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3. Themorphology of polymer particlesmust render the attachment ofmicroor-
ganisms and the formation of a biofilm, while the structure of the polymeric
substrate, e.g., chemical bonds, degree of polymerization, degree of branching,
and parameter, such as hydrophobicity or crystallinity,must not hindermicro-
bial actions.
Since the size of synthetic polymers is generally too large to penetrate the cell
membranesofmicroorganisms, thefirst stepofbioticdegradationis thecleavageof
side chains or the polymer backbone and the formation of smaller polymer units
(monomers, oligomers)byextracellular enzymes [64]. Inmost cases, thisfirst step
of depolymerization involves an enzymatically catalyzed hydrolysis of amides,
esters, or urethane bonds. These smaller molecules can then be absorbed by
microorganisms andmetabolized. Of course, abiotic hydrolysis can also result in
intermediates that are then furthermetabolizedbymicroorganisms [65].
The complete biotic degradations of poly(ε-caprolactam) and water-soluble
polyethylene glycol are well described in literature [66]. However, most of the
plasticsoccurringin theenvironmentarewater insoluble,andmanyof thesynthetic
polymers present in the aquatic environment, such asPE, polypropylene (PP), PS,
and PET, degrade very slowly or not at all. The degradation of these polymers is
usually a combinationof abiotic andbiotic degradationpathways.
Polyolefins, such as PE and PP, represent a class of substances with high
industrial production volumes and are determined frequently in environmental
samples. These polymers are usually not biodegradable, as the alkyl backbone is
not accessible formicroorganismandmustundergoanabiotic transformation.The
alkyl backbone of polyolefins offers a high resistivity against hydrolysis but is
usually susceptible to oxidative degradation. To prevent this, additives are added
during the production process, and the oxidative or photooxidative degradation of
the polymer is delayed until the antioxidants are consumed. After the initial
oxidation of the surface of polyolefins, the degradation could occur in several
weeks but results in the formation of microplastics as possible intermediates
[67]. These smaller and oxidized plastic fragments aremore susceptible tomicro-
bialattack,e.g.,biodegradationofPEisdescribedforpre-oxidizedfragmentsof the
originalmaterial byPseudomonas sp. [68].
4 Conclusion
Theresultsofstudiesworldwidehighlight thegreat importanceofmicroplastics for
freshwater ecosystems, as they are present in high abundance. Microplastics are
emergingcontaminants in theaquaticenvironment,andattentionshouldbefocused
onaharmonizednomenclatureofmicroplasticparticleswithofficialguidelines for
microplastic studies. The definition of microplastics often remains vague, and
different size classes are investigated inmonitoring studies. For a thorough inves-
tigation of microplastic pollution, standardized methods, especially for the
62 S.Klein et al.
Freshwater Microplastics
Emerging Environmental Contaminants?
- Titel
- Freshwater Microplastics
- Untertitel
- Emerging Environmental Contaminants?
- Autoren
- Martin Wagner
- Scott Lambert
- Verlag
- Springer Open
- Datum
- 2018
- Sprache
- englisch
- Lizenz
- CC BY 4.0
- ISBN
- 978-3-319-61615-5
- Abmessungen
- 15.5 x 24.1 cm
- Seiten
- 316
- Kategorien
- Naturwissenschaften Chemie