PubMed · 13207079
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M B LEVIN. 1954. Benzidine test for blood (Levin-Watt).. https://doi.org/10.1007/bf02883991
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We focused our studies on the fabrication of nano-organized systems incorporating redox mediators for NADH. We fabricated gold-modified electrodes of phospholipid layers containing a redox mediator for NADH by means of the Langmuir-Blodgett (LB) technique. We chose tetramethylbenzidine (TMB) which is known to decrease the very large overvoltage involved in the direct oxidation of NADH. The electrochemical characterisation of the films allowed to determine the presence and the electrochemical activity of the mediator in the LB layers. The response of the sensing layer in solutions containing NADH was investigated by means of cyclic voltammetry and fluorescence spectroscopy. We observed that NADH has a strong affinity with the film, and it interacts with the TMB-containing phospholipid layers. In fact, we found that TMB molecules mediate the NADH oxidation reaction, even if the surrounding matrix relatively hinders their mobility.
OBJECTIVE: To test the possibility that certain efficient substrates for lipoxygenase (LOX) produce shuttle oxidants that stimulate the generation of reactive oxygen species from other chemicals. METHODS: Metabolic interactions were conducted in vitro between chlorpromazine (BZ) or other phenothiazines and benzidine or other xenobiotics mediated by soybean lipoxygenase (SLO) or purified human term placental lipoxygenase (HTPLO) in the presence of hydrogen peroxide, and the rates of xenobiotics oxidation were measured by spectroscopic analysis. RESULTS: Chlorpromazine cation radical (CPZ(*+)) generated by lipoxygenase triggered a rapid oxidation of benzidine to benzidine diimine cation. Under the experimental conditions used, the metabolic interaction resulted in a 42-fold greater stimulation than BZ alone in the rate of BZ oxidation. The magnitude of stimulation of benzidine oxidation exhibited a dependence on the pH of the reaction medium, amount of the enzyme, and concentration of chlorpromazine, BZ, and hydrogen peroxide. A number of other phenothiazines were also found to stimulate BZ oxidation, albeit to a lesser degree. Chlorpromazine cation radical stimulated the oxidation of all six other xenobiotics tested. The highest stimulation (94-fold) was noted in the oxidation of tetramethyl phenylenediamine to Wursters blue radical, while the lowest stimulatory response (2-fold) was observed in guaiacol. Preliminary data showed that purified HTPLO also displayed a similar stimulatory response to benzidine oxidation in the presence of chlorpromazine. CONCLUSION: Both soybean lipoxygenase and purified human term placental lipoxygenase can mediate stimulatory response to the oxidation of benzidine and other xenobiotics in the presence of phenothiazines.
Ralstonia eutropha H850 was labelled chromosomally with a gfp marker gene encoding for the green fluorescent protein, and designated R. eutropha H850g13. Visual observation of green fluorescent cells under an epifluorescence microscope, and PCR amplification products, confirmed that the bacterium was labelled with gfp. Southern blot hybridization products further confirmed the gfp was chromosomally labelled. Using resting cell assays, it was determined that insertion of the gfp gene decreased the microorganisms' ability to degrade biphenyl compared to the parent strain. However, this marker facilitated the identification and monitoring of R. eutropha H850g13 survival in soil microcosm experiments. Survival and polychlorinated biphenyl degradation by R. eutropha H850g13 was analysed in soil microcosms spiked with 2,2',5,5'-tetrachlorobiphenyl (TeCB). R. eutropha H850g13 was detected by viable plate counts and most-probable-number/PCR after 102 days in TeCB-contaminated soil microcosms, and was likely outcompeted by indigenous soil microorganisms in microcosms amended with oil and Daramend (an organic amendment, http://www.adventusremediation.com). R. eutropha H850g13 did not degrade TeCB in any of the soil microcosms. This research confirmed that gfp was useful as a marker to distinguish R. eutropha H850g13 from indigenous soil microorganisms over a 102 day period and that, under the experimental conditions used, R. eutropha H850g13 did not degrade TeCB.