Microplastic Effect Thresholds for Freshwater Benthic Macroinvertebrates
Open accessAbstract
Now that microplastics have been detected in lakes, rivers, and estuaries all over the globe, evaluating their effects on biota has become an urgent research priority. This is the first study that aims at determining the effect thresholds for a battery of six freshwater benthic macroinvertebrates with different species traits, using a wide range of microplastic concentrations. Standardized 28 days single species bioassays were performed under environmentally relevant exposure conditions using polystyrene microplastics (20–500 μm) mixed with sediment at concentrations ranging from 0 to 40% sediment dry weight (dw). Microplastics caused no effects on the survival of Gammarus pulex, Hyalella azteca, Asellus aquaticus, Sphaerium corneum, and Tubifex spp. and no effects were found on the reproduction of Lumbriculus variegatus. No significant differences in growth were found for H. azteca, A. aquaticus, S. corneum, L. variegatus, and Tubifex spp. However, G. pulex showed a significant reduction in growth (EC10 = 1.07% sediment dw) and microplastic uptake was proportional with microplastic concentrations in sediment. These results indicate that although the risks of environmentally realistic concentrations of microplastics may be low, they still may affect the biodiversity and the functioning of aquatic communities which after all also depend on the sensitive species.
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Written from the paper’s full text.
TL;DR
This study measured microplastic effect thresholds in six freshwater benthic macroinvertebrates using 28-day sediment bioassays with polystyrene particles (20–500 μm) at 0–40% sediment dry weight. Most species showed no effects, but *Gammarus pulex* had reduced growth with an EC10 of 1.07% sediment dw and EC50 of 3.57% sediment dw.
Key findings
- No significant mortality occurred in *G. pulex*, *Hyalella azteca*, *Asellus aquaticus*, *Sphaerium corneum*, or *Tubifex* spp. up to 40% sediment dw, and no significant reproduction effects were found for *Lumbriculus variegatus*.
- Growth was unaffected in *H. azteca*, *A. aquaticus*, *S. corneum*, *L. variegatus*, and *Tubifex* spp., but *G. pulex* showed significant growth reduction at 10–40% sediment dw, with EC10 = 1.07% sediment dw and EC50 = 3.57% sediment dw (±3.22).
- Microplastic uptake by *G. pulex* was proportional to sediment concentration, with trophic transfer factors of (4.47 ± 0.35) × 10⁻¹¹ by number and (10.5 ± 1.3) × 10⁻³ by mass; no microplastics were found in *H. azteca* bodies or faecal pellets.
- Feeding rate of *G. pulex* and *H. azteca* and egestion rate of *L. variegatus* and *Tubifex* spp. showed no negative effects from microplastic exposure.
Methods
- Standardized 28-day single-species bioassays were run with six species in 750 mL glass beakers containing 211 g wet sediment and 300 mL copper-free Dutch Standard Water, using eight polystyrene microplastic concentrations: 0, 0.1, 1, 5, 10, 20, 30, and 40% plastic weight in total sediment mixture.
- Four replicates were used per concentration, except *H. azteca* had three replicates and the 5% concentration was excluded; endpoints included mortality, growth, feeding/egestion rates, and microplastic ingestion, retention, and egestion.
- Data were analyzed with generalized linear models with binomial/probit models for survival, one-way ANOVA and regression for growth and feeding/egestion, repeated-measures ANOVA for egestion over time, and four-parameter log-logistic dose–response models when significant effects were found.
Limitations
- The paper states that the EC50 for *G. pulex* had high uncertainty due to variability among replicates, that field-measured freshwater microplastic concentrations are often provisional due to methodological limitations, and that the particle-volume approximation is not accurate for individual particles but becomes robust for larger numbers of irregular particles.
- The paper also states that *L. variegatus* mortality could not be determined because of reproduction by fragmentation, that *G. pulex* control survival was 66%, and that the observed trophic transfer factors may change over time.
- Evident from the text: the study did not aim to assess chemical effects, so conclusions are limited to physical effects of the tested polystyrene particles under these laboratory conditions.
Model-written summary. Check it against the paper before relying on it.
Integrity signals
Registry
Cites
Statistics
Claims the paper makes
22 of 71 cited sources checked · 11 supported · 1 flagged · accuracy not yet measured
- Premisecitation
Nonstandardized laboratory bioassays and unrealistic exposure scenarios impede understanding of microplastic risks.
“The use of nonstandardized laboratory bioassays and unrealistic exposure scenarios hinders the understanding of the risks associated with microplastics.9,22,23”
Quote in the paperSubstantial claim1 of 3 sources checked- cites [9] Koelmans, 2017, Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief, Environ. Sci. Technol. source
- cites [22] Connors, 2017, Advancing the quality of environmental microplastic research, Environ. Toxicol. Chem. source
- cites [23] Karami, 2017, Gaps in aquatic toxicological studies of microplastics, Chemosphere source
- Premisecitation
Chronic exposure of G. fossarum to PMMA and PHB microplastics in water reduced growth at 100,000 particles per individual.
“However, chronic exposure of a closely related freshwater shrimp, G. fossarum, to poly(methyl methacrylate) (PMMA) and polyhydroxybutyrate (PHB) microplastics in water caused a decrease in growth at a concentration of 100 000 microplastics particles per individual with a similar size range.12”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
- Interpretationcitation
Based on excretion studies with other freshwater amphipods, G. pulex is expected to completely depurate if given enough time and if ingestion stops.
“Based on microplastic excretion studies performed with other freshwater amphipods exposed to different microplastic types,11,12G. pulex is expected to be able to completely depurate if enough time is given and if the ingestion of particles concludes.”
Quote in the paperNot a substantial claim1 of 2 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
Methods §2.5.1 describes transferring G. fossarum to microplastic-free beakers, and Results §3.1 reports substantial excretion over 64 hours. The study did not test G. pulex or establish complete depuration: some particles remained in G. fossarum guts at 64 hours. Page numbers are unavailable in our copy. (LLM, conf=0.87)
Experimental — accuracy not yet measured
- Premisecitation
Field-measured microplastic concentrations in freshwater sediments are far below the calculated EC10 or EC50 effect thresholds for G. pulex.
“Field measured concentrations in freshwater sediments2−4,7,8 although often provisional due to methodological limitations, are far below the calculated EC10 or EC50 effect threshold values for G. pulex.”
Quote in the paperSubstantial claim2 of 5 sources checked- cites [2] Horton, 2017, Microplastics in freshwater and terrestrial environments: Evaluating the current understanding to identify the knowledge gaps and future research priorities, Sci. Total Environ. source
- cites [3] Wagner, 2014, Microplastics in freshwater ecosystems: what we know and what we need to know, Environ. Sci. Eur. source
- cites [4] Eerkes-Medrano, 2015, Microplastics in freshwater systems: A review of the emerging threats, identification of knowledge gaps and prioritisation of research needs, Water Res. source
- cites [7] Klein, 2015, Occurrence and Spatial Distribution of Microplastics in River Shore Sediments of the Rhine-Main Area in Germany, Environ. Sci. Technol. source
- cites [8] Leslie, 2017, Microplastics en route: Field measurements in the Dutch river delta and Amsterdam canals, wastewater treatment plants, North Sea sediments and biota, Environ. Int. source
- Findingown data
No significant growth differences were found for H. azteca, A. aquaticus, S. corneum, L. variegatus, and Tubifex spp.
“No significant differences in growth were found for H. azteca, A. aquaticus, S. corneum, L. variegatus, and Tubifex spp.”
Quote in the paperSubstantial claim
- Findingown data
G. pulex exposed to sediment with 10-40% PS microplastics showed a significant size reduction relative to controls (ANOVA p = 0.002).
“However, individuals of G. pulex exposed to sediment containing high microplastic concentrations (from 10 to 40%) showed a significant reduction in size compared to controls (ANOVA, p-value = 0.002).”
Quote in the paperSubstantial claim - Findingown data
A significant positive linear relation exists between mass-based microplastic concentration inside G. pulex and mass-based concentration in sediment (n = 23, p = 3.97 × 10−7).
“A linear relationship was also found when mass-based concentrations were used (linear regression, n = 23, p-value = 3.97 × 10–7, Figure 3B).”
Quote in the paperNot a substantial claim - Findingown data
The weight of PS microplastics egested per organism dw increased linearly with the weight of PS microplastics in sediment dw (n = 23, p = 4.9 × 10−7).
“Similarly, the weight of PS microplastics egested per organism dw (g kg–1) also increased linearly with the weight of the PS microplastics in sediment dw (g kg–1) (linear regression, n = 23, p-value = 4.9 × 10–07) (SI Figure S7B).”
Quote in the paperNot a substantial claim - Findingown data
Feeding activity of G. pulex and H. azteca did not differ after 28-day exposure to sediment PS microplastic levels reaching 40% dw.
“No differences were found on the feeding activity of G. pulex and H. azteca after a 28 day exposure to PS microplastic concentrations up to 40% in sediment dw (SI Figure S4).”
Quote in the paperSubstantial claim - Findingown data
PS microplastics were found at all concentrations in the body and faecal pellets of G. pulex after 24 h depuration.
“In contrast to H. azteca, PS microplastics were found at all concentrations in the body of G. pulex, as well as in their faecal pellets after a 24 h depuration time.”
Quote in the paperNot a substantial claim - Findingown data
In the 28-day sediment exposure, PS microplastic concentration was not related to growth for A. aquaticus, S. corneum, H. azteca, L. variegatus, or Tubifex spp.
“One-way ANOVA and regression analysis showed no relation between PS microplastic concentrations in sediment and the growth of A. aquaticus, S. corneum, H. azteca, L. variegatus, and Tubifex spp.”
Quote in the paperSubstantial claim - Findingown data
Microplastics in faeces (n = 840) ranged from 16 to 165 μm, with an average of 57 μm.
“The size frequency distribution of the microplastics found in the faeces (n = 840) ranged from 16 to 165 μm, with an average size of 57 μm (SI Figure S6B).”
Quote in the paperNot a substantial claim - Findingown data
A significant positive linear relation exists between the number of PS microplastics in G. pulex faeces and the number in sediment (n = 23, p = 6.63 × 10−6).
“There was also a significant, positive relation between the number of PS microplastics in the faeces egested by G. pulex and the number of PS microplastics in sediment (linear regression, n = 23, p-value 6.63 × 10–06) (SI Figure S7A).”
Quote in the paperNot a substantial claim - Findingown data
Microplastic exposure had no negative effect on egestion rate of L. variegatus and Tubifex spp.
“However, microplastic exposure had no negative effect on the egestion rate of the worms”
Quote in the paperNot a substantial claim - Findingown data
No PS microplastics were detected in the body or faecal pellets of H. azteca at any concentration.
“No microplastics were found in the body nor in the faecal pellets of H. azteca at any concentration”
Quote in the paperSubstantial claim - Findingown data
A significant positive linear relation exists between the number of microplastics inside G. pulex and the number in the sediment exposure medium (n = 23, p = 6.65 × 10−8).
“A linear regression revealed a significant, positive relation between the number of microplastics inside the body of G. pulex and the number of microplastics in the sediment exposure medium (linear regression, n = 23, p-value 6.65 × 10–8; Figure 3A).”
Quote in the paperNot a substantial claim - Findingown data
The model estimated an EC50 of 3.57% sediment dw (±3.22) for G. pulex growth.
“resulted in a EC50 value of 3.57% sediment dw (±3.22)”
Quote in the paperSubstantial claim - Findingown data
The log-logistic model fit for G. pulex growth against PS concentration was highly significant (p = 2.27 × 10−4).
“The fit of the log–logistic model (eq 2) was highly significant (p-value = 2.27 × 10–4)”
Quote in the paperSubstantial claim - Findingown data
The interaction between microplastic exposure and sampling time on egestion rate was not significant.
“and the interactive effect between microplastic exposure and sampling time was also not significant.”
Quote in the paperNot a substantial claim - Findingown data
The difference in egestion rates between L. variegatus and Tubifex spp. was significant along sampling time (RM ANOVA p < 0.05).
“and this difference was significant along the sampling time (RM ANOVA, p-value < 0.05).”
Quote in the paperNot a substantial claim - Findingown data
The model estimated an EC10 of 1.07% sediment dw for G. pulex growth.
“and an EC10 value of 1.07% (SI Figure S3)”
Quote in the paperSubstantial claim - Findingown data
Total ingested particles (retained plus egested; n = 1031) ranged from 16 to 165 μm, with an average of 58 μm.
“The total amount of ingested particles (retained + egested) (n = 1031) ranged from 16 to 165 μm, with an average size of 58 μm (SI Figure S6C).”
Quote in the paperNot a substantial claim - Premisecitation
Freshwater benthic organisms appear to face greater exposure risk because microplastics sink into sediments.
“This is especially important in the case of freshwater benthic organisms, that seem to have a higher risk of exposure due to the sinking of microplastics onto sediments.5”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [5] Besseling, 2017, Fate of nano- and microplastic in freshwater systems: A modeling study, Environ. Pollut. source
- Premisecitation
Concerns have been raised about the quality, reliability, and usability of the limited ecological effect data on microplastics.
“Current studies have mainly focused on the ingestion of microplastics;3 however, the quality, reliability, and usability of the few ecological effect data published have been put into question.22,23”
Quote in the paperSubstantial claim0 of 2 sources checked - Premisereasoning
Polystyrene particles ground to a broad, environmentally relevant range of sizes and shapes were treated as a reasonable proxy for assessing physical effects of environmental microplastics.
“Polystyrene, ground to a wide and environmentally relevant range of sizes and shapes, was considered as a fair approximation to assess the physical effects of “environmental microplastics”.7”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [7] Klein, 2015, Occurrence and Spatial Distribution of Microplastics in River Shore Sediments of the Rhine-Main Area in Germany, Environ. Sci. Technol. source
- Interpretationown data
The absence of microplastic ingestion by H. azteca is consistent with the lack of growth effect for this species in the 28-day test.
“This is consistent with the lack of effect found for this species in the present 28 day exposure test.”
Quote in the paperNot a substantial claim - Study design and conductown data
Mortality of L. variegatus could not be determined because the worms reproduced by fragmentation during the experiment.
“Mortality of L. variegatus could not be determined due to their reproduction by fragmentation during the experiment.”
Quote in the paperNot a substantial claim - Premisecitation
Earlier studies with benthic macroinvertebrates exposed to microplastics also reported no mortality effects.
“Same lack of effects on mortality has been reported in earlier studies with benthic macroinvertebrates exposed to microplastics.”
Quote in the paperNot a substantial claim - Premisecitation
A previous study found reduced growth of H. azteca after 28-day exposure to PE microplastics in water at 5,000 and 10,000 particles per mL.
“In contrast, a previous study showed a decrease in the growth of H. azteca after a 28 day exposure to PE microplastics in water at concentrations of 5000 and 10 000 PE microplastic particles per mL.11”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- Premisecitation
Weber et al. (2018) found no effects on G. pulex feeding activity after exposure to PET microplastics in water.
“These results are in accordance with Weber et al., 2018, where no effects on the feeding activity of G. pulex were found after an exposure to PET microplastics in water.14”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [14] Weber, 2018, PET microplastics do not negatively affect the survival, development, metabolism and feeding activity of the freshwater invertebrate Gammarus pulex, Environ. Pollut. source
- Interpretationown data
Chronic PS microplastic exposure produces a species-specific and dose-dependent effect on growth of the tested benthic macroinvertebrates.
“These outcomes reveal that a chronic exposure to PS microplastic results in a species specific and dose-dependent effect of PS microplastics on the growth of the benthic macroinvertebrates tested.”
Quote in the paperSubstantial claim - Interpretationown data
The TTF, the ratio of microplastic concentration in the organism to that in sediment, appears constant up to 40% sediment dw.
“The TTF represents the ratio of the microplastic concentration in the organism and that in the sediment exposure medium, which appears to be constant up to 40% sediment dw.”
Quote in the paperSubstantial claim - Interpretationown data
H. azteca did not ingest PS microplastic particles in the 20-500 μm size range.
“indicating that these organisms did not ingest microplastic particles in the size range of 20–500 μm PS.”
Quote in the paperSubstantial claim - Interpretationreasoning
Responses at community and ecosystem levels could occur over time due to effects on G. pulex.
“which means that responses at community and ecosystem levels could occur over time.”
Quote in the paperSubstantial claim
- Classified as probably not a substantial claim. 27
- May combine two claims. 52
- The quote only partly states this claim. 1
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationNo mortality was reported for the marine isopod Idotea emarginata exposed to PE, PS, and PA microplastics, or for the marine lugworm Arenicola marina exposed to PE microplastics.
“Furthermore, no mortality was reported for the marine isopod Idotea emarginata exposed to PE, PS, and PA (polyamide) microplastics and the marine lugworm A. marina exposed to PE microplastics.19”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [19] Besseling, 2017, The Effect of Microplastic on the Uptake of Chemicals by the Lugworm Arenicola marina (L.) under Environmentally Relevant Exposure Conditions, Environ. Sci. Technol. source
The Results and discussion section (“Lugworm Survival, Feeding Activity, Weight, and Lipid Content”) reports 81% overall lugworm survival, meaning mortality did occur. It found no significant difference in survival between PE treatments, which is not the same as no mortality. The cited paper does not examine Idotea emarginata. (LLM, conf=0.88)
Checked by a reasoning model — may be wrong.
Experimental — accuracy not yet measured
Probably not a substantial claim: may not pass S2 (checkable), S3 (load-bearing). May combine two claims.
PremisecitationUnderstanding how microplastics interact with freshwater biota is a high-priority research need, and there is general agreement that exposure risk should be assessed.
“Understanding the interaction between microplastics and biota in freshwater systems has been identified as a high priority research need4 and there is a general agreement on the idea that an effect assessment should be performed to evaluate the risk of exposure to microplastics.9”
Quote in the paperNot a substantial claim1 of 2 sources checked- cites [4] Eerkes-Medrano, 2015, Microplastics in freshwater systems: A review of the emerging threats, identification of knowledge gaps and prioritisation of research needs, Water Res. source
- cites [9] Koelmans, 2017, Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief, Environ. Sci. Technol. source
May combine two claims.
PremisecitationThe selected species are common freshwater community members, frequently used in laboratory experiments, and differ in living and feeding strategies and in sensitivity to environmental pollutants.
“These species are common members of freshwater communities, are often used in laboratory experiments and differ in their living and feeding strategies, as well as in their sensitivity to environmental pollutants.26−28”
Quote in the paperSubstantial claim1 of 3 sources checked- cites [26] Maltby, 1995, Sensitivity of the crustaceans Gammarus pulex (L.) and Asellus aquaticus (L.) to short-term exposure to hypoxia and unionized ammonia: observations and possible mechanisms, Water Res. source
- cites [27] Kupryianchyk, 2011, Ecotoxicological Effects of Activated Carbon Amendments on Macroinvertebrates in Nonpolluted and Polluted Sediments, Environ. Sci. Technol. source
- cites [28] Diepens, 2016, Prospective environmental risk assessment for sediment-bound organic chemicals: A proposal for tiered effect assessment source
No passage from our copy matched the claim. Searches for freshwater species, laboratory use, feeding strategies, and pollutant sensitivity returned no passages, so the copy does not establish these characteristics of the selected species. (LLM, conf=0.68)
Experimental — accuracy not yet measured
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationIt is still unclear whether microplastic adverse effects arise from physical particle impact, chemical toxicity, or both.
“Furthermore, it remains unclear if adverse effects are caused by a physical impact of the particles themselves, by chemical toxicity or by a combination of both.2”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [2] Horton, 2017, Microplastics in freshwater and terrestrial environments: Evaluating the current understanding to identify the knowledge gaps and future research priorities, Sci. Total Environ. source
Probably not a substantial claim: may not pass S2 (checkable). May combine two claims.
PremisecitationEffect assessments for microplastics should target traditional ecotoxicological thresholds such as LC50 or EC50, and fitting dose-response models requires sufficient doses and replication.
“Moreover, an effect assessment for microplastics should aim at detecting the effect thresholds for traditional end points in ecotoxicology (i.e., LC50 or EC50),22 and for this, sufficient doses and replication are needed in order to fit dose–response models, which are commonly used in chemical risk assessment.9”
Quote in the paperNot a substantial claim1 of 2 sources checkedProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationMicroplastic uptake had no effect on the marine isopod Idotea emarginata, but it caused weight loss and lower feeding activity in the marine lugworm Arenicola marina.
“Microplastic uptake did not cause any effects on the marine isopod Idotea emarginata(16) but did cause weight loss and a reduced feeding activity for the marine lugworm Arenicola marina.17−19”
Quote in the paperNot a substantial claim2 of 4 sources checked- cites [16] Hämer, 2014, Fate of microplastics in the marine isopod Idotea emarginata, Environ. Sci. Technol. source
The Discussion (p. 4) reports no distinct adverse effects on the isopods’ survival, intermolt duration, or growth. But the Discussion (p. 6) also reports reduced uptake of food supplemented with microplastics, so “did not cause any effects” is too absolute. The lugworm finding is attached to citations 17–19, not this source. (LLM, conf=0.86)
Experimental — accuracy not yet measured - cites [17] Wright, 2013, Microplastic ingestion decreases energy reserves in marine worms, Curr. Biol. source
- cites [18] Besseling, 2013, Effects of microplastic on fitness and PCB bioaccumulation by the lugworm Arenicola marina (L.), Environ. Sci. Technol. source
- cites [19] Besseling, 2017, The Effect of Microplastic on the Uptake of Chemicals by the Lugworm Arenicola marina (L.) under Environmentally Relevant Exposure Conditions, Environ. Sci. Technol. source
The Results and discussion section, “Lugworm Survival, Feeding Activity, Weight, and Lipid Content” (page not supplied), reports significantly lower faeces-heap mass in polyethylene treatments, supporting reduced feeding activity in Arenicola marina. Lugworms also lost weight, but weight loss did not significantly differ among treatments, so this paper does not support attributing the weight loss to microplastic. The isopod finding is attached to a different citation in the citing sentence. (LLM, conf=0.91)
Experimental — accuracy not yet measured
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationIn Gammarus fossarum, microplastic uptake was linked to reduced growth after exposure to PMMA and PHB particles.
“Moreover, this uptake was related to a decrease in the growth of Gammarus fossarum exposed to poly(methyl methacrylate) (PMMA) and polyhydroxybutyrate (PHB) microplastics.12”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
May combine two claims.
PremisecitationFreshwater species take up microplastics from sediments, and the ingestion capacity of freshwater invertebrates varies with feeding type.
“Previous studies have indeed demonstrated that microplastics are taken up from sediments by freshwater species10−15 and that the capacity of freshwater invertebrates to ingest microplastics depends on their feeding type.15”
Quote in the paperNot a substantial claim2 of 6 sources checked- cites [10] Imhof, 2013, Contamination of beach sediments of a subalpine lake with microplastic particles, Curr. Biol. source
- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
The Methods (section 2.4) describe microplastics sinking to the bottom of experimental beakers, where Gammarus fossarum ingested them; the study does not demonstrate uptake from natural sediments. The Discussion (sections 4.1 and 4.4) identifies the amphipods as shredders that readily ingest certain particle sizes, but it does not compare invertebrates with different feeding types or establish that ingestion capacity depends on feeding type. (LLM, conf=0.84)
Experimental — accuracy not yet measured - cites [13] Hurley, 2017, Ingestion of Microplastics by Freshwater Tubifex Worms, Environ. Sci. Technol. source
- cites [14] Weber, 2018, PET microplastics do not negatively affect the survival, development, metabolism and feeding activity of the freshwater invertebrate Gammarus pulex, Environ. Pollut. source
- cites [15] Scherer, 2017, Feeding type and development drive the ingestion of microplastics by freshwater invertebrates, Sci. Rep. source
The Abstract and Results and Discussion (Species; pages not provided) show that freshwater invertebrates ingested microplastics at rates that varied with feeding type. The paper also reports ingestion by benthic feeders and observes that larger beads settled, but it does not directly demonstrate uptake of microplastics from sediments; it describes ingestion of settling particles at the sediment surface as likely. (LLM, conf=0.82)
Experimental — accuracy not yet measured
May combine two claims.
PremisecitationGrowth of G. fossarum was reduced after 28-day exposure to PMMA and PHB particles, while its feeding rate was unaffected.
“Similarly, while the growth of G. fossarum was reduced after a 28 day exposure to PMMA and PHB particles, the feeding rate was also unaffected.12”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
May combine two claims.
InterpretationcitationDifferences between study outcomes may be due to exposure medium and greater bioavailability of suspended particles compared with sediment-mixed particles.
“Such differences between study outcomes may relate to (a) differences in the exposure medium, as the presence of natural particles seems to reduce the ingestion of microplastics in freshwater invertebrates,15 and (b) to a higher bioavailability of particles in suspension as compared to particles mixed in the sediment as in the present bioassays.”
Quote in the paperSubstantial claim1 of 1 sources checked- cites [15] Scherer, 2017, Feeding type and development drive the ingestion of microplastics by freshwater invertebrates, Sci. Rep. source
Classified as probably not a substantial claim. May combine two claims.
Study design and conductcitationMicroplastic concentrations spanned environmentally relevant levels (0-1% plastic weight in sediment dry weight) to very high levels, in order to evaluate dose-response relationships and maximize detection of the effect threshold.
“Concentrations ranged from environmentally relevant (0–1% plastic weight in sediment dw) to very high concentrations, to evaluate dose–response relations and to maximize the chance of accurately detecting the effect threshold.9”
Quote in the paperSubstantial claim1 of 1 sources checked- cites [9] Koelmans, 2017, Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief, Environ. Sci. Technol. source
In “Measure Effect Thresholds” (page not provided), Koelmans recommends testing a range of concentrations to detect effect thresholds and fit dose–effect models. The paper does not give the claimed 0–1% sediment-dry-weight range or report that such concentrations were used in an experiment; it makes a recommendation rather than describing a completed test. (LLM, conf=0.87)
Experimental — accuracy not yet measured
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationNo growth effects were found for the marine isopod I. emarginata exposed to PE, PS, and PA microplastics in water.
“No effects were found on growth for the marine isopod I. emarginata exposed to PE, PS, and PA microplastics in water,16”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [16] Hämer, 2014, Fate of microplastics in the marine isopod Idotea emarginata, Environ. Sci. Technol. source
The Discussion (p. 4) reports no distinct adverse effect on growth, and the Materials and Methods (p. 2) describe food containing PE fragments; the Introduction (p. 2) identifies PS particles and polyacrylic fibers. But the isopods ingested microplastics embedded in artificial food, rather than being exposed to microplastics dispersed in water. (LLM, conf=0.90)
Experimental — accuracy not yet measured
May combine two claims.
InterpretationcitationGrowth reduction of G. pulex was a sublethal effect caused by reduced food assimilation due to PS microplastic ingestion and by gut blockage from longer excretion time.
“our results indicate that growth reduction of G. pulex was a sublethal effect caused by a lower ability of these organisms to assimilate food due to the ingestion of PS microplastics,11,12 as well as by the gut blockage by these particles due to a longer excretion time needed to depurate their gut.11”
Quote in the paperSubstantial claim1 of 2 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- cites [12] Straub, 2017, Biodegradable and Petroleum-Based Microplastics Do Not Differ in Their Ingestion and Excretion but in Their Biological Effects in a Freshwater Invertebrate Gammarus fossarum, Int. J. Environ. Res. Public Health source
The Results (§3.2) report reduced assimilation efficiency and wet-weight gain, and the Discussion (§§4.2, 4.6) proposes prolonged gut retention and possible obstruction as explanations. But this paper studied G. fossarum exposed to PMMA and PHB, not G. pulex exposed to PS; it also presents gut obstruction as a possibility rather than an established cause. (LLM, conf=0.88)
Experimental — accuracy not yet measured
May combine two claims.
InterpretationcitationThe high mobility of G. pulex could have increased its microplastic uptake compared with other epibenthic species, highlighting species-specific traits in microplastic effects.
“Moreover, the high mobility of G. pulex(46) could have increased microplastic uptake in comparison to the other epibenthic species, revealing the importance of species specific traits in the effects of microplastics on benthic invertebrates.”
Quote in the paperNot a substantial claim1 of 1 sources checked- cites [46] Vadher, 2015, Fine sediment reduces vertical migrations of Gammarus pulex (Crustacea: Amphipoda) in response to surface water loss, Hydrobiologia source
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationPrevious studies show that microplastic uptake by freshwater invertebrates is size-specific and feeding-type dependent, and irregularly shaped microplastics need longer clearance time than spherical ones.
“This is in accordance with previous studies showing that microplastic uptake by freshwater invertebrates is size- specific and feeding type dependent and that irregularly shaped microplastics need a significant longer clearance time in comparison to spherical microplastics.11,15”
Quote in the paperNot a substantial claim1 of 2 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- cites [15] Scherer, 2017, Feeding type and development drive the ingestion of microplastics by freshwater invertebrates, Sci. Rep. source
The Abstract and Results and Discussion (Species) show that uptake varies with particle size and feeding strategy. Results and Discussion (Size) says the study tested only spheres and suggests that depuration of irregular particles may differ; it does not establish that irregular particles take significantly longer to clear. (LLM, conf=0.90)
Experimental — accuracy not yet measured
May combine two claims.
Findingown dataThe polystyrene particles had a unimodal size distribution from 20 to 500 μm, with a volume mode at 229 μm and a number mode at 36 μm.
“Particle size distribution (PSD), measured with a Mastersizer 3000 (Malvern Instruments), revealed an unimodal distribution spanning from 20 to 500 μm, with a modus centered at 229 μm in volume and 36 μm in number (SI Figure S1).”
Quote in the paperNot a substantial claimMay combine two claims.
FindingcitationIn controls, the average number of surviving L. variegatus worms per replicate increased by at least 1.8-fold, and reproduction factor was calculated as final worm number divided by initial worm number.
“As the average number of surviving worms per replicate in controls was increased by a factor of at least 1.8, the reproduction factor could be calculated as the number of worms at the end of the experiment divided by the number of worms at the beginning of the experiment.31”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [31] OECD., 2007, OECD Guidelines for the testing of chemicals source
May combine two claims.
Findingown dataAll L. variegatus and Tubifex spp. survived the experiment, and no reproduction was observed in the additional 15-day period.
“At the end of the experiment, all L. variegatus and Tubifex spp. survived and no reproduction was observed in the additional 15 day period experiment.”
Quote in the paperNot a substantial claimThe quote only partly states this claim.
Findingown dataMicroplastic uptake increased proportionally with microplastic concentrations in sediment.
“However, G. pulex showed a significant reduction in growth (EC10 = 1.07% sediment dw) and microplastic uptake was proportional with microplastic concentrations in sediment.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Findingown dataThe sediment total organic matter content was 31.6% ± 3.5 (n = 4).
“Four representative subsamples were taken to determine the % TOM through loss on ignition (3 h, 550 °C), which was 31.6% ± 3.5 (n = 4).”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataL. variegatus egestion rate increased in the first week then decreased until the end, whereas Tubifex spp. egestion rate increased over time until the end.
“The egestion rate of L. variegatus increased during the first week of exposure and then decreased until the end of experiment, whereas the egestion rate for Tubifex spp. increased over time until the end of experiment (SI Figure S5).”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataAverage egestion rates were 0.43 mg dry faeces per mg dry organism per h for L. variegatus and 0.32 for Tubifex spp.
“The average egestion rates of L. variegatus and Tubifex spp. were 0.43 and 0.32 mg dry faeces per mg dry organism per h, respectively”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataG. pulex showed a significant growth reduction, with an EC10 of 1.07% sediment dry weight.
“However, G. pulex showed a significant reduction in growth (EC10 = 1.07% sediment dw) and microplastic uptake was proportional with microplastic concentrations in sediment.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataMicroplastics in G. pulex bodies (n = 191) ranged from 22 to 165 μm, with an average of 61 μm.
“Size frequency distribution of the microplastics found in the body of all organisms (n = 191) ranged from 22 to 165 μm, with an average size of 61 μm (SI Figure S6A).”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataChronic exposure to PS microplastic concentrations up to 40% sediment dry weight caused no significant mortality in G. pulex, A. aquaticus, S. corneum, H. azteca, and Tubifex spp., and no significant effects on L. variegatus reproduction.
“Microplastics caused no effects on the survival of Gammarus pulex, Hyalella azteca, Asellus aquaticus, Sphaerium corneum, and Tubifex spp. and no effects were found on the reproduction of Lumbriculus variegatus.”
- Also stated in: § Mortality · plain
“Chronic exposure to PS microplastic concentrations up to 40% in sediment dw caused no significant mortality in G. pulex, A. aquaticus, S. corneum, H. azteca, and Tubifex spp. (Figure 1A–E), and no significant effects were found on the reproduction of L. variegatus (Figure 1F).”
Quote in the paperSubstantial claim- Also stated in: § Mortality · plain
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationThe Rhine river has the highest microplastic concentrations recorded among freshwater bodies studied, with up to 4000 particles per kg or 1 g per kg dry weight in German shore sediments, and the smallest fraction (63-630 μm) is most abundant by number.
“Recent data shows that the Rhine river contains the highest microplastic concentrations detected in all freshwater bodies studied. Concentrations up to 4000 particles kg–1 or 1 g kg–1 (dw) were recorded in the German Rhine river shore sediments, with the smallest microplastic fraction (63–630 μm) being the most abundant in numbers.7”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [7] Klein, 2015, Occurrence and Spatial Distribution of Microplastics in River Shore Sediments of the Rhine-Main Area in Germany, Environ. Sci. Technol. source
May combine two claims.
PremisecitationPolystyrene density matches that of the average environmental microplastic, and polymer density has little influence on physical effects.
“After all, polystyrene density matches that of the average environmental microplastic5,25 (see calculation in Supporting Information (SI) Table S1) and polymer density has limited impact on physical effects.”
Quote in the paperSubstantial claim0 of 2 sources checkedClassified as probably not a substantial claim. May combine two claims.
PremisecitationAmong the selected species, G. pulex, H. azteca, and A. aquaticus are mainly shredders; S. corneum is a facultative suspension feeder; and L. variegatus and Tubifex spp. are endobenthic deposit feeders, with L. variegatus a bulk feeder and Tubifex spp. selective.
“G. pulex, H. azteca, and A. aquaticus are regarded as being mainly shredders, whereas S. corneum is classified as a facultative suspension feeder.”
- Also stated in: § Test Organisms · plain
“L. variegatus and Tubifex spp. are both endobenthic deposit feeders, with L. variegatus regarded as a bulk feeder while Tubifex spp. exhibits selectivity in its feeding behavior.29”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [29] Rodriguez, 2001, Selective feeding by the aquatic oligochaete Tubifex tubifex (Tubificidae, Clitellata), Hydrobiologia source
- Also stated in: § Test Organisms · plain
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationAfter taking up PET microplastics, Gammarus pulex showed no effects on survival, molting, metabolism, or feeding activity.
“However, no effects were reported on the survival, molting, metabolism and feeding activity of Gammarus pulex after the uptake of polyethylene terephtalate (PET) microplastics.14”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [14] Weber, 2018, PET microplastics do not negatively affect the survival, development, metabolism and feeding activity of the freshwater invertebrate Gammarus pulex, Environ. Pollut. source
May combine two claims.
Study design and conductreasoningFor every endpoint, the study simulated environmentally relevant exposure by using natural sediments and including the highest concentration reported in freshwater sediment.
“For all end points, environmentally relevant exposure conditions were simulated by using natural sediments and by including the highest concentration found in a freshwater sediment.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningThe evidence suggests that benthic macroinvertebrates are affected by microplastics, but susceptibility may differ among species.
“This suggests that benthic macroinvertebrates are affected by the presence of microplastics but also that the susceptibility could be species specific.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationSediments can serve as a sink for microplastics, as indicated by the strong influence of particle size on river-sediment microplastic hotspots.
“In fact, particle size has been found to strongly affect the presence of microplastic hotspots along river sediments, indicating that sediments can act as a sink for microplastics.5”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [5] Besseling, 2017, Fate of nano- and microplastic in freshwater systems: A modeling study, Environ. Pollut. source
May combine two claims.
Study design and conductown dataFTIR spectrometry confirmed polymer identity and purity, and stereomicroscopy confirmed particle shape.
“Polymer identity and purity were confirmed with FTIR spectrometry (Nicolet iN10, ThermoFisher) and particle shape was confirmed with an Olympus SZX10 stereomicroscope (Figure S2, SI).”
Quote in the paperSubstantial claimMay combine two claims.
Study design and conductcitationSediments came from a noncontaminated ditch, with ∑PAH and ∑PCBs more than 8 and 70 times below toxicity thresholds, respectively, and heavy metals below negligible risk levels under Dutch sediment quality criteria.
“Freshwater sediments were collected from a noncontaminated ditch in Veenkampen (Wageningen, The Netherlands) using a standard dip net. Background concentrations of ∑PAH and ∑PCBs were factors of >8 and >70 below toxicity thresholds,27 whereas heavy metals were below negligible risk levels according to Dutch sediment quality criteria (SI Table S2).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [27] Kupryianchyk, 2011, Ecotoxicological Effects of Activated Carbon Amendments on Macroinvertebrates in Nonpolluted and Polluted Sediments, Environ. Sci. Technol. source
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationOther marine invertebrates have shown no or limited effects from microplastics.
“No or limited effects have also been found for other marine invertebrates.20,21”
Quote in the paperNot a substantial claim0 of 2 sources checkedMay combine two claims.
PremisecitationExposure to polyethylene microplastics reduced both growth and reproduction in Hyalella azteca.
“Also, a reduction in the growth and reproduction of Hyalella azteca was found after the exposure to polyethylene (PE) microplastics.11”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
Classified as probably not a substantial claim.
Study design and conductreasoningPotential additives in the microplastics were removed so that the cause of any particle effect would not be ambiguous.
“Any potential additives present were removed from the microplastics to eliminate any ambiguity concerning what caused the effect of the particles.”
- Also stated in: § Microplastics · plain
“To remove additives present, if any, the microplastics were washed with methanol three times, shaken, filtered with a 20 μm metal sieve and dried for at least 2 days in a fume hood at room temperature.”
Quote in the paperSubstantial claim- Also stated in: § Microplastics · plain
May combine two claims.
Study design and conductown dataUn-ionized ammonia decreased over the experiment, reaching an average of 0.002 ± 0.001 mg NH3/L at the end, and remained below available LC50 values for the species.
“Un-ionised levels of ammonia decreased along the experiment for all species, reaching an average of 0.002 ± 0.001 mg NH3/l at the end of the experiment. All un-ionized ammonia levels were always below the LC50 values available for these species.26,32−34”
Quote in the paperNot a substantial claim0 of 4 sources checked- cites [26] Maltby, 1995, Sensitivity of the crustaceans Gammarus pulex (L.) and Asellus aquaticus (L.) to short-term exposure to hypoxia and unionized ammonia: observations and possible mechanisms, Water Res. source
- cites [32] Ankley, 1995, Influence of pH and hardness on toxicity of ammonia to the amphipod Hyalella azteca, Can. J. Fish. Aquat. Sci. source
- cites [33] Schubaur-Berigan, 1995, Influence of pH on the toxicity of ammonia to Chironomus tentans and Lumbriculus variegatus, Environ. Toxicol. Chem. source
- cites [34] Arrate, 2014, Tubifex tubifex chronic toxicity test using artificial sediment: methodological issues, Limnetica
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductreasoningOrganisms and faecal pellets from the 1% treatment and one replicate of the 30% treatment were used to optimize microplastic extraction, and their data were excluded from further analysis.
“Organisms and faecal pellets from the 1% treatment, as well as one replica of the 30% treatment, were used to optimize the extraction of microplastics and, therefore, their data were omitted from further analysis.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductcitationWater quality variables stayed constant in all beakers except in Tubifex spp. and L. variegatus treatments, where pH approached below recommended limits at days 14 and 24; this was corrected by replacing surface water with fresh DSW.
“Water quality variables remained constant in all beakers along the experiment (Table S3, SI), except for the treatments with Tubifex spp. and L. variegatus where pH approached values below the recommended limits (6–9) at day 14 and 24, respectively.31”
- Also stated in: § Experimental Design · plain
“This was solved by replacing 100 mL from the surface water layer in the bioassay by fresh DSW.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [31] OECD., 2007, OECD Guidelines for the testing of chemicals source
- Also stated in: § Experimental Design · plain
May combine two claims.
Interpretationown dataUp to 40% concentration, PS microplastic uptake by G. pulex is proportional to sediment concentration, whether expressed as number or mass.
“These data show that up to a concentration of 40%, uptake by G. pulex (Figure 3) is proportional to the concentration in the sediment, either expressed as number or as mass.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductown dataNo mortality occurred during the 15-day egestion experiment.
“No mortality occurred during the 15 day experiment.”
Quote in the paperNot a substantial claimMay combine two claims.
Interpretationown dataWeight loss of G. pulex was probably not caused by reduced consumption of Populus sp. leaves, and sediment microplastics did not alter feeding rate of these amphipods.
“These findings indicate that weight loss of G. pulex was probably not caused by a reduction in the consumption of Populus sp. leaves during the experiment and that the presence of microplastics in the sediment did not alter the feeding rate of these benthic amphipods.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningAfter correction for the 165-500 μm biounavailable fraction, net transfer TTF estimates are (5.16 ± 0.40) × 10−11 for number and 0.028 ± 0.0036 for mass.
“When corrected for the 165–500 μm biounavailable fraction, pure estimates of net transfer are obtained, being TTF = (5.16 ± 0.40) × 10–11 (number) and 0.028 ± 0.0036 (mass).”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningThe results suggest that risks from environmentally realistic microplastic concentrations may be low, but such concentrations may still affect aquatic community biodiversity and functioning because these depend on sensitive species.
“These results indicate that although the risks of environmentally realistic concentrations of microplastics may be low, they still may affect the biodiversity and the functioning of aquatic communities which after all also depend on the sensitive species.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningFor the five species whose growth was unaffected up to 40% plastic in sediment dw, EC10 values exceed 40% plastic in sediment dw.
“Hence, the EC10 values for these species are higher than 40% plastic in sediment dw.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductown dataControl blanks contained 0.10 retained and 0.6 egested particles per organism, and these values were subtracted from treatment replicates.
“The numbers of particles found in controls for the retained and egested particles were subtracted from the numbers of particles found in each replica of each PS treatment, and were 0.10 and 0.6 particles per organism, respectively.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based).
Interpretationnone givenThe observed constancy and magnitude of TTF may still change over time.
“Therefore, the observed constancy and magnitude of TTF may still change over time.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationWeight loss of the marine lugworm A. marina was reported at 7.4% PS microplastics and >5% uPVC microplastics in sediment dw.
“while weight loss of the marine lugworm A. marina was reported at concentrations of 7.4% PS microplastics18 and >5% uPVC microplastics in sediment dw.17”
Quote in the paperNot a substantial claim0 of 2 sources checkedProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductown dataAverage measured exposure conditions were 16 ± 0.3 °C, pH 7.3 ± 0.5, oxygen 8.9 ± 0.2 mg/L, and conductivity 477 ± 45 μS/cm.
“On average, the measured temperature was 16 ± 0.3 °C, pH was 7.3 ± 0.5, oxygen concentration was 8.9 ± 0.2 mg/L and conductivity was 477 ± 45 μS/cm.”
Quote in the paperNot a substantial claimMay combine two claims.
Study design and conductown dataControl survival exceeded 80% for all species except G. pulex, which averaged 66%.
“Survival for the other species was higher than 80% in controls, except for G. pulex, for which the average survival was 66%.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductown dataOne concentration was identified as an outlier by Iglewics and Hoaglin's robust test and excluded from regression parameter determination.
“One of the concentrations was designated as an outlier (Iglewics and Hoaglin’s robust test) which was not taken into account in the subsequent determination of the regression parameters.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningThe slope of the exposure-uptake relation can be interpreted as trophic transfer factors, with TTFnumber = (4.47 ± 0.35) × 10−11 and TTFmass = (10.5 ± 1.3) × 10−3.
“Given the demonstrated proportionality between exposure and uptake, the slope of the line in Figure 3A and B can be interpreted as trophic transfer factors (TTF) with a value of (4.47 ± 0.35) × 10–11 (TTFnumber; Figure 3A) and (10.5 ± 1.3) × 10–3 (TTFmass; Figure 3B).”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationSurvival of G. pulex and H. azteca was unaffected by PET and PE microplastics, respectively.
“For instance, survival of the freshwater amphipods G. pulex and H. azteca were not affected by the exposure to PET and PE microplastics, respectively.11,14”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites [11] Au, 2015, Responses of Hyalella azteca to acute and chronic microplastic exposures, Environ. Toxicol. Chem. source
- cites [14] Weber, 2018, PET microplastics do not negatively affect the survival, development, metabolism and feeding activity of the freshwater invertebrate Gammarus pulex, Environ. Pollut. source
May combine two claims.
Study design and conductown dataMicroplastics larger than 165 μm accounted for <0.01% of the total and were treated as external contamination and excluded from analysis.
“Microplastics with a size >165 μm accounted for only <0.01% of the total amount (in number) and were considered to originate from an external source of microplastics (i.e., particles attached to the external body of the organisms), and were removed from the analysis.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningThe low TTF values can be explained by only a limited part of the sediment size range being taken up, so TTFs reflect transfer and size selection.
“These TTF values are low, which can be explained by the fact that only a limited part of the size range in the sediment is actually taken up, that is, the TTFs mechanistically reflect transfer and size selection.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
Study design and conductnone givenResidual normality and variance homogeneity were tested using Shapiro-Wilk and Levene's tests, respectively.
“Normality of the residuals and homogeneity of variances were tested with a Shapiro-Wilk Normality test and Levene’s test, respectively.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationcitationOnly G. pulex showed significant growth reduction, likely explained by size-selective PS uptake and slow excretion leading to energy reserve depletion.
“Only for one of the species, G. pulex, a significant reduction in growth was found, which is likely to be explained by the demonstrated size-selective uptake of PS microplastics and their slow excretion, leading to a depletion of energy reserves as found earlier for marine worms as a result of microplastic ingestion.17”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [17] Wright, 2013, Microplastic ingestion decreases energy reserves in marine worms, Curr. Biol. source
May combine two claims.
InterpretationreasoningExtrapolating these results to the environment implies small chances of such physical effects and consequently low current risk for the freshwater benthic community.
“This means that extrapolating these results to the environment leads to small chances of such physical effects, and consequently low current risk for the benthic community of freshwater systems.”
Quote in the paperSubstantial claim- Rests on an assumption: The range of PS particle sizes and shapes used is a fair approximation of environmental microplastics for physical effects.
- Rests on an assumption: The test conditions are environmentally relevant.
May combine two claims.
PremisecitationG. pulex plays a key role in processing coarse particulate organic matter in streams, is important prey for fish, and its feeding inhibition can alter the benthic macroinvertebrate community.
“In fact, G. pulex plays a key role in the processing of coarse particulate organic matter in streams,48 is an important prey for fish,49 and its feeding inhibition has shown to alter the benthic macroinvertebrate community,36”
Quote in the paperSubstantial claim0 of 3 sources checked- cites [48] Kelly, 2002, The functional role of Gammarus (Crustacea, Amphipoda): shredders, predators, or both?, Hydrobiologia source
- cites [49] Macneil, 1997, The Thropic Ecology of Freshwater Gammarus spp. (Crustacea: Amphipoda): Problems and Perspectives Concerning the Functional Feeding Group Concept, Biol. Rev. Cambridge Philos. Soc. source
- cites [36] Maltby, 2002, Evaluation of the Gammarus pulex in situ feeding assay as a biomonitor of water quality: Robustness, responsiveness, and relevance, Environ. Toxicol. Chem. source
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
InterpretationcitationMicroplastic concentrations are expected to increase in the environment, implying that effects are not unthinkable in the future.
“However, microplastic concentrations are expected to increase in the environment,47 which implies that effects are not unthinkable in the future.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [47] Rochman, 2013, Policy: Classify plastic waste as hazardous, Nature source
May combine two claims.
InterpretationcitationMicroplastic uptake is size-dependent, and particle shape might affect the ability of organisms to excrete them.
“These findings indicate that microplastic uptake is size-dependent and that shape might affect the ability of organisms to excrete them.”
Quote in the paperSubstantial claim
The paper relies on this without support.
No earlier studies systematically assessed microplastic effect thresholds for a range of organisms.
“We are not aware of earlier studies systematically assessing microplastic effect thresholds for a range of organisms.”
The paper relies on this without support.
This is the first study to determine effect thresholds for six freshwater benthic macroinvertebrates across a wide range of microplastic concentrations.
“This is the first study that aims at determining the effect thresholds for a battery of six freshwater benthic macroinvertebrates with different species traits, using a wide range of microplastic concentrations.”
The authors state this as an assumption.
The unknown third dimension of the polystyrene particles is the smallest and can be approximated as half of the second dimension.
“This unknown third dimension was assumed to be the smallest and was thus approximated as half of the second dimension.”
The authors state this as an assumption.
The polystyrene particles prefer a flat position on the filter, so their length and width are directly measurable and larger than their depth.
“First it was assumed that the particles would prefer a flat position on the filter, such that their length and width dimensions directly measurable from the 2D map top view, each are larger than the third (depth) dimension, which is not observable from the 2D maps.”
The authors state this as an assumption.
For larger numbers of irregular particles, the distribution of the third (depth) dimension is symmetrical.
“where the distribution of the third (depth) dimension can be assumed to be symmetrical.”
The authors state this as an assumption.
The weight of faecal pellets represents the feeding rate of worms.
“assuming that the weight of the faecal pellets represents the feeding rate of worms.38”
The paper relies on this without support.
Growth inhibition of G. pulex by chronic PS microplastics exposure from sediment had not been reported before this study.
“Growth inhibition of G. pulex by a chronic PS microplastics exposure from sediment has not been reported before.”
The paper relies on this without support.
The range of PS particle sizes and shapes used is a fair approximation of environmental microplastics for physical effects.
“our wide range of PS particle sizes and shapes can be considered as a fair approximation of environmental microplastics when it concerns their physical effects.”
The paper relies on this without support.
The test conditions are environmentally relevant.
“under the same environmentally relevant conditions”
The paper relies on this without support.
The six species tested represent a range of freshwater species with different traits sufficient to generalise about benthic macroinvertebrates.
“for a range of freshwater species with different traits exposed to PS microplastics in sediment under the same environmentally relevant conditions”
Cites
Microplastics in the marine environment
Andrady, A. L. (2011) · Marine Pollution Bulletin · doi:10.1016/j.marpolbul.2011.05.030 · Cited by 8,105 · see citing works
Draper, N. R., & Smith, H. (1998) · Wiley series in probability and statistics · doi:10.1002/9781118625590 · Cited by 5,086 · see citing works
Horton, A. A., Walton, A., Spurgeon, D. J., Lahive, E., & Svendsen, C. (2017) · Science of The Total Environment · doi:10.1016/j.scitotenv.2017.01.190 · Cited by 3,756 · see citing works
Plastics, the environment and human health: current consensus and future trends
Thompson, R. C., Moore, C. J., Saal, F. S. V., & Swan, S. H. (2009) · Philosophical Transactions of the Royal Society B Biological Sciences · doi:10.1098/rstb.2009.0053 · Cited by 3,068 · see citing works
Eerkes-Medrano, D., Thompson, R. C., & Aldridge, D. C. (2015) · Water Research · doi:10.1016/j.watres.2015.02.012 · Cited by 2,638 · see citing works
Classify plastic waste as hazardous
Rochman, C. M., Browne, M. A., Halpern, B. S., Hentschel, B. T., Hoh, E., Karapanagioti, H. K., Rios-Mendoza, L. M., Takada, H., Teh, S., & Thompson, R. C. (2013) · Nature · doi:10.1038/494169a · Cited by 1,752 · see citing works
Microplastics in freshwater ecosystems: what we know and what we need to know
Wagner, M., Scherer, C., Alvarez-Muñoz, D., Brennholt, N., Bourrain, X., Buchinger, S., Fries, E., Grosbois, C., Klasmeier, J., Marti, T., et al. (2014) · Environmental Sciences Europe · doi:10.1186/s12302-014-0012-7 · Cited by 1,543 · see citing works
Klein, S., Worch, E., & Knepper, T. P. (2015) · Environmental Science & Technology · doi:10.1021/acs.est.5b00492 · Cited by 1,181 · see citing works
Browne, M. A., Niven, S. J., Galloway, T. S., Rowland, S. J., & Thompson, R. C. (2013) · Current Biology · doi:10.1016/j.cub.2013.10.012 · Cited by 1,160 · see citing works
Leslie, H. A., Brandsma, S. H., van Velzen, M. J. M., & Vethaak, A. D. (2017) · Environment International · doi:10.1016/j.envint.2017.01.018 · Cited by 1,149 · see citing works
Microplastic ingestion decreases energy reserves in marine worms
Wright, S. L., Rowe, D., Thompson, R. C., & Galloway, T. S. (2013) · Current Biology · doi:10.1016/j.cub.2013.10.068 · Cited by 1,079 · cited 2× · see citing works
“14 17 − 19 No or limited e ff ects have also been found for other marine invertebrates.”
Besseling, E., Wegner, A., Foekema, E. M., van den Heuvel-Greve, M. J., & Koelmans, A. A. (2013) · Environmental Science & Technology · doi:10.1021/es302763x · Cited by 1,012 · cited 1× · see citing works
“We did not aim to assess chemical e ff ects as this has been dealt with in many earlier studies, for example, refs 18, 19, and 24, and because it has been argued recently that chemical risks of microplastics should be separated from risks associated with physical e ff ects.”
Self-citationNew techniques for the detection of microplastics in sediments and field collected organisms
Claessens, M., Cauwenberghe, L. V., Vandegehuchte, M., & Janssen, C. (2013) · Marine Pollution Bulletin · doi:10.1016/j.marpolbul.2013.03.009 · Cited by 1,009 · see citing works
Fate of nano- and microplastic in freshwater systems: A modeling study
Besseling, E., Quik, J. T. K., Sun, M., & Koelmans, A. A. (2017) · Environmental Pollution · doi:10.1016/j.envpol.2016.10.001 · Cited by 919 · see citing works
Contamination of beach sediments of a subalpine lake with microplastic particles
Imhof, H. K., Ivleva, N. P., Schmid, J., Niessner, R., & Laforsch, C. (2013) · Current Biology · doi:10.1016/j.cub.2013.09.001 · Cited by 699 · see citing works
Responses of <i>Hyalella azteca</i> to acute and chronic microplastic exposures
Au, S. Y., Bruce, T. F., Bridges, W. C., & Klaine, S. J. (2015) · Environmental Toxicology and Chemistry · doi:10.1002/etc.3093 · Cited by 628 · see citing works
Feeding type and development drive the ingestion of microplastics by freshwater invertebrates
Scherer, C., Brennholt, N., Reifferscheid, G., & Wagner, M. (2017) · Scientific Reports · doi:10.1038/s41598-017-17191-7 · Cited by 448 · cited 2× · see citing works
“11,15 Moreover, the high mobility of G. pulex 46 could have increased microplastic uptake in comparison to the other epibenthic species, revealing the importance of species speci fi c traits in the e ff ects of microplastics on benthic invertebrates.”
Ingestion of Microplastic Has Limited Impact on a Marine Larva
Kaposi, K. L., Mos, B., Kelaher, B. P., & Dworjanyn, S. A. (2014) · Environmental Science & Technology · doi:10.1021/es404295e · Cited by 406 · see citing works
Risks of Plastic Debris: Unravelling Fact, Opinion, Perception, and Belief
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. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b02219 · Cited by 381 · see citing works
Self-citationToward a unified approach to dose–response modeling in ecotoxicology
Ritz, C. (2010) · Environmental Toxicology and Chemistry · doi:10.1002/etc.7 · Cited by 329 · see citing works
MACNEIL, C., DICK, J. T. A., & ELWOOD, R. W. (1997) · Biological Reviews of the Cambridge Philosophical Society · doi:10.1017/s0006323196005038 · Cited by 320 · see citing works
Fate of Microplastics in the Marine Isopod <i>Idotea emarginata</i>
Hämer, J., Gutow, L., Köhler, A., & Saborowski, R. (2014) · Environmental Science & Technology · doi:10.1021/es501385y · Cited by 286 · see citing works
Ingestion of Microplastics by Freshwater Tubifex Worms
Hurley, R. R., Woodward, J. C., & Rothwell, J. J. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b03567 · Cited by 286 · see citing works
Maltby, L., Clayton, S. A., Wood, R. M., & McLoughlin, N. (2002) · Environmental Toxicology and Chemistry · doi:10.1002/etc.5620210219 · Cited by 278 · see citing works
Weber, A., Scherer, C., Brennholt, N., Reifferscheid, G., & Wagner, M. (2018) · Environmental Pollution · doi:10.1016/j.envpol.2017.11.014 · Cited by 233 · cited 3× · see citing works
“11,14 Furthermore, no mortality was reported for the marine isopod Idotea emarginata exposed to PE, PS, and PA (polyamide) microplastics and the marine lugworm A. marina exposed to PE microplastics.”
Negative effects of microplastic exposure on growth and development of Crepidula onyx
Lo, H. K. A., & Chan, K. Y. K. (2018) · Environmental Pollution · doi:10.1016/j.envpol.2017.10.095 · Cited by 216 · cited 1× · see citing works
“20,21 This suggests that benthic macroinvertebrates are a ff ected by the presence of microplastics but also that the susceptibility could be species speci fi c. Current studies have mainly focused on the ingestion of microplastics; 3 however, the quality, reliability, and usability of the few…”
Straub, S., Hirsch, P. E., & Burkhardt-Holm, P. (2017) · International Journal of Environmental Research and Public Health · doi:10.3390/ijerph14070774 · Cited by 209 · see citing works
Modeling the Fate and Transport of Plastic Debris in Freshwaters: Review and Guidance
Kooi, M., Besseling, E., Kroeze, C., van Wezel, A. P., & Koelmans, A. A. (2017) · The handbook of environmental chemistry · doi:10.1007/978-3-319-61615-5_7 · Cited by 179 · see citing works
Self-citationThe functional role of Gammarus (Crustacea, Amphipoda): shredders, predators, or both?
Kelly, D. W., Dick, J. T. A., & Montgomery, W. I. (2002) · Hydrobiologia · doi:10.1023/a:1021370405349 · Cited by 176 · see citing works
Advancing the quality of environmental microplastic research
Connors, K. A., Dyer, S. D., & Belanger, S. E. (2017) · Environmental Toxicology and Chemistry · doi:10.1002/etc.3829 · Cited by 172 · see citing works
Besseling, E., Foekema, E. M., van den Heuvel-Greve, M. J., & Koelmans, A. A. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b02286 · Cited by 153 · see citing works
Self-citationGaps in aquatic toxicological studies of microplastics
Karami, A. (2017) · Chemosphere · doi:10.1016/j.chemosphere.2017.06.048 · Cited by 118 · see citing works
Maltby, L. (1995) · Water Research · doi:10.1016/0043-1354(94)00231-u · Cited by 115 · see citing works
Influence of pH on the toxicity of ammonia to Chironomus tentans and Lumbriculus variegatus
Schubauer-Berigan, M. K., Monson, P. D., West, C. W., & Ankley, G. T. (1995) · Environmental Toxicology and Chemistry · doi:10.1897/1552-8618(1995)14[713:iopott]2.0.co;2 · Cited by 93 · see citing works
Kupryianchyk, D., Reichman, E. P., Rakowska, M. I., Peeters, E. T. H. M., Grotenhuis, J. T. C., & Koelmans, A. A. (2011) · Environmental Science & Technology · doi:10.1021/es2014538 · Cited by 88 · see citing works
Self-citationModeling dose response using generalized linear models
Kerr, D. R., & Meador, J. P. (1996) · Environmental Toxicology and Chemistry · doi:10.1002/etc.5620150325 · Cited by 85 · see citing works
Influence of pH and hardness on toxicity of ammonia to the amphipod <i>Hyalella azteca</i>
Ankley, G. T., Schubauer-Berigan, M. K., & Monson, P. D. (1995) · Canadian Journal of Fisheries and Aquatic Sciences · doi:10.1139/f95-801 · Cited by 80 · see citing works
Rasmussen, J. B. (1984) · Canadian Journal of Zoology · doi:10.1139/z84-145 · Cited by 77 · see citing works
Leppänen, M. T., & Kukkonen, J. V. K. (1998) · Hydrobiologia · doi:10.1023/a:1003252520704 · Cited by 75 · see citing works
Growth of shredders on leaf litter biofilms: the effect of light intensity
Franken, R. J. M., WALUTO, B., Peeters, E. T. H. M., et al. (2005) · Freshwater Biology · doi:10.1111/j.1365-2427.2005.01333.x · Cited by 73 · see citing works
Self-citationSelective feeding by the aquatic oligochaete Tubifex tubifex (Tubificidae, Clitellata)
Rodriguez, P., Martinez-Madrid, M., Arrate, J. A., & Navarro, E. (2001) · Hydrobiologia · doi:10.1023/a:1013199507341 · Cited by 67 · see citing works
Vadher, A. N., Stubbington, R., & Wood, P. J. (2015) · Hydrobiologia · doi:10.1007/s10750-015-2193-5 · Cited by 63 · see citing works
OECD. (2007) · doi:10.1787/9789264067356-en · Cited by 57 · see citing works
Diepens, N. J., Koelmans, A. A., Baveco, H., van den Brink, P. J., van den Heuvel-Greve, M. J., & Brock, T. C. M. (2016) · Reviews of Environmental Contamination and Toxicology · doi:10.1007/398_2015_5004 · Cited by 44 · see citing works
Self-citationReviews of Environmental Contamination and Toxicology
(1999) · Reviews of Environmental Contamination and Toxicology · doi:10.1007/978-1-4612-1528-8 · Cited by 40 · see citing works
Trait-based modelling of bioaccumulation by freshwater benthic invertebrates
Sidney, L. A., Diepens, N. J., Guo, X., & Koelmans, A. A. (2016) · Aquatic Toxicology · doi:10.1016/j.aquatox.2016.04.017 · Cited by 38 · see citing works
Self-citationWilhelm, F. M., & Lasenby, D. C. (1998) · Crustaceana · doi:10.1163/156854098x00518 · Cited by 28 · see citing works
Tubifex tubifex chronic toxicity test using artificial sediment: methodological issues
Arrate, J. (2004) · Limnetica · doi:10.23818/limn.23.03 · Cited by 19 · see citing works
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- Mintenig, S.; Bauerlein, P.; Koelmans, A. A.; Dekker, S.; van Wezel, A. Closing the Gap between Small and Smaller: Towards an Analytical Protocol for the Detection of Micro- And Nanoplastic in Freshwater Systems., MICRO 2016 Conference; Lanzarote, Spain, May 25–27, 2016.
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Microplastics in Freshwaters and Drinking Water: Critical Review and Assessment of Data Quality
Koelmans, A. A., Mohamed Nor, N. H., Hermsen, E., Kooi, M., Mintenig, S. M., & De France, J. (2019) · Water Research · doi:10.1016/j.watres.2019.02.054 · Cited by 2,535 · see citing works
Self-citationde Sá, L. C., Oliveira, M., Ribeiro, F., Rocha, T. L., & Futter, M. N. (2018) · Science of The Total Environment · doi:10.1016/j.scitotenv.2018.07.207 · Cited by 1,316 · see citing works
Risk assessment of microplastic particles
Koelmans, A., Redondo-Hasselerharm, P., Nor, N. H. M., de Ruijter, V. D., Mintenig, S., & Kooi, M. (2022) · Nature Reviews Materials · doi:10.1038/s41578-021-00411-y · Cited by 964 · see citing works
Self-citationEnvironmental source, fate, and toxicity of microplastics
Wang, C., Zhao, J. L., & Xing, B. (2020) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2020.124357 · Cited by 1,093 · see citing works
The world of plastic waste: A review
Nayanathara Thathsarani Pilapitiya, P. G. C., & Ratnayake, A. S. (2024) · Cleaner Materials · doi:10.1016/j.clema.2024.100220 · Cited by 1,034 · see citing works
Effect of microplastics in water and aquatic systems
Issac, M. N., & Kandasubramanian, B. (2021) · Environmental Science and Pollution Research · doi:10.1007/s11356-021-13184-2 · Cited by 843 · see citing works
Akdoğan, Z., & Güven, B. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113011 · Cited by 829 · see citing works
Phytoplankton response to polystyrene microplastics: Perspective from an entire growth period
Mao, Y., Ai, H., Chen, Y., Zhang, Z., Zeng, P., Kang, L., Li, W., Gu, W., He, Q., & Li, H. (2018) · Chemosphere · doi:10.1016/j.chemosphere.2018.05.170 · Cited by 713 · see citing works
Henry, B. K., Laitala, K., & Klepp, I. G. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.10.166 · Cited by 674 · see citing works
Bucci, K., Tulio, M., & Rochman, C. M. (2020) · Ecological Applications · doi:10.1002/eap.2044 · Cited by 658 · see citing works
Simplifying Microplastic via Continuous Probability Distributions for Size, Shape, and Density
Kooi, M., & Koelmans, A. A. (2019) · Environmental Science & Technology Letters · doi:10.1021/acs.estlett.9b00379 · Cited by 639 · see citing works
Self-citationQuality Criteria for the Analysis of Microplastic in Biota Samples: A Critical Review
Hermsen, E., Mintenig, S., Besseling, E., & Koelmans, A. (2018) · Environmental Science and Technology · doi:10.1021/acs.est.8b01611 · Cited by 520 · see citing works
Self-citationQuantifying ecological risks of aquatic micro- and nanoplastic
Besseling, E., Redondo-Hasselerharm, P., Foekema, E. M., & Koelmans, A. A. (2019) · Critical Reviews in Environmental Science and Technology · doi:10.1080/10643389.2018.1531688 · Cited by 564 · see citing works
Self-citationMicroplastics from mulching film is a distinct habitat for bacteria in farmland soil
Zhang, M., Zhao, Y., Qin, X., Jia, W., Chai, L., Huang, M., & Huang, Y. (2019) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2019.06.108 · Cited by 563 · see citing works
Veerasingam, S., Ranjani, M., Venkatachalapathy, R., Bagaev, A., Mukhanov, V., Litvinyuk, D. A., Mugilarasan, M., Gurumoorthi, K., Guganathan, L., Aboobacker, V. M., et al. (2020) · Critical Reviews in Environmental Science and Technology · doi:10.1080/10643389.2020.1807450 · Cited by 579 · see citing works
Micro- and nanoplastic toxicity on aquatic life: Determining factors
Kögel, T., Bjorøy, Ø., Toto, B., Bienfait, A. M., & Sanden, M. (2020) · Science of The Total Environment · doi:10.1016/j.scitotenv.2019.136050 · Cited by 518 · see citing works
van Emmerik, T. H. M., & Schwarz, A. (2019) · Wiley Interdisciplinary Reviews Water · doi:10.1002/wat2.1398 · Cited by 548 · see citing works
“…(Biginagwa et al., 2016, de Souza Petersen, Krüger, Dezevieski, Petry, & Montone, 2016, Horton et al., 2018), invertebrates (Hurley, Woodward, & Rothwell, 2017; Redondo-Hasselerharm, Falahudin, Peeters, & Koelmans, 2018; Windsor, Tilley, et al., 2019), and vertebrates (Reynolds & Ryan, 2018).”
Microplastic ingestion by riverine macroinvertebrates
Windsor, F. M., Tilley, R. M., Tyler, C. R., & Ormerod, S. J. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.07.271 · Cited by 477 · see citing works
Bellasi, A., Binda, G., Pozzi, A., Galafassi, S., Volta, P., & Bettinetti, R. (2020) · Environments · doi:10.3390/environments7040030 · Cited by 449 · see citing works
“The presence of MPs in the digestive tract gives a sense of satiety, causing a reduced uptake of food and decreased energy intake, causing starvation [141,142].”
BackgroundSelvam, S., Kamaraj, J., Senapathi, V., Roy, P. D., & Kumari, V. (2020) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2020.123786 · Cited by 442 · see citing works
A catchment‐scale perspective of plastic pollution
Windsor, F. M., Durance, I., Horton, A. A., Thompson, R. C., Tyler, C. R., & Ormerod, S. J. (2019) · Global Change Biology · doi:10.1111/gcb.14572 · Cited by 420 · see citing works
Zhang, S., Wang, J., Liu, X., Qu, F., Wang, X., Wang, X., Li, Y., & Sun, Y. (2018) · TrAC Trends in Analytical Chemistry · doi:10.1016/j.trac.2018.12.002 · Cited by 416 · see citing works
de Ruijter, V. N., Redondo‐Hasselerharm, P. E., Gouin, T., & Koelmans, A. A. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c03057 · Cited by 379 · see citing works
“6, 11, and 14).21,84,85 The studies by Redondo-Hasselerharm et al. (2018), Qiao et al. (2019), and Von Moos et al. (2012) are assigned a score of 31, 16, and 16 in the QA/QC assessment, respectively.”
BackgroundSelf-citationMicroplastic exposure and effects in aquatic organisms: A physiological perspective
Franzellitti, S., Canesi, L., Auguste, M., Wathsala, R. H. G. R., & Fabbri, E. (2019) · Environmental Toxicology and Pharmacology · doi:10.1016/j.etap.2019.03.009 · Cited by 366 · see citing works
Mintenig, S. M., Bäuerlein, P. S., Koelmans, A. A., Dekker, S. C., & van Wezel, A. P. (2018) · Environmental Science Nano · doi:10.1039/c8en00186c · Cited by 338 · see citing works
Self-citationImpacts of plastic products used in daily life on the environment and human health: What is known?
Rodrigues, M., Abrantes, N., Gonçalves, F. J. M., Nogueira, H. I. S., Marques, J. C., & Gonçalves, A. M. M. (2019) · Environmental Toxicology and Pharmacology · doi:10.1016/j.etap.2019.103239 · Cited by 335 · see citing works
Effects of nanoplastics and microplastics on the growth of sediment-rooted macrophytes
van Weert, S., Redondo‐Hasselerharm, P. E., Diepens, N. J., & Koelmans, A. A. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.11.183 · Cited by 310 · see citing works
Self-citationMateos-Cárdenas, A., Scott, D. T., Seitmaganbetova, G., van Pelt Frank, N. A. M., O’Halloran, J., & Jansen, M. A. K. (2019) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2019.06.359 · Cited by 307 · see citing works
Gong, J. Q., & Xie, P. (2020) · Chemosphere · doi:10.1016/j.chemosphere.2020.126790 · Cited by 311 · see citing works
Guo, X., Hu, G.-L., Fan, X., & Jia, H. (2019) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2019.110118 · Cited by 213 · see citing works
Haegerbaeumer, A., Mueller, M.-T., Fueser, H., & Traunspurger, W. (2019) · Frontiers in Environmental Science · doi:10.3389/fenvs.2019.00017 · Cited by 252 · see citing works
Cytogenotoxic potential of a hazardous material, polystyrene microparticles on Allium cepa L.
Maity, S., Chatterjee, A., Guchhait, R., De, S., & Pramanick, K. (2019) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2019.121560 · Cited by 255 · see citing works
Advances and challenges of microplastic pollution in freshwater ecosystems: A UK perspective
Meng, Y., Kelly, F. J., & Wright, S. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113445 · Cited by 254 · see citing works
Lahive, E., Walton, A., Horton, A. A., Spurgeon, D. J., & Svendsen, C. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113174 · Cited by 245 · see citing works
A close relationship between microplastic contamination and coastal area use pattern
Jang, M., Shim, W. J., Cho, Y., Han, G. M., Song, Y. K., & Hong, S. H. (2019) · Water Research · doi:10.1016/j.watres.2019.115400 · Cited by 249 · see citing works
Sendra, M., Sparaventi, E., Novoa, B., & Figueras, A. J. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.142024 · Cited by 225 · see citing works
Mintenig, S. M., Kooi, M., Erich, M. W., Primpke, S., Redondo‐Hasselerharm, P. E., Dekker, S. C., Koelmans, A. A., & van Wezel, A. P. (2020) · Water Research · doi:10.1016/j.watres.2020.115723 · Cited by 225 · see citing works
Self-citationLusher, A., Munno, K., Hermabessiere, L., & Carr, S. A. (2020) · Applied Spectroscopy · doi:10.1177/0003702820938993 · Cited by 196 · see citing works
Ding, W., Li, Z., Qi, R., Jones, D. L., Liu, Q., Liu, Q., & Yan, C. (2021) · Science of the Total Environment · doi:10.1016/j.scitotenv.2021.146884 · Cited by 175 · see citing works
Merga, L. B., Redondo-Hasselerharm, P., van den Brink, P. J., & Koelmans, A. (2020) · Science of the Total Environment · doi:10.1016/j.scitotenv.2020.140527 · Cited by 171 · see citing works
Self-citationEcotoxicology of micronized tire rubber: Past, present and future considerations
Halle, L., Palmqvist, A., Kampmann, K., & Khan, F. R. (2019) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2019.135694 · Cited by 201 · see citing works
Wan, H., Wang, J., Sheng, X., Yan, J., Zhang, W., & Xu, Y. C. (2022) · Toxics · doi:10.3390/toxics10020070 · Cited by 201 · see citing works
LeMoine, C. M. R., Kelleher, B. M., Lagarde, R., Northam, C., Elebute, O. O., & Cassone, B. J. (2018) · Environmental Pollution · doi:10.1016/j.envpol.2018.08.084 · Cited by 189 · see citing works
Rapid fragmentation of microplastics by the freshwater amphipod Gammarus duebeni (Lillj.)
Mateos-Cárdenas, A., O’Halloran, J., van Pelt, F. N. A. M., & Jansen, M. A. K. (2020) · Scientific Reports · doi:10.1038/s41598-020-69635-2 · Cited by 187 · see citing works
Silva, C. J. M., Silva, A. L. P., Gravato, C., & Pestana, J. L. T. (2019) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2019.04.017 · Cited by 177 · see citing works
Nano- and microplastics affect the composition of freshwater benthic communities in the long term
Redondo‐Hasselerharm, P. E., Gort, G., Peeters, E. T. H. M., & Koelmans, A. A. (2020) · Science Advances · doi:10.1126/sciadv.aay4054 · Cited by 186 · see citing works
“The ability of freshwater benthic macroinvertebrates to ingest MP depends on species characteristics such as their feeding habit or developmental stage (5, 6), as well as on plastic particle properties and environmental conditions (7).”
BackgroundMethodResultInfluentialSelf-citationCombined effects of nanoplastics and copper on the freshwater alga Raphidocelis subcapitata
Bellingeri, A., Bergami, E., Grassi, G., Faleri, C., Redondo‐Hasselerharm, P. E., Koelmans, A. A., & Corsi, I. (2019) · Aquatic Toxicology · doi:10.1016/j.aquatox.2019.02.022 · Cited by 178 · see citing works
Self-citationRozman, U., & Kalčíková, G. (2021) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2021.127529 · Cited by 144 · see citing works
Microplastics in lakes and rivers: An issue of emerging significance to limnology
D’Avignon, G., Gregory-Eaves, I., & Ricciardi, A. (2022) · Environmental Reviews · doi:10.1139/er-2021-0048 · Cited by 169 · see citing works
Wang, Q., Hernández‐Crespo, C., Santoni, M., Hulle, S. W. H. V., & Rousseau, D. P. L. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.137785 · Cited by 172 · see citing works
Kukkola, A. T., Krause, S., Lynch, I., Smith, G. H. S., & Nel, H. (2021) · Environment International · doi:10.1016/j.envint.2021.106504 · Cited by 165 · see citing works
Thornton Hampton, L. M., Brander, S. M., Coffin, S., Cole, M., Hermabessiere, L., Koelmans, A. A., & Rochman, C. M. (2022) · Microplastics and Nanoplastics · doi:10.1186/s43591-022-00040-4 · Cited by 166 · see citing works
“However, most toxicological studies only report the presence or absence of microplastics in the gut, though total plastic volume in the gut of field-collected benthic invertebrates was just recently reported [79, 80].”
BackgroundSelf-citationCastro-Castellon, A. T., Horton, A. A., Hughes, J. M. R., Rampley, C., Jeffers, E. S., Bussi, G., & Whitehead, P. (2022) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.151638 · Cited by 164 · see citing works
Ingestion and Chronic Effects of Car Tire Tread Particles on Freshwater Benthic Macroinvertebrates
Redondo‐Hasselerharm, P. E., de Ruijter, V. N., Mintenig, S. M., Verschoor, A. J., & Koelmans, A. A. (2018) · Environmental Science & Technology · doi:10.1021/acs.est.8b05035 · Cited by 158 · see citing works
“…(Anodisc, Whatman, UK) with a pore size of 0.2 μ m, which were dried in an oven at 45 ° C for at least 48 h. Note that FTIR or Raman microscopy used to identify microplastics in biota, such as in Redondo-Hasselerharm et al., 2018, are not applicable to black particles due to high IR absorption.”
InfluentialSelf-citationHuang, Y., Li, W., Gao, J., Wang, F., Yang, W., Han, L., Lin, D., Min, B., Zhi, Y., Grieger, K., et al. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.142133 · Cited by 148 · see citing works
Food web transfer of plastics to an apex riverine predator
D’Souza, J. M., Windsor, F. M., Santillo, D. J., & Ormerod, S. J. (2020) · Global Change Biology · doi:10.1111/gcb.15139 · Cited by 149 · see citing works
Ecological risks in a ‘plastic’ world: A threat to biological diversity?
Agathokleous, E., Iavicoli, I., Barceló, ., & Calabrese, E. J. (2021) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2021.126035 · Cited by 144 · see citing works
Risk-based management framework for microplastics in aquatic ecosystems
Mehinto, A. C., Coffin, S., Koelmans, A. A., Brander, S. M., Wagner, M., Hampton, L. M. T., Burton, G. A., Miller, E. L., Gouin, T., Weisberg, S. B., et al. (2022) · Microplastics and Nanoplastics · doi:10.1186/s43591-022-00033-3 · Cited by 145 · see citing works
“Exposure to MPs has been associated with various types of biological responses, including disruption of feeding [61], decreases in growth [48], tissue inflammation [43], changes in gene expression [42, 66], and decreases in reproductive success [55].”
Self-citationLong-term exposure to nanoplastics reduces life-time in Daphnia magna
Kelpsiene, E., Torstensson, O., Ekvall, M. T., Hansson, L., & Cedervall, T. (2020) · Scientific Reports · doi:10.1038/s41598-020-63028-1 · Cited by 137 · see citing works
O’Connor, J., Mahon, A. M., Ramsperger, A. F. R. M., Trotter, B., Redondo‐Hasselerharm, P. E., Koelmans, A. A., Lally, H., & Murphy, S. (2019) · Global Challenges · doi:10.1002/gch2.201800118 · Cited by 137 · see citing works
Self-citationOni, B. A., Ayeni, A. O., Agboola, O., Oguntade, T. I., & Obanla, O. R. (2020) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2020.110656 · Cited by 132 · see citing works
Zou, W., Xia, M., Jiang, K., Cao, Z., Zhang, X., & Hu, X. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c05399 · Cited by 127 · see citing works
Microplastics and nanoplastics: would they affect global biodiversity change?
Hu, D., Shen, M., Zhang, Y., Li, H., & Zeng, G. (2019) · Environmental Science and Pollution Research · doi:10.1007/s11356-019-05414-5 · Cited by 123 · see citing works
Sathish, T., Sabarirajan, N., Ravichandran, S., et al. (2022) · Chemosphere · doi:10.1016/j.chemosphere.2022.134997 · Cited by 118 · see citing works
A systems analysis of microplastic pollution in Laizhou Bay, China
Teng, J., Zhao, J., Zhang, C., Cheng, B., Koelmans, A. A., Wu, D., Gao, M. C., Sun, X., Liu, Y., & Wang, Q. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.140815 · Cited by 114 · see citing works
Self-citationAl-Jaibachi, R., Cuthbert, R. N., & Callaghan, A. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.09.236 · Cited by 110 · see citing works
“Given the densities of MPs in freshwater ecosystems, it is likely that they will be ingested by aquatic organisms, and, in turn, probable that they will be transferred up through the food chain (Cole et al., 2013; Sussarellu et al., 2016; Scherer et al., 2017; Redondo-Hasselerharm et al. 2018).”
Bertoli, M., Pastorino, P., Lesa, D., Renzi, M., Anselmi, S., Prearo, M., & Pizzul, E. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.150207 · Cited by 108 · see citing works
Wang, S., Wang, Y., Liang, Y., Cao, W., Sun, C., Ju, P., & Zheng, L. (2020) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2020.111000 · Cited by 109 · see citing works
López‐Rojo, N., Pérez, J., Alonso, A., Correa‐Araneda, F., & Boyero, L. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113898 · Cited by 101 · see citing works
Liu, Y., Zhang, J., Tang, Y., He, Y., Li, Y., You, J., Breider, F., Tao, S., & Liu, W. (2020) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2020.124180 · Cited by 105 · see citing works
Environmentally Accurate Microplastic Levels and Their Absence from Exposure Studies
Cunningham, E. M., & Sigwart, J. D. (2019) · Integrative and Comparative Biology · doi:10.1093/icb/icz068 · Cited by 100 · see citing works
Jakubowska, M., Białowąs, M., Stankevičiūtė, M., Chomiczewska, A., Pažusienė, J., Jonko-Sobuś, K., Hallmann, A., & Urban-Malinga, B. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.139922 · Cited by 95 · see citing works
A framework for systematic microplastic ecological risk assessment at a national scale
Qiu, Y., Zhou, S., Zhang, C., Qin, W., & Lv, C. (2023) · Environmental Pollution · doi:10.1016/j.envpol.2023.121631 · Cited by 94 · see citing works
Fate and removal of microplastics in unplanted lab-scale vertical flow constructed wetlands
Wang, Q., Hernández‐Crespo, C., Du, B., et al. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.146152 · Cited by 95 · see citing works
Kaloyianni, M. G., Bobori, D. C., Xanthopoulou, D., Malioufa, G., Sampsonidis, I., Kalogiannis, S., Feidantsis, K. G., Kastrinaki, G., Dimitriadi, A., Koumoundouros, G., et al. (2021) · Toxics · doi:10.3390/toxics9110289 · Cited by 96 · see citing works
Trotter, B., Wilde, M. V., Brehm, J., Dafni, E., Aliu, A., Arnold, G. J., Fröhlich, T., & Laforsch, C. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.148822 · Cited by 92 · see citing works
Yang, H. L., Sun, F., Liao, H., Guo, Y., Pan, T., & Wu, F. (2023) · Water Research · doi:10.1016/j.watres.2023.120322 · Cited by 93 · see citing works
Pereao, O., Opeolu, B. O., & Fatoki, O. S. (2020) · Environmental Science and Pollution Research · doi:10.1007/s11356-020-08688-2 · Cited by 94 · see citing works
Li, R., Zhang, S., Zhang, L., Yu, K., Wang, S., & Wang, Y. (2020) · Environmental Pollution · doi:10.1016/j.envpol.2020.114368 · Cited by 89 · see citing works
Plastic waste in the terrestrial environment
Hurley, R. R., Horton, A. A., Lusher, A., & Nizzetto, L. (2020) · Elsevier eBooks · doi:10.1016/b978-0-12-817880-5.00007-4 · Cited by 115 · see citing works
Silva, C. J. M., Machado, A. L., Campos, D., Rodrigues, A. C. M., Patrício Silva, A. L., Soares, A. M. V. M., & Pestana, J. L. T. (2022) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.150118 · Cited by 89 · see citing works
Geremia, E., Tomajoli, M. T. M., Murano, C., Petito, A., & Fasciolo, G. (2023) · Environments · doi:10.3390/environments10090161 · Cited by 87 · see citing works
Ehlers, S. M., Manz, W., & Koop, J. (2019) · Aquatic Biology · doi:10.3354/ab00711 · Cited by 84 · see citing works
“Furthermore, bagworm moth larvae construct self-enclosing bags using organic and inorganic materials (Rhainds et al. 2009).”
BackgroundNavarro, V. C., Muñiz‐González, A., Sorvari, J., & Martínez‐Guitarte, J. (2021) · Environmental Pollution · doi:10.1016/j.envpol.2021.117462 · Cited by 80 · see citing works
Redondo-Hasselerharm, P., Rico, A., & Koelmans, A. (2022) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2022.129814 · Cited by 73 · see citing works
Self-citationOccurrence, Fate and Fluxes of Plastics and Microplastics in Terrestrial and Freshwater Ecosystems
Schell, T., Rico, A., & Vighi, M. (2020) · Reviews of Environmental Contamination and Toxicology · doi:10.1007/398_2019_40 · Cited by 84 · see citing works
Hengstmann, E., Weil, E., Wallbott, P. C., Tamminga, M., & Fischer, E. K. (2021) · Environmental Research · doi:10.1016/j.envres.2021.111141 · Cited by 81 · see citing works
Abelouah, M. R., Ben-Haddad, M., Hajji, S., De-la-Torre, G. E., Taoufyq, A., Oualid, J. A., Bannı, M., & Alla, A. A. (2022) · Marine Pollution Bulletin · doi:10.1016/j.marpolbul.2022.113969 · Cited by 85 · see citing works
Singh, N., Khandelwal, N., Tiwari, E., et al. (2020) · Water Research · doi:10.1016/j.watres.2020.116622 · Cited by 80 · see citing works
Jiang, P., Yuan, G., Jiang, B., Zhang, J., Wang, Y., Lv, H.-J., Zhang, Z., Wu, J.-L., Wu, Q., & Li, L. (2021) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2021.112345 · Cited by 79 · see citing works
Doyle, D., Sundh, H., & Almroth, B. C. (2022) · Environmental Pollution · doi:10.1016/j.envpol.2022.120434 · Cited by 62 · see citing works
Advances in magnetic materials for microplastic separation and degradation
Cao, Y., Sathish, C., Guan, X., Wang, S., Thavamani, P., Vinu, A., & Yi, J. (2023) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2023.132537 · Cited by 73 · see citing works
Li, B., Song, J., Guan, M., Chen, Z., Tang, B., Long, Y., Mao, R., Zhao, J., Xu, W., & Zhang, Y. (2023) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2023.132784 · Cited by 76 · see citing works
Kong, X., & Koelmans, A. A. (2019) · Environmental Science & Technology · doi:10.1021/acs.est.9b03905 · Cited by 69 · see citing works
Self-citationSilva, C. J. M., Silva, A. L. P., Campos, D., Soares, A. M. V. M., Pestana, J. L. T., & Gravato, C. (2020) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2020.111375 · Cited by 72 · see citing works
Klein, K., Piana, T., Lauschke, T., Schweyen, P., Dierkes, G., Ternes, T., Schulte-Oehlmann, U., & Oehlmann, J. (2020) · Aquatic Toxicology · doi:10.1016/j.aquatox.2020.105723 · Cited by 58 · see citing works
Tan, Y., Dai, J., Wu, X., Wu, S., & Zhang, J. (2022) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2022.130766 · Cited by 70 · see citing works
Ockenden, A., Tremblay, L. A., Dikareva, N., & Simon, K. S. (2021) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.148507 · Cited by 65 · see citing works
Yıldız, D., Yalçın, G., Jovanović, B., Boukal, D. S., Vebrová, L., Riha, D., Stanković, J., Savić‐Zdravković, D., Metin, M., Akyürek, Y. N., et al. (2022) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2022.155407 · Cited by 62 · see citing works
Progress on the Effects of Microplastics on Aquatic Crustaceans: A Review
Zhang, S., Wu, H., & Hou, J. (2023) · International Journal of Molecular Sciences · doi:10.3390/ijms24065523 · Cited by 70 · see citing works
- Authors
- Redondo-Hasselerharm, P. E., Falahudin, D., Peeters, E. T. H. M., & Koelmans, A. A.
- Affiliations
- Wageningen University & Research , , P.O. Box 47 , ,
- Wageningen University & Research (NL)
- Wageningen Marine Research (NL)
- Venue
- Environmental Science & Technology
- Publisher
- American Chemical Society (ACS)
- Published
- 2018-01-16
- Volume
- 52
- Issue
- 4
- Pages
- 2278-2286
- ISSN
- 0013-936X (ISSN-L)
- 1520-5851
- PMC
- PMC5822217
- OpenAlex
- W2783751248
- Cited by
- 355
- References
- 48
- Citations by year
- 2026: 25 · 2025: 42 · 2024: 37 · 2023: 45 · 2022: 64 · 2021: 51 · 2020: 47 · 2019: 29 · 2018: 15
- FWCI
- 12.30
- Type
- journal article
- Language
- en
- Open access
- hybrid
- doi.org
- Locations
- Environmental Science & Technology (publishedVersion, cc-by-nc-nd)
- PubMed (publishedVersion)
- Socio-Environmental Systems Modeling (acceptedVersion, cc-by-nc-nd)
- Europe PMC (PubMed Central) (submittedVersion)
- PubMed Central (submittedVersion)
- Data Archiving and Networked Services (DANS) (submittedVersion, cc-by-nc-nd)
- Funders
- Wageningen University and Research Centre (NA)
- Ministerie van Volksgezondheid, Welzijn en Sport (NA)
- Stichting voor de Technische Wetenschappen (13940)
- Ministerie van Infrastructuur en Milieu (NA)
- KWR Water Cycle Research Institute (NA)
- Nederlandse Voedsel- en Warenautoritet, Ministerie Landbouw, Natuur en Voedselkwaliteit (NA)
- RIWA-Meuse (NA)
- Stichting Toegepast Onderzoek Waterbeheer (NA)
- Waterschappen en Hoogheemraadschappen (NA)
- Topics
- Physical Sciences › Environmental Science › Pollution › Microplastics and Plastic Pollution
- Physical Sciences › Environmental Science › Health, Toxicology and Mutagenesis › Environmental Toxicology and Ecotoxicology
- Physical Sciences › Environmental Science › Pollution › Pharmaceutical and Antibiotic Environmental Impacts
- Keywords
- microplastics, freshwater benthic macroinvertebrates, effect thresholds, polystyrene microplastics, sediment contamination, Gammarus pulex, Hyalella azteca, Asellus aquaticus, Sphaerium corneum, Tubifex, Lumbriculus variegatus, microplastic ingestion, growth inhibition, survival, reproduction, ecotoxicology
- MeSH terms
- Animals, Fresh Water, Plastics, Water Pollutants, Chemical, Amphipoda, Rivers
About these checks
Registry, retraction, Cites and statistics results are computed, not judged, with one exception: a printed reference that no index lists is read once by a model before it counts as a citation error. Claims are extracted by a model and kept only when their quote appears verbatim in the text; each cited source is then checked, with a model’s help, for whether it says what the claim relies on. Those verdicts can be wrong — read the claim’s quote and the cited source before relying on one.
Claims read by deepseek-v4.1-flash under definition version 3 (extract-v3) on 2026-10-09.
Classified by jev-1.13-20260917 (gold-guideline-v0.2) on 2026-10-09.
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