Development of a xylitol biosensor composed of xylitol dehydrogenase and diaphorase

2000 ◽  
Vol 46 (4) ◽  
pp. 350-357 ◽  
Author(s):  
Kazuhiro Takamizawa ◽  
Shoji Uchida ◽  
Masahiro Hatsu ◽  
Tohru Suzuki ◽  
Keiichi Kawai

In preparation for the development of a xylitol biosensor, the xylitol dehydrogenase of Candida tropicalis IFO 0618 was partially purified and characterized. The optimal pH and temperature of the xylitol dehydrogenase were pH 8.0 and 50°C, respectively. Of the various alcohols tested, xylitol was the most rapidly oxidized, with sorbitol and ribitol being reduced at 65% and 58% of the xylitol rate. The enzyme was completely inactive on arabitol, xylose, glucose, glycerol, and ethanol. The enzyme's xylitol oxidation favored the use of NAD+ (7.9 U/mg) over NADP+ (0.2 U/mg) as electron acceptor, while the reverse reaction, D-xylulose reduction, favored NADPH (7.7 U/mg) over NADH (0.2 U/mg) as electron donor. The Km values for xylitol and NAD+ were 49.8 mM and 38.2 µM, respectively. For the generation of the xylitol biosensor, the above xylitol dehydrogenase and a diaphorase were immobilized on bromocyan-activated sephallose. The gel was then attached on a dissolved oxygen electrode. In the presence of vitamin K3, NAD+ and phosphate buffer, the biosensor recorded a linear response to xylitol concentration up to 3 mM. The reaction was stable after 15 min. When the biosensor was applied to a flow injection system, optimal operation pH and temperature were 8.0 and 30°C, respectively. The strengths and limitations of the xylitol biosensor are its high affinity for NAD+, slow reaction time, narrow linear range of detection, and moderate affinity for xylitol.Key words: xylitol, xylitol dehydrogenase, biosensor, Candida tropicalis.

1995 ◽  
Vol 41 (4-5) ◽  
pp. 366-371 ◽  
Author(s):  
Izumi Kubo ◽  
Isao Karube ◽  
Toshifumi Takeuchi ◽  
Masako Furusawa ◽  
Yoshiko Arikawa ◽  
...  

A biosensor based on Thiobacillus thioparus was developed for the determination of thiosulfate and methanethiol. Thiobacillus thioparus is a chemoautotrophic bacterium and it oxidizes sulfur compounds to sulfuric acid. The sensor consisted of an oxygen electrode and immobilized T. thioparus. When the sensor was used to determine thiosulfate, a linear relation between sensor output and concentration was obtained for the concentration range from 1 to 100 μM in a batch system and from 1 to 10 mM in a flow injection system. Output of the sensor was stable for more than 1 month. For methanethiol, the response of the sensor was measured for the concentration range from 0.2 to 3 mM in a flow injection system.Key words: microbial sensor, thiosulfate, methanethiol, Thiobacillus thioparus TK-m.


2018 ◽  
Vol 84 (9) ◽  
pp. 28-33
Author(s):  
S. D. Tataeva ◽  
A. Sh. Ramazanov ◽  
K. E. Magomedov ◽  
R. Z. Zeynalov

The possibility of using diantipyrylpropylmethane (DAPPM) as an electrode-active membrane component of the mercury-selective electrode (Hg-SE) is shown. To clarify the mechanism of membrane functioning we studied the equilibrium in the “membrane-solution” system as a function of the medium acidity and amount of the ionophore. The potentiometric selectivity coefficients of Hg-SE are determined with respect to some anions and cations by the method of bionic potentials. DAPPM at pH 0 - 1.5 is in the cation form, and mercury ions in 0.1 M HCl — in the form of a trichloromercurium ion. The ion associate DAPPM + [HgCl3]-formed under these conditions is the most stable at pH 1 and pCl 1, and the membrane responds only to trichloromercurate ions.. A mercury-selective electrode with an optimized membrane composition (in wt. %) contains: PVC — 32.32; o-NPOE — 64.63; DAPPM — 3.05 (DAPPM concentration 100 mM). The electrochemical characteristics are determined: the linear range (1 x 10-4- 1 x 10-2M) and slope of the electrode function (50 mV/dec). The operating range (pH 0 - 1.5), detection limit (6.3 x 10-5M), and the response time (15 - 20 sec) are determined. For optimal operation of the flow-injection system, a selection of the carrier stream has been made, which affects the stability of the line, the sensitivity and the performance of the analysis. The proposed electrode is used as a detector in the flow-injection determination of mercury in sewage water and “Achromin” cream. Optimum operation conditions of the flow-injection system which ensure the stability of the baseline, as well as the maximum sensitivity and performance of the analysis, are found. The correctness of the results of the determination of mercury is confirmed in spike tests.


2021 ◽  
Vol 327 ◽  
pp. 128905
Author(s):  
Ming Zhou ◽  
Tianling Li ◽  
Meng Zu ◽  
Shanqing Zhang ◽  
Yang Liu ◽  
...  

2013 ◽  
Vol 15 (4) ◽  
pp. 1203-1223 ◽  
Author(s):  
Eyal Price ◽  
Avi Ostfeld

Linear water balance optimal operation models are common with relative short solution times but suffer from a lack of certainty whether the given solution is at all hydraulically feasible. Introducing hydraulic headloss, water leakage and changing pump energy consumption, effect the resulting system optimal operation but also create a non-linear problem due to the convex relation between flow, headloss, water leakage and total head. This study utilizes a methodology published by the authors for linearization of convex or concave equations. An iterative linear programming (LP) minimal cost optimal operation supply model is solved including the Hazen–Williams headloss equation, pressure related water leakage equation, changing pump energy consumption and source cost. The model is demonstrated using an example application. ‘Greater than’ or ‘less than’ water head constraints at nodes may force the system to maintain certain water levels in water tanks reducing the available operating volume forcing pumping stations to operate in peak tariff periods as less storage is available in low tariff periods. Operationally, reducing water leakage may be achieved by reducing water heads along the system by means of shifting pump operation periods and maintaining low water levels in water tanks. Source costs may serve as penalties or rewards discouraging or encouraging the use of certain water sources.


The Analyst ◽  
1990 ◽  
Vol 115 (5) ◽  
pp. 575-579 ◽  
Author(s):  
Maria Rosario Pereiro García ◽  
Marta Elena Díaz García ◽  
Alfredo Sanz-Medel

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