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chemicals from personal care products). Many of these compounds are pseudo-
persistentandbiologicallyhighlyactivebutdonotoccur inmarineecosystems(due
to dilution or degradation). Accordingly, freshwaterMPs will sorb a completely
different set of chemicals thanmarineones. In addition, being closer to the source
of plastic litter and thus “younger,” freshwaterMPsmight contain higher concen-
trations of plastic additives.With regard to desorption, physical water properties
will affect the transfer of pollutants. The adsorption equilibrium of chemicals to
organic materials is highly dependent on water temperature, quantity of organic
matter, and the content of inorganic salts [83].Therefore, thepartition equilibrium
will be different in salt- and freshwater.
Besides thecapacityofMPsto influence thebioavailabilityof toxiccompounds,
Besseling et al. [41] suggested thatMPs can interferewith intra- and interspecies
signaling (e.g., phero- and kairomones) as an integral component of aquatic bio-
coenosisregulatingpredator-preyinteractionsaswellaspopulationandcommunity
structures [84]. Although they found significant interactions between kairomones
andnano-PSwhen investigating thegrowthof thewater fleaD.magna, it remains
unclearwhether the nano-PSbeads increased the bioavailability of kairomones or
theyobservedanadditiveeffectofbothstressors[41].Anydisturbanceofthis inter-
and intraspeciescommunicationcan lead tomaladaptive responses inbothsignaler
and receiver [85]. So far, it is unclearwhetherMPs act as info-disruptors as is the
case for severalmetalsandpesticides (reviewedin[85]), especiallywhenconsider-
ing the abundance of additional particulate organic and inorganic matter in
aquatic ecosystems.
3.3 Biofilm-Related Impacts
Apart from thepotential ofMPs to act as carriers for chemicals,MPs can serve as
substrates for microorganisms. The formation of biofilms [86] can affect the
interaction ofMPswith biota onmultiple levels. For example, the colonization of
MPswithmicrobesandtheadsorptionofbiopolymers increase thenutritionalvalue
and improve the “taste” making themmore attractive for biota. In contrast, the
colonization of MPs with pathogens [87] and toxic algae/bacteria might induce
infections/chemical toxicity or avoidance of “bad tasting” MPs. Additionally,
biofoulingwas shown to affect the fate ofMPsbychanging theparticle properties
(e.g., density). The formation of biofilms increases the density of floating or
buoyantMPs and leads to sedimentation of these low-density particles (reviewed
in [88]). Furthermore, in the environment, MPs are most likely incorporated in
so-calledhetero-aggregates.Theseaggregatesconsistofparticulatematter (MPsas
well as other suspended solids) and microbes (e.g., protozoans, algae) with bio-
polymers acting as binders. A laboratory study by Lagarde et al. [89] confirmed
170 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