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well as particle interactionwithother stressors, and (b)D.magna seems relatively
resistant toMPexposures.
The lowsensitivity ofD.magna couldbedue to its behavioral andmorpholog-
ical adaptations as a generalist filter feeder. D. magna feeds nonselectively on
seston components encountering multiple particle sizes, shapes, and materials.
High concentrationsofSPMreduce thefiltration rates as daphnids reject collected
particles before ingestion or even narrow their carapace opening to avoid large
particles [44, 45]. Besides pre-ingestion adaptations to unsuitable SPM, the
peritrophicmembrane protects the epitheliumof the digestive tract fromparticle-
induced injury. It consists of a complexmatrix of chitinmicrofibrils, polysaccha-
rides,aswellasproteinsandsurrounds thefoodbolus in thedigestive tractofmany
arthropods[46,47].Poresofseveralnanometers indiameterensure the transportof
digestive fluids and nutrients and protect against pathogens andmechanical dam-
age. The packed food particles pass the digestive tract and are egested with the
surrounding peritrophic membrane. Therefore, a direct interaction of MPs with
epithelial cells in thedigestive tract and thus injuries anda transferofMPs into the
surrounding tissue are unlikely.However, Rosenkranz et al. [48] observed 20 and
1,000nmparticles in theoildropletsofD.magna implyinga translocation through
thegut’sepithelialcells,whereas themajorityofstudieswithnanomaterialsdidnot
confirm this observation [49, 50].
3.1.3 OtherCrustaceans
Null effects were found in the amphipodGammarus pulex exposed to irregular
polyethylene terephthalate (PET) fragments (0.4–4,000PmL 1, size 10–150μm;
[31]).After48days,MPsdidnot induceanyeffectsonbehavior (feedingactivity),
metabolism (energy reserves), development (molting), and growth. Au et al. [18]
testedweathered polypropylene (PP) fibers (20–75 μm, 0–90 PmL 1) as well as
laboratory-made PE fragments (10–27 μm, 0–105 P mL 1) in the amphipod
Hyalella azteca. In a 10-day acute exposure, PP fibers weremore toxic than PE
fragmentswithLC50valuesof71.43and46,400PmL 1, respectively.Thismight
be related to the longer gut retention times of fibers versus fragments and again
highlights the importance of particle shape. In the same study, a 42-day chronic
exposure toPE fragments significantly decreased growth and reproduction.
At present, besides the studieswithD.magna and the amphipods, there is very
limited data regarding other freshwater crustaceans as the majority of research
focuses on marine species. In addition to the increasing number of laboratory
studies, the monitoring of wild populations of the common shrimp Crangon
crangon [51] and theNorway lobsterNephrops norvegicus [52] have shown that
fieldpopulations inmarineenvironmentsareexposed toMPs. Inbothstudies,MPs
(predominantly fibers) were detected in 63% [51] and 83% [52] of the examined
animals. A recent study byWelden andCowie [1] withN. norvegicus confirmed
thatMP exposure negatively affects feeding, bodymass, metabolic activity, and
energy reserves.An8-monthexposure toPPfibers via food (0.2–5mm,fivefibers
Interactions ofMicroplasticswithFreshwaterBiota 165
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