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. Optical whole-cell biosensor using Chlorella vulgaris designed for monitoring herbicides. Biosensors and Bioelectronics, Elsevier, 2003, 18 (4), pp.547-463. <10.1016/S0956-5663(02)00157-4>. & Bioelectronics, 2003& Bioelectronics, , 18(4), 457-63, doi:10.1016 Biosensors AbstractAn optical biosensor was designed for determination of herbicides as aquatic contaminants. Detection was obtained with immobilised Chlorella vulgaris microalgae entrapped on a quartz microfibre filter and placed in a five-membrane-home-made-flow cell. The algal chlorophyll fluorescence modified by the presence of herbicides was collected at the tip of an optical fibre bundle and sent to a fluorimeter. A continuous culture was set up to produce algal cells in reproducible conditions for measurement optimisation. Effects of flow rate, algal density, temperature, and pH on the biosensor response to atrazine were studied. Reversibility and detection limits were determined for DNOC and atrazine, simazine, isoproturon, diuron. Detection of photosystem II (PSII) herbicides was achieved at sub-ppb concentration level. K Ke ey yw wo or rd ds s: :

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A biosensor is constructed to detect heavy metals from inhibition of alkaline phosphatase (AP) present on the external membrane of Chlorella vulgaris microalgae. The microalgal cells are immobilized on removable membranes placed in front of the tip of an optical fiber bundle inside a homemade microcell. C. vulgaris was cultivated in the laboratory and its alkaline phosphatase activity is strongly inhibited in the presence of heavy metals. This property has been used for the determination of those toxic compounds.

A new biosensor was designed for the assessment of aquatic environment quality. Three microalgae were used as toxicity bioindicators: Chlorella vulgaris, Pseudokirchneriella subcapitata and Chlamydomonas reinhardtii. These microalgae were immobilized in alginate and silica hydrogels in a two step procedure. After studying the growth rate of entrapped cells, chlorophyll fluorescence was measured after exposure to (3-(3,4-dichlorophenyl)-1,1-dimethylurea) (DCMU) and various concentrations of the common herbicide atrazine. Microalgae are very sensitive to herbicides and detection of fluorescence enhancement with very good efficiency was realized. The best detection limit was 0.1 μM, obtained with the strain C. reinhardtii after 40 minutes of exposure.

The successful development and analytical performances of two biosensor configurations based on the entrapment of algal cells of Chlorella vulgaris into either a regular alginate gel or a newly synthesized pyrrole-alginate matrix are reported. These biosensors were compared in terms of their amperometric current measurements to p-nitrophenyl phosphate when used as substrate for the detection of an algal alkaline phosphatase activity. The high stability of the pyrrole-alginate gel when compared to that of the alginate coating is herein demonstrated.

The interaction of glyceraldehyde 3-phosphate dehydrogenase with microtubules has been studied by measurement of the amount of enzyme which co-assembles with in vitro reconstituted microtubules. The binding of glyceraldehyde 3-phosphate dehydrogenase to microtubules is a saturable process; the maximum binding capacity is about 0.1 mole of enzyme bound per mole of assembled tubulin. Half saturation of microtubule binding sites is obtained at a concentration of glyceraldehyde 3-phosphate dehydrogenase of about 0.5 microM. Glyceraldehyde 3-phosphate dehydrogenase (between 0.1 and 2 microM) induces a concentration-dependent increase a) in the turbidity of the microtubule suspension without alteration of the net amount of polymer formed and b) in the amount of microtubule protein polymers after cold microtubule disassembly. There is a linear relationship between the intensity of the glyceraldehyde 3-phosphate dehydrogenase-induced effects and the amount of microtubule-bound enzyme. The specificity of the association of glyceraldehyde 3-phosphate dehydrogenase to microtubules has been documented by copolymerization experiments. Assembly-disassembly cycles of purified microtubules in the presence of a crude liver soluble fraction results in the selective extraction of a protein with an apparent molecular weight of 35,000 identified as the monomer of glyceraldehyde 3-phosphate dehydrogenase by peptide mapping and immunoblotting. In conclusion, microtubules possess a limited number of binding sites for glyceraldehyde 3-phosphate dehydrogenase. The binding of the glycolytic enzyme to microtubules shows a considerable specificity and is associated with alterations of assembly and disassembly characteristics of microtubules.