Wu Mingcan, Du Ming, Wu Guimei, Lu Feimiao, Li Jing, Lei Anping, Zhu Hui, Hu Zhangli, Wang Jiangxin
Shenzhen Key Laboratory of Marine Bioresource and Eco-Environmental Science, Shenzhen Engineering Laboratory for Marine Algal Biotechnology, Guangdong Provincial Key Laboratory for Plant Epigenetics, College of Life Sciences and Oceanography, Shenzhen University, Shenzhen, 518060, China.
Key Laboratory of Optoelectronic Devices and Systems of Ministry of Education and Guangdong Province, College of Optoelectronic Engineering, Shenzhen University, Shenzhen, 518060, China.
Biotechnol Biofuels. 2021 Jun 5;14(1):132. doi: 10.1186/s13068-021-01980-4.
Microalgae can contribute to more than 40% of global primary biomass production and are suitable candidates for various biotechnology applications such as food, feed products, drugs, fuels, and wastewater treatment. However, the primary limitation for large-scale algae production is the fact that algae requires large amounts of fresh water for cultivation. To address this issue, scientists around the world are working on ways to reuse the water to grow microalgae so that it can be grown in successive cycles without the need for fresh water.
In this study, we present the results when we cultivate microalgae with cultivation water that is purified and reused. Specifically, we purify the cultivation water using an ultrafiltration membrane (UFM) treatment and investigate how this treatment affects: the biomass and biochemical components of the microalgae; characteristics of microalgae growth inhibitors; the mechanism whereby potential growth inhibitors are secreted (followed using metabolomics analysis); the effect of activated carbon (AC) treatment and advanced oxidation processes (AOPs) on the removal of growth inhibitors of Euglena gracilis. Firstly, the results show that E. gracilis can be only cultivated through two growth cycles with water that has been filtered and reused, and the growth of E. gracilis is significantly inhibited when the water is used a third time. Secondly, as the number of reused water cycles increases, the Cl concentration gradually increases in the cultivation water. When the Cl concentration accumulates to a level of fivefold higher than that of the control, growth of E. gracilis is inhibited as the osmolality tolerance range is exceeded. Interestingly, the osmolality of the reused water can be reduced by replacing NHCl with urea as the source of nitrogen in the cultivation water. Thirdly, E. gracilis secretes humic acid (HA)-which is produced by the metabolic pathways for valine, leucine, and isoleucine biosynthesis and by linoleic acid metabolism-into the cultivation water. Because HA contains large fluorescent functional groups, specifically extended π(pi)-systems containing C=C and C=O groups and aromatic rings, we were able to observe a positive correlation between HA concentration and the rate of inhibition of E. gracilis growth using fluorescence spectroscopy. Moreover, photosynthetic efficiency is adversely interfered by HA, thereby reductions in the synthetic efficiency of paramylon and lipid in E. gracilis. In this way, we are able to confirm that HA is the main growth inhibitor of E. gracilis. Finally, we verify that all the HA is removed or converted into nutrients efficiently by AC or UV/HO/O treatments, respectively. As a result of these treatments, growth of E. gracilis is restored (AC treatment) and the amount of biomass is promoted (UV/HO/O treatment).
These studies have important practical and theoretical significance for the cyclic cultivation of E. gracilis and for saving water resources. Our work may also provide a useful reference for other microalgae cultivation.
微藻对全球初级生物质产量的贡献超过40%,是食品、饲料产品、药物、燃料和废水处理等各种生物技术应用的合适候选者。然而,大规模藻类生产的主要限制在于藻类培养需要大量淡水。为解决这一问题,世界各地的科学家正在研究如何回用这些水来培养微藻,以便能在无需淡水的情况下连续循环培养。
在本研究中,我们展示了用经过净化和回用的培养水培养微藻的结果。具体而言,我们使用超滤膜(UFM)处理来净化培养水,并研究这种处理如何影响:微藻的生物量和生化成分;微藻生长抑制剂的特性;潜在生长抑制剂的分泌机制(通过代谢组学分析追踪);活性炭(AC)处理和高级氧化工艺(AOPs)对去除纤细裸藻生长抑制剂的效果。首先,结果表明,纤细裸藻仅能通过两个生长周期用经过过滤和回用的水进行培养,当第三次使用该水时,纤细裸藻的生长受到显著抑制。其次,随着回用循环次数的增加,培养水中的Cl浓度逐渐升高。当Cl浓度累积到比对照高五倍的水平时,由于超过了渗透压耐受范围,纤细裸藻的生长受到抑制。有趣的是,通过在培养水中用尿素替代氯化铵作为氮源,可以降低回用的水的渗透压。第三,纤细裸藻将腐殖酸(HA)——由缬氨酸、亮氨酸和异亮氨酸生物合成的代谢途径以及亚油酸代谢产生——分泌到培养水中。由于HA含有大量荧光官能团,特别是含有C = C和C = O基团以及芳香环的扩展π(π)体系,我们能够通过荧光光谱观察到HA浓度与纤细裸藻生长抑制率之间的正相关关系。此外,光合效率受到HA的不利干扰,从而降低了纤细裸藻中副淀粉和脂质的合成效率。通过这种方式,我们能够确认HA是纤细裸藻的主要生长抑制剂。最后,我们验证了所有的HA分别通过AC处理或UV/HO/O处理被有效去除或转化为营养物质。这些处理的结果是,纤细裸藻的生长得以恢复(AC处理),生物量增加(UV/HO/O处理)。
这些研究对于纤细裸藻的循环培养和节约水资源具有重要的实践和理论意义。我们的工作也可能为其他微藻培养提供有用的参考。