Model for projecting the generation of used disposable diapers in the era of depopulation and aging in Japan

Abstract

Japan has entered a period of depopulation and aging ahead of any other country. One concern in an aging population is increases in the generation of used disposable diapers. The use of disposable diapers, which are largely composed of plastic, can be an important issue as we work towards building a carbon-free society and break away from using fossil-derived plastics. This study aimed to develop a model to project the future generation of used disposable diapers in each municipality in Japan through 2045 and to identify the effects on municipal solid waste (MSW) management. We revealed the per capita generation of used disposable diapers, distinguishing disposable diaper products, urine and faeces in an online survey of 2000 respondents. The generation of used disposable diapers was estimated to increase in general, but the amount was projected to decrease in rural areas where the population of elderly people would decline. The proportion of used disposable diapers in combustible waste was projected to increase by 2045 in almost all municipalities of Mie Prefecture. Based on the scenario in which disposable diaper products would become lighter in the future because of technical improvements, we concluded that the impact of the decrease in the lower heating value (LHV) of used disposable diapers on the incineration process cannot be ignored in the future.

Keywords

Disposable diaper depopulation aging plastic municipal solid waste incineration

Introduction

Populations in 55 countries are expected to decrease by 2050 as compared to 2019 (United Nations, 2019), and Japan has already entered a period of depopulation and aging (National Institute of Population and Social Security Research, 2019). The population in Japan peaked at 128 million in 2008 and began to decline thereafter. The declining numbers of young (0–14 years old) and working-age (15–64 years old) people are the main reason for the decline of the total population. At the same time, the elderly (65 years old and over) population is increasing. According to the 2015 census, Japan’s aging rate (the ratio of the elderly population to the total population) was 26.6% (National Institute of Population and Social Security Research, 2018a). The National Institute of Population and Social Security Research reported that the elderly population would continue to increase until 2042, after which the young, working-age and elderly populations would all decline, but the aging rate would stabilize at about 36–38%. These are national statistics, but aging is progressing even more rapidly in some regions. As of 2015, 221 of 1747 of Japan’s municipalities had an aging rate of greater than 40%.

Depopulation and aging may have various impacts on municipal solid waste (MSW) management. Waste collection may become more inefficient because of the decrease in population density. Depopulation may lead to decreased tax revenues for municipalities, which may need to suppress MSW management costs. Many older people may have trouble walking to their waste collection points. At the same time, more disposable diapers may be used by elderly people and enter the MSW stream.

In recent years, attention has been focused on the environmental impacts caused by disposable diapers, and several life cycle assessments of disposable diapers have been reported (Cordella et al., 2015; Itsubo et al., 2020; Mendoza et al., 2018; Mirabella et al., 2013). However, since the generation of used disposable diapers, especially for adults, has not yet become an important issue worldwide, only a few studies have estimated the amount of used disposable diapers currently being generated. Tsuchida et al. (2017) determined the usage of disposable adult diapers at 28 nursing care facilities and eight hospitals, as well as that of disposable baby diapers at 108 childcare facilities in Japan. However, they did not cover the usage of disposable diapers at home. Generally, care facilities cater to people with higher needs, and the usage of disposable adult diapers by mild care recipients was not investigated in that study. Takafuji et al. (2017) analysed the physical composition of household waste sampled at the two incineration facilities to estimate the amount of used disposable diapers generated at home and identified the current flows of disposable diapers used by adults and children in Hiroshima Prefecture, Japan as a case study. The Ministry of the Environment (2020), Japan published a guideline that helped estimate the generation of used disposable diapers for each municipality referring to Tsuchida et al. (2017). The guideline, however, does not reflect the proportion of care recipients who use disposable diapers at home or the per capita generation of disposable diapers used at home.

We were interested in the amount of used disposable diapers being generated depending on the attributes of users, regardless of whether they are at home or in care facilities. Furthermore, we were interested in the amount of disposable diapers that will be generated in the future and how it will affect future MSW management because no studies have yet been conducted to estimate the amount of used disposable diapers generated in the future.

We aimed to clarify the per capita generation of disposable diapers for adults and children in Japan through a nationwide online survey on the use of disposable diapers and develop a model for projecting the generation of used disposable diapers in each municipality in Japan through 2045. We estimated the generation of used disposable diapers in 29 municipalities in Mie Prefecture as a case study. In addition to projecting the generation of used disposable diapers by 2045, we clarified the ratio of used disposable diapers to combustible waste, and discussed the quantitative and qualitative effects of used disposable diapers on the incineration process.

Materials and methods

Online survey on diaper usage

To identify the proportion of the population using disposable diapers in the infant and elderly populations, as well as the per capita generation of used disposable diapers, we conducted an online survey in March 2021 through the system of Rakuten Insight, Inc. The company was founded in 2002 and had approximately 2.2 million registered members in Japan as of 2021 for the purpose of market research. It has provided online survey systems to about 1000 customers, including manufacturers, advertising companies, governments and research institutes. Headquartered in Tokyo, Rakuten Group, including Rakuten Insight, Inc., is certified in information security management (ISO27001) and strictly manages customer information. Registered members who matched the survey target were randomly selected based on their attributes and were asked to respond to the online survey. The members responded to the online survey only after agreeing to the condition that the survey may include personal information about them and their family. Before participating in the survey, they were informed that the contents of their answers would be used only for the purposes of this analysis and that they would not be personally identified in their responses.

The online survey targeted people aged 18 to 69 years nationwide in Japan who were registered as part of a special panel related to diseases. The screening condition was that there was one person requiring long-term care in the household aged 65 years or over (excluding the case where the respondent was the person requiring long-term care; Table 1). We assumed that disposable adult diapers were used by those who have qualified for long-term care in the insurance system (Ministry of Health, Labour and Welfare, 2016) and were aged 65 years or over. Persons requiring long-term care were assigned to seven categories: support level 1, support level 2, care level 1, care level 2, care level 3, care level 4 and care level 5 (Table 2) (Shinjuku City Long-term Care Insurance Division, 2018). A total of 1000 respondents, 142 or 143 per category, was set as the target number of responses to answer the questions shown in Table 1.

Table 1.

Questions in the adult diaper survey.

Screening survey

S1a: How old are you?
S2a: What prefecture do you live in?
S3a: How many long-term support and care recipients do you have in the family?
S4a: Are you a long-term support and care recipient?
S5a: How old is the care recipient?
S6a: What level is the care recipient qualified at?

Main survey

Q1a: Where does the care recipient live?
Q2a: Does the care recipient usually use disposable diapers?
Q3a: Does the care recipient use disposable diapers in the daytime?
Q4a: How many outer and inner diapers does the care recipient use in the daytime?
Q5a: How frequently does the care recipient urinate on a disposable diaper in the daytime?
Q6a: How frequently does the care recipient excrete faeces on a disposable diaper in the daytime?
Q7a: Does the care recipient use disposable diapers at night?
Q8a: How many outer and inner diapers does the care recipient use at night?
Q9a: How frequently does the care recipient urinate on a disposable diaper at night?
Q10a: How frequently does the care recipient excrete faeces on a disposable diaper at night?
Q11a: How are the excreted faeces disposed of?

Table 2.

Types of long-term support and care levels and general indicative conditions (Shinjuku City Long-term Care Insurance Division, 2018).

Types	General indicative conditions
Support level 1	✓ Can rise, walk and perform most of essential daily life activities by himself/herself ✓ Needs some long-term support for task-based activities in daily life such as cooking, shopping and taking oral medicine
Support level 2	✓ Has slightly lower ability to handle task-based activities in daily life and requires more long-term support than in support level 1
Care level 1	✓ Faces difficulty in performing essential daily life activities by himself/herself ✓ Has lower ability to handle task-based activities in daily life than in support level 2 ✓ Requires occasional long-term care
Care level 2	✓ Requires more long-term care to be able to perform essential daily life activities than in care level 1
Care level 3	✓ Significantly lower abilities to perform essential daily life activities and task-based activities than in care level 2 ✓ Requires almost constant long-term care
Care level 4	✓ Lower abilities to perform any activities than in care level 3 ✓ Faces difficulty in living without constant long-term care
Care level 5	✓ Lower abilities to perform any activities than care in level 4 ✓ Requires constant long-term care to live

The online survey on the usage of disposable baby diapers targeted women aged 20 to 49 years nationwide in Japan who were registered as part of a special panel related to students and children. The screening condition was that there was one child under the age of 5 in the household (Table 3). The children were assigned to five categories: 0-year-old, 1-year-old, 2-year-old, 3-year-old and 4-year-old. A total of 1000 respondents, 200 per category, was set as the target number of responses to answer the questions shown in Table 3.

Table 3.

Questions in the baby diaper survey.

Screening survey

S1b: What is your gender?
S2b: How old are you?
S3b: What prefecture do you live in?
S4b: How many children aged 0–4 years old live in your household?
S5b: How old is the child?

Main survey

Q1b: What is the weight of the child?
Q2b: Does the child usually use disposable diapers?
Q3b: Does the child use disposable diapers in the daytime?
Q4b: How many diapers does the child use in the daytime?
Q5b: How frequently does the child urinate on a disposable diaper in the daytime?
Q6b: How frequently does the child excrete faeces on a disposable diaper in the daytime?
Q7b: Does the child use disposable diapers at night?
Q8b: How many diapers does the child use at night?
Q9b: How frequently does the child urinate on a disposable diaper at night?
Q10b: How frequently does the child excrete faeces on a disposable diaper at night?
Q11b: How are the excreted faeces disposed of?

Both of the online surveys started on 24 March 2021 and ended when the target number of responses had been reached. Responses with inconsistent answers were invalidated and excluded from the analysis. Responses were collected from all 47 prefectures in Japan for both the adult diaper survey and the baby diaper survey. The number of valid responses was 987 in the adult diaper survey and 986 in the baby diaper survey. A summary of the survey results compiling the answers to the questions in Tables 1 and 3 is shown in the Supplemental Appendix.

Per capita generation of used disposable diapers

In the calculation of per capita generation of used disposable diapers, we distinguished between ‘consumption of diapers’ and ‘excrement of urine and faeces’ as explanatory variables.

Disposable adult diapers are divided into two types in Japan: an outer diaper (pants type and tape type) and an inner diaper (pad type). Generally, the inner diaper is used by being attached to the inside of the outer diaper. There are three main advantages of using a combination of separate inner and outer diapers: (1) inner diapers are easier to change and reduce the burden of labour, (2) the use of inner diapers, which are less expensive than outer diapers, reduces costs and (3) less waste is generated. An all-in-one combination of outer and inner diapers is not produced or used in Japan; that is, all manufacturers of disposable adult diapers currently sell outer diapers to consumers separately from inner diapers. In this study, the consumption amounts of outer diapers and inner diapers were calculated separately because the consumption of outer diapers and inner diapers differ depending on the type of user. The number of diapers consumed by long-term care recipients was calculated by distinguishing between daytime use and overnight use as shown in equations (1) and (2).

\bar{O_{x}} = w_{O} \cdot \frac{1}{n} \cdot \sum_{i = 1}^{n} (O_{daytime_x i} + O_{overnight_x i})

(1)

\bar{I_{x}} = w_{I} \cdot \frac{1}{n} \cdot \sum_{i = 1}^{n} (I_{daytime_x i} + I_{overnight_x i})

(2)

where $\bar{O_{x}}$ is the mean per capita consumption of outer diaper products used by long-term care recipients with care level x (g person⁻¹ day⁻¹), $w_{O}$ is the weight of an outer diaper product (g diaper⁻¹), $O_{daytime_x i}$ is the number of outer diapers used in the daytime by long-term care recipient i with level x (diaper person⁻¹ day⁻¹), $O_{overnight_x i}$ is the number of outer diapers used at night by long-term care recipient i with level x (diaper person⁻¹ day⁻¹), $\bar{I_{x}}$ is the mean per capita consumption of inner diapers used by long-term care recipients with level x (g person⁻¹ day⁻¹), $w_{I}$ is the weight of an inner diaper product (g diaper⁻¹), $I_{daytime_x i}$ is the number of inner diapers used in the daytime by long-term care recipient i with level x (diaper person⁻¹ day⁻¹), and $I_{overnight_x i}$ is the number of inner diapers used at night by long-term care recipient i with level x (diaper person⁻¹ day⁻¹). The results of the online survey were applied as $O_{daytime_x i}$ , $O_{overnight_x i}$ , $I_{daytime_x i}$ , and $I_{overnight_x i}$ . Although various diaper products are currently distributed according to the degree of long-term care required, physical size and gender, we used the average weight in our calculations. $w_{O}$ and $w_{I}$ were calculated as 85 g diaper⁻¹ and 51 g diaper⁻¹, respectively, by using data from the Japan Hygiene Products Industry Association (2016); 121,692 tonnes of outer diapers (1.43 billion diapers) and 173,487 tonnes of inner diapers (3.42 billion diapers) were produced in 2015.

Two-thirds of excrement was assumed to be discharged in the daytime and one-third overnight. The volumes of urine and faeces discharged were determined with equations (3) and (4), respectively.

\bar{U_{x}} = \frac{1}{n} \cdot \sum_{i = 1}^{n} (U_{A} \cdot \frac{2}{3} \cdot U_{daytime_x i} + U_{A} \cdot \frac{1}{3} \cdot U_{overnight_x i})

(3)

\bar{F_{x}} = \frac{1}{n} \cdot \sum_{i = 1}^{n} {(F_{A} \cdot \frac{2}{3} \cdot F_{daytime_x i} + F_{A} \cdot \frac{1}{3} \cdot F_{overnight_x i}) \cdot d_{x i}}

(4)

where $\bar{U_{x}}$ is the mean volume of urine discharged on diapers by long-term care recipients with care level x (g person⁻¹ day⁻¹), $U_{A}$ is the standard volume of urine discharged per day by an adult (g person⁻¹ day⁻¹), $U_{daytime_x i}$ is the discharge factor of urine on diapers in the daytime by long-term care recipient i with level x (g person⁻¹ day⁻¹), $U_{overnight_x i}$ is the discharge factor of urine on diapers at night by long-term care recipient i with level x (g person⁻¹ day⁻¹), $\bar{F_{x}}$ is the mean volume of faeces discharged on diapers by long-term care recipients with level x (g person⁻¹ day⁻¹), $F_{A}$ is the standard volume of faeces discharged per day by an adult (g person⁻¹ day⁻¹), $F_{daytime_x i}$ is the discharge factor of faeces on diapers in the daytime by long-term care recipient i with level x (g person⁻¹ day⁻¹), $F_{overnight_x i}$ is the discharge factor of faeces on diapers at night by long-term care recipient i with level x (g person⁻¹ day⁻¹), and $d_{x i}$ is the disposal factor of faeces discharged on diapers by long-term care recipient i with level x. $U_{A}$ and $F_{A}$ were assumed to be 1500 g person⁻¹ day⁻¹ and 100 g person⁻¹ day⁻¹, respectively. The discharge factors ( $U_{daytime_x i}$ , $U_{overnight_x i}$ , $F_{daytime_x i}$ and $F_{overnight_x i}$ ) and the disposal factor ( $d_{x i}$ ) were derived from answers obtained in the online survey (Tables 4 and 5).

Table 4.

Frequency of excreting on diapers and the corresponding discharge factor.

Frequency of excreting on diapers	Discharge factor
Frequency of excreting on diapers	Urine	Faeces
100% on diapers (0% on the toilet)	1.0	1.0
80% on diapers (20% on the toilet)	0.8	0.8
60% on diapers (40% on the toilet)	0.6	0.6
40% on diapers (60% on the toilet)	0.4	0.4
20% on diapers (80% on the toilet)	0.2	0.2
0% on diapers (100% on the toilet)	0.1	0
Often not excreting at night^a	0	0
Not using diapers	0	0

An option for the question at night.

Table 5.

Methods of faeces disposal and the corresponding disposal factor.

Disposal method	Disposal factor
With diapers	1.0
In the toilet	0
Defecate sitting on the toilet	0

The per capita generation of used disposable adult diapers was calculated by summing $O_{x}$ $I_{x}$ , $U_{x}$ and $F_{x}$ (equation (5)):

M_{A x} = \bar{O_{x}} + \bar{I_{x}} + \bar{U_{x}} + \bar{F_{x}}

(5)

where $M_{A x}$ is per capita generation of used disposal adult diapers by long-term care recipients with care level x (g person⁻¹ day⁻¹).

Per capita generation of used disposable baby diapers was calculated considering the change in the size of disposable diapers and the amount of excrement in line with a child’s growth. As was the case with disposable adult diapers, the number of diapers consumed by children was calculated based on a distinction between daytime use and overnight use (equation (6)):

\bar{D_{y}} = \frac{1}{n} \cdot \sum_{j = 1}^{n} {(D_{daytime_y j} + D_{overnight_y j}) \cdot w_{D y}}

(6)

where $\bar{D_{y}}$ is the mean consumption of disposable diapers used by y-year-old children (g person⁻¹ day⁻¹), $D_{daytime_y j}$ is the number of disposable diapers used in the daytime by y-year-old child j (diaper person⁻¹ day⁻¹), $D_{overnight_y j}$ is the number of disposable diapers used at night by y-year-old child j (diaper person⁻¹ day⁻¹), and $w_{D y}$ is the weight of the disposable diaper product for y-year-old children (g diaper⁻¹). Table 6 shows the size and weight of disposable diapers for 0- to 4-year-olds, which were calculated by referring to 58 types of children’s diaper products distributed in Japan.

Table 6.

Size and weight of disposable baby diaper products before use.

Age (y, years)	Size	Weight ( $w_{D y}$ , g diaper⁻¹)
0	M	29
1	M	29
2	L	31
3	XL	35
4	XL	35

Two-thirds of daily excrement was assumed to be discharged in the daytime and one-third overnight (equations (7) and (8)).

\bar{U_{y}} = \frac{1}{n} \cdot \sum_{j = 1}^{n} (U_{B y} \cdot \frac{2}{3} \cdot U_{daytime_y i} + U_{B y} \cdot \frac{1}{3} \cdot U_{overnight_y i})

(7)

\bar{F_{y}} = \frac{1}{n} \cdot \sum_{j = 1}^{n} {(F_{B y} \cdot \frac{2}{3} \cdot F_{daytime_y i} + F_{B y} \cdot \frac{1}{3} \cdot F_{overnight_y i}) \cdot d_{y i}}

(8)

where $\bar{U_{y}}$ is the mean volume of urine discharged on diapers by y-year-olds (g person⁻¹ day⁻¹), $U_{B y}$ is the standard volume of urine discharged per day by y-year-old children (g person⁻¹ day⁻¹), $U_{daytime_y j}$ is the discharge factor of urine on diapers in the daytime by y-year-old child j (g person⁻¹ day⁻¹), $U_{overnight_y j}$ is the discharge factor of urine on diapers at night by y-year-old child j (g person⁻¹ day⁻¹), $\bar{F_{y}}$ is the mean volume of faeces discharged on diapers by y-year-old children (g person⁻¹ day⁻¹), $F_{B y}$ is the standard volume of faeces discharged per day by y-year-old children (g person⁻¹ day⁻¹), $F_{daytime_y j}$ is the discharge factor of faeces on diapers in the daytime by y-year-old child j (g person⁻¹ day⁻¹), $F_{overnight_y j}$ is the discharge factor of faeces on diapers at night by y-year-old child j (g person⁻¹ day⁻¹), and $d_{y j}$ is the disposal factor of faeces discharged on diapers by y-year-old child j. Table 7 shows the standard volume of urine and faeces discharged per child ( $U_{B y}$ and $F_{B y}$ ). The values were estimated by referring to the Japan Hygiene Products Industry Association (2008b) and Haga and Sakata (2007). The discharge factors ( $U_{daytime_y j}$ , $U_{overnight_y j}$ , $F_{daytime_y j}$ and $F_{overnight_y j}$ ) and the disposal factor ( $d_{y j}$ ) were derived from the answers given in the online survey (Tables 4 and 5).

Table 7.

Standard volume of urine and faeces discharged by 0- to 4-year-olds.

Age (y, years)	Urine ( $U_{B y}$ , g person⁻¹ day⁻¹)	Faeces ( $F_{B y}$ , g person⁻¹ day⁻¹)
0	400	60
1	500	70
2	600	80
3	700	90
4	800	100

Generation of used disposable baby diapers per capita was calculated by summing $D_{y}$ , $U_{y}$ and $F_{y}$ (equation (9)):

M_{B y} = \bar{D_{y}} + \bar{U_{y}} + \bar{F_{y}}

(9)

where $M_{B y}$ is per capita generation of used disposable diapers by y-year-old children (g person⁻¹ day⁻¹).

Projection of used disposable diapers generated

Future generation of used disposable diapers was estimated by multiplying the population of disposable diaper users and the per capita generation. The procedures for adult and children’s diapers are described below.

The amount of used disposable diapers generated by adults was estimated with equations (10) and (11), taking into account the seven care levels and the six age groups.

N_{t_a x} = \sum_{k} (N_{t_a k} \cdot p_{a k x})

(10)

M_{t_A a} = \sum_{x} (N_{t_a x} \cdot p_{x} \cdot M_{A x}) / 10^{6}

(11)

where $N_{t_a x}$ is the population of long-term care recipients with care level x in municipality a in year t (person), $N_{t_a k}$ is the projected population of age group k in municipality a in year t (person), $p_{a k x}$ is the proportion of long-term care recipients with level x in age group k in municipality a in 2015 (person person⁻¹) (Ministry of Health, Labour and Welfare, 2021), $M_{t_A a}$ is the amount of used disposable adult diapers generated in municipality a in year t (t day⁻¹) and $p_{x}$ is the proportion of long-term care recipients with level x who use disposable adult diapers (person person⁻¹). Age group k is divided into the following six groups: 65–69, 70–74, 75–79, 80–84, 85–89 and over 90. $N_{t_a k}$ was cited from a report on the estimated population of age groups in 5-year increments for each municipality of Japan through 2045 (National Institute of Population and Social Security Research, 2018b). The amount of used disposable diapers generated by long-term care recipients aged 64 years or under was excluded from the projection because we focused on aging in this study to project the generation of used disposable adult diapers. The amount of used disposable diapers generated by users who were not qualified for long-term care in the insurance system was also excluded because the amount would be relatively small, and it was very difficult to identify that population. The results of the online survey were used to determine $p_{a k x}$ and $p_{x}$ , and they were assumed to be constant in the future. The percentage of those who used cloth diapers in the online survey was also added to the percentage of people who would use disposable diapers in the future.

The amount of used disposable diapers generated by children was estimated with equation (12):

M_{t_B a} = \frac{1}{5} \cdot \sum_{y} (N_{t_{a 0 - 4}} \cdot p_{y} \cdot M_{B y}) / 10^{6}

(12)

where $M_{t_B a}$ is the amount of used disposable baby diapers generated in municipality a in year t (tonnes day⁻¹), $N_{t_{a 0 - 4}}$ is the projected population of the age group from 0 to 4 years old in municipality a in year t (person), and $p_{y}$ is the proportion of y-year-olds who used disposable baby diapers in the online survey (person person⁻¹). $N_{t_{a 0 - 4}}$ was cited from the population projected by the National Institute of Population and Social Security Research (2018b). $p_{y}$ was assumed to be constant in the future.

Projection of combustible waste generated

Used disposable diapers are generally managed as combustible waste in Japan. Some used disposable diapers generated in nursing care facilities and hospitals are managed as industrial waste, but all used disposable diapers generated were assumed to be managed as combustible MSW in this study regardless of the source. The amount of combustible waste generated was estimated by distinguishing between the amount of used disposable diapers and the amount of combustible waste excluding used disposable diapers (equations (13) and (14)). The per capita generation of combustible waste excluding used disposable diapers was calculated with the amount of combustible waste generated from 2013 to 2017 and the estimated amount of used disposable diapers generated from 2013 to 2017.

M_{t_C^{'} a} = \frac{1}{5} \cdot p_{t_a} \cdot \sum_{t = 2013}^{2017} {(\begin{array}{l} M_{t_I a} + M_{t_R a} \\ - M_{t_A a} - M_{t_B a} \end{array}) / p_{t_a}}

(13)

M_{t_C a} = M_{t_A a} + M_{t_B a} + M_{t_C^{'} a}

(14)

where $M_{t_C^{'} a}$ is the amount of combustible waste generated excluding used disposable diapers in municipality a in year t (tonnes day⁻¹), $p_{t_a}$ is the total population of municipality a in year t (person), $M_{t_I a}$ is the amount of combustible waste treated at incineration facilities (tonnes day⁻¹), $M_{t_R a}$ is the amount of combustible waste treated at refuse derived fuel (RDF) production facilities (tonnes day⁻¹), $p_{t_a}$ is the total population of municipality a in year t (person) and $M_{t_C a}$ is the estimated amount of combustible waste generated (tonnes day⁻¹).

Lower heating value (LHV) of used disposable diaper and combustible waste

Table 8 shows the properties of disposable diaper products for adults and children, which are composed of pulp, superabsorbent polymer (SAP), polyethylene (PE), polypropylene (PP) and polystyrene (PS). The chemical composition of pulp retrieved from an outer diaper and an inner diaper (n = 3 of each) was analysed with a J-Science MICRO CORDER JM10 and JMA10 to identify the concentration of carbon, hydrogen and nitrogen on a dry basis. The LHV of pulp and SAP was calculated with equation (15), known as Steuer’s equation (Ibikunle et al., 2019), assuming a moisture content of 8%:

\begin{array}{l} l_{q} = 339.4 \cdot (C_{q} - 3 \cdot \frac{O_{q}}{8}) + 238.8 \cdot 3 \cdot \frac{O_{q}}{8} \\ + 1445.6 \cdot (H_{q} - \frac{O_{q}}{16}) + 104.8 \cdot S_{q} - 25 \cdot (9 \cdot H_{q} + W_{q}) \end{array}

(15)

Table 8.

Properties of disposable diaper products for adults and children.

Properties	Pulp	SAP	PE	PP	PS
Chemical composition (%)
Carbon (C_q)	42.5	37.9	85.7	85.7	92.3
Hydrogen (H_q)	6.6	4.2	14.3	14.3	7.7
Nitrogen (N_q)	0.3	−	−	−	−
Oxygen (O_q)	50.6	33.7	−	−	−
Sodium (Na_q)	−	24.2	−	−	−
Moisture content (W_q, %)	8.0	8.0	3.0	3.0	3.0
LHV on wet basis (l_q, kJ kg⁻¹)	14,020	12,392	41,427	39,487	37,240
Physical composition (%)
Adult diapers^a (m_Aq)	52.2	19.8	5.6	16.8	5.6
Baby diapers^a (m_Bq)	33.3	33.3	6.7	20.0	6.7

SAP: superabsorbent polymer; PE: polyethylene; ^cPP: polypropylene; ^dPS: polystyrene.

Itsubo et al. (2020).

where $l_{q}$ is the LHV of component q on a wet basis (kJ kg⁻¹), $C_{q}$ is the carbon concentration of component q on a wet basis (%), $O_{q}$ is the oxygen concentration of component q on a wet basis (%), $H_{q}$ is the hydrogen concentration of component q on a wet basis (%), $S_{q}$ is the sulfur concentration of component q on a wet basis (%) and $W_{q}$ is the moisture content of component q (%).

The higher heating value (HHV) on a dry basis of PE, PP and PS reported as 46,000, 44,000 and 40,200 kJ kg⁻¹, respectively (Plastic Waste Management Institute, 2019), was converted to LHV on a wet basis by assuming a moisture content of 3% and using equation (16):

l_{q} = h_{q} \cdot (1 - W_{q} / 100) - 25 \cdot (9 \cdot H_{q} + W_{q})

(16)

where $h_{q}$ is the HHV of component q on a dry basis (kJ kg⁻¹).

The wet-basis LHVs of disposable diaper products for adults and children were estimated as 20,811 and 21,963 kJ kg⁻¹, respectively, with equations (17) and (18):

l_{A} = \sum_{q} (l_{q} \cdot m_{A q}) / 100

(17)

l_{B} = \sum_{q} (l_{q} \cdot m_{B q}) / 100

(18)

where $l_{A}$ is the wet-basis LHV of disposable diaper products for adults (kJ kg⁻¹), $m_{A q}$ is the physical composition of component q in disposable diaper products for adults (%), $l_{B}$ is the LHV of disposable diaper products for children (kJ kg⁻¹) and $m_{B q}$ is the physical composition of component q in disposable diaper products for children (%).

LHV on wet basis of urine was set as −2500 kJ kg⁻¹, the moisture content of faeces was assumed to be 80%, and the wet-basis LHV of faeces was converted from HHV on a dry basis and set as 2800 kJ kg⁻¹ (Onabanjo et al., 2016).

The LHV of used disposable diapers for adults and children and that of combustible waste excluding used disposable diapers were set to be constant in the future. The future LHV of combustible waste was estimated with equation (19):

L_{t_a} = (L_{t_A a} + L_{t_B a} + L_{t_C ’ a}) / M_{t_C a}

(19)

where $L_{t_a}$ is the LHV of combustible waste in municipality a in year t (kJ kg⁻¹), $L_{t_A a}$ is the total LHV of used disposable diapers for adults in municipality a in year t (MJ day⁻¹), $L_{t_B a}$ is the total LHV of used disposable diapers for children in municipality a in year t (MJ day⁻¹) and $L_{t_C ’ a}$ is the total LHV of combustible waste excluding used disposable diapers in municipality a in year t (MJ day⁻¹).

In addition, a scenario was considered in which disposable diaper products would become lighter in the future due to advances in disposable diaper technology. In this scenario, the weights of pulp, SAP and plastic used in disposable diaper products were each reduced by 50% in 2045, assuming that the performance of the lighter disposable diapers would be equivalent to current products. The LHV of used disposable diapers and combustible waste in 2045 was then estimated based on this scenario.

Municipalities in Mie Prefecture

This study illustrated the generation of used disposable diapers in 29 municipalities in Mie Prefecture as a case study. The total population in Mie Prefecture in 2015 was approximately 1.82 million, and it is projected to decrease by 21.2% to approximately 1.43 million in 2045 (Table 9). Although the northern part of Mie Prefecture is an industrial area and the population will decrease in the future, the depopulation and aging are projected to be more severe in the southern part of the prefecture.

Table 9.

Population and aging rate of 29 municipalities in Mie Prefecture in 2015 and 2045 (National Institute of Population and Social Security Research, 2019).

ID	Cities and towns	2015		2045
		Population	Aging rate (%)	Population	Aging rate (%)
C1	Tsu City	279,886	27.7	227,357	36.8
C2	Yokkaichi City	311,031	24.3	283,410	34.3
C3	Ise City	127,817	29.3	100,547	38.6
C4	Matsusaka City	163,863	27.9	127,382	39.0
C5	Kuwana City	140,303	24.7	125,058	35.0
C6	Suzuka City	196,403	23.2	156,407	39.5
C7	Nabari City	78,795	28.0	56,667	41.4
C8	Owase City	18,009	41.0	7496	55.6
C9	Kameyama City	50,254	24.8	43,256	36.3
C10	Toba City	19,448	35.1	8572	55.2
C11	Kumano City	17,322	41.7	7652	56.9
C12	Inabe City	45,815	25.3	40,629	33.5
C13	Shima City	50,341	37.0	24,848	58.0
C14	Iga City	90,581	31.6	52,258	45.5
T1	Kisosaki Town	6357	30.2	3753	50.7
T2	Toin Town	25,344	27.5	18,916	39.0
T3	Komono Town	40,210	25.3	37,208	34.8
T4	Asahi Town	10,560	19.1	13,039	28.0
T5	Kawagoe Town	14,752	18.5	16,588	26.8
T6	Taki Town	14,878	31.3	10,716	43.4
T7	Meiwa Town	22,586	28.9	17,685	41.9
T8	Odai Town	9557	39.7	4939	53.7
T9	Tamaki Town	15,431	25.6	14,148	36.4
T10	Watarai Town	8309	31.8	5236	45.6
T11	Taiki Town	8939	45.2	3796	61.5
T12	Minamiise Town	12,788	49.1	3892	71.2
T13	Kihoku Town	16,338	42.2	7783	56.1
T14	Mihama Town	8741	37.5	4964	55.3
T15	Kiho Town	11,207	33.8	6602	48.6
	Mie Prefecture	1,815,865	27.6	1,430,804	38.3

The aging rate is the ratio of the elderly population (65+ years old) to the total population.

Results and discussion

Diaper usage

In Japan, when people require full assistance for standing up, walking, eating, excreting and bathing, they are certified as requiring long-term care level 3. People requiring long-term care level 3 or above are given priority to access to nursing care facilities, where long-term care is available 24 hours a day. Figure 1 shows where long-term care recipients aged 65 years or over reside, according to the online survey. More than 90% of long-term care recipients with support level 1, support level 2 and care level 1 lived at home. As the degree of care increased, the proportion of people living in care facilities increased. More than half of people classified as long-term care levels 4 and 5 lived in care facilities.

Figure 1.

Place of residence for long-term care recipients.

Figure 2(a) shows the survey results for diaper use by care level and diaper type. As the degree of long-term care became more serious, the proportion using diapers increased, reaching 93.8% (including cloth diapers) for care level 5. The usage rates of disposable diapers observed in this study were higher than those suggested by the Ministry of the Environment in their guideline.

Figure 2.

Type of diapers used by (a) adults and (b) babies.

People requiring long-term care level 3 or above consumed more disposable adult diaper products per user than people in the other categories (Figure 3(a)). The Ministry of the Environment suggested that the recipients used one outer diaper and four inner diapers per day in their guideline. However, we found that recipients used more outer diapers. The results suggest that many of the users replaced their disposable diapers before bedtime and at the time of awakening; in addition, the recipients with care level 3 or above used two or more outer diapers in the daytime.

Figure 3.

Average consumption of disposable diaper products for (a) adults and (b) babies.

Caretakers often used both disposable diapers and cloth diapers for children in the 1980s; for example, it was common to use disposable diapers only at night or when going out (Kai et al., 1990). Since the 1990s, boosted by positive opinions about disposable diapers being ‘convenient’ and ‘hygienic’ (Yakura et al., 1996), the proportion of disposable diapers used has increased steadily (Katsuki, 2004; Takeshita and Kai, 2011). The survey results showed that disposable diapers were by far more commonly used compared to cloth diapers. Figure 2(b) shows that babies were completely dependent on diapers until the age of 2 and began ‘graduating from diapers’ at the age of 3. Users under the age of 4 years (n = 729) consumed an average of 5.6 disposable diapers per person per day, and infants (<1-year-old) consumed 7.3 disposable diapers a day (Figure 3(b)). As the children grew older, the consumption of disposable diapers decreased. On average, 4-year-olds consumed 1.4 diapers person⁻¹ day⁻¹. The percentages of diaper users in the 3- and 4-year-old age groups were notably higher than the results of Tsuchida et al. (2017), who reported that 4.8% of 3-year-olds and 0.7% of 4-year-olds used disposable diapers in a survey of childcare facilities. In our online survey, 41.5% of 3-year-olds and 88.6% of 4-year-olds did not use diapers in the daytime, but they did use them at night.

Per capita generation and LHV of used disposable diapers

Figure 4(a) shows the amount of used disposable adult diapers generated per user per day by weight. Care level 3, care level 4 and care level 5 users generated 1275, 1386 and 1622 g person⁻¹ day⁻¹ of disposable diapers, respectively. These values all exceeded the national average per capita generation of MSW of 918 g person⁻¹ day⁻¹ in FY2019 (Ministry of the Environment, 2021). As the level of long-term care increased, the proportion of excrement in used disposable diapers increased. Urine accounted for more than 50% of the total weight of used disposable diapers for adults. The Japan Hygiene Products Industry Association (2008a) stated that, from the viewpoint of hygiene, faeces in disposable diapers should be removed and disposed of in the toilet before diaper disposal. However, 37.3% of the people using disposable diapers disposed of their faeces together with disposable diapers, and that percentage increased to 44.7% for care level 4 and 62.3% for care level 5.

Figure 4.

Per user amount of used disposable diapers generated by (a) adults and (b) babies.

Figure 5(a) shows the LHV results for each care level. People requiring long-term support levels 1 and 2 generated disposable diapers with relatively high LHVs because they discharged disposable diapers containing less excrement. The average LHV of used disposable diapers for adults vary depending on the number of long-term care recipients using disposable diapers, but it was estimated to be approximately 7500 kJ kg⁻¹ in Mie Prefecture. The Ministry of the Environment reported that the LHV of combustible waste treated at incineration or RDF production facilities in Mie Prefecture was 5929 to 9305 kJ kg⁻¹. Used disposable adult diapers, therefore, do not seem to have any negative effect on the treatment process of combustible waste in terms of heating value.

Figure 5.

The LHV of disposable diapers used by (a) adults and (b) babies.

The largest amount of disposable diapers (by weight) was generated by 1- and 2-year-olds (Figure 4(b)). Per user generation of disposable diapers was less for children than for adults, and the proportion of urine and faeces in children’s used disposable diapers was higher than that of adults. As a result, the LHV of children’s disposable diapers was lower (Figure 5(b)). Used disposable diapers generated by 2-year-olds and older contained a higher proportion of urine and might be difficult to combust by themselves without any additional fuels at incineration facilities (Kawai et al., 2015; Tanaka et al., 2003). The weighted average of the LHV of used disposable diapers generated by children aged 0 to 4 years was 4562 kJ kg⁻¹, which was 23.1–51.0% lower than the value of the combustible waste treated at facilities in Mie Prefecture.

Projection of used disposable diapers generated

The amount of used disposable adult diapers generated in Mie Prefecture in 2045 was estimated to be 89.9 tonnes day⁻¹, 50.8% higher than that of 2015. Although the generation of used disposable adult diapers increased notably in the northern part of Mie Prefecture, it tended to decrease in the southern part (Figure 6(a)). By 2045, the aging rate will rise in all municipalities, but the population aged 65 years and over will decline in the southern part of the prefecture. The amount of used disposable adult diapers generated in Owase City (C8), Kumano City (C11), Taiki Town (T11) and Kihoku Town (T13) peaks around 2025 to 2030, and then declines. In Minamiise Town (T12), the amount generated peaks in 2020 and then starts to decrease.

Figure 6.

Percentage change (p) in the amount of used disposable diapers projected in 2045 as compared to the amount estimated in 2015 in 29 municipalities in Mie Prefecture. The cities and towns are listed in Table 9. (a) Adults, (b) Babies and (c) Total.

The amount of used disposable diapers generated by children in 2045 was projected to be 24.6 tonnes day⁻¹ in Mie Prefecture. The amount will decrease in most municipalities, except in Asahi Town (T4), the only municipality in Mie Prefecture with an increasing population of children (Figure 6(b)). The amount of used disposable diapers will decrease by 31.9% in Mie Prefecture over the study period. Ten municipalities in the southern part of the prefecture will experience decreases of more than 60%.

Of the total amount of used disposable diapers generated in Mie Prefecture in 2015 (95.6 tonnes day⁻¹), 62.3% was by adult diapers and 37.7% for children’s diapers. In 2045, the proportion for adults will increase to 78.5%. As a result of the increase in the amount of adult used disposable diapers and the decrease in the amount for children in many areas in Mie Prefecture (Figure 6(c)), the total amount of used diapers in Mie Prefecture was projected to increase by 19.7% in 2045 compared to the amount in 2015. In the southern part of the prefecture, where both the elderly population and the infant population are expected to decline, the total amount of used disposable diapers will decrease.

The population in Mie Prefecture is declining in 28 municipalities (all except Asahi Town). Because the amount of combustible waste generated excluding used disposable diapers was projected by multiplying the total population by the per capita amount of combustible waste, the amount of combustible waste generated was estimated to decrease as the population decreased. Yokkaichi City (C2), which has the largest population in Mie Prefecture, had the largest estimated amount of combustible waste generated in 2020 (a 6.4% increase compared to 2015), but it was projected to gradually decrease, reaching a 1.7% decrease by 2045 compared to 2015 (Figure 7). In the southern part of Mie Prefecture, where the population is declining notably, the rate of decrease in combustible waste will be large, especially in Minamiise Town, where it will decrease by 67.1% by 2045. In areas where the amount of combustible waste generated will decrease significantly in the future, it is necessary to carefully prepare MSW management plans according to changes in the amount of waste to be generated. In areas with a declining population, it may become impossible for each municipality to independently manage MSW, and neighbouring municipalities may need to work together to integrate MSW management. The reduction in the amount of waste will make the collection of waste more inefficient, so municipalities must also reconsider the frequency and methods of collection.

Figure 7.

Percentage change (p) in the amount of combustible waste projected in 2045 as compared to the amount estimated in 2015 in 29 municipalities in Mie Prefecture. The cities and towns are listed in Table 9.

As the amount of combustible waste generated decreases and the amount of used disposable diapers generated increases, the proportion of used disposable diapers in combustible waste will increase. The proportion of used disposable diapers in combustible waste is expected to increase in all municipalities from 2015 to 2045 (Figure 8), accounting for about 10% in the north and 15–20% in the south in 2045.

Figure 8.

Percentage (p) of used disposable diapers in combustible waste in 29 municipalities in Mie Prefecture in (a) 2015 and (b) 2045. The cities and towns are listed in Table 9.

LHV of combustible waste

The percent change of the LHV of combustible waste in the 29 municipalities in 2045 would vary from −0.9% to 1.6% compared to 2015 levels. We had assumed that the LHV of used disposable diapers must be relatively low because they contain excrement and that the LHV of combustible waste would then decrease considerably as the proportion of used disposable diapers increased. Because of the high LHV of disposable diaper products composed of pulp, SAP and plastic, the LHV of used disposable diapers containing excrement was found to be almost the same as that of conventional combustible waste.

However, future improvements in the materials that make up disposable diapers may change the LHV of used disposable diapers. In the scenario in which disposable diaper products were assumed to be 50% lighter in 2045, the LHV of used disposable adult diapers in 2045 decreased by up to 57%, and the LHV of used disposable baby diapers decreased by up to 82% compared to conventional used disposable diapers. In this scenario, the proportion of used disposable diapers in combustible waste in 2045 would decrease, and the LHV of combustible waste would also decrease in all municipalities in Mie Prefecture compared to 2015, with a maximum decrease of about 10%. It will be important to consider the impact of improvements in disposable diaper products and the corresponding reductions of LHV on incineration processes in the future.

Furthermore, the LHV of combustible waste other than used disposable diapers may change especially by suppressing the generation of disposable plastics and promoting the recycling of plastics due to the effect of the new law on plastic waste enforced on 1 April 2022. We must continue to carefully observe changes in the composition of combustible waste, including used disposable diapers, and evaluate the impact on the incineration process.

As shown in Table 8, disposable diapers contain sodium derived from SAP, and the sodium concentration in the used disposable diapers is higher than that of other combustible waste. It is important, therefore, to be aware that the chemical composition of ash generated after incineration will change as a result of any increase in the amount of used disposable diapers generated in the future.

Conclusion

This study clarified the per capita generation of used disposable diapers for adults and children by analysing the results of an online survey. The consumption of disposable diapers per user was larger than previously reported. In line with depopulation and aging, the generation of used disposable diapers was found to increase in general. However, the generation of used disposable diapers will decrease in rural areas where the population of elderly people is projected to decline. The proportion of used disposable diapers in combustible waste was projected to increase by up to approximately 20% by 2045 in almost all municipalities of Mie Prefecture. If disposable diaper products become lighter in the future, the incineration process could be impacted because of a reduction in LHV. Because of their higher moisture content, the LHV of used disposable diapers for children was much lower than that for adults. In countries where the population is growing rapidly, it will be better to pay attention to increases in the generation of used disposable diapers for children rather than for adults.

We developed a model for projecting the generation of used disposable diapers that can be applied to any population size, and it can be used to estimate the amount generated on a national or a local scale. Because the number of care levels can be changed, the model can be applied to countries other than Japan. However, the usage of disposable diapers and the per capita generation of used disposable diapers may vary from country to country. Therefore, these data should be investigated when applying this model in countries other than Japan.

Used disposable diapers could be the second largest component after food waste in combustible waste in areas with dynamic depopulation and aging, and municipalities need to start discussing the collection, treatment and recycling of used disposable diapers (Fujiyama et al., 2012) from the point of view of sanitation as well as resource management towards building a sustainable society in an era of depopulation and aging.

The next challenge is to identify greenhouse gas emissions associated with the treatment and recycling of used disposable diapers generated in the future. Currently, plastic is a major component of disposable diapers. The use of disposable diapers may become an important issue as we move towards a carbon-free society and decrease our use of fossil-derived plastics. Manufacturers of disposable diapers may be required to reduce the use of fossil-derived plastics and switch to the use of biomass plastics. We believe that this study will be of use to countries and regions facing an increase in the generation of used disposable diapers.

Supplemental Material

sj-docx-1-wmr-10.1177_0734242X221140031 – Supplemental material for Model for projecting the generation of used disposable diapers in the era of depopulation and aging in Japan

Supplemental material, sj-docx-1-wmr-10.1177_0734242X221140031 for Model for projecting the generation of used disposable diapers in the era of depopulation and aging in Japan by Kosuke Kawai, Kazuyuki Oshita and Takasei Kusube in Waste Management & Research

Footnotes

Declaration of conflicting interests

The authors declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.

Funding

The authors disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This research was performed by the Environment Research and Technology Development Fund (JPMEERF20193007) of the Environmental Restoration and Conservation Agency of Japan.

ORCID iD

Kosuke Kawai

Supplemental material

Supplemental material for this article is available online.

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