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mightdifferconsiderably indifferent regions.Fibersappeared tobemoreabundant
inmore populated areas.
3.2.2 ParticleSize
Size isanotherparameterusuallymeasuredformicroplastics,butnounifiedcriteria
are currently available. Different size classes were reported by different authors,
whichmake it difficult to compare the data fromdifferentworks [50].Due to the
restriction of the samplingmethods used, usually onlymicroplastics>0.333mm
(mesh size of themanta trawl net) are assessed in neustonic samples collected by
trawling.Smallermicroplasticscanbeexaminedfor sedimentandbiota samplesas
density separation combined with filtration is used.Whereas the examination of
microplastics<0.05mmwill get increasinglydifficult, advanced instruments such
asRamanmicroscopy,micro-Fourier transforminfraredspectroscopy(ΞΌ-FTIR),or
scanning electronmicroscope (SEM)with energy dispersive spectroscopy (EDS)
should be used [36].Generally,microplastic abundance increaseswith decreasing
size[51β53]. InlakeHovsgol,0.355β0.999,1.00β4.749,and>4.75mmsizeclasses
accounted for 41, 40, and 19% of the total plastics, respectively [30]. In the
freshwaters of Wuhan, 0.05β0.5, 0.5β1, and 1β2 mm size classes together
accounted for over 80%of the totalmicroplastics, and0.05β0.5mmmicroplastics
were themost abundant in most of the studied waters [32]. In Yangtze Estuary,
0.5β1,1β2.5,2.5β5,and>5mmsizeclassesmadeup67,28.4,4.4,and0.2%of the
total plastics, respectively [33]. In the estuaryofMinjiang,Oujiang, and Jiaojiang,
thesmallest sizeclass (0.5β1.0mm)wasalso found themostabundant followedby
the 1.0β2.0mmsize class, and these two size classes together accounted for over
70% of the total plastics [34]. However, among the four size classes (0.112β0.3,
0.3β0.5, 0.5β1.6, 1.6β5mm), 0.5β1.6 mmmicroplastics were themost abundant
fromthemajorityof site in theThreeGorgesReservoir,whichmadeup30β57%of
the total microplastics [22]. While for microplastic samples from the lakeshore
sediment of the SilingCobasin, different size distribution patternswere observed
fromdifferentsamplingsites[23].Thepatternsofmicroplasticsizedistributioncan
be related to the sources of microplastics and might also reflect the degree of
weathering.A higher degree ofweatheringmight result in a higher abundance of
smaller particles. Biofouling and hydrodynamic conditions were also believed to
affect the size distributionofmicroplastics [54β56].
3.2.3 Color
In some studies, colors of the microplastics were described. Microplastics can
inherit their colors from their parent plastic products, but their colors can change
due to weathering. Previous research infers that predators may preferably ingest
microplasticswith colors resembling their prey [57β59].Therefore, color informa-
tion of microplastics may be used to indicate their potential to be ingested by
92 C.Wuet 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