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1.
PLoS One ; 15(11): e0242464, 2020.
Article in English | MEDLINE | ID: mdl-33211752

ABSTRACT

In several marine hosts of microalgae, fluorescent natural products may play an important role. While the ecological function of these compounds is not well understood, an interaction of these molecules with the photosynthesis of the symbionts has been suggested. In this study, the effect of Ageladine A (Ag A), a pH-dependent fluorophore found in sponges of the genus Agelas, on microalgal fluorescence was examined. The spectra showed an accumulation of Ag A within the cells, but with variable impacts on fluorescence. While in two Synechococcus strains, fluorescence of phycoerythrin increased significantly, the fluorescence of other Synechococcus strains was not affected. In four out of the five eukaryote species examined, chlorophyll a (Chl a) fluorescence intensity was modulated. In Tisochrysis lutea, for example, the position of the fluorescence emission maximum of Chl a was shifted. The variety of these effects of Ag A on microalgal fluorescence suggests that fluorophores derived from animals could play a crucial role in shaping the composition of marine host/symbiont systems.


Subject(s)
Agelas/chemistry , Microalgae/drug effects , Pyrroles/pharmacology , Symbiosis , Animals , Chlorophyll A/chemistry , Fluorescence , Micrasterias/drug effects , Micrasterias/metabolism , Microalgae/metabolism , Photosynthesis/drug effects , Photosynthesis/radiation effects , Phycobilisomes/chemistry , Phycobilisomes/drug effects , Phycoerythrin/chemistry , Pigments, Biological/chemistry , Pyrroles/isolation & purification , Species Specificity , Spectrometry, Fluorescence , Synechococcus/drug effects , Synechococcus/metabolism , Ultraviolet Rays
2.
Chemosphere ; 91(4): 448-54, 2013 Apr.
Article in English | MEDLINE | ID: mdl-23266414

ABSTRACT

Aquatic environments like peat bogs are affected by anthropogenic metal input into the environment. These ecosystems are inhabited by unicellular green algae of the class Zygnematophyceae. In this study the desmid Micrasterias denticulata was stressed with 600 nM Cd, 10 µM Cr and 300 nM Cu for 3 weeks. GSH levels were measured with HPLC and did not differ between the different treatments or the control. According to the metallo-thiolomics concept, mass spectrometry was used as a method for unambiguous thiol peptide identification. PC2, PC3 and PC4 were clearly identified in the Cd stressed sample with UPLC-MS by their MS spectrum and molecular masses. PC2 and PC3 were determined to be the main thiol compounds, while PC4 was only abundant in traces in Micrasterias. In addition, the identity of PC2 and PC3 was confirmed by MS/MS. No PCs were detected in the Cu stressed algae sample. However, in the Cr stressed sample traces of PC2 were indicated by a peak in UPLC-MS at the retention time of the PC2 standard, but the intensity was too low to acquire reliable MS and MS/MS spectra. In this study PCs have been detected for the first time in a green alga of the division Streptophyta, a close relative to higher plants.


Subject(s)
Cadmium/toxicity , Micrasterias/drug effects , Phytochelatins/metabolism , Water Pollutants, Chemical/toxicity , Glutathione/metabolism , Micrasterias/physiology
3.
Aquat Toxicol ; 109: 59-69, 2012 Mar.
Article in English | MEDLINE | ID: mdl-22204989

ABSTRACT

Various contaminants like metals and heavy metals are constantly released into the environment by anthropogenic activities. The heavy metal chromium has a wide industrial use and exists in two stable oxidation states: trivalent and hexavalent. Chromium can cause harm to cell metabolism and development, when it is taken up by plants instead of necessary micronutrients such as for example iron. The uptake of Cr VI into plant cells has been reported to be an active process via carriers of essential anions, while the cation Cr III seems to be taken up inactively. Micrasterias denticulata, an unicellular green alga of the family Desmidiaceae is a well-studied cell biological model organism. Cr III and VI had inhibiting effects on its cell development, while cell division rates were only impaired by Cr VI. Transmission electron microscopy (TEM) revealed ultrastructural changes such as increased vacuolization, condensed cytoplasm and dark precipitations in the cell wall after 3 weeks of Cr VI treatment. Electron energy loss spectroscopy (EELS) and electron spectroscopic imaging (ESI) were applied to measure intracellular chromium distribution. Chromium was only detected after 3 weeks of 10 µM Cr VI treatment in electron dense precipitations found in bag-like structures along the inner side of the cell walls together with iron and elevated levels of oxygen, pointing toward an accumulation respectively extrusion of chromium in form of an iron-oxygen compound. Atomic emission spectroscopy (EMS) revealed that Micrasterias cells are able to accumulate considerable amounts of chromium and iron. During chromium treatment the Cr:Fe ratio shifted in favor of chromium, which implied that chromium may be taken up instead of iron. Significant and rapid increase of ROS production within the first 5 min of treatment confirms an active Cr VI uptake. SOD and CAT activity after Cr VI treatment did not show a response, while the glutathione pool determined by immuno-TEM decreased significantly in chromium treated cells, showing that glutathione is playing a major role in intracellular ROS and chromium detoxification.


Subject(s)
Chromium/metabolism , Chromium/toxicity , Micrasterias/drug effects , Micrasterias/metabolism , Water Pollutants, Chemical/metabolism , Water Pollutants, Chemical/toxicity , Cell Differentiation/drug effects , Cell Proliferation/drug effects , Cell Survival/drug effects , Intracellular Space/metabolism , Micrasterias/enzymology , Microscopy, Electron, Transmission , Microscopy, Energy-Filtering Transmission Electron , Oxidoreductases/metabolism , Photosynthesis/drug effects , Reactive Oxygen Species/analysis , Spectroscopy, Electron Energy-Loss
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