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Article

Microplastic Contamination in Human Stools, Foods, and Drinking Water Associated with Indonesian Coastal Population

by
Arif Luqman
1,*,
Husna Nugrahapraja
2,*,
Ruri Agung Wahyuono
3,*,
Izzatul Islami
1,
Muhammad Husain Haekal
3,
Yasri Fardiansyah
4,
Balqis Qonita Putri
5,
Fahmi Ikhlasul Amalludin
5,
Elsalisa Ainur Rofiqa
5,
Friedrich Götz
6 and
Anjar Tri Wibowo
5,*
1
Biology Department, Institut Teknologi Sepuluh Nopember, Surabaya 60111, Indonesia
2
Biology Department, Institut Teknologi Bandung, Bandung 40132, Indonesia
3
Physics Engineering Department, Institut Teknologi Sepuluh Nopember, Surabaya 60111, Indonesia
4
Environmental Engineering Department, Institut Teknologi Sepuluh Nopember, Surabaya 60111, Indonesia
5
Department of Biology, Faculty of Science and Technology, Airlangga University, Surabaya 60115, Indonesia
6
Microbial Genetics Department, Eberhard Karls University of Tuebingen, 72076 Tuebingen, Germany
*
Authors to whom correspondence should be addressed.
Environments 2021, 8(12), 138; https://doi.org/10.3390/environments8120138
Submission received: 15 November 2021 / Revised: 3 December 2021 / Accepted: 13 December 2021 / Published: 16 December 2021
(This article belongs to the Special Issue Feature Papers in Environments in 2021)
Browse Figures
Versions Notes

Abstract

:
Approximately 381 million tons of plastic are produced globally every year, and the majority of it ends up as pollutants. In the environment, plastic waste is fragmented into microplastic particles less than 5 mm in size; owing to their small size, durability, and abundance, they can easily be dispersed, incorporated into the food chains, and enter the human body. The extent of microplastic exposure in the human body has become a major concern in many countries, including in Indonesia, the second largest plastic waste contributor in the world. Here, we report the detection of microplastics in human stools collected from a fisherman community in the coastal area of Surabaya, Indonesia. Microplastics were found in more than 50% of samples analyzed with a concentration ranging from 3.33 to 13.99 µg of microplastic per gram of feces (µg/g). HDPE was observed as the most prevalent type of microplastic, with an average concentration of 9.195 µg/g in positive samples. Different types of microplastics were also detected in seafood, staple foods, drinking water, table salts, and toothpaste, which were regularly used and consumed by the study participants. Results from this preliminary study indicate widespread contamination of microplastic in the human body and in consumables associated with the coastal populations of Indonesia.

Graphical Abstract

1. Introduction

Indonesia is the second largest plastic polluting country worldwide; with nearly 17,508 islands and 54,716 km coastline, plastic pollution has become a source of major environmental problems for Indonesian marine and coastal ecosystems [1]. Nearly 1.29 million tons of plastics are entering the Indonesian ocean annually [2], high population density in coastal regions and inadequate waste management might contribute to this high pollution rate [3]. In nature, plastic waste is degraded and fragmented into smaller micro- and nanoparticles with sizes less than 5 mm [4]. Owing to their small size, micro-plastic can be easily dispersed and become waterborne [5,6,7,8], soil-borne [9,10], airborne pollutants [11]. From the domestic and industrial environment microplastic could enter the aquatic and terrestrial ecosystem through incomplete removal in wastewater treat-ment plants and its accumulation in sewage sludge [8,12]. Due to their abundance, dura-bility, and size, microplastic can be ingested and incorporated into the tissue and organs of various aquatic and terrestrial organisms [13]. Currently, it is established that microplastic has already entered marine food chains ]; it can be found in the gastrointestinal tracts of various marine organisms, including in fishes, bivalves, and crustaceans that are frequently consumed by humans [14,15,16,17,18,19].
Nearly 74,000 to 121,000 microplastic particles are entering the human body every year through ingestion and inhalation [20]. Exposure to microplastic might have long-term effects on human health; several works have reported potential adverse effects on the immune, nervous, and reproductive systems [21,22,23,24]. Several publications have re-ported microplastic contamination in various human foods and drinking water [25,26,27]. However, evidence for microplastic exposure in the human body remains very limited. Early evidence for human exposure came from microplastic detection in stool samples which represent contamination in the gastrointestinal tract [28,29,30,31]. It is also found in co-lectomy samples [32], saliva, the surface of skins, and head hair [33]. Recently, microplas-tics were also detected in human placenta [34,35] and lung tissue [36], providing evidence for microplastic penetration and incorporation in the human tissue.
The extent of microplastic exposure in the human body has become a major concern for many countries, including in Indonesia. Microplastic has been abundantly detected in Indonesian seafood [18,37,38], river fish [1,15], and salts [39] intended for human con-sumption. Nevertheless, reports about contamination in the human body and measure-ment in human specimens is still limited. Moreover, these reports are often not accompa-nied with data explaining the possible source of contamination (microplastic contamina-tion rate in daily consumables, drinking water, and air associated with the study partici-pants). In this preliminary study, we reported evidence for microplastic contamination in the human stool collected from Indonesians living in the coastal area and in the seafood, staple foods, salts, drinking water, and toothpaste that are frequently used and consumed by the study participants.

2. Materials and Methods

2.1. Study Participants and Stool Sample Collection

The stool samples were collected from 11 healthy participants (9 male and 2 female) coming from a fisherman community living in the coastal region of Kenjeran, Surabaya, Indonesia. The participants were selected on the basis of the following criteria: good general health, 20–50 years old, and did not consume any antibiotics 2 months before sample collection. The details of participants’ diet and general health conditions were also recorded 7 days prior to sample collection. To ensure that no contamination of microplastics occurred during the stool sample collection, we provided the participants with a glass container with a lid and spoon made of steel. We also used glass and steel utensils during sample preparation and microplastic analysis.

2.2. Collection of Drinking Water, Seafood, Staple Foods, Table Salts, and Toothpaste Samples

The recorded dietary data from the participants were used as information to collect drinking water, seafood, staple foods, table salts, and toothpaste commonly used and consumed by the study participants. Drinking water was collected from 2 different brands of bottled water and 3 different drinking water refilling stations that were regularly used by the participants. Meanwhile, seafood, staple foods, table salts, and toothpaste were collected from the local markets where the participants typically acquired these products. Three replicates were collected and measured for each item. Detailed information about the analyzed consumables is provided in Supplementary Table S3.

2.3. Sample Preparation

Microplastics were extracted from stool, foods, salts, and toothpaste according to the previous publication [40], with some modification. Briefly, the collected stool samples and other samples were incubated at 70 °C for at least 1 week until the weight of the samples was constant. The dried stool samples (1 g for each sample) were mixed with 50 mL of Fenton solution and incubated at room temperature for 5 h. The mixture was then subjected to filtration using cellulose nitrate–cellulose acetate filter (CN-CA filter). The filters were then digested using 65% HNO3 at 50 °C for 30 min followed by incubation at 70 °C for 10 min. The solution obtained following digestion was then diluted with distilled water at 1:2 ratio, and microplastic content in the samples was measured using Raman spectroscopy. For the collected drinking water, samples were directly subjected to Raman spectroscopy measurement without any preparation.

2.4. Microplastic Analysis

Microplastic identification and quantification from the digested samples were performed using Raman spectroscopy (off-resonance) with excitation wavelength of 785 nm. StellarNet Raman HR-TEC-785 was used with a diode laser 785 nm (100 mW) as an optical excitation. For the reference spectrum, several concentrations of microplastics were prepared by dispersing different types of microplastics, such as polyethylene terephthalate (PET), polystyrene (PS), polypropylene (PP), linear low-density polyethylene (LLDPE), high-density polyethylene (HDPE), and low-density polyethylene (LDPE) in 0.1 M of HNO3. The spectrum profiles produced by each type of microplastic type were then used as calibration curves to quantify the microplastic content in the samples.
To identify the microplastic content in the samples, the Raman spectrums within the range of 500–2750 cm−1 were used as spectrum with the spectral identifier of each reference polymer. The Raman spectrums obtained from the samples were then fitted to the reference spectrum and calculated using the particle swarm optimization algorithm [41,42], with the following assumption:
I ( ω ) = ∑ i = 1 n α i I i ( ω )
where I(ω) indicates the Raman spectrum of the sample, Ii(ω) indicates the Raman spectrum of the microplastic reference, α indicates the fraction of the microplastic mass, and I indicates the microplastic type index, e.g., PET, PS, PP, LLDPE, LDPE, or HDPE.
The values of α were then used to determine the intensity contribution of the Raman spectral identifier from each type of identified microplastic in the samples, and the intensity contribution values were used to quantify the microplastic content in the samples using the calibration curve.
To investigate the possible origin of the microplastic contamination in stool samples, we performed correlation analyses between the seafood and plastic-packaged food consumption frequency and total microplastic content in the stool samples was analyzed using Pearson’s correlation with significance defined as p < 0.05.

2.5. Ethical Statement

The collection of human stool samples was approved by the Health Research Ethic Committee of Universitas Surabaya (No. 005-OL/KE/III/2021). Stool samples were obtained from 11 adult participants from the highland population of Kenjeran, Surabaya, Indonesia. All samples were anonymized and obtained with written consent from the participants.

3. Results

3.1. Detection of Microplastic in Human Stools

Human stool samples were collected from 11 participants (9 males and 2 females) who came from a fisherman community living in the coastal region of Surabaya, Indonesia (Supplementary Table S1). Microplastics were detected in six participants with a total concentration ranging from 3.33 to 13.99 µg/g (microgram of microplastic per gram of feces). Six types of microplastics were detected across all samples, including HDPE, LDPE, LLDPE, PP, PS, and PET. Interestingly, each positive sample contained different types and compositions of microplastic, suggesting that the participant might be exposed to microplastic through different means. The most prevalent microplastic was HDPE, which was found in four samples with an average concentration of 9.195 µg/g, followed by PS, which was found in two samples with an average concentration of 9.885 µg/g. The other types of microplastic, LDPE, LLDPE, PP, and PET, were only present in one sample with average concentrations of 3.48, 7.00, 3.13, and 2.44 µg/g, respectively (Figure 1 and Supplementary Table S2). Our results show that more than 50% of study participants had microplastic contamination in their digestive tract with HDPE detected as the most common and abundant microplastic.

3.2. Microplastic Contamination in Drinking Water

Previous work has reported microplastic contamination in the Surabaya water supply system [43]. However, tap water in Indonesia is non-potable, and Surabaya inhabitants commonly acquire their drinking water from bottled water gallons or water refilling stations. In this study, we collected drinking water samples from two of the most popular bottled water gallon brands and three water refilling stations that were frequently used by the participants. PET was observed in one of the bottled water brands with an average concentration of 7.585 µg/g (microgram of microplastic per gram of water), while high concentrations of LDPE (30.21 µg/g) were detected from one of the water refilling stations (Table 1). These results indicate that drinking water could be a source of microplastic contamination in the studied population. However, it might not be the only source of contamination given that we could only detect PET and LDPE in the sampled water. The high abundance of HDPE found in the stool samples might originate from other consumables.

3.3. Widespread Microplastic Contamination in Seafood, Staple Foods, and Hygiene Products

Apart from drinking water, we also measured microplastic concentration in various seafood, river fish, staple foods, and table salts that were frequently consumed by the study participants (Table 2). Microplastic in the form of PP was detected in salted marine fish, while LDPE was found in marine catfish, each with concentrations of 11.61 and 5.15 µg/g, respectively. High concentrations of PP were also found in rice (15.36 µg/g) and tempeh (4.07 µg/g), two popular staple foods in Indonesia. Rice is the main carbohydrate source for Indonesians, while tempeh (fermented soybean cake) is a staple source of proteins. To further investigate the extent of microplastic contamination in human consumables, we also measured microplastic in different brands of table salts and toothpaste regularly used by participants. All analyzed salt and toothpaste samples were found to be contaminated with microplastic, with high concentrations of PP (8.69 µg/g) and LLDPE (26.27 µg/g) found in table salts, whereas the toothpaste contained high amounts of PP (23.47 µg/g) and HDPE (14.79 µg/g) (Table 3). In general, we observed widespread microplastic contamination in various consumables associated with the coastal fisherman population of Surabaya, Indonesia. Despite the relatively low number of samples we collected, we were able to detect microplastic in several seafoods, staple foods, salts, and toothpaste samples, indicating that microplastic is prevalent in human consumables.

4. Discussion

Owing to the high accumulation of plastic waste in the coastal areas and their dietary habits, coastal inhabitants, especially the fisherman community, are prone to be exposed to microplastic contamination. A long-term microplastic contamination can cause ad-verse effects on health [21,22,23,24]. However, the extent of microplastic contamination in the Indonesian coastal population has never been investigated before. Here, we found that more than 50% of the study participants (6 out of 11) have microplastic contamination in their stools. This number is lower than the previous report for microplastic contamination in the colectomy specimen collected from residents of Northeastern Peninsular Malaysia where microplastic is detected in all 11 specimens they collected [32]. A difference also exists regarding microplastic composition found in the samples, previous works reported PP as the most prevalent type of microplastic in human stools [28,29,31] and colectomy samples [32]. However, the current study detects HDPE as the most common contami-nant. Differences in microplastic prevalence and composition likely originate from varia-tion in dietary habits, life styles, and environmental quality between the studied popula-tion, since exposure in the human body is largely dependent on microplastic intake from consumed foods and the inhaled air. To investigate possible connections between micro-plastic in stools with dietary habits we performed correlation analysis between micro-plastic occurrence in stool with frequency of consuming seafood and foods wrapped in plastic, but we did not find a statistically significant correlation between them. Note that a limited number of samples are analyzed either in this preliminary study or in previous studies, therefore, the result might not represent the overall prevalence, composition, and correlation in the general population. Follow-up studies with a higher number of sam-ples are required to establish statistically sound correlation between microplastic con-tamination in the human body and dietary habits.
Microplastic could enter the human body through food and water. To evaluate the extent of microplastic contamination in daily consumables, we also measured micro-plastic concentrations in drinking water, seafood, and staple foods that are regularly con-sumed by the participants. We found widespread microplastic contamination in various products, and it is alarmingly high in several brands of drinking water, seafood, and rice. Different types of microplastic were found in the analyzed consumables, with PP observed as the most common contaminant. The abundance of microplastic in various products might explain the diversity of microplastic composition found in the stool samples, given that participants consumed various products in differing frequencies. For example, sea-food consumption frequency among participants varies from 0 to 10 times a week with the average seafood consumption of 4.18 times in a week (Supplementary Table S1). The study participants also consume different combinations of drinking water, seafood, and staple foods packaged in plastic (Supplementary Table S1).
Apart from food and water, microplastic was also previously reported in salts [44] and toothpaste [45]. To further explore the potential source of microplastic contamination in the studied population, we also analyzed the presence of microplastic in table salts and toothpaste frequently used by the participants. All samples were contaminated with mi-croplastic, with high concentrations of PE (26.27 µg/g) found in one brand of table salt and HDPE (23.47 µg/g) in one brand of toothpaste. Considering that HDPE is the most com-mon type of microplastic detected in the stool samples, ingestion through toothpaste might be an important source of HDPE contamination. Apart from toothpaste, HDPE contamination might also come from plastic packaging and products. HDPE is widely used in the production of food packaging and various household items [46], previous work reported that HDPE could leach out from plastic products due to the withering pro-cess by high temperature and UV exposure [47]. The food and water by itself might not contain HDPE (as found in this study), but HDPE might leach out from the container, plastic packaging, and cooking utensils during storage and food processing. HDPE is considered to be relatively safe for humans, it is reported to have no toxic effect on the human mammary cell line [48]. Nevertheless, other work reported that HDPE exhibits es-trogenic activities that are harmful for the human reproductive system [49].
Overall, our preliminary study provides evidence for microplastic exposure in the coastal Indonesian population and high prevalence of microplastic in various human consumables. This finding is alarming because long-term microplastic contamination can cause toxicity, metabolic disturbance, and adverse health effects. Further studies with larger samples are required to estimate the rate and extent of microplastic contamination in the Indonesian population and to formulate effective mitigation strategies.

5. Conclusions

In this study, we were able to detect microplastics in human stools and daily consumables collected from a fishermen community in the coastal area of Indonesia. More than half of the participants (6 out of 11) have microplastic contamination in their gastrointestinal tract with HDPE detected as the most prevalent contaminant. Microplastic was also detected in daily consumables commonly used by the participants, with PP observed as the most common and abundant contaminant in foods, while LDPE was observed as the most abundant contaminant in drinking water. High concentrations of HDPE were found in toothpaste; since this type of microplastic was abundant in stool samples, intake of HDPE from toothpaste might be an important but underestimated source of microplastic contamination. Taken together, we have provided evidence for the widespread contamination of microplastic in the Indonesian coastal population, both in the human body and in various daily consumables. Results from these preliminary studies can be used as a basis for follow-up work with larger and more diverse participants to find correlations between microplastic exposure and dietary habits, calculating microplastic intake rate per capita, and to fully elucidate the extent of microplastic contamination in the Indonesian population.

Supplementary Materials

The following are available online at https://www.mdpi.com/article/10.3390/environments8120138/s1, Table S1: Microplastic concentration found in participants’ stool samples, Table S2: Summary of data collected from interview with participants and the total of microplastics found in each stool sample, Table S3: Detailed informations about the analyzed consumables.

Author Contributions

Conceptualization, A.T.W., A.L., H.N.; methodology, A.T.W., A.L.; formal analysis, A.T.W., A.L., R.A.W.; investigation, I.I., M.H.H., Y.F., B.Q.P., F.I.A., E.A.R.; resources, A.T.W., A.L., R.A.W., F.G.; data curation, A.T.W., H.N., A.L., R.A.W.; writing—original draft preparation, A.T.W., A.L.; supervision, A.T.W., H.N., A.L.; project administration, A.T.W., H.N., A.L.; funding acquisition, A.T.W., H.N., A.L. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the PPKI program from the Indonesian World Class University Research Scheme (1325/PKS/ITS/2021; 177/UN3.15/PT/2021; 542/IT1.B07.1/TA.00/2021).

Institutional Review Board Statement

The collection of human stool samples was approved by the Health Research Ethic Committee of Universitas Surabaya (No. 005-OL/KE/III/2021). Stool samples were obtained from 11 adult participants from the highland population of Pacet, Mojokerto, Indonesia. All samples were anonymized and obtained with written consent from the participants.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study. Written informed consent has been obtained from the patient(s) to publish this paper.

Acknowledgments

We acknowledge a collaborative PPKI program from the Indonesian World Class University Research Scheme.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

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Environments 08 00138 g001 550
Figure 1. Concentration and prevalence of microplastics in stool samples collected from coastal populations of Kenjeran, Surabaya, Indonesia. (A) Various types of microplastics were detected in 6 out of 11 stool samples; (B) prevalence of different microplastic types in the studied population.
Figure 1. Concentration and prevalence of microplastics in stool samples collected from coastal populations of Kenjeran, Surabaya, Indonesia. (A) Various types of microplastics were detected in 6 out of 11 stool samples; (B) prevalence of different microplastic types in the studied population.
Environments 08 00138 g001
Table
Table 1. Microplastic content in drinking water.
Table 1. Microplastic content in drinking water.
SamplesType of MicroplasticContent (µg/g)
Drinking water in gallon brand 1PET9.18 ± 1.30
Drinking water in gallon brand 2ndnd
Drinking water in gallon from refilling station 1ndnd
Drinking water in gallon from refilling station 2ndnd
Drinking water in gallon from refilling station 3LDPE30.21 ± 4.26
nd: not detected.
Table
Table 2. Microplastic content in seafood and staple foods.
Table 2. Microplastic content in seafood and staple foods.
SamplesType of MicroplasticContent (µg/g)
Salted fish 1PP11.61 ± 4.68
Salted fish 2ndnd
Seawater catfish 1LDPE5.15 ± 2.48
Seawater catfish 2ndnd
Seawater catfish 3ndnd
Musselndnd
Shrimpndnd
Freshwater catfishndnd
Tofu Brand 1ndnd
Tofu Brand 2ndnd
Tempeh Brand 1PP4.07 ± 1.35
Tempeh Brand 2ndnd
Rice Brand 1PP15.36 ± 4.79
Rice Brand 2ndnd
nd: not detected.
Table
Table 3. Microplastic content in table salt and toothpaste.
Table 3. Microplastic content in table salt and toothpaste.
SamplesType of MicroplasticContent (µg/g)
Table salt
Brand 1PP8.69 ± 1.26
Brand 2LLDPE26.27 ± 3
Toothpaste
Brand 1PP23.47 ± 5.77
Brand 2HDPE14.79 ± 5.37
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Luqman, A.; Nugrahapraja, H.; Wahyuono, R.A.; Islami, I.; Haekal, M.H.; Fardiansyah, Y.; Putri, B.Q.; Amalludin, F.I.; Rofiqa, E.A.; Götz, F.; et al. Microplastic Contamination in Human Stools, Foods, and Drinking Water Associated with Indonesian Coastal Population. Environments 2021, 8, 138. https://doi.org/10.3390/environments8120138

AMA Style

Luqman A, Nugrahapraja H, Wahyuono RA, Islami I, Haekal MH, Fardiansyah Y, Putri BQ, Amalludin FI, Rofiqa EA, Götz F, et al. Microplastic Contamination in Human Stools, Foods, and Drinking Water Associated with Indonesian Coastal Population. Environments. 2021; 8(12):138. https://doi.org/10.3390/environments8120138

Chicago/Turabian Style

Luqman, Arif, Husna Nugrahapraja, Ruri Agung Wahyuono, Izzatul Islami, Muhammad Husain Haekal, Yasri Fardiansyah, Balqis Qonita Putri, Fahmi Ikhlasul Amalludin, Elsalisa Ainur Rofiqa, Friedrich Götz, and et al. 2021. "Microplastic Contamination in Human Stools, Foods, and Drinking Water Associated with Indonesian Coastal Population" Environments 8, no. 12: 138. https://doi.org/10.3390/environments8120138

APA Style

Luqman, A., Nugrahapraja, H., Wahyuono, R. A., Islami, I., Haekal, M. H., Fardiansyah, Y., Putri, B. Q., Amalludin, F. I., Rofiqa, E. A., Götz, F., & Wibowo, A. T. (2021). Microplastic Contamination in Human Stools, Foods, and Drinking Water Associated with Indonesian Coastal Population. Environments, 8(12), 138. https://doi.org/10.3390/environments8120138

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