TY - JOUR
T1 - How the sulfur dioxide in the flue gas influence microalgal carbon dioxide fixation
T2 - From gas dissolution to cells growth
AU - Fu, Jingwei
AU - Huang, Yun
AU - Xia, Ao
AU - Zhu, Xianqing
AU - Zhu, Xun
AU - Chang, Jo Shu
AU - Liao, Qiang
N1 - Funding Information:
The authors are grateful for the financial support provided by the Innovative research group project of the National Natural Science Foundation of China (No. 52021004 ), the Natural Science Foundation of China (No. 52076023 ), and the Natural Science Foundation of Chongqing , China (No. cstc2022ycjh-bgzxm0141 , cstc2021jcyj-msxmX0116 ).
Funding Information:
A visualization experimental system was established to investigate the dissolution process of a single stationary bubble containing SO2 (0, 200, and 400 ppm), CO2 (15%, v/v), and N2 in microalgae suspension (Fig. 2). The four subsystems and their functions were as follows: 1) The gas injection system was made up of a syringe pump (LSP04-1A, Longer Precision Pump Co., Ltd.) and a 5 mL syringe. The mixed gas was first injected into the test section slowly through the gas injection system until a bubble with a specific diameter was acquired. 2) The test section included a transparent photobioreactor (50 mm in length, 10 mm in width, and 50 mm in height) that was filled with 20 mL microalgae suspension, a capillary with an internal diameter of 1.3 mm, and a capillary rod with a diameter of 1 mm. When the bubble was formed, quickly pushed up the capillary rod so that bubble was fixed to the tip of the capillary rod, in this case, the bubble was isolated from the gas source. 3) The camera recording system used to observe the dissolution process of the single bubble in microalgae suspension mainly was composed of an industrial CCD camera (GS3-U3-41C6C–C, FLIR Systems, Inc.) with a supporting light source and macro lens. The frame rate of the camera was set at 50 fps. 4) The data acquisition system consisted of a computer and data acquisition card. The final data obtained from experiments were processed and analyzed using I-Speed Suite and MATLAB software. Furthermore, the effect of microalgae suspensions and initial bubble diameters on bubble dissolution was also discussed.The authors are grateful for the financial support provided by the Innovative research group project of the National Natural Science Foundation of China (No. 52021004), the Natural Science Foundation of China (No. 52076023), and the Natural Science Foundation of Chongqing, China (No. cstc2022ycjh-bgzxm0141, cstc2021jcyj-msxmX0116).
Publisher Copyright:
© 2022 Elsevier Ltd
PY - 2022/10
Y1 - 2022/10
N2 - Aiming at realizing efficient microalgae-based CO2 sequestration from coal-fired power plants, this study investigated the interaction between the mass transfer of SO2-contained flue gas and microalgae growth. The results indicate that the CO2 dissolution in microalgae suspension and the growth of Chlorella vulgaris could be hindered by solution acidification and oxidative molecular species produced in the conversion of bisulfite to sulfate. With the SO2 concentration increased from 0 to 400 ppm, the pH of the culture medium decreased from 7 to 2, and the SO42− concentration reached 1 g L−1, resulting in a decrement of 18.1% in the CO2 dissolution rate. Moreover, the Chlorella cells could only maintain their growth within the SO42− concentration of 800 mg L−1 accompanied by a decrement of 58% in maximum biomass concentration. The cultivation collapsed under excessive SO2 (over 400 ppm) as the plasmolysis and chloroplast decomposition occurred which severely inhibited the microalgal photosynthesis. This work provides a guide to cultivating microalgae using real flue gas.
AB - Aiming at realizing efficient microalgae-based CO2 sequestration from coal-fired power plants, this study investigated the interaction between the mass transfer of SO2-contained flue gas and microalgae growth. The results indicate that the CO2 dissolution in microalgae suspension and the growth of Chlorella vulgaris could be hindered by solution acidification and oxidative molecular species produced in the conversion of bisulfite to sulfate. With the SO2 concentration increased from 0 to 400 ppm, the pH of the culture medium decreased from 7 to 2, and the SO42− concentration reached 1 g L−1, resulting in a decrement of 18.1% in the CO2 dissolution rate. Moreover, the Chlorella cells could only maintain their growth within the SO42− concentration of 800 mg L−1 accompanied by a decrement of 58% in maximum biomass concentration. The cultivation collapsed under excessive SO2 (over 400 ppm) as the plasmolysis and chloroplast decomposition occurred which severely inhibited the microalgal photosynthesis. This work provides a guide to cultivating microalgae using real flue gas.
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U2 - 10.1016/j.renene.2022.08.057
DO - 10.1016/j.renene.2022.08.057
M3 - Article
AN - SCOPUS:85136141267
SN - 0960-1481
VL - 198
SP - 114
EP - 122
JO - Renewable Energy
JF - Renewable Energy
ER -