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Organisationseinheit der BAM
UV-induced transformation of dissolved
organic matter (DOC) is often accompanied by reduction
of molecular weight and aromaticity and an increase of
low-molecular weight (LMW) matter that can be utilized as
a substrate by heterotrophic bacteria. Moreover, the generation
of reactive transients and mineralization of DOC
occurs. For a better understanding of the modification that
starts after irradiation and to distinguish between possible
chemical and biological modifications, we selected different
natural organic matter (NOM) from Norway and
Germany. The aqueous solutions were treated by UV
irradiation and divided into two aliquot samples. NaN3
anti-bacterial treatment was applied to one sample, and
high-pressure size-exclusion chromatography (HPSEC)
analysis was used for both. In all samples, we found typical
modifications of NOM after UV irradiation. Incubation
(>7 days) of UV-irradiated NOM samples resulted in
lower levels of LMW matter and increased aromaticity.
Parallel to these changes of carbon fractions, an increase in
bacterial cell numbers was observed. Addition of NaN3 to
NOM, however, inhibited the reduction of LMW matter,
indicating that microbial activity accounted for the
observed changes in NOM. Analysis of the bacterial
community composition by denaturing gradient gel electrophoresis
(DGGE) of the amplified 16S rRNA genes
revealed that bacterial communities of non-irradiated and
UV-irradiated NOM were different and that UV selected
for specific members of α-proteobacteria, β-proteobacteria,
and Bacteriodetes. Our results imply that after UV-irradiation
of NOM, specific bacterial members are well adapted
to low pH, high LMW DOC concentrations, and oxidative
stress, and therefore thrive well on UV-irradiated humic
matter.
Despite the increasing concern about the harmful effects of micro- and
nanoplastics (MNPs), there are no harmonized guidelines or protocols yet available for MNP ecotoxicity testing. Current ecotoxicity studies often use commercial spherical particles as models for MNPs, but in nature, MNPs occur in variable shapes, sizes and chemical compositions. Moreover, protocols developed for chemicals that dissolve or form stable dispersions are currently used for assessing the ecotoxicity of MNPs. Plastic particles, however, do not dissolve and also show dynamic behavior in the exposure medium, depending on, for example, MNP physicochemical properties and the medium’s conditions such as pH and ionic strength. Here we describe an exposure protocol that considers the particle-specific properties of MNPs and their dynamic behavior in exposure systems. Procedure 1 describes the top-down production of more realistic MNPs as representative of MNPs in nature and particle characterization (e.g., using thermal extraction desorption-gas chromatography/mass spectrometry). Then, we describe exposure system development for short- and long-term toxicity tests for soil (Procedure 2) and aquatic (Procedure 3) organisms. Procedures 2 and 3 explain how to modify existing ecotoxicity guidelines for chemicals to target testing MNPs in selected exposure systems. We show some examples that were used to develop the protocol to test, for example, MNP toxicity in marine rotifers, freshwater mussels, daphnids and earthworms. The present protocol takes between 24 h and 2 months, depending on the test of interest and can be applied by students, academics, environmental risk assessors and industries.