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in the gills (5 and 20 μm), gut (5 and 20 μm), and liver (5 μm) [38]. Indeed,
histopathological analysis revealed an inflammatory response andaccumulationof
lipids in the liver as well as oxidative stress. However, these findings were only
significant at high concentrations (2mgL 1) of 0.07 and 5μmbeads. In compar-
ison,Karamiet al. [37]observedhistological alterations in thegills (e.g., basal cell
hyperplasia and necrosis in connective tissue) and blood biochemistry parameters
(e.g., plasma cholesterol levels, bloodHDL levels) of theAfrican catfish (Clarias
gariepinus) at lower concentrations ofHDPEfragments (50μgL 1).More severe
changes (epithelial lifting, hyperplasia, extensivecell sloughing)were reported for
higher particle concentration (500 μg L 1). Additionally, concentrations of
500μgL 1significantlyaffected thedegreeof tissuechange in the liverofexposed
individuals. Overall, the authors point toward ethylenemonomers (released from
HDPE) and internal as well as external abrasions (caused by sharp edges of the
fragments) as possiblemechanisms for the changes in biomarker responses.
It is well documented that suspended solids can damage organs in several fish
species andcause adverse effects similar to thoseobserved forMPs.Highconcen-
trations of SPMcan accumulate in the gills, disturb the respiratory function, and
have been found to translocate into epithelial cells, cause lipid peroxidation, and
reduce the tolerance of infection bypathogens [67, 68].Additionally, studieswith
gill epithelial cells (rainbow trout, RTgill-W1) and fluvial fine sediment revealed
translocation of fineminerals (<2 μm, 10–250mgL 1) into the cells as well as
material-related cytotoxicity [69]. Here, quartz and feldspar only caused sporadic
changes inbiomarker response, andexposure tomica (silicateminerals)andkaolin
inducedcytotoxicityaswellas free radicalsandcellmembranedamage.Therefore,
Michel et al. [69]conclude that theuptakeoffineparticlesbygill epithelial cells is
a common natural event in aquatic species with the material, size, shape, and
concentrationdetermining the impacts.
3.2 Chemical Impacts
Sofar,MPsdetectedinfreshwaterenvironmentsrepresentarangeofmaterial types
(e.g., PE,PS,PET,PVC,PA, andPP), originate fromvarious sources andapplica-
tions, and represent a plethora ofmaterial characteristics. In general, plasticmate-
rials are highly functional compounds of synthetic polymers and additives (e.g.,
plasticizers, flame retardants, colorants). Leachates from diverse plastic products
were found to cause chemical toxicity [70, 71] induced bymonomers, residues of
production processes (e.g., catalyzers, stabilizers), and additives. For instance,
some leaching components were classified as endocrine disrupting chemicals
168 C.Scherer et al.
Freshwater Microplastics
Emerging Environmental Contaminants?
- Title
- Freshwater Microplastics
- Subtitle
- Emerging Environmental Contaminants?
- Authors
- Martin Wagner
- Scott Lambert
- Publisher
- Springer Open
- Date
- 2018
- Language
- English
- License
- CC BY 4.0
- ISBN
- 978-3-319-61615-5
- Size
- 15.5 x 24.1 cm
- Pages
- 316
- Categories
- Naturwissenschaften Chemie