.
,
Kjellén
M.
&
Pensulo
C.
2013
Girls’ and women's unmet needs for menstrual hygiene management (MHM): the interactions between MHM and sanitation systems in low-income countries
.
Journal of Water Sanitation and Hygiene for Development
3
,
283
297
.
https://doi.org/10.2166/washdev.2013.101
.
Sommer
M.
,
Hirsch
J. S.
,
Nathanson
C.
&
Parker
R. G.
2015
Comfortably, safely, and without shame: defining menstrual hygiene management as a public health issue
.
American Journal of Public Health
105
,
1302
1311
.
https://doi.org/10.2105/ajph.2014.302525
.
Sommer
M.
,
Gruer
C.
,
Smith
R. C.
,
Maroko
A.
&
Hopper
K.
2020
Menstruation and homelessness: challenges faced living in shelters and on the street in New York City
.
Health & Place
66
,
102431
.
https://doi.org/10.1016/j.healthplace.2020.102431
.
Soni
S.
,
Srivastava
M.
,
Jha
S.
&
Sornapudi
S. D.
2019
Working women's perspective on sustainable practices for management of menstruation
.
Journal of Community Mobilization and Sustainable Development
14
,
267
270
.
Spizzirri
G.
,
Eufrásio
R.
,
Pereira Lima
M. C.
,
de Carvalho Nunes
H. R.
,
Kreukels
B. P. C.
,
Steensma
T. D.
&
Najjar Abdo
C. H.
2021
Proportion of people identified as transgender and non-binary gender in Brazil
.
Scientific Reports
11
,
2240
.
https://doi.org/10.1038/s41598-021-81411-4
.
Subash
M. C.
&
Muthiah
P.
2021
Eco-friendly degumming of natural fibers for textile applications: a comprehensive review
.
Cleaner Engineering and Technology
5
,
100304
.
https://doi.org/10.1016/j.clet.2021.100304
.
Takebayashi
T.
,
Omae
K.
,
Ishizuka
C.
,
Nomiyama
T.
&
Sakurai
H.
1998
Cross sectional observation of the effects of carbon disulphide on the nervous system, endocrine system, and subjective symptoms in rayon manufacturing workers
.
Occupational and Environmental Medicine
55
,
473
479
.
http://dx.doi.org/10.1136/oem.55.7.473
.
Tanpichai
S.
,
Biswas
S. K.
,
Witayakran
S.
&
Yano
H.
2019
Water hyacinth: a sustainable lignin-poor cellulose source for the production of cellulose nanofibers
.
ACS Sustainable Chemistry & Engineering
7
,
18884
188893
.
https://doi.org/10.1021/acssuschemeng.9b04095
.
Technavio
2022
Organic Sanitary Napkins Market by Distribution Channel, Type, and Geography – Forecast and Analysis 2022–2026
. .
The World Bank
2018
Menstrual Hygiene Management Enables Women and Girls to Reach Their Full Potential
. .
The World Bank
2021
Population, Female (% of Total Population)
.
Available from: https://data.worldbank.org/indicator/SP.POP.TOTL.FE.ZS (accessed 14 October 2021)
.
Toft
J. D.
,
Simenstad
C. A.
,
Cordell
J. R.
&
Grimaldo
L. F.
2003
The effects of introduced water hyacinth on habitat structure, invertebrate assemblages, and fish diets
.
Estuaries and Coasts
26
,
746
758
.
https://doi.org/10.1007/BF02711985
.
Tudu
P. N.
2019
Saathi sanitary pads: eco-friendly pads which will make you go bananas!
.
Journal of Philanthropy and Marketing
25
,
e1667
.
https://doi.org/10.1002/nvsm.1667
.
Tull
K.
2019
Period Poverty Impact on the Economic Empowerment of Women
.
K4D Helpdesk Report 536
.
Institute of Development Studies
,
Brighton
,
UK
. .
Umeora
O. U.
&
Egwuatu
V. E.
2008
Menstruation in rural Igbo women of south east Nigeria: attitudes, beliefs and practices
.
African Journal of Reproductive Health
12
,
109
115
.
United Nations
.
2021
Water, Sanitation and Hygiene
. .
Velasco Perez
M.
,
Sotelo Navarro
P. X.
,
Vazquez Morrilas
A.
,
Espinosa Valdemar
R. M.
&
Lopez Araiza
J. P. H.
2021
Waste management and environmental impact of absorbent hygiene products: a review
.
Waste Management & Research: The Journal for A Sustainable Circular Economy
39
,
767
783
.
https://doi.org/10.1177/0734242X20954271
.
Vishwakarma
D.
,
Puri
P.
&
Sharma
S. K.
2021
Interlinking menstrual hygiene with women's empowerment and reproductive tract infections: evidence from India
.
Clinical Epidemiology and Global Health
10
,
100668
.
https://doi.org/10.1016/j.cegh.2020.11.001
.
Vostral
S. L.
2018
Toxic Shock: A Social History (Biopolitics, 6)
.
New York University Press
,
New York
.
Weidemann
H. G.
&
Bayer
G.
1983
Papyrus, the paper of ancient Egypt
.
Analytical Chemistry
55
,
1220A
1230A
.
Weissfeld
A. S.
2010
The history of tampons: from ancient times to an FDA-regulated medical device
.
Clinical Microbiology Newsletter
32
,
73
76
.
https://doi.org/10.1016/j.clinmicnews.2010.04.003
.
Weuve
J.
,
Hauser
R.
,
Calafat
A. M.
,
Missmer
S. A.
&
Wise
L. A.
2010
Association of exposure to phthalates with endometriosis and uterine leiomyomata: findings from NHANES, 1999–2004
.
Environmental Health Perspectives
118
,
825
832
.
https://doi.org/10.1289/ehp.0901543
.
Wijaya
C. J.
,
Ismadji
S.
,
Aparamarta
H. W.
&
Gunawan
S.
2019
Optimization of cellulose nanocrystals from bamboo shoots using response surface methodology
.
Heliyon
5
,
e02807
.
https://doi.org/10.1016/j.heliyon.2019.e02807
.
Wong
E. Y.
,
Ray
R. M.
,
Gao
D.-L.
,
Wernli
K. J.
,
Li
W.
,
Fitzgibbons
E. D.
,
Camp
J. E.
,
Astrakianakis
G.
,
Heagerty
P. J.
,
De Roos
A. J.
,
Holt
V. L.
,
Thomas
D. B.
&
Checkoway
H.
2009
Dust and chemical exposures, and miscarriage risk among women textile workers in Shanghai, China
.
Occupational & Environmental Medicine
66
,
161
168
.
http://dx.doi.org/10.1136/oem.2008.039065
.
WVE
2014
Testing Reveals Toxic Chemicals in Procter & Gamble's Always Pads
.
Women's Voices for the Earth
. .
Yang
Z.
,
Xu
S.
,
Ma
X.
&
Wang
S.
2008
Characterization and acetylation behavior of bamboo pulp
.
Wood Science and Technology
42
,
621
632
.
https://doi.org/10.1007/s00226-008-0194-5
.
Yilmaz
S. K.
,
Bohara
A. K.
&
Thapa
S.
2021
The stressor in adolescence of menstruation: coping strategies, emotional stress & impacts on school absences among young women in Nepal
.
International Journal of Environmental Research and Public Health
18
,
8894
.
https://doi.org/10.3390/ijerph18178894
.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits copying, adaptation and redistribution, provided the original work is properly cited (http://creativecommons.org/licenses/by/4.0/).