The relevance of interaction of chemicals/pollutants and microplastic samples as route for transporting contaminants

https://doi.org/10.1016/j.psep.2020.03.033Get rights and content

Highlights

  • PE and PS showed higher adsorption capacity for amoxicillin than PET, PP and PVC.
  • PET and PS showed higher adsorption capacity for phenol than PP and PVC.
  • Experimental data of sorption kinetics fit good to pseudo-second order model.
  • Sorption equilibrium fit better with Langmuir model than Freundlich model.
  • Desorption was more favourable at high temperature and pH around 6.

Abstract

Microplastics have been converted a very important issue during current time. In addition, their capacity to adsorb other pollutants implies an additional problem. In this work, the potential of five types of microplastics derived from plastic waste, that include polyethylene, polyethylene terephthalate, polypropylene, polystyrene and polyvinyl chloride, to act as transporters of amoxicillin, atrazine, diuron, paracetamol, phenol and vancomycin was studied. Results suggested that microplastics, especially polyethylene, polyethylene terephthalate, polystyrene and polyvinyl chloride, revealed an essential protagonist as carriers of amoxicillin and phenol. The kinetic study showed that the sorption processes (from water to plastic) was slow and needs more than 28 days (amoxicillin) or about 21 days (phenol) to reach equilibrium. The modelling of equilibrium showed a better fit of the Langmuir model. The maximum Langmuir sorption capacities reached values between 4.03 and 8.80 mg/g for amoxicillin and between 1.25 and 2.80 mg/g for phenol. With respect to release tests, the liberation of the loaded pollutants was minor at the lower tested temperature (T =25 °C) and lower tested pH (pH = 2). Percentage of chemicals released increased between 1.3 and 7.9 times as the temperature increased until 40 °C. Similarly, the results revealed that release was greatly pH dependent. In these experiments, a singular behaviour was observed for amoxicillin at 25 °C, a combined effect of adsorption-release seems happen.

Introduction

The "microplastics" (MPs) are defined as small plastic particles, with regular or irregular shape, specifically those smaller than or equal to 5 mm in diameter, which are present in the oceans, seas and rivers of the entire planet, mainly, in addition to being deposited and accumulated in sand, river basins and all kinds of landfills (Arthur et al., 2009; Cole et al., 2011; Frias and Nash, 2019; GESAMP, 2016). They are formed by the breakdown of larger plastic particles (secondary origin) or are intentionally manufactured for use in cosmetic products, detergents or clothing (primary origin).
In the last years, concern for microplastics pollution problem worldwide has resulted in a great increase of microplastics literature. To help address the problem of plastics, in early 2018 the European Union (EU) proposed the European Strategy for Plastics in a Circular Economy. The strategy aims to "transform the way products are designed, produced, used and recycled in the EU". However, at present, microplastics are found in a high amount of foods or drinks. For example, In Spain, Iñiguez et al. (2017) identified traces of plastics in the table salt that reaches consumers and a report from the Organization of Consumers and Users (OCU, 2018) found a remarkable presence of microplastics in 69 of the 102 foods analyzed in the study (all of them present in a varied diet in Spain).
The adsorption capacity of microplastics on some chemicals and pollutants present in the environment is well established in literature. Microplastic adsorption studies exist on a wide range of chemicals including all types of persistent organic pollutants, bioaccumulative substances, pharmaceuticals, pesticides and herbicides or metals. (Antunes et al., 2013; Brennecke et al., 2016; Mato et al., 2001; Rios et al., 2007; Teuten et al., 2007).
Recently, Camacho et al. (2019) published a detailed work monitoring 81 different chemical compounds that PE and PP pellets and fragments can adsorb in the sea.The most important conclusion is the evidence of a spatial variation in the adsorption of contaminants, depending on the type of anthropogenic activity that happens at each sampling site. For example, they found higher amounts of polychlorinated biphenyls and diphenyl-dichloro-ethane (DDT) in industrialized areas, ultraviolet filters (UV-filters) in tourist beaches, or higher presence of flame retardants in urbanized locations. Another widely studied factor is the tendency of some polymers to adsorb more contaminants than others. For example, Llorca et al. (2018) found a greater tendency for polystyrene compounds to adsorb perfluoroalkyl substances than high-density polyethylene (HDPE). In contrast to, Wang and Wang (2018) found a higher capacity of polyethylene versus PS and PVC to adsorb pyrene. The adsorption of some flame retardants (Tris-(2,3-dibromopropyl) isocyanurate (TBC) and Hexabromocyclododecans (HBCDs)) on polypropylene was tested by Liu et al. (2018). The adsorption capacity of these substances depends on many factors, including the characteristics of the polymer (particle size, specific surface area, etc.) and chemical interfaces, such as hydrophobic interactions, van der Waals bonds or intraparticle diffusion..
There are also some studies that have proven the adsorption capacity of microplastics on pharmaceuticals. For example, Wu et al. (2016) showed that PE is capable of adsorbing some of these substances, such as carbamazepine (CBZ), 4-methylbenzylidene camphor (4MBC), triclosan (TCS), and 17α-ethinyl estradiol (EE2). This adsorption occurred specially with the most hydrophobic compounds. Li et al. (2018) found a high sorption potential of polyamide (PA) for antibiotics (amoxicillin, ciprofloxacin, sulfadiazine, tetracycline and trimethoprim). Also, Guo et al. (2018) investigated the capacity of PE, PP, PS and PVC to adsorb tylosin (TYL) and found maximum sorption capacities of 1.67 mg/g (PE) and 3.33 mg/g (PP, PS and PVC). However, there is a greater tendency for polyethylene to adsorb tylosin in a process also dominated by hydrophobic interactions.
Regards to other substances, Wu et al. (2019) analyzed kinetics and isotherms for bisphenols sorption onto PVC microplastics to study its role as carrier of these contaminants. The maximum sorption capacities were between 0.15 (bisphenol S) and 0.24 mg/g (bisphenol AF). The adsorption mechanisms of bisphenols were explicated with respect to hydrophobic interactions, electrostatic forces, and non-covalent bonds. Gong et al. (2019) analyzed the sorption of fipronil on PE, PP, PS, PVC, polylactic acid (PLA) and polybutylene succinate (PBS) microplastics. The results suggested that microplastics, especially PLA and PBS, could act as carriers to transport fipronil. Finally, some other studies were focused on demonstrated the metals sorption capacity of different types of microplastics (Brennecke et al., 2016; Holmes et al., 2012; Wang et al., 2018).
With regards to desorption of adsorbed pollutants, these studies are less frequent and need further research. Hartmann et al. (2017) explored desorption of some hydrophobic organic chemicals focusing on the parameters with remarkably impact in the process. The authors consider that the weathering or pristine of microplastics should be considered in the desorption processes, as well as the crystallinity of the polymer. Lee et al., (2018) also provided an interesting study about desorption of hydrophobic organic chemicals from PE and PP microplastics. The authors fitted experimental desorption data with a model that assumed ideal geometries, however, the experimental results were different to those of the model due to the heterogeneity of the particle size distribution. Razanajatovo et al., (2018) evaluated the sulfamethoxazole, propranolol and sertraline desorption of from PE microplastics. The desorption results showed that any of the sulfamethoxazole was desorbed and only 8% and 4% of propranolol and sertraline, respectively, were release within 48 h from the PE fragments. Also, Bakir et al. (2014) analyzed desorption rates of persistent organic pollutants (POPs) in seawater and under simulated gut conditions. This study is a good representative of the influence of pH on desorption processes. They found desorption rates were faster with gut surfactant and under temperature conditions simulating warm blooded organisms.
Recently, other authors as Ho and Leung (2019) studied sorption and desorption processes of multiple organic contaminants from ultraviolet filters by PE and PS. They included interesting approach about sorption and desorption behaviors in multi-solute systems. Also, Wang et al. (2019) studied the desorption characteristics of cadmium from MPs and found that Cd was easily desorbed, with desorption rates higher than 90 %. These high desorption rates show, according to the authors, that the bonding forces between the Cd and the microplastics are weak and that chemical adsorption should not be the main mechanism. In contrast to this study, Hodson et al. (2017) found that desorption rates of Zn from HDPE plastic bags were quite low.
Also, Fang et al. (2019) analyzed the sorption and desorption of three triazole fungicides on PS. They found the higher the sorption capacity, the lower the desorption rate. But, in any case, as PS was capable to adsorb and desorb triazole fungicides, it can become a source and sink of these pollutants on water environment. In any case, the interactions between microplastics and the wide diversity of contaminants that may be present in different watercourses are complex and depend on many factors. The pH and temperature are often influential factors, which variations can cause the same pollutant to behave differently.
The present study aims to increase knowledge about the complex issue of interaction of chemicals/pollutants and microplastics. It is based on the role of microplastics derived from post-consumer plastic waste, such as polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS) and polyvinyl chloride (PVC), as carriers of amoxicillin (AMX), atrazine (ATZ), diuron (DIR), paracetamol (PAC), phenol (PHN) and vancomycin (VAC). Two antibiotics (amoxicillin and vancomycin) and an analgesic (paracetamol) that are widely consumed and used, two pesticides (atrazine and diuron) that rank among the most toxic substances in the world, and phenol, which is present in many cleaning and hygiene products and also used by the plastics industry, were chosen. Their chemical properties and the characteristics for which they were chosen in this study are presented in Table 1.
First, the sorption kinetics and isotherms were analyzed. Then, the effect of pH and temperature on the release of the loaded pollutants was studied. Specially, the release of the adsorbed pollutants to water environments and organisms is yet poorly understood. In our opinion, more works about the effect of the factors influencing desorption are needed since results could have a relevant importance in the prevention of harms linked to microplastics due to the great potential of them to transport other pollutants to organisms. In addition, most studies relied on pristine or artificially aged plastics rather than post-consumer plastic samples for studies on chemical sorption by plastics (Fred-Ahmadu et al., 2020). Our experimental work advances this field by showing thatmicroplastics from plastic waste can adsorbed and then desorbed pollutants and therefore, transfer them to organisms.

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Section snippets

Materials

Five polymers named as “commodities by the Plastic Industries Society (SPI) were chosen, as they are the most frequent in daily use objects, and are identified with a number within a triangle at the bottom of the container. These polymers were: polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS) and polyvinyl chloride (PVC). The PE came from recycled pellets, made from post-consumer plastic waste from the Solid Waste Treatment Plant in Granada (Spain),

Preliminary tests to determine the sorption of pollutants onto MPs. Effect of characteristics of pollutants and plastic materials

Fig. 2 showed the percentage of contaminant adsorbed by each of the polymers tested. The results indicated that phenol and amoxicillin were the contaminants that had greater affinity for polymers, since they were retained in greater amounts by all microplastics. However, the results found for phenol were especially high for PET and PS, which reached values of sorption percentage higher than 80 %. In the case of amoxicillin, the highest retention values were found in PE with 37.5 % and PP with

Conclusions

The present study aims to increase knowledge about the complex issue of interaction of chemicals/pollutants and microplastics. It is based on the role of PE, PET, PP, PS and PVC microplastics, as carrier of AMX, ATZ, DIR, PAC, PHN and VAC. The sorption capacity of microplastics was much higher for AMX and PHN pollutants. PET and PS were the polymers that best adsorbed phenol, while PE was the polymer that adsorbed amoxicillin in greater amount than others polymers. However, the characteristics

Author contributions

The manuscript was written through contributions of all authors. All authors have given approval to the final version of the manuscript.

Funding sources

The authors received no financial support for the research, authorship, and/or publication of this article.

CRediT authorship contribution statement

V. Godoy: Methodology, Software, Validation, Formal analysis, Investigation. M.A. Martín-Lara: Conceptualization, Methodology, Writing - original draft, Writing - review & editing, Supervision, Project administration, Formal analysis. M. Calero: Conceptualization, Resources, Writing - original draft, Supervision, Project administration. G. Blázquez: Methodology, Software, Validation, Formal analysis, Project administration.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

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