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Quality Criteria for the Analysis of Microplastic in Biota Samples: A Critical Review
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Critical Review

Quality Criteria for the Analysis of Microplastic in Biota Samples: A Critical Review
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  • Enya Hermsen
    Enya Hermsen
    Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The Netherlands
    More by Enya Hermsen
  • Svenja M. Mintenig
    Svenja M. Mintenig
    Copernicus Institute of Sustainable Development, Utrecht University, Utrecht, The Netherlands
    KWR Watercycle Research Institute, Nieuwegein, The Netherlands
  • Ellen Besseling
    Ellen Besseling
    Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The Netherlands
    Wageningen Marine Research, IJmuiden, The Netherlands
  • Albert A. Koelmans*
    Albert A. Koelmans
    Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The Netherlands
    Wageningen Marine Research, IJmuiden, The Netherlands
    *E-mail: [email protected]
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Environmental Science & Technology

Cite this: Environ. Sci. Technol. 2018, 52, 18, 10230–10240
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https://doi.org/10.1021/acs.est.8b01611
Published August 23, 2018

Copyright © 2018 American Chemical Society. This publication is licensed under CC-BY-NC-ND.

Abstract

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Data on ingestion of microplastics by marine biota are quintessential for monitoring and risk assessment of microplastics in the environment. Current studies, however, portray a wide spread in results on the occurrence of microplastic ingestion, highlighting a lack of comparability of results, which might be attributed to a lack of standardization of methods. We critically review and evaluate recent microplastic ingestion studies in aquatic biota, propose a quality assessment method for such studies, and apply the assessment method to the reviewed studies. The quality assessment method uses ten criteria: sampling method and strategy, sample size, sample processing and storage, laboratory preparation, clean air conditions, negative controls, positive controls, target component, sample (pre)treatment, and polymer identification. The results of this quality assessment show a dire need for stricter quality assurance in microplastic ingestion studies. On average, studies score 8.0 out of 20 points for “completeness of information” and 0 for “reliability”. Alongside the assessment method, a standardized protocol for detecting microplastic in biota samples incorporating these criteria is provided.

Copyright © 2018 American Chemical Society

Introduction

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The ubiquity of microplastic (plastic particles < 5 mm (1)), combined with associated effects, has raised concerns regarding marine species, ecosystems, and the impact it may have on human health. Microplastics have been detected in a wide variety of habitats in the ocean from shallow coasts to the deep sea. (2−4) Increasing numbers of studies report the ingestion of microplastic by marine biota across multiple trophic levels, including animals often targeted by fisheries (Table 1). (5−9) The ingestion of microplastics seemingly concerns a wider range of species than the ingestion of meso- and macroplastics; indeed, it is considered the most frequent interaction between plastic debris and marine organisms. (10)
Table 1. Scoring of the Reviewed Articles in the Current Quality Assessmenta
  criterion
  12345678910 
studyyearsampling methodssample sizesample processing and storagelaboratory preparationclean air conditionsnegative controlpositive controltarget componentsample treatmentpolymer identificationaccumulated score
Lusher et al. (48)2016222212022015
Tanaka and Takada (78)2016222001022213
Davidson and Dudas (59)2016112202220012
Rummel et al. (58)2016220212001212
Courtene-Jones et al. (49)2017002201022211
Devriese et al. (56)2015212022020011
Mathalon and Hill (8)2014112112120011
Wesch et al. (79)2016022020022111
Cannon et al. (43)2016022020020210
Desforges and Galbraith (50)2015222002020010
Li et al. (80)2016220001120210
Murphy et al. (81)2017210201020210
Vandermeersch et al. (27)2015112022020010
Davison and Asch (41)201122200120009
Foekema et al. (6),b201322100002209
Karlsson et al. (53)201711210202009
Nadal et al. (82)201622220100009
Torre et al. (54)201602221200009
Bellas et al. (47)201621210100108
Jabeen et al. (44)201602010102028
Lusher et al. (5)201322200000028
Van Cauwenberghe et al. (60)201410102202008
Brate et al. (83)201602020100027
Anastasopoulou et al. (84)201302200002006
Besseling et al. (16),b201520000000226
Jantz et al. (85)201312200000106
Murray and Cowie (51)201122200000006
Peters et al. (70)201712200100006
Vendel et al. (86)201722100000005
Boerger et al. (52)201022000000004
Liboiron et al. (55)201602000002004
Neves et al. (7)201500100000023
Wojcik-Fudalewska et al. (87)201601200000003
Romeo et al. (9)201511000000002
Miranda and de Carvalho-Souza (88)201600000000000
Av all-study score (n = 35) 1.141.461.310.570.400.860.171.030.430.668.0
a

Scores of 0–2 were assigned to each publication in each of the 10 categories. The publications are sorted from high to low based on the “accumulated score”. The overall reliability score was 0 for all studies and is not indicated.

b

Studies with involvement of 1 or more of the authors of the present paper.

Ingested microplastic particles are thought able to evoke a biological response through both physical and chemical mechanisms, although many of these effects have yet to be studied. Ingestion of microplastics is thought to cause physical damage in small organisms (2) and has been speculated to provide a pathway for some associated chemicals to enter and spread in the food web all the way up to humans with microplastic particles as vectors. (11−13) Additionally, ingestion by biota is considered a possible sink for microplastics. (14) Therefore, measuring quantities of ingested plastic is of high priority to properly assess the risk of such hazards.
Physical impacts for small organisms like internal abrasions and blockages have been reported. (2) Moreover, microplastic particles were shown to cause damage leading to cellular necrosis, inflammation, and lacerations of tissues in gastrointestinal tracts according to a review of plastic impact on biota. (15) In bigger organisms, ingestion of larger objects (i.e., macroplastics) has been demonstrated too. (16,17)
In addition to the impact of ingested microplastics proper, persistent organic pollutants (POPs) may concentrate on the particles. It is suggested this could pose a possible new route for POPs to enter the food chain; (11,12) however, it has not been irrefutably shown that this actually happens. (18−20) Contrarily, evidence in Northern Fulmars (Fulmarus glacialis) suggests a transfer of POPs from the lipids in the animal to the plastic rather than the other way around. (18)
The concerns for the impacts of microplastic are reinforced by the hypothesis that microplastics may be able to spread through the food web by means of trophic transfer, a phenomenon that has been observed in a few instances. (21,22) This is cause for concern especially in commercially valuable species as it possibly poses a threat to human food safety. (23) To what extent this transfer occurs in the food web remains to be studied further.
Despite these worries concerning microplastic ingestion, the effects in the natural environment and implications for the food web remain poorly understood. Because of the absence of suitable standardized methods, data are too often incomparable, are not representative, and lack quality assurance. (24−28) Hence, our knowledge on the fate and impacts of microplastics remains incomplete. The microplastic research field is young, and as research performed now lays down the foundations for later studies, there is a dire need for a standardized protocol for carrying out studies on the ingestion of microplastics by marine biota to mitigate this issue. (27) Although first steps toward standardization of methodologies in environmental samples are being made, (27,28) the comparability of current data is being impeded by the wide variety of methodologies, which has led to data of different quality. (24,29) For dealing with the wide spread in quality of the data produced by studies, an example can be taken from the field of toxicology. In toxicology, it is common practice to assess the reliability of studies with consensus criteria, like the so-called Klimisch score, (30) or the recently proposed Criteria for Reporting and Evaluating Ecotoxicity Data (CRED). (31) These methods both offer scoring systems with different reliability categories, generating standardized documentation of validity evaluation. They were developed to guide risk assessors in performing unbiased, transparent, and detailed evaluations while guiding researchers in performing and reporting studies in a manner deemed appropriate. (31) We argue that research and risk assessment with respect to the impacts of plastic debris are in urgent need for the development and use of such criteria. (32)
The aim of the present study is to critically review the literature on ingestion of microplastic by marine biota. On the basis of this review, we develop a scoring method for ecological studies and the analytical methodologies employed to detect plastic debris in aquatic biota samples. The scoring method is subsequently applied retrospectively to the reviewed studies. This assessment does not result in an absolute judgment but is an indicator of the usefulness of these studies for risk assessment and monitoring purposes of microplastic ingestion in natural populations. We also provide average scores per evaluation criterion, illustrating which methodological aspects need improvements most. Finally, our synthesis provides the basis for a quality assurance protocol for the analysis of microplastic debris in biota samples.

Materials and Methods

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An extensive literature review was undertaken by accessing the Web of Science, ScienceDirect, and Scopus databases for studies of microplastic ingestion in marine biota in natural populations, including studies from all years up until those published in June 2017. Queries included the following search terms: “microplastic AND ingestion AND marine”, “microplastic AND uptake AND marine”, “microplastic AND marine biota”, and “microplastic AND biota AND monitor*”. Reference lists of the found articles, reviews, and “reversed searches” were consulted as well, resulting in a representative collection of 35 currently available studies. Laboratory exposure experiments were excluded from the collection. Furthermore, studies were only included if they provided data on the ingestion of microplastic. For these studies, the ingestion incidence was calculated as the fraction of sampled individuals containing microplastic. The 95% confidence intervals for these binominal proportions were assessed using the Wilson method. (33) Subsequently, studies were scored according to method quality criteria discussed in the next section. All studies were assessed by two separate authors independently, after which differences in scoring were discussed and tuned until the assessment was done consistently across all studies. For maximizing transparency and traceability, the scoring explanations, scoring criteria, and scorings for all papers are provided as Supporting Information (Tables S1–S3, respectively). The eventual assessments do not express the value of studies. In hindsight, they only reflect the compliance of studies to reliability criteria as perceived by the authors of the present paper. Although we maximized our effort to be complete and thorough in this process, misinterpretations or misjudgements cannot be completely excluded.
The scoring method presented here was designed to assess current studies on reliability of their data on microplastic ingestion in marine field biota and is based on several aspects that define a reproducible and controlled study. The method evaluates the inherent adequacy of the employed methods for monitoring and risk assessment purposes relating to a standardized methodology and the description of the procedure and results. By scoring high in all categories, a study can be defined as “reliable”, providing reproducibility, clarity, and plausibility of its findings.

Quality Assessment System

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Previous scoring systems that have been proposed for assessing the reliability of ecotoxicology studies are the Klimisch (30) and the more recent CRED scoring systems. (31) The Klimisch criteria have received critiques for being unspecific and for lacking essential criteria and guidance, leaving too much room for interpretation. (31) The CRED evaluation method gives extensive guidance on how to use the set criteria and gives recommendations for reporting. (31) Following the example set by the CRED method, the present evaluation method for microplastic ingestion studies provides several criteria that must be assessed, including guidance on how to assess each criterion. The quality assessment method is made up of ten criteria: (1) sampling method and strategy, (2) sample size, (3) sample processing and storage, (4) laboratory preparation, (5) clean air conditions, (6) negative controls, (7) positive controls, (8) target component, (9) sample (pre)treatment, and (10) polymer identification (Table 1). For each criterion, a score of 0, 1, or 2 can be assigned to the publication under review. Scores signify the following: 2 = reliable without restrictions, 1 = somewhat reliable but with restrictions, 0 = not reliable. If information is lacking on certain aspects in the publication, this is considered unreliable, leading to a lower score. After each criterion is scored, an overall reliability score is calculated by taking the product of all criteria scores, resulting in a maximum attainable overall theoretical reliability score of 1024 points, indicating a high reliability of a publication. This contrasts with both the CRED and Klimisch method: these methods assign a category of reliability to each criterion but do not quantify it with a score. (30,31) In the evaluation method presented here, the quantification through scoring is deemed important because each criterion is considered crucial and equally important to the reliability of the results of a study. This means when a study scores 0 points on a criterion, too much uncertainty still surrounds the results of the study, marking the results unreliable. This also means that when only one criterion is evaluated as “not reliable” (0 points) the overall reliability score of the study will be 0. Besides this overall reliability score, we provide an accumulated score calculated as the sum of the individual scores. This score has a maximum of 20 points and can be seen as a combination of the reliability and the completeness of information in a publication.
In the following ten paragraphs, argumentation is provided on each of the ten scoring categories, including explanation based on the currently reviewed studies and specification of scoring criteria. A supporting, more detailed overview of the scoring criteria is provided as Supporting Information (Tables S1 and S2).

Sampling Methods and Strategy

Several factors related to sampling method and strategy affect the results of microplastic detection in biota samples. For instance, because of differences in density and sinking as a result of biofouling, plastic is found at different depths of the water column. (10,34) Microplastics are also known to accumulate in the sediment (28,35,36) with deep sea bottoms likely to make up a sink for the particles. (34,37,38) It is plausible that feeding strategy has an influence on the type and amount of microplastic ingested (39,40) with planktivorous and filter feeders expected to be more susceptible to ingestion of low density particles floating in the top layers of the water column and demersal and bottom dwelling species more likely to encounter high density microplastics. Additionally, some species are known for diurnal vertical migration and are subjected to a wide variety of microplastic encountered, possibly affecting their ingestion rates. Nonecological factors such as mesh size will influence life stage of the caught individuals in the sample, whereas a small mesh size could lead to cod-end feeding. (41) Sampling methods can greatly influence the outcome of a study; therefore, it is important that such characteristics of the sampling are recorded to create a reproducible study. (28,42) Furthermore, by reporting such details, it could be easier to interpret the outcome and account for possible contamination in the results.
In this section, studies are scored on reportage, and therefore reproducibility, of the sampling, but also on choice of sampling method itself. Studies scoring high in this section reported extensively on their methods (e.g., type of gear, sampling location and depth) and controlled their own sampling or were fully aware of what had happened to the specimens during sampling. Articles with low scores either failed to report on (parts of) their sampling (Table 2), or used, for instance, store-bought individuals when making inferences on natural populations. (43,44) The use of store- or market-bought individuals is not inherently wrong as long as the interest of the study lies on contamination of sea food and not on natural populations. Scores of 1 indicate that, for part of the sample, sampling was not performed correctly, whereas for another part of the sample it was: the aim of the study should be correctly matched to the sampling method. For example, Vandermeersch et al. (2015) (27) partially used store-bought individuals while using self-sampled ones for a different part of the study. The microplastic uptake in mussels from different estuaries was compared with the uptake by commercial mussels. The commercial mussels were bought in stores, leading to uncertainty about the treatment of these mussels prior to the analysis: microplastic found in these mussels could have originated from contamination during handling in the production chain rather than from microplastic ingestion by the mussels themselves. Would the aim of this study have been to check microplastic content in store-bought individuals (i.e., checking on general contamination, not ingestion), this would not have been an issue. This study scored 1 in this section because part of the study can be considered reliable with sampling method correctly matched to the aim of the specific part of the study.
Table 2. Standardized Protocol for the Detection of Ingested Microplastic in (Marine) Biota
1. Sampling methodsSampling characteristics that should be recorded:
- Gear
- Mesh size and mesh size at cod-end (if applicable)
- Material
- Location
- Depth
- Date and time of day
- Presence of plastic materials
2. Sample sizeA suitable sample size of 50 individuals per research unit (species, food web, ecoregion, feeding type, etc.) is required. (42,45)
The confidence interval of the ingestion incidences should be reported (Figure 1).
3. Sample processing and storageBetween the moment of capture and the examination in the lab the biota samples should be stored on ice or frozen at −20 °C. Smaller organisms can also be preserved in a glass container with ethanol or formaldehyde. Any sample handling, such as dissections, should be left for the lab.
4. Laboratory preparationAll materials, equipment, and laboratory surfaces need to be thoroughly washed and rinsed; afterward, all materials should be kept under clean air conditions. Used solutions and filters should be checked before use; the same applies for the outside of the sample specimens. (6)
5. Clean air conditionsThe handling of samples should be performed in clean air facilities. (28) Samples should not be taken out of the clean air facilities without being sealed off. If sampling processing and analysis cannot fully be conducted under clean air conditions, the implementation of negative controls (see criterion 6) will get even more important.
6. Negative controlA replicate of 3 negative controls is advised that are included for each batch of samples and treated in parallel to the sample treatment. (42)
Additionally, if the samples have to be analyzed outside of the clean air facilities, clean Petri dishes should be placed next to the sample, and checked for any occurred air- borne contamination.
7. Positive controlsA replicate of 3 is advised in which microplastics of known polymer identity and of targeted sizes are added to “clean” samples, which are then treated and analyzed the same way as the actual samples. The particle recoveries are calculated by tallying the numbers of retrieved particles to the amounts added.
8. Target componentTo ensure monitoring all ingested microplastic, the full gastrointestinal tract (esophagus to vent) of fish and the entire body of smaller species, e.g. bivalves, should be examined.
9. Sample treatmentA digestion step must be included to dissolve organic matter in the sample when aiming in the detection of small microplastics (<300 μm). The digestion method described by Foekema et al. (2013) (6) using a 10% KOH solution and enzymatic digestion methods (yet only for small organisms) are most suitable. (49,61,65) In any case, heating or drying of the samples at high temperatures should be avoided.
10. Polymer identificationUntil now, most common methods in the field of microplastic research are FTIR or Raman spectroscopy, pyrolysis or TGA- GC-MS. The polymer identification is required for all, or at least a subsample of particles: When numbers of pre- sorted particles are <100, all particles should be analyzed. For particle numbers >100, >50% should be identified with a minimum of 100 particles. Particle counts with confidence intervals, detection limits for the count and for minimum particle size, polymer types and percentages (of different polymer types, of synthetic vs natural material), and particle sizes should be reported.

Sample Size

Both the International Council for the Exploration of the Sea ICES (2015) (42) and the European Strategy Framework Directive’s Technical Subgroup on Marine Litter (MSFD-TSGML) (2013) (45) recommend a sample size of at least 50 individuals. This sample size of 50 is arbitrarily chosen, since, due to the wide variety in microplastic ingestion reported by different studies, no clear indication of the true ingestion incidence of microplastic by biota can be estimated. When more clarity can be given in the future, this recommended sample size should be adjusted accordingly. If ingestion incidence appears to be low, higher sample sizes will be needed to give reliable results; if populations show high incidence of microplastic ingestion, lower sample sizes will suffice.
The scoring in this category is fairly straightforward using the recommended 50 individuals as a threshold until it is possible to perform a reliable power analysis to calculate a more appropriate sample size for ingestion studies. Too low a sample size may provide interesting data, but no conclusions should be drawn as the statistical power of such a study would be simply too low to infer any trends. A larger sample size is always advisible because it will lead to more reliable results, i.e., narrower confidence intervals (Figure 1). Studies with a sample size over 50 specimens taken from a food web or ecoregion scored 2. A score of 0 was ascribed to studies using less than 50 specimens. Studies with >50 specimens in total and >25 specimens per research unit (e.g., a species, food web, or ecoregion) received a score of 1. For now, we also applied these criteria to a study that reported the presence of microplastic in a single-stranded whale, (16) leading to a very wide confidence interval (Figure 1). However, for whales or for rare and protected species, the n = 50 criterion is difficult or even unethical to achieve in a sampling effort meant to assess trends in microplastic ingestion. For such big or protected organisms, retrospective data obtained from stranded animals and from bycatch through different reports need to be combined to reach a sample size with sufficient rigor. (17) This would require harmonization of protocols to increase comparability of studies, guidance for which is beyond scope of the current review.

Figure 1

Figure 1. Ingestion incidence and 95% confidence intervals recalculated from data provided in microplastic ingestion studies. Data are combined to obtain a “whole ocean” biota ingestion incidence value (○).

We further advise provision of the confidence interval in the reported count (e.g., refs (5and46)); however, this was not yet included as criterion in the current scoring. On the basis of the total number of animals and the number of animals that ingested microplastics, we calculated the confidence intervals and provide an overview in Figure 1.

Sample Processing and Storage

After sampling, samples need to be stored until examination in the laboratory. Samples are often frozen, (5,9,47,48) or whole specimens of smaller species are preserved in fixatives such as formalin, ethanol, or formaldehyde. (49−53) ICES (2015) (42) recommends storing biota samples on board using aluminum foil for freezing at −20 °C or preservation in ethanol in glass containers. In the present study, it was not considered necessary to wrap each individual in aluminum foil as long as specimens were quickly frozen after capture at −20 °C and stored in a closed container. If this is combined with a pre-examination rinse of the specimens (see “laboratory preparation”), it should suffice in mediating contamination of the exterior of the specimen. Under no circumstance should the specimen be opened on board. This is considered as a high and difficult to assess risk for contamination due to unregulated conditions on board. We further recommend avoiding the dissection of individuals outside clean air conditions at all times (see “clean air conditions”).
High scores were assigned to studies freezing their samples shortly after capture at −20 °C or storing them on ice, leaving any further handling until the laboratory. Alternative methods storing the samples in closed off containers with a fixative were also given the highest scores in case potential effects of these chemicals on different plastics were studied before application. Recently, the resistance of microplastics to formaldehyde/ethanol has been confirmed. (49) Studies scoring low in this section performed dissections, or otherwise opened the specimens, on board. Middle scores again indicate some aspects of the study do not comply but still partially meet the standards (e.g., different processing for different subsamples).

Laboratory Preparation

Contamination is a prevalent issue in microplastic research, creating uncertainty around the results of many studies. (27,28,54) This risk and uncertainty have been dealt with in different ways. Different forms of prevention have been applied with varying degrees of success. Foekema et al. (2013) (6) decided to exclude small fibers from analyses after finding a sharply decreased abundance when working under clean air conditions. ICES (2015) (42) proposed in their preliminary protocol to exclude all fibers smaller than 5 mm in length from results. Although this may provide a way to reduce the issue of contamination in results, it is less than ideal; by excluding all small fibers from results, truly ingested fibers will be excluded from the results too. This could lead to an underestimation of ingestion rates and a potential knowledge gap in the ingestion of microplastic. Therefore, proper prevention is needed. In the laboratory, contaminations with synthetic polymers should be avoided as they may influence ingestion results. (6,27) Equipment, tools, and work surfaces should be free of particles to avoid easy contamination. To this end, all materials used should be washed and rinsed thoroughly with high quality water (e.g., Milli-Q water) before use and preferably kept in a clean air cabinet.
Factors such as clothing should be considered. Often, contamination arises in the form of microfibers. (27,28) Additional contamination originating from researchers’ clothing can easily be avoided by solely wearing 100% natural fiber clothing, such as cotton. Only wearing a 100% cotton lab coat may not suffice; if one was to wear a polyester shirt underneath, it would not be unimaginable that some fibers could end up in the samples. For the current scoring in this study, if all other precautions were met, a 100% cotton lab coat was considered sufficient.
In some studies, precautions were made by wiping surfaces and tools using alcohol. (55) This method is probably not thorough enough to deal with contamination; merely wiping surfaces, be it with alcohol or water, could still leave particles. They could be missed, detach from the wipe during wiping, or the wipe itself could even prove to be a source of contamination (i.e., the material or dust already collected on the wipe before use). Rigorously washing and rinsing of the equipment are considered to be the only proper option here.
Additional to the preparation of surfaces and tools, the sample specimens themselves require some preparation. The exterior of the animal should be rinsed (6,46) and checked for contamination. In the case of small specimens such as zooplankton, this is not an easy feat. In a study performed by Desforges et al. (2015), (50) this issue was overcome by individually checking each specimen under a microscope and picking off any external contamination with a pair of tweezers.
In summary, a score of 2 was assigned when nonsynthetic clothing and a lab coat were used and equipment and organism exterior were rinsed. A score of 1 was assigned for solely wiping laboratory surfaces and equipment or not wearing a lab coat as long as negative control samples were run in parallel and examined for contamination. A score of 0 was assigned when no precautions were met.

Clean Air Conditions

Problems with airborne contamination are unavoidable unless work is performed under clean air conditions. (6,27,28) To this end, sample handling should be done in a laminar flow cabinet (42,46,56) or in a “clean room”, which is designed to minimize airborne contamination during sample handling and analysis. (28,57) The use of such facilities is a necessity in microplastic research; any handling of samples outside clean air conditions creates a high risk of airborne contamination. (57)
Other studies placed their samples in a fume hood to minimize the risk of contamination. (56) However, because a fume hood draws air from the room into the hood (contrarily to a positive pressure laminar flow cabinet, which blows filtered air through the cabinet into the room), the risk of airborne contamination remains. (57)
A few studies were seen that mitigated contamination by closing off samples as much as possible and handling them as fast as possible. (44,53) These methods are not foolproof and should not be relied upon without further indication on results of negative samples treated in parallel to actual samples.
The proper use of clean air conditions was given a score of 2. A score of 0 was assigned to studies taking no regard for airborne contamination. Studies mitigating contamination by carefully keeping samples in a closed off situation as much possible scored 1 in this category, provided that negative controls were run in parallel and examined for contamination.

Negative Controls

Although increasing in recent studies, the use of controls in microplastic research is not standard practice. During sample handling, the chances of contamination by microplastic particles and fibers are high; thus, the use of controls, treated and analyzed in parallel to actual samples, is crucial.
For a study to score 2, proper blanks should be included for each batch of samples with at least three replicate blanks per batch. These controls should be performed without tissue, or with tissue that was confirmed to be devoid of microplastic, in parallel with samples containing the target component. (42,58) By doing so, the controls are given the same full treatment as the studied specimens. Controls should be run regularly and with special attention to moments of high risk of contamination, such as moving specimens in and out of the laminar flow cabinet. (29) Furthermore, the visual examination of samples forms a moment of high risk, which is why additionally placed and examined Petri dishes next to the sample might be advisible. (46)
Scores of 1 indicate a blank analysis of some form, nevertheless deemed insufficient here. This includes, for instance, solely open Petri dishes or soaked paper that were placed next to the work surface and checked for contamination (46,48) or the filtration of air. These do not account for contamination derived from used chemicals or equipment. Studies scored 0 when no form of negative control was included in the study.

Positive Controls

It is generally difficult to assess whether all microplastics present in a sample are effectively recovered from that sample. Small particles in particular may be overlooked or missed, and losses may occur during all steps of sample preparation, processing, and analysis. Therefore, it is considered crucial to include controls (triplicate) with added microplastic particles that are treated in parallel to the samples to determine the recovery rate (score of 2 points). Ideally, positive controls should also be included for the smallest targeted size class, and the limit in the detected size should be reported. We are aware of only three studies that included reliable positive controls. (41,46,59) Davison and Asch, for instance, (41) blindly added random numbers of spherical beads from two size classes into fish stomach contents, so that the researcher would not know this number, and were able to trace back all added particles to achieve 100% recovery. A score of 1 was assigned to studies with some form of a positive control (e.g., testing only a part of the protocol), and a score of 0 was assigned when no positive controls were included.

Target Component

Among the reviewed studies, different target components were described that are mainly (parts of) the digestive tracts for larger biota, like fish, (5,6,9,46,52) or whole specimens for smaller species, like bivalves (27,50,60) Choosing a suitable target component is an important part of the study setup. For accurate estimation of microplastic ingestion, it is important to examine the entire gastrointestinal tract (GIT) (esophagus to vent). By only examining the stomach, particles in the gut would be missed, leading to an underestimation of ingestion rate. When small animals such as bivalves and zooplankton are being studied, the entire specimen should be used.
Studies examining full specimens or entire GITs received the highest score. Examination of parts of the GIT were scored lowest. In case a study examined a part of the GIT for a subsample yet full GITs for the rest of the sample, it was scored 1.

Sample (Pre)treatment

For extracting and characterizing microplastics in biological samples, a digestion step is a crucial component, namely, dissolving organic matter without degrading plastic polymers. Detection of microplastic in a biological sample without getting rid of the organic matter makes for an unreliable method; the chance of missing particles is high, especially small particles that are not visually detectable. (27) Therefore, it is advised to make use of a digestion pretreatment. (42,61)
Dehaut et al. (2016) (62) performed a study testing six existing methods (including enzymatic, alkaline, and acidic digestion), comparing their effects on 15 different plastic polymers as well as their efficiency in biological samples. Their tests showed that, out of the six protocols, an adapted protocol of Foekema et al. (2013) (6) was most successful. The original protocol involves the samples being left for digestion in 10% KOH solution and kept at room temperature for 3 weeks. The adapted protocol used 10% KOH solution with 24 h of incubation at 60 °C. (62) This adaptation was made to shorten the incubation time. The heating of samples during digestion pretreatments to speed up the process is fairly common, and especially with acidic digestion methods, this is often part of the protocol. However, this practice may be ill advised because the heating of the samples could cause some microplastic particles to deform or clump together. (63) Therefore, it is advised to apply the original protocol of Foekema et al. (2013). (6) The adequacy of the 10% KOH protocol has recently been confirmed by Kühn et al. (2017) (64) and Munno et al. (2018). (63) However, for smaller organisms, like the soft tissue of mussels or plankton species, enzymatic methods have also been shown to provide high digestion rates with no damage to microplastic. (65,66)
On the basis of these findings, studies using a 10% KOH solution-based digestion, or an enzymatic digestion, received the highest score of 2. Studies not incorporating a digestion step received no points. Studies using other digestion methods were scored 1. A score of 1 was also assigned to studies that did not need a digestion step because the size of particles was large enough, which can be achieved by sieving the samples over 300 μm. This mesh size allows adequate particle sorting as is done frequently for, e.g., water samples. (67−69)

Polymer Identification

Accurate identification of polymer types in environmental samples can be laborious. Hence, two aspects are relevant when assessing the polymer identities of a microplastic sample: (1) the quality of the method used for the identification (efficiency, sensitivity, accuracy, reproducibility) and (2) the quality of the selection of the subsample (representativeness).

Polymer Identity

Visual inspection (i.e., characterizing microplastic by eye under a dissection or stereomicroscope) was found to be a frequently used identification method. (8,9,47,50,56,58,70) However, visual examination cannot be used to identify the (polymer) identity of a particle. Without formal evidence of polymer identity, a particle cannot be reported as being a microplastic particle. The quality of visual examination is influenced by the observer, properties of the plastic, targeted microplastic size, magnification of the microscope, and sample type. (28) In a case study on microplastics in North Sea sediments, the usage of focal plane array (FPA) micro-Fourier transform infrared (micro-FTIR) spectroscopy revealed that only 1.4% of the particles visually sorted as microplastic were actually synthetic polymers. (29) Fibers with a size over 500 μm were found to be of natural origin after an initial selection as microplastic. (28,71) This uncertainty of visual identification further increases as particle size decreases, which illustrates the importance of verifying the chemical origin of potential microplastics.
To date, potential microplastics are identified mostly using spectroscopic (29,69,72) or thermal degradation analyses. (73−75) Particles sorted manually are mostly analyzed using attenuated total reflectance (ATR) Fourier transform infrared (FTIR) spectroscopy, (49,58) but pyrolysis GC-MS is also applied. (73) Both techniques result in a clear identification but are restricted to bigger particles due to the manual particle handling. When aiming for microscopic particle determination, the coupling of a microscope to FTIR or Raman spectroscopy reveals the chemical identity of particles and allows particle sizes to be estimated. Both techniques are limited by a certain minimum particle size. (72,76,77) Alternatively, unsorted samples, i.e., where a polymer mixture might be present, can be analyzed using thermal degradation techniques. (74,75) Because particles are not sorted manually, these techniques are not limited by a minimum particle size required; however, they do not provide information on microplastic size either. Furthermore, they do provide information on ingested polymer masses instead of presenting the numbers of ingested microplastic particles. One of these techniques should be applied and should always be favored over the so-called “hot point-test” applied by several studies. (27,42,56) Plastic particles are “identified” when a particle shows a sticky dark mark when touched with a hot needle. However, this test does not allow polymer identification, is less suitable for thermoset and smaller plastics, and should therefore only be seen as a facilitation for visual sorting.

Representative Subsample of Particles

Many studies report polymer identities for a small subset of sorted particles only. (6,53) This leaves considerable uncertainty with respect to the actual distribution of polymer types among samples. On the basis of practical experience using ATR-FTIR to determine polymer identities, (6,16,46) we advise that when numbers of presorted particles are <100, all particles should be analyzed. For particle numbers >100, analysis becomes more laborious, but >50% should be identified for a representative subsample with a minimum of 100 particles being analyzed. The information given in the results section should contain the following: particle counts with confidence intervals, detection limits for the count and for minimum particle size, the polymer types determined, their percentages with regard to other polymer types and natural particles, and the microplastic size (classes).
If a study identified polymer identities and applied the latter criteria, 2 points were assigned. For insufficient numbers of identified particles that could result in an unrepresentative subsample, 1 point was assigned. Zero points were given if no polymer identification (i.e., purely visual sorting) was conducted.

Protocol for Microplastic Ingestion Studies in Biota

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In this article, as a synthesis of our review and method assessment, we propose a standardized protocol for the detection of ingested microplastic in (marine) biota alongside the quality assessment method (Table 2). The protocol is adaptable for both vertebrates and invertebrates as long as the components of the quality assessment system are upheld. The protocol was developed taking the recommended protocol by ICES (2015) (42) into account and amending with knowledge and evaluation of currently existing methodologies as outlined above. The protocol and quality assessment system are such that, when following the protocol successfully, high reliability scores can be acquired. This protocol relies on the same literature analysis and argumentation as the assessment method and follows the categories step-by-step.

General Discussion

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Considerable uncertainty with respect to methodology was observed and quantified via the scoring system. Accumulated reliability scores ranged from 0 to 15 out of a maximum of 20 with an average of 8.0 (Table 1). As mentioned before, the results of such an assessment are not an absolute judgment, and the results should not be used as a ranking list of the value of studies. The scores are an indicator of the usefulness of these studies for risk assessment and monitoring purposes with respect to natural populations. The assessment evaluates common characteristics of a variety of studies. Not all decisions in a study can be captured in the scoring system; therefore, it is still important to critically look at a study and reflect upon its plausibility and comparability to other studies and not just upon its results.
Often studies could not be assigned a high score due to missing information on certain characteristics, such as details of the sampling or analytical procedures. Average scores (n = 35) per evaluation criterion were especially low (<1) for the criterion “positive controls” (0.17), “clean air conditions” (0.40), “sample treatment” (0.43), “laboratory preparation” (0.57), “polymer identification” (0.66), and “negative controls” (0.86) (Table 1). By leaving out such essential information, a study immediately becomes irreproducible and thus less reliable. One reason for initiating the present review was to systematically define this crucial information, such that future studies can avoid this by using standardized consensus methods.
On the basis of the assessment of reviewed papers (considered representative for currently available knowledge, Table S3), we conclude that all reviewed studies are not fully reliable. All studies scored 0 in at least one category, indicating an uncertainty around at least one of its aspects. Therefore, the overall reliability scores, calculated as the product of individual scores, were all 0 and thus were not included in Table 1. Each category of the assessment was defined by the consideration that if its set criteria were not up to par, the possibility of contamination could not be excluded. This is problematic, and for future studies the use of the proposed protocol is strongly recommended to obtain reliable and reproducible results. Following the proposed protocol, we conducted a study focusing on microplastic detection in North Sea fish while giving special attention to quality assurance and full reportage. (46)
Our meta-analysis of microplastic ingestion data shows a wide variability among studies, which may be due to methodological, ecological, and/or spatial differences. Ingestion incidence ranges from 0 to 100% with confidence intervals that are narrower for higher sample sizes (Figure 1). On the basis of pooled data from all studies, an overall biota ingestion incidence of 16.6% (15.9–17.2 95% CI) was calculated. This “whole ocean” value can be interpreted as the percentage of the 13722 biota individuals sampled across all oceans in which microplastic was detected in the period of 2010–2017. The data underlying Figure 1 further reveal that, with sample sizes lower than 50, the confidence intervals can become as wide as 35–80% (Figure 1).

Perspective and Outlook

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We provided an evaluation method for the quality of studies reporting microplastic ingestion by biota. The applied quality criteria were defined based on a critical review of the literature available. Current studies are not of such a level of reliability that they could be used confidently for risk assessment or monitoring of microplastic by biota in the natural environment. Reliable ingestion rate studies are needed to define whether there is a risk posed by microplastic ingestion to the natural environment and to human food-safety. The proposed protocol can be used to perform these studies; the quality assessment system can be applied to control the quality of these data and enable an easier comparison of studies to move toward standardization and reliability. The quality assessment system may provide a tool and set an example that will help regulators and policy makers in their activities to mitigate contamination with plastic debris. Until now, the majority of studies focused on visually sortable microplastics. Our present scoring system is tuned to this research aim and used today’s best available information. However, we foresee that our recommendations may need adaptations when the focus is on much smaller microplastic, which is more difficult to detect. It is also conceivable that our proposed scoring system needs modification if the research field evolves, for instance, when new analytical technologies become available, just like the aforementioned CRED criteria (31) can be seen as evolving from the original Klimisch criteria (30) for ecotoxicology studies. For now, all criteria were weighed equally as we considered all of them to be crucial for generating reliable results. Future research, however, may provide a rationale for using unequal weights, which thus would lead to another outcome of the scoring. Finally, we emphasize that a protocol and scoring system for microplastic analytical studies should be seen as a product of the scientific community rather than a product of a limited set of authors. In this sense, we see the present paper as a starting point in assessing quality assurance criteria for microplastic analytical studies rather than the final stage.

Supporting Information

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The Supporting Information is available free of charge on the ACS Publications website at DOI: 10.1021/acs.est.8b01611.

  • Explanation and definition of scores and scoring of individual papers (PDF)

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Most electronic Supporting Information files are available without a subscription to ACS Web Editions. Such files may be downloaded by article for research use (if there is a public use license linked to the relevant article, that license may permit other uses). Permission may be obtained from ACS for other uses through requests via the RightsLink permission system: http://pubs.acs.org/page/copyright/permissions.html.

Author Information

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  • Corresponding Author
  • Authors
    • Enya Hermsen - Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The Netherlands
    • Svenja M. Mintenig - Copernicus Institute of Sustainable Development, Utrecht University, Utrecht, The NetherlandsKWR Watercycle Research Institute, Nieuwegein, The Netherlands
    • Ellen Besseling - Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The NetherlandsWageningen Marine Research, IJmuiden, The NetherlandsOrcidhttp://orcid.org/0000-0003-0686-2173
  • Author Contributions

    E.H. and S.M.M. contributed equally to this work.

  • Notes
    The authors declare no competing financial interest.

Acknowledgments

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S.M.M. and A.A.K. acknowledge funding from the Dutch Technology Foundation TTW (project number 13940) and additional support from KWR, IMARES, NVWA, RIKILT, the Dutch Ministry of Infrastructure and the Environment, The Dutch Ministry of Health, Welfare and Sport, Wageningen Food & Biobased Research, STOWA, RIWA, and the Dutch water boards.

References

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This article references 88 other publications.

  1. 1
    GESAMP Sources, fate and effects of microplastics in the marine environment: part two of a global assessment; Kershaw, P. J., Rochman, C. M., eds.; IMO/FAO/UNESCO-IOC/UNIDO/WMO/IAEA/UN/ UNEP/UNDP Joint Group of Experts on the Scientific Aspects of Marine Environmental Protection; Rep. Stud. GESAMP, 2016; Vol. 93, p 220.
  2. 2
    Wright, S. L.; Thompson, R. C.; Galloway, T. S. The physical impacts of microplastics on marine organisms: A review. Environ. Pollut. 2013, 178, 483492,  DOI: 10.1016/j.envpol.2013.02.031
  3. 3
    Browne, M. A.; Galloway, T.; Thompson, R. Microplastic—an emerging contaminant of potential concern?. Integr. Environ. Assess. Manage. 2007, 3 (4), 559561,  DOI: 10.1002/ieam.5630030412
  4. 4
    Chen, Q.; Reisser, J.; Cunsolo, S.; Kwadijk, C.; Kotterman, M.; Proietti, M.; Slat, B.; Ferrari, F. F.; Schwarz, A.; Levivier, A.; Yin, D.; Hollert, H.; Koelmans, A. A. Pollutants in Plastics within the North Pacific Subtropical Gyre. Environ. Sci. Technol. 2018, 52 (2), 446456,  DOI: 10.1021/acs.est.7b04682
  5. 5
    Lusher, A. L.; McHugh, M.; Thompson, R. C. Occurrence of microplastics in the gastrointestinal tract of pelagic and demersal fish from the English Channel. Mar. Pollut. Bull. 2013, 67 (1), 9499,  DOI: 10.1016/j.marpolbul.2012.11.028
  6. 6
    Foekema, E. M.; De Gruijter, C.; Mergia, M. T.; van Franeker, J. A.; Murk, A. J.; Koelmans, A. A. Plastic in North Sea Fish. Environ. Sci. Technol. 2013, 47 (15), 88188824,  DOI: 10.1021/es400931b
  7. 7
    Neves, D.; Sobral, P.; Ferreira, J. L.; Pereira, T. Ingestion of microplastics by commercial fish off the Portuguese coast. Mar. Pollut. Bull. 2015, 101 (1), 119126,  DOI: 10.1016/j.marpolbul.2015.11.008
  8. 8
    Mathalon, A.; Hill, P. Microplastic fibers in the intertidal ecosystem surrounding Halifax Harbor, Nova Scotia. Mar. Pollut. Bull. 2014, 81 (1), 6979,  DOI: 10.1016/j.marpolbul.2014.02.018
  9. 9
    Romeo, T.; Pietro, B.; Pedà, C.; Consoli, P.; Andaloro, F.; Fossi, M. C. First evidence of presence of plastic debris in stomach of large pelagic fish in the Mediterranean Sea. Mar. Pollut. Bull. 2015, 95 (1), 358361,  DOI: 10.1016/j.marpolbul.2015.04.048
  10. 10
    Lusher, A. Microplastics in the Marine Environment: Distribution, Interactions and Effects. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Cham, 2015; pp 245307.
  11. 11
    Teuten, E. L.; Saquing, J. M.; Knappe, D. R. U.; Barlaz, M. A.; Jonsson, S.; Björn, A.; Rowland, S. J.; Thompson, R. C.; Galloway, T. S.; Yamashita, R.; Ochi, D.; Watanuki, Y.; Moore, C.; Viet, P. H.; Tana, T. S.; Prudente, M.; Boonyatumanond, R.; Zakaria, M. P.; Akkhavong, K.; Ogata, Y.; Hirai, H.; Iwasa, S.; Mizukawa, K.; Hagino, Y.; Imamura, A.; Saha, M.; Takada, H. Transport and release of chemicals from plastics to the environment and to wildlife. Philos. Trans. R. Soc., B 2009, 364 (1526), 20272045,  DOI: 10.1098/rstb.2008.0284
  12. 12
    Mato, Y.; Isobe, T.; Takada, H.; Kanehiro, H.; Ohtake, C.; Kaminuma, T. Plastic resin pellets as a transport medium for toxic chemicals in the marine environment. Environ. Sci. Technol. 2001, 35 (2), 318324,  DOI: 10.1021/es0010498
  13. 13
    Diepens, N. J.; Koelmans, A. A. Accumulation of plastic debris and associated contaminants in aquatic food webs. Environ. Sci. Technol. 2018, 52, 85108520,  DOI: 10.1021/acs.est.8b02515
  14. 14
    Cozar, A.; Echevarria, F.; Gonzalez-Gordillo, J. I.; Irigoien, X.; Ubeda, B.; Hernandez-Leon, S.; Palma, A. T.; Navarro, S.; Garcia-de-Lomas, J.; Ruiz, A.; Fernandez-de-Puelles, M. L.; Duarte, C. M. Plastic debris in the open ocean. Proc. Natl. Acad. Sci. U. S. A. 2014, 111 (28), 1023910244,  DOI: 10.1073/pnas.1314705111
  15. 15
    Rochman, C. M.; Browne, M. A.; Underwood, A. J.; van Franeker, J. A.; Thompson, R. C. T.; Amaral-Zettler, L. A. The ecological impacts of marine debris: unraveling the demonstrated evidence from what is perceived. Ecology 2016, 97 (2), 302312,  DOI: 10.1890/14-2070.1
  16. 16
    Besseling, E.; Foekema, E. M.; Van Franeker, J. A.; Leopold, M. F.; Kuhn, S.; Rebolledo, E. L. B.; Hesse, E.; Mielke, L.; Ijzer, J.; Kamminga, P.; Koelmans, A. A. Microplastic in a macro filter feeder: Humpback whale Megaptera novaeangliae. Mar. Pollut. Bull. 2015, 95 (1), 248252,  DOI: 10.1016/j.marpolbul.2015.04.007
  17. 17
    Lusher, A. L.; Hernandez-Milian, G.; Berrow, S.; Rogan, E.; O’Connor, I. Incidence of marine debris in cetaceans stranded and bycaught in Ireland: Recent findings and a review of historical knowledge. Environ. Pollut. 2018, 232, 467476,  DOI: 10.1016/j.envpol.2017.09.070
  18. 18
    Herzke, D.; Anker-Nilssen, T.; Nøst, T. H.; Götsch, A.; Christensen-Dalsgaard, S.; Langset, M.; Fangel, K.; Koelmans, A. A. Negligible Impact of Ingested Microplastics on Tissue Concentrations of Persistent Organic Pollutants in Northern Fulmars off Coastal Norway. Environ. Sci. Technol. 2016, 50 (4), 19241933,  DOI: 10.1021/acs.est.5b04663
  19. 19
    Koelmans, A. A. Modeling the Role of Microplastics in Bioaccumulation of Organic Chemicals to Marine Aquatic Organisms. A Critical Review. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Cham, 2015; pp 309324.
  20. 20
    Koelmans, A. A.; Besseling, E.; Wegner, A.; Foekema, E. M. Plastic as a Carrier of POPs to Aquatic Organisms: A Model Analysis. Environ. Sci. Technol. 2013, 47 (14), 78127820,  DOI: 10.1021/es401169n
  21. 21
    Setälä, O.; Fleming-Lehtinen, V.; Lehtiniemi, M. Ingestion and transfer of microplastics in the planktonic food web. Environ. Pollut. 2014, 185 (0), 7783,  DOI: 10.1016/j.envpol.2013.10.013
  22. 22
    Farrell, P.; Nelson, K. Trophic level transfer of microplastic: Mytilus edulis (L.) to Carcinus maenas (L.). Environ. Pollut. 2013, 177, 13,  DOI: 10.1016/j.envpol.2013.01.046
  23. 23
    Wright, S. L.; Kelly, F. J. Plastic and Human Health: A Micro Issue?. Environ. Sci. Technol. 2017, 51 (12), 66346647,  DOI: 10.1021/acs.est.7b00423
  24. 24
    Filella, M. Questions of size and numbers in environmental research on microplastics: methodological and conceptual aspects. Environmental Chemistry 2015, 12 (5), 527538,  DOI: 10.1071/EN15012
  25. 25
    Connors, K. A.; Dyer, S. D.; Belanger, S. E. Advancing the quality of environmental microplastic research. Environ. Toxicol. Chem. 2017, 36 (7), 16971703,  DOI: 10.1002/etc.3829
  26. 26
    Hanvey, J. S.; Lewis, P. J.; Lavers, J. L.; Crosbie, N. D.; Pozo, K.; Clarke, B. O. A review of analytical techniques for quantifying microplastics in sediments. Anal. Methods 2017, 9 (9), 13691383,  DOI: 10.1039/C6AY02707E
  27. 27
    Vandermeersch, G.; Van Cauwenberghe, L.; Janssen, C. R.; Marques, A.; Granby, K.; Fait, G.; Kotterman, M. J. J.; Diogène, J.; Bekaert, K.; Robbens, J.; Devriese, L. A critical view on microplastic quantification in aquatic organisms. Environ. Res. 2015, 143, 4655,  DOI: 10.1016/j.envres.2015.07.016
  28. 28
    Wesch, C.; Bredimus, K.; Paulus, M.; Klein, R. Towards the suitable monitoring of ingestion of microplastics by marine biota: A review. Environ. Pollut. 2016, 218, 12001208,  DOI: 10.1016/j.envpol.2016.08.076
  29. 29
    Löder, M. G. J.; Gerdts, G. Methodology Used for the Detection and Identification of Microplastics - A Critical Appraisal. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Berlin, 2015; pp 201227.
  30. 30
    Klimisch, H. J.; Andreae, M.; Tillmann, U. A Systematic Approach for Evaluating the Quality of Experimental Toxicological and Ecotoxicological Data. Regul. Toxicol. Pharmacol. 1997, 25 (1), 15,  DOI: 10.1006/rtph.1996.1076
  31. 31
    Kase, R.; Korkaric, M.; Werner, I.; Ågerstrand, M. Criteria for Reporting and Evaluating ecotoxicity Data (CRED): comparison and perception of the Klimisch and CRED methods for evaluating reliability and relevance of ecotoxicity studies. Environ. Sci. Eur. 2016, 28 (1), 7,  DOI: 10.1186/s12302-016-0073-x
  32. 32
    Koelmans, A. A.; Besseling, E.; Foekema, E.; Kooi, M.; Mintenig, S.; Ossendorp, B. C.; Redondo-Hasselerharm, P. E.; Verschoor, A.; van Wezel, A. P.; Scheffer, M. Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief. Environ. Sci. Technol. 2017, 51 (20), 1151311519,  DOI: 10.1021/acs.est.7b02219
  33. 33
    Brown, L. D.; Cai, T. T.; DasGupta, A. Interval Estimation for a Binomial Proportion. Statistical Science 2001, 16 (2), 101117,  DOI: 10.1214/ss/1009213286
  34. 34
    Kooi, M.; Nes, E. H. v.; Scheffer, M.; Koelmans, A. A. Ups and Downs in the Ocean: Effects of Biofouling on Vertical Transport of Microplastics. Environ. Sci. Technol. 2017, 51 (14), 79637971,  DOI: 10.1021/acs.est.6b04702
  35. 35
    Gall, S. C.; Thompson, R. C. The impact of debris on marine life. Mar. Pollut. Bull. 2015, 92 (1), 170179,  DOI: 10.1016/j.marpolbul.2014.12.041
  36. 36
    Claessens, M.; De Meester, S.; Van Landuyt, L.; De Clerck, K.; Janssen, C. R. Occurrence and distribution of microplastics in marine sediments along the Belgian coast. Mar. Pollut. Bull. 2011, 62 (10), 2199204,  DOI: 10.1016/j.marpolbul.2011.06.030
  37. 37
    Woodall, L. C.; Gwinnett, C.; Packer, M.; Thompson, R. C.; Robinson, L. F.; Paterson, G. L. J. Using a forensic science approach to minimize environmental contamination and to identify microfibres in marine sediments. Mar. Pollut. Bull. 2015, 95 (1), 4046,  DOI: 10.1016/j.marpolbul.2015.04.044
  38. 38
    Van Cauwenberghe, L.; Vanreusel, A.; Mees, J.; Janssen, C. R. Microplastic pollution in deep-sea sediments. Environ. Pollut. 2013, 182, 495499,  DOI: 10.1016/j.envpol.2013.08.013
  39. 39
    Setälä, O.; Norkko, J.; Lehtiniemi, M. Feeding type affects microplastic ingestion in a coastal invertebrate community. Mar. Pollut. Bull. 2016, 102 (1), 95101,  DOI: 10.1016/j.marpolbul.2015.11.053
  40. 40
    Redondo-Hasselerharm, P. E.; Falahudin, D.; Peeters, E. T. H. M.; Koelmans, A. A. Microplastic Effect Thresholds for Freshwater Benthic Macroinvertebrates. Environ. Sci. Technol. 2018, 52 (4), 22782286,  DOI: 10.1021/acs.est.7b05367
  41. 41
    Davison, P.; Asch, R. G. Plastic ingestion by mesopelagic fishes in the North Pacific Subtropical Gyre. Mar. Ecol.: Prog. Ser. 2011, 432, 173180,  DOI: 10.3354/meps09142
  42. 42
    OSPAR request on development of a common monitoring protocol for plastic particles in fish stomachs and selected shellfish on the basis of existing fish disease surveys. IICES Advice 2015, 1, 16.
  43. 43
    Cannon, S. M. E.; Lavers, J. L.; Figueiredo, B. Plastic ingestion by fish in the Southern Hemisphere: A baseline study and review of methods. Mar. Pollut. Bull. 2016, 107, 286291,  DOI: 10.1016/j.marpolbul.2016.03.057
  44. 44
    Jabeen, K.; Su, L.; Li, J.; Yang, D.; Tong, C.; Mu, J.; Shi, H. Microplastics and mesoplastics in fish from coastal and fresh waters of China. Environ. Pollut. 2017, 221, 141149,  DOI: 10.1016/j.envpol.2016.11.055
  45. 45
    MSFD (Technical Subgroup on Marine Litter). Guidance on Monitoring of Marine Litter in European Seas , 2013.
  46. 46
    Hermsen, E.; Pompe, R.; Besseling, E.; Koelmans, A. A. Detection of low numbers of microplastics in North Sea fish using strict quality assurance criteria. Mar. Pollut. Bull. 2017, 122 (1), 253258,  DOI: 10.1016/j.marpolbul.2017.06.051
  47. 47
    Bellas, J.; Martínez-Armental, J.; Martínez-Cámara, A.; Besada, V.; Martínez-Gómez, C. Ingestion of microplastics by demersal fish from the Spanish Atlantic and Mediterranean coasts. Mar. Pollut. Bull. 2016, 109 (1), 5560,  DOI: 10.1016/j.marpolbul.2016.06.026
  48. 48
    Lusher, A. L.; O’Donnell, C.; Officer, R.; O’Connor, I. Microplastic interactions with North Atlantic mesopelagic fish. ICES J. Mar. Sci. 2016, 73 (4), 12141225,  DOI: 10.1093/icesjms/fsv241
  49. 49
    Courtene-Jones, W.; Quinn, B.; Murphy, F.; Gary, S. F.; Narayanaswamy, B. E. Optimisation of enzymatic digestion and validation of specimen preservation methods for the analysis of ingested microplastics. Anal. Methods 2017, 9, 14371445,  DOI: 10.1039/C6AY02343F
  50. 50
    Desforges, J.-P. W.; Galbraith, M.; Ross, P. S. Ingestion of Microplastics by Zooplankton in the Northeast Pacific Ocean. Arch. Environ. Contam. Toxicol. 2015, 69 (3), 320330,  DOI: 10.1007/s00244-015-0172-5
  51. 51
    Murray, F.; Cowie, P. R. Plastic contamination in the decapod crustacean Nephrops norvegicus (Linnaeus, 1758). Mar. Pollut. Bull. 2011, 62 (6), 12071217,  DOI: 10.1016/j.marpolbul.2011.03.032
  52. 52
    Boerger, C. M.; Lattin, G. L.; Moore, S. L.; Moore, C. J. Plastic ingestion by planktivorous fishes in the North Pacific Central Gyre. Mar. Pollut. Bull. 2010, 60 (12), 22752278,  DOI: 10.1016/j.marpolbul.2010.08.007
  53. 53
    Karlsson, T. M.; Vethaak, A. D.; Almroth, B. C.; Ariese, F.; van Velzen, M.; Hassellöv, M.; Leslie, H. A. Screening for microplastics in sediment, water, marine invertebrates and fish: Method development and microplastic accumulation. Mar. Pollut. Bull. 2017, 122 (1), 403408,  DOI: 10.1016/j.marpolbul.2017.06.081
  54. 54
    Torre, M.; Digka, N.; Anastasopoulou, A.; Tsangaris, C.; Mytilineou, C. Anthropogenic microfibres pollution in marine biota. A new and simple methodology to minimize airborne contamination. Mar. Pollut. Bull. 2016, 113 (1), 5561,  DOI: 10.1016/j.marpolbul.2016.07.050
  55. 55
    Liboiron, M.; Liboiron, F.; Wells, E.; Richárd, N.; Zahara, A.; Mather, C.; Bradshaw, H.; Murichi, J. Low plastic ingestion rate in Atlantic cod (Gadus morhua) from Newfoundland destined for human consumption collected through citizen science methods. Mar. Pollut. Bull. 2016, 113 (1), 428437,  DOI: 10.1016/j.marpolbul.2016.10.043
  56. 56
    Devriese, L. I.; van der Meulen, M. D.; Maes, T.; Bekaert, K.; Paul-Pont, I.; Frère, L.; Robbens, J.; Vethaak, A. D. Microplastic contamination in brown shrimp (Crangon crangon, Linnaeus 1758) from coastal waters of the Southern North Sea and Channel area. Mar. Pollut. Bull. 2015, 98 (1), 179187,  DOI: 10.1016/j.marpolbul.2015.06.051
  57. 57
    Wesch, C.; Elert, A. M.; Wörner, M.; Braun, U.; Klein, R.; Paulus, M. Assuring quality in microplastic monitoring: About the value of clean-air devices as essentials for verified data. Sci. Rep. 2017, 7 (1), 5424,  DOI: 10.1038/s41598-017-05838-4
  58. 58
    Rummel, C. D.; Löder, M. G. J.; Fricke, N. F.; Lang, T.; Griebeler, E. M.; Janke, M.; Gerdts, G. Plastic ingestion by pelagic and demersal fish from the North Sea and Baltic Sea. Mar. Pollut. Bull. 2016, 102 (1), 134141,  DOI: 10.1016/j.marpolbul.2015.11.043
  59. 59
    Davidson, K.; Dudas, S. E. Microplastic Ingestion by Wild and Cultured Manila Clams (Venerupis philippinarum) from Baynes Sound, British Columbia. Arch. Environ. Contam. Toxicol. 2016, 71 (2), 147156,  DOI: 10.1007/s00244-016-0286-4
  60. 60
    Van Cauwenberghe, L.; Janssen, C. R. Microplastics in bivalves cultured for human consumption. Environ. Pollut. 2014, 193, 6570,  DOI: 10.1016/j.envpol.2014.06.010
  61. 61
    Löder, M. G. J.; Imhof, H. K.; Ladehoff, M.; Löschel, L. A.; Lorenz, C.; Mintenig, S.; Piehl, S.; Primpke, S.; Schrank, I.; Laforsch, C.; Gerdts, G. Enzymatic purification of microplastics in environmental samples. Environ. Sci. Technol. 2017, 51 (24), 1428314292,  DOI: 10.1021/acs.est.7b03055
  62. 62
    Dehaut, A.; Cassone, A.-L.; Frère, L.; Hermabessiere, L.; Himber, C.; Rinnert, E.; Rivière, G.; Lambert, C.; Soudant, P.; Huvet, A.; Duflos, G.; Paul-Pont, I. Microplastics in seafood: Benchmark protocol for their extraction and characterization. Environ. Pollut. 2016, 215, 223233,  DOI: 10.1016/j.envpol.2016.05.018
  63. 63
    Munno, K.; Helm, P. A.; Jackson, D. A.; Rochman, C.; Sims, A. Impacts of temperature and selected chemical digestion methods on microplastic particles. Environ. Toxicol. Chem. 2018, 37 (1), 9198,  DOI: 10.1002/etc.3935
  64. 64
    Kühn, S.; van Werven, B.; van Oyen, A.; Meijboom, A.; Bravo Rebolledo, E. L.; van Franeker, J. A. The use of potassium hydroxide (KOH) solution as a suitable approach to isolate plastics ingested by marine organisms. Mar. Pollut. Bull. 2017, 115 (1–2), 8690,  DOI: 10.1016/j.marpolbul.2016.11.034
  65. 65
    Cole, M.; Webb, H.; Lindeque, P.; Fileman, E. S.; Halsband, C.; Galloway, T. S. Isolation of microplastics in biota-rich seawater samples and marine organisms. Sci. Rep. 2015, 4 (4528), 18,  DOI: 10.1038/srep04528
  66. 66
    Catarino, A. I.; Thompson, R.; Sanderson, W.; Henry, T. B. Development and optimization of a standard method for extraction of microplastics in mussels by enzyme digestion of soft tissues. Environ. Toxicol. Chem. 2017, 36 (4), 947951,  DOI: 10.1002/etc.3608
  67. 67
    Law, K. L.; Moret-Ferguson, S. E.; Goodwin, D. S.; Zettler, E. R.; De Force, E.; Kukulka, T.; Proskurowski, G. Distribution of Surface Plastic Debris in the Eastern Pacific Ocean from an 11-Year Data Set. Environ. Sci. Technol. 2014, 48 (9), 47324738,  DOI: 10.1021/es4053076
  68. 68
    Eriksen, M.; Mason, S.; Wilson, S.; Box, C.; Zellers, A.; Edwards, W.; Farley, H.; Amato, S. Microplastic pollution in the surface waters of the Laurentian Great Lakes. Mar. Pollut. Bull. 2013, 77 (1–2), 17782,  DOI: 10.1016/j.marpolbul.2013.10.007
  69. 69
    Imhof, H. K.; Laforsch, C.; Wiesheu, A. C.; Schmid, J.; Anger, P. M.; Niessner, R.; Ivleva, N. P. Pigments and plastic in limnetic ecosystems: A qualitative and quantitative study on microparticles of different size classes. Water Res. 2016, 98, 6474,  DOI: 10.1016/j.watres.2016.03.015
  70. 70
    Peters, C. A.; Thomas, P. A.; Rieper, K. B.; Bratton, S. P. Foraging preferences influence microplastic ingestion by six marine fish species from the Texas Gulf Coast. Mar. Pollut. Bull. 2017, 124 (1), 8288,  DOI: 10.1016/j.marpolbul.2017.06.080
  71. 71
    Remy, F.; Collard, F.; Gilbert, B.; Compère, P.; Eppe, G.; Lepoint, G. When Microplastic Is Not Plastic: The Ingestion of Artificial Cellulose Fibers by Macrofauna Living in Seagrass Macrophytodetritus. Environ. Sci. Technol. 2015, 49 (18), 1115811166,  DOI: 10.1021/acs.est.5b02005
  72. 72
    Käppler, A.; Windrich, F.; Loder, M. G. J.; Malanin, M.; Fischer, D.; Labrenz, M.; Eichhorn, K. J.; Voit, B. Identification of microplastics by FTIR and Raman microscopy: a novel silicon filter substrate opens the important spectral range below 1300 cm(−1) for FTIR transmission measurements. Anal. Bioanal. Chem. 2015, 407 (22), 67916801,  DOI: 10.1007/s00216-015-8850-8
  73. 73
    Fries, E.; Dekiff, J. H.; Willmeyer, J.; Nuelle, M. T.; Ebert, M.; Remy, D. Identification of polymer types and additives in marine microplastic particles using pyrolysis-GC/MS and scanning electron microscopy. Environmental Science-Processes & Impacts 2013, 15 (10), 19491956,  DOI: 10.1039/c3em00214d
  74. 74
    Dümichen, E.; Eisentraut, P.; Bannick, C. G.; Barthel, A.-K.; Senz, R.; Braun, U. Fast identification of microplastics in complex environmental samples by a thermal degradation method. Chemosphere 2017, 174, 572584,  DOI: 10.1016/j.chemosphere.2017.02.010
  75. 75
    Fischer, M.; Scholz-Böttcher, B. M. Simultaneous Trace Identification and Quantification of Common Types of Microplastics in Environmental Samples by Pyrolysis-Gas Chromatography–Mass Spectrometry. Environ. Sci. Technol. 2017, 51 (9), 50525060,  DOI: 10.1021/acs.est.6b06362
  76. 76
    Löder, M. G. J.; Kuczera, M.; Mintenig, S.; Lorenz, C.; Gerdts, G. Focal plane array detector-based micro-Fourier-transform infrared imaging for the analysis of microplastics in environmental samples. Environmental Chemistry 2015, 12 (5), 563581,  DOI: 10.1071/EN14205
  77. 77
    Mintenig, S. M.; Bauerlein, P. S.; Koelmans, A. A.; Dekker, S. C.; van Wezel, A. P. Closing the gap between small and smaller: towards a framework to analyse nano- and microplastics in aqueous environmental samples. Environ. Sci.: Nano 2018, 5, 16401649,  DOI: 10.1039/C8EN00186C
  78. 78
    Tanaka, K.; Takada, H. Microplastic fragments and microbeads in digestive tracts of planktivorous fish from urban coastal waters. Sci. Rep. 2016, 6, 34351,  DOI: 10.1038/srep34351
  79. 79
    Wesch, C.; Barthel, A. K.; Braun, U.; Klein, R.; Paulus, M. No microplastics in benthic eelpout (Zoarces viviparus): An urgent need for spectroscopic analyses in microplastic detection. Environ. Res. 2016, 148, 3638,  DOI: 10.1016/j.envres.2016.03.017
  80. 80
    Li, J.; Yang, D.; Li, L.; Jabeen, K.; Shi, H. Microplastics in commercial bivalves from China. Environ. Pollut. 2015, 207, 190195,  DOI: 10.1016/j.envpol.2015.09.018
  81. 81
    Murphy, F.; Russell, M.; Ewins, C.; Quinn, B. The uptake of macroplastic & microplastic by demersal & pelagic fish in the Northeast Atlantic around Scotland. Mar. Pollut. Bull. 2017, 122 (1), 353359,  DOI: 10.1016/j.marpolbul.2017.06.073
  82. 82
    Nadal, M. A.; Alomar, C.; Deudero, S. High levels of microplastic ingestion by the semipelagic fish bogue Boops boops (L.) around the Balearic Islands. Environ. Pollut. 2016, 214, 517523,  DOI: 10.1016/j.envpol.2016.04.054
  83. 83
    Bråte, I. L. N.; Eidsvoll, D. P.; Steindal, C. C.; Thomas, K. V. Plastic ingestion by Atlantic cod (Gadus morhua) from the Norwegian coast. Mar. Pollut. Bull. 2016, 112 (1), 105110,  DOI: 10.1016/j.marpolbul.2016.08.034
  84. 84
    Anastasopoulou, A.; Mytilineou, C.; Smith, C. J.; Papadopoulou, K. N. Plastic debris ingested by deep-water fish of the Ionian Sea (Eastern Mediterranean). Deep Sea Res., Part I 2013, 74 (0), 1113,  DOI: 10.1016/j.dsr.2012.12.008
  85. 85
    Jantz, L. A.; Morishige, C. L.; Bruland, G. L.; Lepczyk, C. A. Ingestion of plastic marine debris by longnose lancetfish (Alepisaurus ferox) in the North Pacific Ocean. Mar. Pollut. Bull. 2013, 69 (1), 97104,  DOI: 10.1016/j.marpolbul.2013.01.019
  86. 86
    Vendel, A. L.; Bessa, F.; Alves, V. E. N.; Amorim, A. L. A.; Patrício, J.; Palma, A. R. T. Widespread microplastic ingestion by fish assemblages in tropical estuaries subjected to anthropogenic pressures. Mar. Pollut. Bull. 2017, 117 (1), 448455,  DOI: 10.1016/j.marpolbul.2017.01.081
  87. 87
    Wójcik-Fudalewska, D.; Normant-Saremba, M.; Anastácio, P. Occurrence of plastic debris in the stomach of the invasive crab Eriocheir sinensis. Mar. Pollut. Bull. 2016, 113 (1), 306311,  DOI: 10.1016/j.marpolbul.2016.09.059
  88. 88
    Miranda, D. d. A.; de Carvalho-Souza, G. F. Are we eating plastic-ingesting fish?. Mar. Pollut. Bull. 2016, 103 (1), 109114,  DOI: 10.1016/j.marpolbul.2015.12.035

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  23. Xiao-xia Zhou, Li-teng Hao, Huang-ying-zi Wang, Ying-jie Li, Jing-fu Liu. Cloud-Point Extraction Combined with Thermal Degradation for Nanoplastic Analysis Using Pyrolysis Gas Chromatography–Mass Spectrometry. Analytical Chemistry 2019, 91 (3) , 1785-1790. https://doi.org/10.1021/acs.analchem.8b04729
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  25. Hengchen Li, Hongwei Lu, Sansan Feng, Yuxuan Xue, Xiaohan Zhang. Environmental drivers and assembly mechanisms of microplastics in plateau lakes. Journal of Hydrology 2025, 660 , 133388. https://doi.org/10.1016/j.jhydrol.2025.133388
  26. G. Cesarini, I. Donázar-Aramendía, L. Gallitelli, S. Secco, M. Orsini, S. De Santis, M. Scalici, A.J. Green, C. Coccia. Microplastic contamination in bivalves from urban estuaries: Are they sentinels for differences in pollution levels?. Marine Pollution Bulletin 2025, 218 , 118227. https://doi.org/10.1016/j.marpolbul.2025.118227
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  30. Tauqeer Hussain, Muhammad Summer, Shaukat Ali, Rana Rashad Mahmood Khan, Muhammad Pervaiz, Zohaib Saeed. Micro and Nanoplastics in Ecosystems: Interrelated Sources, Risks, Pathways, Consequences, Mitigation, Challenges and Future Recommendations. Water, Air, & Soil Pollution 2025, 236 (7) https://doi.org/10.1007/s11270-025-08063-2
  31. Su Ji Heo, Nalae Moon, Ju Hee Kim. A systematic review and quality assessment of estimated daily intake of microplastics through food. Reviews on Environmental Health 2025, 40 (2) , 371-392. https://doi.org/10.1515/reveh-2024-0111
  32. Marina Rocha de Carvalho, Alef Fontinele Teixeira, Luana do Nascimento Dias, Larissa Gabrielle Pinheiro Ferreira, Suzany Pedrosa Nascimento, Amanda Caroline Nascimento Sousa, Antonio Carlos Leal de Castro, James Werllen de Jesus Azevedo, Marcelo Henrique Lopes Silva. Presence of microplastics in Sciades herzbergii (Bloch, 1794) captured in harbor areas of the Amazon coast, Maranhão, Brazil. Marine Pollution Bulletin 2025, 215 , 117862. https://doi.org/10.1016/j.marpolbul.2025.117862
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  35. Chathura Dhanasinghe, Chih‐Ming Kao, Pu‐Fong Liu, Rao Y. Surampalli, Tian C. Zhang, Bashir M. Al‐Hashimi. Advanced Techniques for Sampling, Quantification, and Characterization of Microplastics. 2025, 69-106. https://doi.org/10.1002/9781394251100.ch4
  36. D.S. Wijetunge, S.P.K.K.A. Perera, N.M.O.A. Karunathilake, R.R.M.K.P. Ranatunga. Macro Issues of Microplastics. 2025, 465-494. https://doi.org/10.1002/9781394237029.ch24
  37. Ayankoya Yemi Ayankunle, Natalja Buhhalko, Karin Pachel, Erki Lember, Asya Drenkova-Tuhtan, Margit Heinlaan. Microplastics in Estonian wastewater treatment plants: First evaluation of baseline concentrations and stage-wise removal efficiency. Aquatic Toxicology 2025, 281 , 107305. https://doi.org/10.1016/j.aquatox.2025.107305
  38. Yureshi Umanda Jayaweera, Hennayaka Mudiyanselage Amasha Indu Hennayaka, Herath Mudiyanselage Lalinka Priyas Herath, Gajanayake Mudalige Pradeep Kumara, Mahagama Gedara Yohan Lasantha Mahagamage, Undugodage Dulanjali Rodrigo, Danushika Charyangi Manatunga. A Comprehensive Investigation of Microplastic Contamination and Polymer Toxicity in Farmed Shrimps; L. vannamei and P. monodon. Water, Air, & Soil Pollution 2025, 236 (3) https://doi.org/10.1007/s11270-025-07800-x
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  40. Yanning Qiu, Svenja Mintenig, Margherita Barchiesi, Albert A. Koelmans. Using artificial intelligence tools for data quality evaluation in the context of microplastic human health risk assessments. Environment International 2025, 197 , 109341. https://doi.org/10.1016/j.envint.2025.109341
  41. Vera N. de Ruijter, Paula E. Redondo-Hasselerharm, Albert A. Koelmans. A brief history of microplastics effect testing: Guidance and prospect. Environmental Pollution 2025, 368 , 125711. https://doi.org/10.1016/j.envpol.2025.125711
  42. Amarachi P. Onyena, Mary E. Tekeme, Jessica C. Uwakwe, Deborah Aderibigbe, Kabari Sam. Baseline characterisation of microplastics in surface water, sediment, and seafood from the Escravos Estuary, Nigeria. Scientific African 2025, 27 , e02591. https://doi.org/10.1016/j.sciaf.2025.e02591
  43. Hailong Zhang, Qiannan Duan, Pengwei Yan, Jianchao Lee, Weidong Wu, Chi Zhou, Baoxin Zhai, Xiangyi Yang. Advancements and challenges in microplastic detection and risk assessment: Integrating AI and standardized methods. Marine Pollution Bulletin 2025, 212 , 117529. https://doi.org/10.1016/j.marpolbul.2025.117529
  44. Mohammed Manik, Md. Tauhid Hossain, Paolo Pastorino. Characterization and risk assessment of microplastics pollution in Mohamaya Lake, Bangladesh. Journal of Contaminant Hydrology 2025, 269 , 104487. https://doi.org/10.1016/j.jconhyd.2024.104487
  45. Yiping Luo, Ruiqi Hu, Ye Zheng, Ling Ding, Xinran Qiu, Jiansheng Yang, Xujun Liang, Xuetao Guo. Sampling, extraction, and analysis of micro- and nano-plastics in environmental and biological compartments: A review. TrAC Trends in Analytical Chemistry 2025, 183 , 118056. https://doi.org/10.1016/j.trac.2024.118056
  46. Mohammad Mehdi Chiani, Majid Rasta, Mojtaba S. Taleshi, Fatemeh Elmi. The role of organisms’ size in microplastic pollution monitoring: Insights from Mytilaster lineatus and Amphibalanus improvisus. Marine Environmental Research 2025, 204 , 106863. https://doi.org/10.1016/j.marenvres.2024.106863
  47. Noor Us Saher, Asmat Saleem Siddiqui, Abdul Hameed Baloch, Wajid Ali, Raheema Tahir, Dur e Shahwar, Muntaha Shah, Nayab Kanwal, Fakhar I. Abbas, Naureen Aziz Qureshi. A Review Notes on Role, Behavior, Risk Assessment Tools, and Adverse Outcomes of Metal and Microplastic Pollution in Benthic Sea Food Ecosystem. 2025, 285-332. https://doi.org/10.1007/978-3-031-75713-6_12
  48. João Pinto da Costa, Virgínia Gonçalves. The steps of microplastic analysis and their consistency. 2025, 81-114. https://doi.org/10.1016/B978-0-443-15779-0.00014-6
  49. Muhammad Adli Hanif, Naimah Ibrahim, Zaity Syazwani Mohd Odli. Overview of analysis of microplastics and nanoplastics. 2025, 39-61. https://doi.org/10.1016/B978-0-443-15779-0.00015-8
  50. Alexandra Ershova, Yulia Frank. Separation and purification of microplastics from the environmental samples. 2025, 135-154. https://doi.org/10.1016/B978-0-443-15779-0.00019-5
  51. Pavel Pořízka, Daniel Holub, Martin Kizovský, Ota Samek, Jozef Kaiser, Gabriela Kalčikova. Hyphenated Raman and laser spectroscopy for the characterization of microplastics in tissues. 2025, 441-451. https://doi.org/10.1016/B978-0-443-21834-7.00026-8
  52. Yi Gong, Huachen Gao, Zehao Guo, Xuemin Huang, Yunkai Li, Zezheng Li, Chenxuan Du, Feng Wu. Uncovering the global status of plastic presence in marine chondrichthyans. Reviews in Fish Biology and Fisheries 2024, 34 (4) , 1351-1369. https://doi.org/10.1007/s11160-024-09877-9
  53. Majid Rasta, Ali Khodadoust, Mojtaba S. Taleshi, Niloofar S. Lashkaryan, Xiaotao Shi. Potential use of gammarus (Pontogammarus maeoticus) and shrimp (Palaemon elegans) as biomonitors of microplastics pollution in coastal environments. Environmental Pollution 2024, 362 , 124959. https://doi.org/10.1016/j.envpol.2024.124959
  54. Dave T.F. Kuo, Yang-hsin Shih. How effective is score-based data quality assessment? An illustration with fish BCF data. Environmental Research 2024, 262 , 119880. https://doi.org/10.1016/j.envres.2024.119880
  55. Hiraku Tanoiri, Haruka Nakano, Hisayuki Arakawa, Masashi Yokota. Assessment of microplastic occurrence in tidal flat biota of the Tsurumi River estuary (Tokyo Bay, Japan): Preliminary study and first evidence. Regional Studies in Marine Science 2024, 77 , 103661. https://doi.org/10.1016/j.rsma.2024.103661
  56. M. Dewika, Kalaimani Markandan, J. Nor Ruwaida, Y.Y. Sara, Anjan Deb, N. Ahmad Irfan, Mohammad Khalid. Integrating the quintuple helix approach into atmospheric microplastics management policies for planetary health preservation. Science of The Total Environment 2024, 954 , 176063. https://doi.org/10.1016/j.scitotenv.2024.176063
  57. Benjamin de Jourdan, Danielle Philibert, Davide Asnicar, Craig Warren Davis. Microplastic biomonitoring studies in aquatic species: A review & quality assessment framework. Science of The Total Environment 2024, 957 , 177541. https://doi.org/10.1016/j.scitotenv.2024.177541
  58. Nelle Meyers, Kathrin Kopke, Natalja Buhhalko, Karin Mattsson, Colin R. Janssen, Gert Everaert, Bavo De Witte. Value for money: a cost-effectiveness analysis of microplastic analytics in seawater. Microplastics and Nanoplastics 2024, 4 (1) https://doi.org/10.1186/s43591-024-00081-x
  59. David Vanavermaete, Amy Lusher, Jakob Strand, Esteban Abad, Marinella Farré, Emilie Kallenbach, Michael Dekimpe, Katrien Verlé, Sebastian Primpke, Stefano Aliani, Bavo De Witte. Plastics in biota: technological readiness level of current methodologies. Microplastics and Nanoplastics 2024, 4 (1) https://doi.org/10.1186/s43591-024-00083-9
  60. Jordan A. Pitt, Scott M. Gallager, Sarah Youngs, Anna P. M. Michel, Mark E. Hahn, Neelakanteswar Aluru. The abundance and localization of environmental microplastics in gastrointestinal tract and muscle of Atlantic killifish (Fundulus heteroclitus): a pilot study. Microplastics and Nanoplastics 2024, 4 (1) https://doi.org/10.1186/s43591-024-00101-w
  61. Benedicta Yayra Fosu-Mensah, Nathanael Nii-Odai Laryea, Daniel Darko, Michael Mensah. Assessing microplastics contamination and characteristics in organic soil amendments in the Greater Accra Metropolitan Area of Ghana. Heliyon 2024, 10 (23) , e40882. https://doi.org/10.1016/j.heliyon.2024.e40882
  62. Caitlin Brawn, Bonnie M. Hamilton, Matthew S. Savoca, Mark L. Mallory, Jennifer F. Provencher. Examining ingested microplastics in fish: Considerations on filter pore size, analysis time, and material costs to design cost-effective projects. Marine Environmental Research 2024, 202 , 106785. https://doi.org/10.1016/j.marenvres.2024.106785
  63. Kun Pang, Fangyu Fu, Haoqi Wang, Shun Ding, Yanfen Fang, Xiang Liu. Sustainability-inspired upcycling of plastic waste into porous carbon nanobulks for water decontamination via peroxymonosulfate activation. Science of The Total Environment 2024, 950 , 175242. https://doi.org/10.1016/j.scitotenv.2024.175242
  64. V. V. Dhoble, L. B. Dama. Extraction of Polyethylene and Polypropylene Microplastic from Agriculture Soil. International Journal of Scientific Research in Science and Technology 2024, 11 (6) , 100-107. https://doi.org/10.32628/IJSRST2411495
  65. Rao M Uppu, Willie Peijnenburg, Sean M Hays. Comment on: “ Microplastic presence in dog and human testis and its potential association with sperm count and weights of testis and epididymis”. Toxicological Sciences 2024, 74 https://doi.org/10.1093/toxsci/kfae136
  66. Aunurohim Aunurohim, Miftakhul Sefti Raufanda, Dian Saptarini, Farid Kamal Muzaki, Romanus Edy Prabowo, Martinus Surya Ari Pamungkas, Sobrian Cahya Perdana Putra, Ekawati Ekawati, Nur Maulidhaturrafida, Shinta Cahyaning Dewi, Edo Danilyan. Microplastic-contamination in the flesh and gastrointestinal tract of nile tilapia (Oreochromis niloticus) reared in floating net cages at lake Ranu Grati, Pasuruan, East Java, Indonesia. Environmental Advances 2024, 17 , 100587. https://doi.org/10.1016/j.envadv.2024.100587
  67. Nelle Meyers, Gert Everaert, Kris Hostens, Natascha Schmidt, Dorte Herzke, Jean-Luc Fuda, Colin R. Janssen, Bavo De Witte. Towards reliable data: Validation of a machine learning-based approach for microplastics analysis in marine organisms using Nile red staining. Marine Pollution Bulletin 2024, 207 , 116804. https://doi.org/10.1016/j.marpolbul.2024.116804
  68. Kevin Leuenberger, Gabriel Erni-Cassola, Clara Leistenschneider, Patricia Burkhardt-Holm. Microplastic ingestion in five demersal, bathydemersal and bathypelagic fish species from the eastern Weddell Sea, Antarctica. Science of The Total Environment 2024, 946 , 174320. https://doi.org/10.1016/j.scitotenv.2024.174320
  69. Andrei-Emil Briciu. A Graphic Review of Studies on Ocean and Mediterranean Sea Environment Quality. Hydrology 2024, 11 (10) , 175. https://doi.org/10.3390/hydrology11100175
  70. Bahati Shabani Nzeyimana, Swagata Chakraborty, R. Priyadharshini, Mariaselvam Sheela Mary, M. Govindaraju. Micro/Nano-Plastic Pollution in Aquarium Systems. 2024, 225-256. https://doi.org/10.4018/979-8-3693-3447-8.ch010
  71. Luca Nalbone, Filippo Giarratana, Martina Genovese, Antonio Panebianco. Occurrence of microplastics in store-bought fresh and processed clams in Italy. Marine Pollution Bulletin 2024, 206 , 116739. https://doi.org/10.1016/j.marpolbul.2024.116739
  72. Qing Huang, Xiaoyi Wu, Guodong Cao, Jing Zhang, Pengfei Wu, Zongwei Cai. Mass spectrometry-based techniques for determination of microplastics in terrestrial ecosystems. TrAC Trends in Analytical Chemistry 2024, 178 , 117853. https://doi.org/10.1016/j.trac.2024.117853
  73. Dorcas Uaciquete, Kensuke Mitsunaga, Katsumi Aoyama, Keisuke Kitajima, Takashi Chiba, Daud Liace Jamal, Jheng-Jie Jiang, Yoshifumi Horie. Microplastic abundance in the semi-enclosed Osaka Bay, Japan. Environmental Science and Pollution Research 2024, 31 (36) , 49455-49467. https://doi.org/10.1007/s11356-024-34444-x
  74. Cui-Lan Bai, Dan Wang, Yu-Ling Luan, Si-Nan Huang, Liang-Ying Liu, Ying Guo. A review on micro- and nanoplastics in humans: Implication for their translocation of barriers and potential health effects. Chemosphere 2024, 361 , 142424. https://doi.org/10.1016/j.chemosphere.2024.142424
  75. Stephen Kneel, Caroline Gilleran Stephens, Alec Rolston, Ana M. Mendes, Liam Morrison, Suzanne Linnane. Microplastic contamination of intertidal sediment and cockles (Cerastoderma edule). Marine Pollution Bulletin 2024, 205 , 116568. https://doi.org/10.1016/j.marpolbul.2024.116568
  76. Nina Wootton, Bronwyn M. Gillanders, Sophie Leterme, Warwick Noble, Scott P. Wilson, Michelle Blewitt, Stephen E. Swearer, Patrick Reis-Santos. Research priorities on microplastics in marine and coastal environments: An Australian perspective to advance global action. Marine Pollution Bulletin 2024, 205 , 116660. https://doi.org/10.1016/j.marpolbul.2024.116660
  77. Yueping Zheng, Sirui Huang, Houyong Fan, Hanqi Liu, Jianan Xu, Nicholas J. Craig, Juan-Ying Li, Wenhui He, Lei Su. Microplastics in different tissues of historical and live samples of endangered mega-fish (Acipenser sinensis) and their potential relevance to exposure pathways. Aquatic Toxicology 2024, 272 , 106943. https://doi.org/10.1016/j.aquatox.2024.106943
  78. Kayla Mladinich, Bridget A. Holohan, Sandra E. Shumway, J. Evan Ward. Abundance of microplastics at and near a shellfish aquaculture farm: An eastern oyster (Crassostrea virginica) transplant study. Marine Environmental Research 2024, 199 , 106606. https://doi.org/10.1016/j.marenvres.2024.106606
  79. Zeliang Su, Liangfu Wei, Linyong Zhi, Xiaomei Huang, Xu Wang, Jun Wang. Microplastics in aquafeeds: Occurrence, sources, effects and considerations for aquatic food production. TrAC Trends in Analytical Chemistry 2024, 176 , 117760. https://doi.org/10.1016/j.trac.2024.117760
  80. Kamil Jurowski, Maciej Noga, Damian Kobylarz, Łukasz Niżnik, Alicja Krośniak. Multimodal Imaging Using Raman Spectroscopy and FTIR in a Single Analytical Instrument with a Microscope (Infrared Raman Microscopy AIRsight, Shimadzu): Opportunities and Applications. International Journal of Molecular Sciences 2024, 25 (13) , 6884. https://doi.org/10.3390/ijms25136884
  81. Pooja Yadav, Sweety Dahiya, Sangita Yadav, Deepak Dahiya, Manju Rani, Sudesh Chaudhary. Examining the Ecological Footprint of Microplastics: A Holistic Exploration from Genesis to Demise. Oriental Journal Of Chemistry 2024, 40 (3) , 788-793. https://doi.org/10.13005/ojc/400321
  82. Melkamu Biyana Regasa. New Approaches for Micro(Nano)Plastics Analysis. 2024, 471-492. https://doi.org/10.1002/9781394238163.ch20
  83. Vania Aparecida Sacco, Natana Raquel Zuanazzi, Amanda Selinger, João Henrique Alliprandini da Costa, Érika Spanhol Lemunie, Camila Luiza Comelli, Vinícius Abilhoa, Fernando Carlos de Sousa, Luis Fernando Fávaro, Lorena M. Rios Mendoza, Nédia de Castilhos Ghisi, Rosilene Luciana Delariva. What are the global patterns of microplastic ingestion by fish? A scientometric review. Environmental Pollution 2024, 350 , 123972. https://doi.org/10.1016/j.envpol.2024.123972
  84. Sijia Gao, Natalie Orlowski, Franziska Kristin Bopf, Lutz Breuer. A review on microplastics in major European rivers. WIREs Water 2024, 11 (3) https://doi.org/10.1002/wat2.1713
  85. Prabhakar Sharma, Prateek Sharma, Kumar Abhishek. Sampling, separation, and characterization methodology for quantification of microplastic from the environment. Journal of Hazardous Materials Advances 2024, 14 , 100416. https://doi.org/10.1016/j.hazadv.2024.100416
  86. Xiaoping Sun, Ruiping Yang, Jing Ji, Zebin Zhu, Jason C. White, Yu Shen. An evaluation of microplastic contamination in the marine waters and species in the coastal region of the South Yellow Sea, China. Journal of Hazardous Materials 2024, 469 , 134018. https://doi.org/10.1016/j.jhazmat.2024.134018
  87. Elvis D. Okoffo, Kevin V. Thomas. Mass quantification of nanoplastics at wastewater treatment plants by pyrolysis–gas chromatography–mass spectrometry. Water Research 2024, 254 , 121397. https://doi.org/10.1016/j.watres.2024.121397
  88. Parisa Falakdin, Adrian Lopez-Rosales, Jose Andrade, Elisa Terzaghi, Antonio Di Guardo, Soledad Muniategui-Lorenzo. Comparison of microplastic type, size, and composition in atmospheric and foliage samples in an urban scenario. Environmental Pollution 2024, 349 , 123911. https://doi.org/10.1016/j.envpol.2024.123911
  89. Paula E. Redondo-Hasselerharm, Andreu Rico, Esperanza Huerta Lwanga, Cornelis A.M. van Gestel, Albert A. Koelmans. Source-specific probabilistic risk assessment of microplastics in soils applying quality criteria and data alignment methods. Journal of Hazardous Materials 2024, 467 , 133732. https://doi.org/10.1016/j.jhazmat.2024.133732
  90. Natalya S. Salikova, Javier Rodrigo-Ilarri, Lyudmila A. Makeyeva, María-Elena Rodrigo-Clavero, Zhulduz O. Tleuova, Anar D. Makhmutova. Monitoring of Microplastics in Water and Sediment Samples of Lakes and Rivers of the Akmola Region (Kazakhstan). Water 2024, 16 (7) , 1051. https://doi.org/10.3390/w16071051
  91. Pazhamthavalathil Anil Athulya, Yojana Waychal, Andres Rodriguez-Seijo, Sandhya Devalla, C. George Priya Doss, Natarajan Chandrasekaran. Microplastic interactions in the agroecosystems: methodological advances and limitations in quantifying microplastics from agricultural soil. Environmental Geochemistry and Health 2024, 46 (3) https://doi.org/10.1007/s10653-023-01800-8
  92. Narges Nejat, Masoud Sattari, Reza Mohsenpour, Xiaotao Shi, Majid Rasta. Microplastics abundance, distribution and composition in surface waters, sediments and fish species from Amir˗Kalayeh Wetland, Northern Iran. Environmental Science and Pollution Research 2024, 31 (14) , 22024-22037. https://doi.org/10.1007/s11356-024-32627-0
  93. Yinan He, Jungang Lu, Changjun Li, Xiaohui Wang, Chunhua Jiang, Lixin Zhu, Xinyu Bu, Khalida Jabeen, TuanLinh Tran Vo, Daoji Li. From pollution to solutions: Insights into the sources, transport and management of plastic debris in pristine and urban rivers. Environmental Research 2024, 245 , 118024. https://doi.org/10.1016/j.envres.2023.118024
  94. Nina R. Jones, Alix M. de Jersey, Jennifer L. Lavers, Thomas Rodemann, Jack Rivers-Auty. Identifying laboratory sources of microplastic and nanoplastic contamination from the air, water, and consumables. Journal of Hazardous Materials 2024, 465 , 133276. https://doi.org/10.1016/j.jhazmat.2023.133276
  95. João Frias, Haleigh Joyce, Loann Brozzetti, Elena Pagter, Mateja Švonja, Fiona Kavangh, Róisín Nash. Spatial monitoring of microplastics in environmental matrices from Galway Bay, Ireland. Marine Pollution Bulletin 2024, 200 , 116153. https://doi.org/10.1016/j.marpolbul.2024.116153
  96. Anita Jemec Kokalj, Gabriela Kalčíková, Salla Selonen, Thijs Bosker, Damjana Drobne, Darina Dvořáková, Jakub Hofman, Rachel Hurley, Sarmite Kernchen, Christian Laforsch, Martin G.J. Löder, Sam van Loon, Paula E. Redondo-Hasselerharm, Vili Saartama, Klára Šmídová, Aristeidis S. Tsagkaris, Laura J. Zantis, Luca Nizzetto, Cornelis A.M. van Gestel. Strategy towards producing relevant and reliable data for the hazard assessment of micro- and nanoplastics in agricultural soils. TrAC Trends in Analytical Chemistry 2024, 172 , 117567. https://doi.org/10.1016/j.trac.2024.117567
  97. Mansoor Ahmad Bhat, Eftade O. Gaga, Kadir Gedik. How can contamination be prevented during laboratory analysis of atmospheric samples for microplastics?. Environmental Monitoring and Assessment 2024, 196 (2) https://doi.org/10.1007/s10661-024-12345-3
  98. Angel Negrete Velasco, Alicia Ellero, Stéphan Ramseier Gentile, Stéphane Zimmermann, Pascal Ramaciotti, Serge Stoll. Impact of a nanofiltration system on microplastic contamination in Geneva groundwater (Switzerland). Environmental Science and Pollution Research 2024, 31 (9) , 13512-13522. https://doi.org/10.1007/s11356-024-31940-y
  99. Hsuan-Cheng Lu, Julia L. Smith, Shima Ziajahromi, Frederic D.L. Leusch. Microplastics and other anthropogenic fibres in large apex shark species: Abundance, characteristics, and recommendations for future research. Chemosphere 2024, 349 , 140957. https://doi.org/10.1016/j.chemosphere.2023.140957
  100. Yonghao Sun, Jun Zhang, Zhoujie Jiang, Yi Wang, Peng Duan, Wei Min, Weicheng Zhang. Polystyrene microplastics enhance oxidative dissolution but suppress the aquatic acute toxicity of a commercial cadmium yellow pigment under simulated irradiation. Journal of Hazardous Materials 2024, 463 , 132881. https://doi.org/10.1016/j.jhazmat.2023.132881
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  • Abstract

    Figure 1

    Figure 1. Ingestion incidence and 95% confidence intervals recalculated from data provided in microplastic ingestion studies. Data are combined to obtain a “whole ocean” biota ingestion incidence value (○).

  • References


    This article references 88 other publications.

    1. 1
      GESAMP Sources, fate and effects of microplastics in the marine environment: part two of a global assessment; Kershaw, P. J., Rochman, C. M., eds.; IMO/FAO/UNESCO-IOC/UNIDO/WMO/IAEA/UN/ UNEP/UNDP Joint Group of Experts on the Scientific Aspects of Marine Environmental Protection; Rep. Stud. GESAMP, 2016; Vol. 93, p 220.
    2. 2
      Wright, S. L.; Thompson, R. C.; Galloway, T. S. The physical impacts of microplastics on marine organisms: A review. Environ. Pollut. 2013, 178, 483492,  DOI: 10.1016/j.envpol.2013.02.031
    3. 3
      Browne, M. A.; Galloway, T.; Thompson, R. Microplastic—an emerging contaminant of potential concern?. Integr. Environ. Assess. Manage. 2007, 3 (4), 559561,  DOI: 10.1002/ieam.5630030412
    4. 4
      Chen, Q.; Reisser, J.; Cunsolo, S.; Kwadijk, C.; Kotterman, M.; Proietti, M.; Slat, B.; Ferrari, F. F.; Schwarz, A.; Levivier, A.; Yin, D.; Hollert, H.; Koelmans, A. A. Pollutants in Plastics within the North Pacific Subtropical Gyre. Environ. Sci. Technol. 2018, 52 (2), 446456,  DOI: 10.1021/acs.est.7b04682
    5. 5
      Lusher, A. L.; McHugh, M.; Thompson, R. C. Occurrence of microplastics in the gastrointestinal tract of pelagic and demersal fish from the English Channel. Mar. Pollut. Bull. 2013, 67 (1), 9499,  DOI: 10.1016/j.marpolbul.2012.11.028
    6. 6
      Foekema, E. M.; De Gruijter, C.; Mergia, M. T.; van Franeker, J. A.; Murk, A. J.; Koelmans, A. A. Plastic in North Sea Fish. Environ. Sci. Technol. 2013, 47 (15), 88188824,  DOI: 10.1021/es400931b
    7. 7
      Neves, D.; Sobral, P.; Ferreira, J. L.; Pereira, T. Ingestion of microplastics by commercial fish off the Portuguese coast. Mar. Pollut. Bull. 2015, 101 (1), 119126,  DOI: 10.1016/j.marpolbul.2015.11.008
    8. 8
      Mathalon, A.; Hill, P. Microplastic fibers in the intertidal ecosystem surrounding Halifax Harbor, Nova Scotia. Mar. Pollut. Bull. 2014, 81 (1), 6979,  DOI: 10.1016/j.marpolbul.2014.02.018
    9. 9
      Romeo, T.; Pietro, B.; Pedà, C.; Consoli, P.; Andaloro, F.; Fossi, M. C. First evidence of presence of plastic debris in stomach of large pelagic fish in the Mediterranean Sea. Mar. Pollut. Bull. 2015, 95 (1), 358361,  DOI: 10.1016/j.marpolbul.2015.04.048
    10. 10
      Lusher, A. Microplastics in the Marine Environment: Distribution, Interactions and Effects. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Cham, 2015; pp 245307.
    11. 11
      Teuten, E. L.; Saquing, J. M.; Knappe, D. R. U.; Barlaz, M. A.; Jonsson, S.; Björn, A.; Rowland, S. J.; Thompson, R. C.; Galloway, T. S.; Yamashita, R.; Ochi, D.; Watanuki, Y.; Moore, C.; Viet, P. H.; Tana, T. S.; Prudente, M.; Boonyatumanond, R.; Zakaria, M. P.; Akkhavong, K.; Ogata, Y.; Hirai, H.; Iwasa, S.; Mizukawa, K.; Hagino, Y.; Imamura, A.; Saha, M.; Takada, H. Transport and release of chemicals from plastics to the environment and to wildlife. Philos. Trans. R. Soc., B 2009, 364 (1526), 20272045,  DOI: 10.1098/rstb.2008.0284
    12. 12
      Mato, Y.; Isobe, T.; Takada, H.; Kanehiro, H.; Ohtake, C.; Kaminuma, T. Plastic resin pellets as a transport medium for toxic chemicals in the marine environment. Environ. Sci. Technol. 2001, 35 (2), 318324,  DOI: 10.1021/es0010498
    13. 13
      Diepens, N. J.; Koelmans, A. A. Accumulation of plastic debris and associated contaminants in aquatic food webs. Environ. Sci. Technol. 2018, 52, 85108520,  DOI: 10.1021/acs.est.8b02515
    14. 14
      Cozar, A.; Echevarria, F.; Gonzalez-Gordillo, J. I.; Irigoien, X.; Ubeda, B.; Hernandez-Leon, S.; Palma, A. T.; Navarro, S.; Garcia-de-Lomas, J.; Ruiz, A.; Fernandez-de-Puelles, M. L.; Duarte, C. M. Plastic debris in the open ocean. Proc. Natl. Acad. Sci. U. S. A. 2014, 111 (28), 1023910244,  DOI: 10.1073/pnas.1314705111
    15. 15
      Rochman, C. M.; Browne, M. A.; Underwood, A. J.; van Franeker, J. A.; Thompson, R. C. T.; Amaral-Zettler, L. A. The ecological impacts of marine debris: unraveling the demonstrated evidence from what is perceived. Ecology 2016, 97 (2), 302312,  DOI: 10.1890/14-2070.1
    16. 16
      Besseling, E.; Foekema, E. M.; Van Franeker, J. A.; Leopold, M. F.; Kuhn, S.; Rebolledo, E. L. B.; Hesse, E.; Mielke, L.; Ijzer, J.; Kamminga, P.; Koelmans, A. A. Microplastic in a macro filter feeder: Humpback whale Megaptera novaeangliae. Mar. Pollut. Bull. 2015, 95 (1), 248252,  DOI: 10.1016/j.marpolbul.2015.04.007
    17. 17
      Lusher, A. L.; Hernandez-Milian, G.; Berrow, S.; Rogan, E.; O’Connor, I. Incidence of marine debris in cetaceans stranded and bycaught in Ireland: Recent findings and a review of historical knowledge. Environ. Pollut. 2018, 232, 467476,  DOI: 10.1016/j.envpol.2017.09.070
    18. 18
      Herzke, D.; Anker-Nilssen, T.; Nøst, T. H.; Götsch, A.; Christensen-Dalsgaard, S.; Langset, M.; Fangel, K.; Koelmans, A. A. Negligible Impact of Ingested Microplastics on Tissue Concentrations of Persistent Organic Pollutants in Northern Fulmars off Coastal Norway. Environ. Sci. Technol. 2016, 50 (4), 19241933,  DOI: 10.1021/acs.est.5b04663
    19. 19
      Koelmans, A. A. Modeling the Role of Microplastics in Bioaccumulation of Organic Chemicals to Marine Aquatic Organisms. A Critical Review. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Cham, 2015; pp 309324.
    20. 20
      Koelmans, A. A.; Besseling, E.; Wegner, A.; Foekema, E. M. Plastic as a Carrier of POPs to Aquatic Organisms: A Model Analysis. Environ. Sci. Technol. 2013, 47 (14), 78127820,  DOI: 10.1021/es401169n
    21. 21
      Setälä, O.; Fleming-Lehtinen, V.; Lehtiniemi, M. Ingestion and transfer of microplastics in the planktonic food web. Environ. Pollut. 2014, 185 (0), 7783,  DOI: 10.1016/j.envpol.2013.10.013
    22. 22
      Farrell, P.; Nelson, K. Trophic level transfer of microplastic: Mytilus edulis (L.) to Carcinus maenas (L.). Environ. Pollut. 2013, 177, 13,  DOI: 10.1016/j.envpol.2013.01.046
    23. 23
      Wright, S. L.; Kelly, F. J. Plastic and Human Health: A Micro Issue?. Environ. Sci. Technol. 2017, 51 (12), 66346647,  DOI: 10.1021/acs.est.7b00423
    24. 24
      Filella, M. Questions of size and numbers in environmental research on microplastics: methodological and conceptual aspects. Environmental Chemistry 2015, 12 (5), 527538,  DOI: 10.1071/EN15012
    25. 25
      Connors, K. A.; Dyer, S. D.; Belanger, S. E. Advancing the quality of environmental microplastic research. Environ. Toxicol. Chem. 2017, 36 (7), 16971703,  DOI: 10.1002/etc.3829
    26. 26
      Hanvey, J. S.; Lewis, P. J.; Lavers, J. L.; Crosbie, N. D.; Pozo, K.; Clarke, B. O. A review of analytical techniques for quantifying microplastics in sediments. Anal. Methods 2017, 9 (9), 13691383,  DOI: 10.1039/C6AY02707E
    27. 27
      Vandermeersch, G.; Van Cauwenberghe, L.; Janssen, C. R.; Marques, A.; Granby, K.; Fait, G.; Kotterman, M. J. J.; Diogène, J.; Bekaert, K.; Robbens, J.; Devriese, L. A critical view on microplastic quantification in aquatic organisms. Environ. Res. 2015, 143, 4655,  DOI: 10.1016/j.envres.2015.07.016
    28. 28
      Wesch, C.; Bredimus, K.; Paulus, M.; Klein, R. Towards the suitable monitoring of ingestion of microplastics by marine biota: A review. Environ. Pollut. 2016, 218, 12001208,  DOI: 10.1016/j.envpol.2016.08.076
    29. 29
      Löder, M. G. J.; Gerdts, G. Methodology Used for the Detection and Identification of Microplastics - A Critical Appraisal. In Marine Anthropogenic Litter; Bergmann, M., Gutow, L., Klages, M., Eds.; Springer International Publishing: Berlin, 2015; pp 201227.
    30. 30
      Klimisch, H. J.; Andreae, M.; Tillmann, U. A Systematic Approach for Evaluating the Quality of Experimental Toxicological and Ecotoxicological Data. Regul. Toxicol. Pharmacol. 1997, 25 (1), 15,  DOI: 10.1006/rtph.1996.1076
    31. 31
      Kase, R.; Korkaric, M.; Werner, I.; Ågerstrand, M. Criteria for Reporting and Evaluating ecotoxicity Data (CRED): comparison and perception of the Klimisch and CRED methods for evaluating reliability and relevance of ecotoxicity studies. Environ. Sci. Eur. 2016, 28 (1), 7,  DOI: 10.1186/s12302-016-0073-x
    32. 32
      Koelmans, A. A.; Besseling, E.; Foekema, E.; Kooi, M.; Mintenig, S.; Ossendorp, B. C.; Redondo-Hasselerharm, P. E.; Verschoor, A.; van Wezel, A. P.; Scheffer, M. Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief. Environ. Sci. Technol. 2017, 51 (20), 1151311519,  DOI: 10.1021/acs.est.7b02219
    33. 33
      Brown, L. D.; Cai, T. T.; DasGupta, A. Interval Estimation for a Binomial Proportion. Statistical Science 2001, 16 (2), 101117,  DOI: 10.1214/ss/1009213286
    34. 34
      Kooi, M.; Nes, E. H. v.; Scheffer, M.; Koelmans, A. A. Ups and Downs in the Ocean: Effects of Biofouling on Vertical Transport of Microplastics. Environ. Sci. Technol. 2017, 51 (14), 79637971,  DOI: 10.1021/acs.est.6b04702
    35. 35
      Gall, S. C.; Thompson, R. C. The impact of debris on marine life. Mar. Pollut. Bull. 2015, 92 (1), 170179,  DOI: 10.1016/j.marpolbul.2014.12.041
    36. 36
      Claessens, M.; De Meester, S.; Van Landuyt, L.; De Clerck, K.; Janssen, C. R. Occurrence and distribution of microplastics in marine sediments along the Belgian coast. Mar. Pollut. Bull. 2011, 62 (10), 2199204,  DOI: 10.1016/j.marpolbul.2011.06.030
    37. 37
      Woodall, L. C.; Gwinnett, C.; Packer, M.; Thompson, R. C.; Robinson, L. F.; Paterson, G. L. J. Using a forensic science approach to minimize environmental contamination and to identify microfibres in marine sediments. Mar. Pollut. Bull. 2015, 95 (1), 4046,  DOI: 10.1016/j.marpolbul.2015.04.044
    38. 38
      Van Cauwenberghe, L.; Vanreusel, A.; Mees, J.; Janssen, C. R. Microplastic pollution in deep-sea sediments. Environ. Pollut. 2013, 182, 495499,  DOI: 10.1016/j.envpol.2013.08.013
    39. 39
      Setälä, O.; Norkko, J.; Lehtiniemi, M. Feeding type affects microplastic ingestion in a coastal invertebrate community. Mar. Pollut. Bull. 2016, 102 (1), 95101,  DOI: 10.1016/j.marpolbul.2015.11.053
    40. 40
      Redondo-Hasselerharm, P. E.; Falahudin, D.; Peeters, E. T. H. M.; Koelmans, A. A. Microplastic Effect Thresholds for Freshwater Benthic Macroinvertebrates. Environ. Sci. Technol. 2018, 52 (4), 22782286,  DOI: 10.1021/acs.est.7b05367
    41. 41
      Davison, P.; Asch, R. G. Plastic ingestion by mesopelagic fishes in the North Pacific Subtropical Gyre. Mar. Ecol.: Prog. Ser. 2011, 432, 173180,  DOI: 10.3354/meps09142
    42. 42
      OSPAR request on development of a common monitoring protocol for plastic particles in fish stomachs and selected shellfish on the basis of existing fish disease surveys. IICES Advice 2015, 1, 16.
    43. 43
      Cannon, S. M. E.; Lavers, J. L.; Figueiredo, B. Plastic ingestion by fish in the Southern Hemisphere: A baseline study and review of methods. Mar. Pollut. Bull. 2016, 107, 286291,  DOI: 10.1016/j.marpolbul.2016.03.057
    44. 44
      Jabeen, K.; Su, L.; Li, J.; Yang, D.; Tong, C.; Mu, J.; Shi, H. Microplastics and mesoplastics in fish from coastal and fresh waters of China. Environ. Pollut. 2017, 221, 141149,  DOI: 10.1016/j.envpol.2016.11.055
    45. 45
      MSFD (Technical Subgroup on Marine Litter). Guidance on Monitoring of Marine Litter in European Seas , 2013.
    46. 46
      Hermsen, E.; Pompe, R.; Besseling, E.; Koelmans, A. A. Detection of low numbers of microplastics in North Sea fish using strict quality assurance criteria. Mar. Pollut. Bull. 2017, 122 (1), 253258,  DOI: 10.1016/j.marpolbul.2017.06.051
    47. 47
      Bellas, J.; Martínez-Armental, J.; Martínez-Cámara, A.; Besada, V.; Martínez-Gómez, C. Ingestion of microplastics by demersal fish from the Spanish Atlantic and Mediterranean coasts. Mar. Pollut. Bull. 2016, 109 (1), 5560,  DOI: 10.1016/j.marpolbul.2016.06.026
    48. 48
      Lusher, A. L.; O’Donnell, C.; Officer, R.; O’Connor, I. Microplastic interactions with North Atlantic mesopelagic fish. ICES J. Mar. Sci. 2016, 73 (4), 12141225,  DOI: 10.1093/icesjms/fsv241
    49. 49
      Courtene-Jones, W.; Quinn, B.; Murphy, F.; Gary, S. F.; Narayanaswamy, B. E. Optimisation of enzymatic digestion and validation of specimen preservation methods for the analysis of ingested microplastics. Anal. Methods 2017, 9, 14371445,  DOI: 10.1039/C6AY02343F
    50. 50
      Desforges, J.-P. W.; Galbraith, M.; Ross, P. S. Ingestion of Microplastics by Zooplankton in the Northeast Pacific Ocean. Arch. Environ. Contam. Toxicol. 2015, 69 (3), 320330,  DOI: 10.1007/s00244-015-0172-5
    51. 51
      Murray, F.; Cowie, P. R. Plastic contamination in the decapod crustacean Nephrops norvegicus (Linnaeus, 1758). Mar. Pollut. Bull. 2011, 62 (6), 12071217,  DOI: 10.1016/j.marpolbul.2011.03.032
    52. 52
      Boerger, C. M.; Lattin, G. L.; Moore, S. L.; Moore, C. J. Plastic ingestion by planktivorous fishes in the North Pacific Central Gyre. Mar. Pollut. Bull. 2010, 60 (12), 22752278,  DOI: 10.1016/j.marpolbul.2010.08.007
    53. 53
      Karlsson, T. M.; Vethaak, A. D.; Almroth, B. C.; Ariese, F.; van Velzen, M.; Hassellöv, M.; Leslie, H. A. Screening for microplastics in sediment, water, marine invertebrates and fish: Method development and microplastic accumulation. Mar. Pollut. Bull. 2017, 122 (1), 403408,  DOI: 10.1016/j.marpolbul.2017.06.081
    54. 54
      Torre, M.; Digka, N.; Anastasopoulou, A.; Tsangaris, C.; Mytilineou, C. Anthropogenic microfibres pollution in marine biota. A new and simple methodology to minimize airborne contamination. Mar. Pollut. Bull. 2016, 113 (1), 5561,  DOI: 10.1016/j.marpolbul.2016.07.050
    55. 55
      Liboiron, M.; Liboiron, F.; Wells, E.; Richárd, N.; Zahara, A.; Mather, C.; Bradshaw, H.; Murichi, J. Low plastic ingestion rate in Atlantic cod (Gadus morhua) from Newfoundland destined for human consumption collected through citizen science methods. Mar. Pollut. Bull. 2016, 113 (1), 428437,  DOI: 10.1016/j.marpolbul.2016.10.043
    56. 56
      Devriese, L. I.; van der Meulen, M. D.; Maes, T.; Bekaert, K.; Paul-Pont, I.; Frère, L.; Robbens, J.; Vethaak, A. D. Microplastic contamination in brown shrimp (Crangon crangon, Linnaeus 1758) from coastal waters of the Southern North Sea and Channel area. Mar. Pollut. Bull. 2015, 98 (1), 179187,  DOI: 10.1016/j.marpolbul.2015.06.051
    57. 57
      Wesch, C.; Elert, A. M.; Wörner, M.; Braun, U.; Klein, R.; Paulus, M. Assuring quality in microplastic monitoring: About the value of clean-air devices as essentials for verified data. Sci. Rep. 2017, 7 (1), 5424,  DOI: 10.1038/s41598-017-05838-4
    58. 58
      Rummel, C. D.; Löder, M. G. J.; Fricke, N. F.; Lang, T.; Griebeler, E. M.; Janke, M.; Gerdts, G. Plastic ingestion by pelagic and demersal fish from the North Sea and Baltic Sea. Mar. Pollut. Bull. 2016, 102 (1), 134141,  DOI: 10.1016/j.marpolbul.2015.11.043
    59. 59
      Davidson, K.; Dudas, S. E. Microplastic Ingestion by Wild and Cultured Manila Clams (Venerupis philippinarum) from Baynes Sound, British Columbia. Arch. Environ. Contam. Toxicol. 2016, 71 (2), 147156,  DOI: 10.1007/s00244-016-0286-4
    60. 60
      Van Cauwenberghe, L.; Janssen, C. R. Microplastics in bivalves cultured for human consumption. Environ. Pollut. 2014, 193, 6570,  DOI: 10.1016/j.envpol.2014.06.010
    61. 61
      Löder, M. G. J.; Imhof, H. K.; Ladehoff, M.; Löschel, L. A.; Lorenz, C.; Mintenig, S.; Piehl, S.; Primpke, S.; Schrank, I.; Laforsch, C.; Gerdts, G. Enzymatic purification of microplastics in environmental samples. Environ. Sci. Technol. 2017, 51 (24), 1428314292,  DOI: 10.1021/acs.est.7b03055
    62. 62
      Dehaut, A.; Cassone, A.-L.; Frère, L.; Hermabessiere, L.; Himber, C.; Rinnert, E.; Rivière, G.; Lambert, C.; Soudant, P.; Huvet, A.; Duflos, G.; Paul-Pont, I. Microplastics in seafood: Benchmark protocol for their extraction and characterization. Environ. Pollut. 2016, 215, 223233,  DOI: 10.1016/j.envpol.2016.05.018
    63. 63
      Munno, K.; Helm, P. A.; Jackson, D. A.; Rochman, C.; Sims, A. Impacts of temperature and selected chemical digestion methods on microplastic particles. Environ. Toxicol. Chem. 2018, 37 (1), 9198,  DOI: 10.1002/etc.3935
    64. 64
      Kühn, S.; van Werven, B.; van Oyen, A.; Meijboom, A.; Bravo Rebolledo, E. L.; van Franeker, J. A. The use of potassium hydroxide (KOH) solution as a suitable approach to isolate plastics ingested by marine organisms. Mar. Pollut. Bull. 2017, 115 (1–2), 8690,  DOI: 10.1016/j.marpolbul.2016.11.034
    65. 65
      Cole, M.; Webb, H.; Lindeque, P.; Fileman, E. S.; Halsband, C.; Galloway, T. S. Isolation of microplastics in biota-rich seawater samples and marine organisms. Sci. Rep. 2015, 4 (4528), 18,  DOI: 10.1038/srep04528
    66. 66
      Catarino, A. I.; Thompson, R.; Sanderson, W.; Henry, T. B. Development and optimization of a standard method for extraction of microplastics in mussels by enzyme digestion of soft tissues. Environ. Toxicol. Chem. 2017, 36 (4), 947951,  DOI: 10.1002/etc.3608
    67. 67
      Law, K. L.; Moret-Ferguson, S. E.; Goodwin, D. S.; Zettler, E. R.; De Force, E.; Kukulka, T.; Proskurowski, G. Distribution of Surface Plastic Debris in the Eastern Pacific Ocean from an 11-Year Data Set. Environ. Sci. Technol. 2014, 48 (9), 47324738,  DOI: 10.1021/es4053076
    68. 68
      Eriksen, M.; Mason, S.; Wilson, S.; Box, C.; Zellers, A.; Edwards, W.; Farley, H.; Amato, S. Microplastic pollution in the surface waters of the Laurentian Great Lakes. Mar. Pollut. Bull. 2013, 77 (1–2), 17782,  DOI: 10.1016/j.marpolbul.2013.10.007
    69. 69
      Imhof, H. K.; Laforsch, C.; Wiesheu, A. C.; Schmid, J.; Anger, P. M.; Niessner, R.; Ivleva, N. P. Pigments and plastic in limnetic ecosystems: A qualitative and quantitative study on microparticles of different size classes. Water Res. 2016, 98, 6474,  DOI: 10.1016/j.watres.2016.03.015
    70. 70
      Peters, C. A.; Thomas, P. A.; Rieper, K. B.; Bratton, S. P. Foraging preferences influence microplastic ingestion by six marine fish species from the Texas Gulf Coast. Mar. Pollut. Bull. 2017, 124 (1), 8288,  DOI: 10.1016/j.marpolbul.2017.06.080
    71. 71
      Remy, F.; Collard, F.; Gilbert, B.; Compère, P.; Eppe, G.; Lepoint, G. When Microplastic Is Not Plastic: The Ingestion of Artificial Cellulose Fibers by Macrofauna Living in Seagrass Macrophytodetritus. Environ. Sci. Technol. 2015, 49 (18), 1115811166,  DOI: 10.1021/acs.est.5b02005
    72. 72
      Käppler, A.; Windrich, F.; Loder, M. G. J.; Malanin, M.; Fischer, D.; Labrenz, M.; Eichhorn, K. J.; Voit, B. Identification of microplastics by FTIR and Raman microscopy: a novel silicon filter substrate opens the important spectral range below 1300 cm(−1) for FTIR transmission measurements. Anal. Bioanal. Chem. 2015, 407 (22), 67916801,  DOI: 10.1007/s00216-015-8850-8
    73. 73
      Fries, E.; Dekiff, J. H.; Willmeyer, J.; Nuelle, M. T.; Ebert, M.; Remy, D. Identification of polymer types and additives in marine microplastic particles using pyrolysis-GC/MS and scanning electron microscopy. Environmental Science-Processes & Impacts 2013, 15 (10), 19491956,  DOI: 10.1039/c3em00214d
    74. 74
      Dümichen, E.; Eisentraut, P.; Bannick, C. G.; Barthel, A.-K.; Senz, R.; Braun, U. Fast identification of microplastics in complex environmental samples by a thermal degradation method. Chemosphere 2017, 174, 572584,  DOI: 10.1016/j.chemosphere.2017.02.010
    75. 75
      Fischer, M.; Scholz-Böttcher, B. M. Simultaneous Trace Identification and Quantification of Common Types of Microplastics in Environmental Samples by Pyrolysis-Gas Chromatography–Mass Spectrometry. Environ. Sci. Technol. 2017, 51 (9), 50525060,  DOI: 10.1021/acs.est.6b06362
    76. 76
      Löder, M. G. J.; Kuczera, M.; Mintenig, S.; Lorenz, C.; Gerdts, G. Focal plane array detector-based micro-Fourier-transform infrared imaging for the analysis of microplastics in environmental samples. Environmental Chemistry 2015, 12 (5), 563581,  DOI: 10.1071/EN14205
    77. 77
      Mintenig, S. M.; Bauerlein, P. S.; Koelmans, A. A.; Dekker, S. C.; van Wezel, A. P. Closing the gap between small and smaller: towards a framework to analyse nano- and microplastics in aqueous environmental samples. Environ. Sci.: Nano 2018, 5, 16401649,  DOI: 10.1039/C8EN00186C
    78. 78
      Tanaka, K.; Takada, H. Microplastic fragments and microbeads in digestive tracts of planktivorous fish from urban coastal waters. Sci. Rep. 2016, 6, 34351,  DOI: 10.1038/srep34351
    79. 79
      Wesch, C.; Barthel, A. K.; Braun, U.; Klein, R.; Paulus, M. No microplastics in benthic eelpout (Zoarces viviparus): An urgent need for spectroscopic analyses in microplastic detection. Environ. Res. 2016, 148, 3638,  DOI: 10.1016/j.envres.2016.03.017
    80. 80
      Li, J.; Yang, D.; Li, L.; Jabeen, K.; Shi, H. Microplastics in commercial bivalves from China. Environ. Pollut. 2015, 207, 190195,  DOI: 10.1016/j.envpol.2015.09.018
    81. 81
      Murphy, F.; Russell, M.; Ewins, C.; Quinn, B. The uptake of macroplastic & microplastic by demersal & pelagic fish in the Northeast Atlantic around Scotland. Mar. Pollut. Bull. 2017, 122 (1), 353359,  DOI: 10.1016/j.marpolbul.2017.06.073
    82. 82
      Nadal, M. A.; Alomar, C.; Deudero, S. High levels of microplastic ingestion by the semipelagic fish bogue Boops boops (L.) around the Balearic Islands. Environ. Pollut. 2016, 214, 517523,  DOI: 10.1016/j.envpol.2016.04.054
    83. 83
      Bråte, I. L. N.; Eidsvoll, D. P.; Steindal, C. C.; Thomas, K. V. Plastic ingestion by Atlantic cod (Gadus morhua) from the Norwegian coast. Mar. Pollut. Bull. 2016, 112 (1), 105110,  DOI: 10.1016/j.marpolbul.2016.08.034
    84. 84
      Anastasopoulou, A.; Mytilineou, C.; Smith, C. J.; Papadopoulou, K. N. Plastic debris ingested by deep-water fish of the Ionian Sea (Eastern Mediterranean). Deep Sea Res., Part I 2013, 74 (0), 1113,  DOI: 10.1016/j.dsr.2012.12.008
    85. 85
      Jantz, L. A.; Morishige, C. L.; Bruland, G. L.; Lepczyk, C. A. Ingestion of plastic marine debris by longnose lancetfish (Alepisaurus ferox) in the North Pacific Ocean. Mar. Pollut. Bull. 2013, 69 (1), 97104,  DOI: 10.1016/j.marpolbul.2013.01.019
    86. 86
      Vendel, A. L.; Bessa, F.; Alves, V. E. N.; Amorim, A. L. A.; Patrício, J.; Palma, A. R. T. Widespread microplastic ingestion by fish assemblages in tropical estuaries subjected to anthropogenic pressures. Mar. Pollut. Bull. 2017, 117 (1), 448455,  DOI: 10.1016/j.marpolbul.2017.01.081
    87. 87
      Wójcik-Fudalewska, D.; Normant-Saremba, M.; Anastácio, P. Occurrence of plastic debris in the stomach of the invasive crab Eriocheir sinensis. Mar. Pollut. Bull. 2016, 113 (1), 306311,  DOI: 10.1016/j.marpolbul.2016.09.059
    88. 88
      Miranda, D. d. A.; de Carvalho-Souza, G. F. Are we eating plastic-ingesting fish?. Mar. Pollut. Bull. 2016, 103 (1), 109114,  DOI: 10.1016/j.marpolbul.2015.12.035
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