scholarly journals Effect of pH on metabolite excretion and cell morphology of Euglena gracilis under dark, anaerobic conditions

2020 ◽  
Vol 51 ◽  
pp. 102084
Author(s):  
Kazumasa Yoshioka ◽  
Kengo Suzuki ◽  
Takashi Osanai
2020 ◽  
Author(s):  
Kazumasa Yoshioka ◽  
Kengo Suzuki ◽  
Takashi Osanai

Abstract Background Euglena gracilis is a unicellular eukaryotic microalgae found in aquatic environments. It can adapt its morphology in response to various environmental stress factors such as changes in temperature, light, and ion concentrations. E. gracilis cells excrete succinate and amino acids under dark and anaerobic conditions; however, only a few studies on the effect of these conditions on the cell morphology of E. gracilis have been conducted thus far. In the present study, we aimed to evaluate the effects of pH on succinate, glutamine and glutamate production in E. gracilis and the correlation between the levels of these metabolites and cell morphology under dark, anaerobic conditions. Results The production of succinate, glutamine and glutamate by E. gracilis was pH dependent. Glutamate and glutamine excretion increased under acidic conditions (pH 3–5), irrespective of the buffer salts. On the contrary, succinate production depended on the buffer salts; succinate levels were higher when GTA or citrate buffer were used and were lower when acetate buffer was used (pH 4 or 5). The number of spindle cells tended to increase under acidic conditions and the aspect ratio of the cells was positively correlated with glutamine and glutamate levels. Increase in cell density particularly enhanced glutamine and succinate production; in particular, the succinate titre reached 1.5 g/L, which is the highest reported level of succinate produced from photosynthetic eukaryotes till date. Conclusions Our findings indicate that pH of the media alters metabolite production and cell morphology of E. gracilis cells under dark, anaerobic conditions. A deeper understanding of eukaryotic fermentation will benefit the biorefinery industry, mainly for the production of value-added products using anaerobic microorganisms.


2016 ◽  
Vol 7 ◽  
Author(s):  
Yuko Tomita ◽  
Kazumasa Yoshioka ◽  
Hiroko Iijima ◽  
Ayaka Nakashima ◽  
Osamu Iwata ◽  
...  

BMC Genomics ◽  
2016 ◽  
Vol 17 (1) ◽  
Author(s):  
Yuta Yoshida ◽  
Takuya Tomiyama ◽  
Takanori Maruta ◽  
Masaru Tomita ◽  
Takahiro Ishikawa ◽  
...  

2019 ◽  
Vol 37 ◽  
pp. 169-177
Author(s):  
Yuko Tomita ◽  
Masahiro Takeya ◽  
Kengo Suzuki ◽  
Nobuko Nitta ◽  
Chieko Higuchi ◽  
...  

2007 ◽  
Vol 74 (3) ◽  
pp. 667-675 ◽  
Author(s):  
George R. Golding ◽  
Richard Sparling ◽  
Carol A. Kelly

ABSTRACT The effects of pH on the uptake and accumulation of Hg(II) by Escherichia coli were determined at trace, environmentally relevant, concentrations of Hg and under anaerobic conditions. Hg(II) accumulation was measured using inducible light production from E. coli HMS174 harboring a mer-lux bioreporter plasmid (pRB28). The effect of pH on the toxicity of higher concentrations of Hg(II) was measured using a constitutive lux plasmid (pRB27) in the same bacterial host. In this study, intracellular accumulation and toxicity of Hg(II) under anaerobic conditions were both significantly enhanced with decreasing pH over the pH range of 8 to 5. The pH effect on Hg(II) accumulation was most pronounced at pHs of <6, which substantially enhanced the Hg(II)-dependent light response. This enhanced response did not appear to be due to pH stress, as similar results were obtained whether cells were grown at the same pH as the assay or at a different pH. The enhanced accumulation of Hg(II) was also not related to differences in the chemical speciation of Hg(II) in the external medium resulting from the changes in pH. Experiments with Cd(II), also detectable by the mer-lux bioreporter system, showed that Cd(II) accumulation responded differently to pH changes than the net accumulation of Hg(II). Potential implications of these findings for our understanding of bacterial accumulation of Hg(II) under anaerobic conditions and for bacteria-mediated cycling of Hg(II) in aquatic ecosystems are discussed. Arguments are provided suggesting that this differential accumulation is due to changes in uptake of mercury.


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