CN115029248A - Method for improving microalgae lipid yield by utilizing recycled wastewater - Google Patents
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Abstract
Description
技术领域technical field
本发明属于生物工程技术领域,尤其涉及一种利用回用废水提高微藻脂质产量的方法。The invention belongs to the technical field of bioengineering, and in particular relates to a method for improving the lipid yield of microalgae by utilizing recycled wastewater.
背景技术Background technique
目前,随着化石燃料的开采,能源危机与环境污染给人类社会带来了严重的问题,开发新型可持续资源满足未来日益增长的需求十分迫切。作为新兴的原料,微藻较传统经济作物的生物质具有以下几个优点:1)没有竞争耕地;2)光合效率高,相对较短生长期;3)对恶劣条件的广泛适应性。因此,基于微藻脂质的第三代生物燃料备受关注。虽然微藻可积累大量脂质,但成本高、产率低一直是限制其产业化的主要因素,如何降低微藻培养成本、提高微藻脂质含量和产率是近年来亟待解决的问题。两阶段培养模式是一种微藻快速积累生物质和脂质的策略。At present, with the exploitation of fossil fuels, the energy crisis and environmental pollution have brought serious problems to human society, and it is very urgent to develop new sustainable resources to meet the growing demand in the future. As an emerging raw material, microalgae have the following advantages over biomass from traditional commercial crops: 1) no competition for cultivated land; 2) high photosynthetic efficiency and relatively short growth period; 3) broad adaptability to harsh conditions. Therefore, third-generation biofuels based on microalgal lipids have attracted much attention. Although microalgae can accumulate a large amount of lipids, high cost and low yield have always been the main factors limiting their industrialization. How to reduce the cost of microalgae culture and improve the lipid content and yield of microalgae is an urgent problem to be solved in recent years. The two-stage culture model is a strategy for microalgae to rapidly accumulate biomass and lipids.
为了进一步微藻培养降低成本,利用废水培养微藻可吸收利用废水中的氮、磷等有机物,同时可以替代传统的培养基。微藻培养过程中会产生大量的废水,也会造成环境污染,而利用微藻培养的产生的废水重新培养微藻报道较少。另一方面,使用纯废水培养微藻,由于废水中的一些有毒物质往往导致微藻的生长速率较慢,降低微藻的生物量产率,从而影响整体的油脂产量。因此,配比一定的营养物可提高微藻整体的生物量和脂质产率,这种策略可能有助于增加微藻脂质产量、降低微藻培养成本、减少淡水使用,也为废水的回用提供了新的技术思路。In order to further reduce the cost of microalgae cultivation, the use of wastewater to cultivate microalgae can absorb and utilize organic substances such as nitrogen and phosphorus in wastewater, and can also replace traditional culture media. A large amount of wastewater will be generated during the cultivation of microalgae, and it will also cause environmental pollution. However, there are few reports on the use of wastewater produced by the cultivation of microalgae to re-cultivate microalgae. On the other hand, when using pure wastewater to cultivate microalgae, due to some toxic substances in wastewater, the growth rate of microalgae is often slow, which reduces the biomass yield of microalgae, thereby affecting the overall oil production. Therefore, a certain ratio of nutrients can improve the overall biomass and lipid yield of microalgae. This strategy may help to increase the lipid production of microalgae, reduce the cost of microalgae cultivation, reduce the use of fresh water, and also contribute to the improvement of wastewater. Reuse provides new technical ideas.
通过上述分析,现有技术存在的问题及缺陷为:现有微藻成本高、产率低;微藻培养过程中会产生大量的废水,而利用微藻培养的产生的废水重新培养微藻报道较少;由于废水中的有毒物质会导致微藻的生长速率较慢,使用纯废水培养微藻的脂质产量偏低。Through the above analysis, the existing problems and defects in the prior art are: the cost of the existing microalgae is high and the yield is low; a large amount of waste water will be generated during the microalgae cultivation process, and the waste water generated by the microalgae culture is used to re-cultivate the microalgae. Less; lipid yields of microalgae cultured with pure wastewater are low due to the slower growth rate of microalgae caused by toxic substances in wastewater.
发明内容SUMMARY OF THE INVENTION
针对现有技术存在的问题,本发明提供了一种利用回用废水提高微藻脂质产量的方法。Aiming at the problems existing in the prior art, the present invention provides a method for improving the lipid yield of microalgae by utilizing recycled wastewater.
本发明是这样实现的,一种利用回用废水提高微藻脂质产量的方法,所述利用回用废水提高微藻脂质产量的方法包括:The present invention is achieved in this way, a method for improving the lipid yield of microalgae by utilizing the reused wastewater, and the method for improving the lipid yield of microalgae by utilizing the reused wastewater comprises:
采用两阶段培养模式,在第一阶段进行藻种兼养的培养使藻细胞在短期内快速生长,随后收集微藻培养后的废水,简单过滤后配比BG-11形成混合培养基,结合光生物反应器,利用混合培养基培养微藻。The two-stage culture mode is adopted. In the first stage, the algae and species are cultivated to make the algal cells grow rapidly in a short period of time. Then, the wastewater after the microalgae culture is collected. After simple filtration, BG-11 is mixed to form a mixed medium. Bioreactors that use mixed media to grow microalgae.
进一步,所述利用回用废水提高微藻脂质产量的方法还包括:Further, the method for improving the lipid yield of microalgae by recycling wastewater also includes:
以葡萄糖为碳源兼养培养纤维藻,待微藻生长至对数生长期后期,待藻细胞沉降后倒出上清液,收集剩余的藻细胞作为种子液,上清液经抽滤后得到养藻废水;将养藻废水配比BG-11作为混合培养基,用不同配比的混合培养基重悬微藻于柱式光生物反应器,连续通入10%的CO2和空气混合气体,并置于一定的温度和照强度的环境下培养,检测、分析微藻生物量、脂质含量和产率。The cellulosic algae are cultivated with glucose as the carbon source, and the microalgae grow to the late logarithmic growth phase. After the algal cells settle, the supernatant is poured out, and the remaining algal cells are collected as the seed liquid. The supernatant is obtained after suction filtration. Algae-cultivation wastewater; the algae-cultivation wastewater ratio BG-11 is used as the mixed medium, the microalgae are resuspended in the column photobioreactor with the mixed medium of different ratios, and 10% CO 2 and air mixed gas are continuously introduced , and cultivated under a certain temperature and light intensity environment, to detect and analyze the biomass, lipid content and yield of microalgae.
进一步,所述利用回用废水提高微藻脂质产量的方法包括以下步骤:Further, the method for improving the lipid yield of microalgae by using the reused wastewater comprises the following steps:
步骤一,进行回用废水的收集;The first step is to collect the reused waste water;
步骤二,利用回用废水配比BG-11培养微藻;In
步骤三,利用有机溶剂提取步骤二得到的培养液中藻细胞内的脂质。In
进一步,所述步骤一中的回用废水的收集包括:Further, the collection of reused wastewater in the
以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后得到回用废水。The BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase. The algal cells are used as the seed solution, and the collected supernatant is filtered to obtain reused wastewater.
进一步,所述微藻为纤维藻Ankistrodesmus sp.EHY。Further, the microalgae is the cellulosic alga Ankistrodesmus sp.EHY.
进一步,所述步骤二中的利用回用废水配比BG-11培养微藻包括:Further, the utilization and reuse of wastewater in the second step to cultivate microalgae with the ratio of BG-11 includes:
将回用废水配比新鲜的BG-11作为混合培养基,重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量为0.9g/L;连续通入10%的CO2和空气混合气体,并置于一定温度和照强度的环境下培养,得到最终的培养液。The reused wastewater was mixed with fresh BG-11 as a mixed medium, and the seed solution of the first stage was resuspended into a 1L column-type photobioreactor to ensure that the microalgae inoculation amount was 0.9g/L; % CO 2 and air mixed gas, and placed in a certain temperature and light intensity environment to cultivate to obtain the final culture solution.
进一步,所述混合培养基中回用废水浓度为30~60%。Further, the concentration of reused wastewater in the mixed medium is 30-60%.
进一步,所述温度为25℃,光照强度为7000~8000lux。Further, the temperature is 25°C, and the light intensity is 7000-8000 lux.
进一步,所述步骤三中的利用有机溶剂提取步骤二得到的培养液中藻细胞内的脂质包括:Further, the lipids in the algal cells in the nutrient solution obtained in the
将由步骤二得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重;称取0.2g干藻粉,加入石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相得总脂质,利用重量法测得微藻藻粉的脂质含量。Centrifuge the final culture solution obtained in
进一步,所述有机溶剂为氯仿-甲醇溶液,其中氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;所述石英砂的质量为干藻粉质量的2倍。Further, the organic solvent is a chloroform-methanol solution, wherein the volume ratio of chloroform and methanol in the chloroform-methanol solution is 2:1; the mass of the quartz sand is twice the mass of the dry algal powder.
结合上述的技术方案和解决的技术问题,请从以下几方面分析本发明所要保护的技术方案所具备的优点及积极效果为:In combination with the above-mentioned technical solutions and the technical problems solved, please analyze the advantages and positive effects of the technical solutions to be protected by the present invention from the following aspects:
第一、针对上述现有技术存在的技术问题以及解决该问题的难度,紧密结合本发明的所要保护的技术方案以及研发过程中结果和数据等,详细、深刻地分析本发明技术方案如何解决的技术问题,解决问题之后带来的一些具备创造性的技术效果。具体描述如下:First, in view of the technical problems existing in the above-mentioned prior art and the difficulty of solving the problems, closely combine the technical solutions to be protected of the present invention and the results and data in the research and development process, etc., and analyze in detail and profoundly how to solve the technical solutions of the present invention. Technical problems, some creative technical effects brought about by solving problems. The specific description is as follows:
本发明结合兼养-光自养两阶段培养模式,在光自养培养阶段,40%的回用废水可显著提高微藻的脂质含量和脂质产率,通过此培养方法,既实现了藻细胞中脂质的快速合成,同时降低了淡水的使用和微藻培养的成本,为利用废水培养微藻和回用费用的处理提供了新的研究方向。本发明显著提高了微藻的脂质含量,当回用废水浓度为40%时,微藻脂质含量和脂质产率分别52.01%(细胞干重)和250.72mg L-1d-1,分别比单独BG-11组提高了14.95%和14.00%。The invention combines the facultative-photoautotrophic two-stage cultivation mode, and in the photoautotrophic cultivation stage, 40% of the reused wastewater can significantly improve the lipid content and lipid yield of the microalgae. The rapid synthesis of lipids in algal cells reduces the use of fresh water and the cost of microalgae cultivation, and provides a new research direction for the use of wastewater to cultivate microalgae and the treatment of recycling costs. The invention significantly improves the lipid content of microalgae, when the concentration of recycled wastewater is 40%, the lipid content and lipid yield of microalgae are 52.01% (cell dry weight) and 250.72 mg L -1 d -1 respectively, 14.95% and 14.00% higher than the BG-11 group alone, respectively.
第二,把技术方案看做一个整体或者从产品的角度,本发明所要保护的技术方案具备的技术效果和优点,具体描述如下:Second, considering the technical solution as a whole or from the product point of view, the technical effects and advantages of the technical solution to be protected by the present invention are specifically described as follows:
本发明工序简单、易操作、环保,可显著提高微藻的脂质含量和产率,降低了微藻生产成本,同时为养藻废水的回用提供了新的思路。减少养藻废水的导致的污染;降低微藻培养成本、吸收利用回用废水中的有机物、减少淡水的使用、提高微藻培养的经济可行性;获得高附加值代谢物,用于生产生物柴油。The invention has simple procedures, easy operation and environmental protection, can significantly improve the lipid content and yield of microalgae, reduce the production cost of microalgae, and at the same time provides a new idea for the reuse of algae-cultivating wastewater. Reduce pollution caused by algae culture wastewater; reduce the cost of microalgae cultivation, absorb and reuse organic matter in wastewater, reduce the use of fresh water, and improve the economic feasibility of microalgae cultivation; obtain high value-added metabolites for the production of biodiesel .
第三,作为本发明的权利要求的创造性辅助证据,还体现在以下几个重要方面:Third, as an auxiliary evidence of inventive step for the claims of the present invention, it is also reflected in the following important aspects:
本发明的技术方案转化后的预期收益和商业价值为:为微藻产业化上废水的回用提供了新的技术途径,降低微藻的培养成本,减少淡水的使用。The expected income and commercial value after the transformation of the technical solution of the present invention are as follows: a new technical approach is provided for the reuse of wastewater in the industrialization of microalgae, the cultivation cost of microalgae is reduced, and the use of fresh water is reduced.
附图说明Description of drawings
为了更清楚地说明本发明实施例的技术方案,下面将对本发明实施例中所需要使用的附图做简单的介绍,显而易见地,下面所描述的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下还可以根据这些附图获得其他的附图。In order to illustrate the technical solutions of the embodiments of the present invention more clearly, the following will briefly introduce the accompanying drawings that need to be used in the embodiments of the present invention. Obviously, the drawings described below are only some embodiments of the present invention. For those of ordinary skill in the art, other drawings can also be obtained from these drawings without creative effort.
图1是本发明实施例提供的利用回用废水提高微藻脂质产量的方法流程图;Fig. 1 is the method flow chart that utilizes reused waste water to improve microalgae lipid output provided by the embodiment of the present invention;
图2A是本发明实施例提供的不同浓度回用培养基对微藻生物量的影响图;2A is a graph showing the effect of different concentrations of reused medium on microalgal biomass provided in the embodiment of the present invention;
图2B是本发明实施例提供的不同浓度回用培养基对油脂含量和优质产率的影响示意图。Fig. 2B is a schematic diagram showing the effect of different concentrations of reused medium on oil content and high-quality yield provided by the embodiment of the present invention.
具体实施方式Detailed ways
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the objectives, technical solutions and advantages of the present invention clearer, the present invention will be further described in detail below with reference to the embodiments. It should be understood that the specific embodiments described herein are only used to explain the present invention, but not to limit the present invention.
针对现有技术存在的问题,本发明提供了一种利用回用废水提高微藻脂质产量的方法,下面结合附图对本发明作详细的描述。Aiming at the problems existing in the prior art, the present invention provides a method for improving the lipid yield of microalgae by utilizing recycled wastewater. The present invention is described in detail below with reference to the accompanying drawings.
一、解释说明实施例。为了使本领域技术人员充分了解本发明如何具体实现,该部分是对权利要求技术方案进行展开说明的解释说明实施例。1. Explain the embodiment. In order for those skilled in the art to fully understand how the present invention is specifically implemented, this part is an explanatory embodiment to expand the description of the technical solutions of the claims.
如图1所示,本发明实施例提供的利用回用废水提高微藻脂质产量的方法包括以下步骤:As shown in Figure 1, the method for improving the lipid yield of microalgae by utilizing recycled wastewater provided by the embodiment of the present invention comprises the following steps:
S101,进行回用废水的收集;S101, collecting reused wastewater;
S102,利用回用废水配比BG-11培养微藻;S102, cultivating microalgae by using recycled wastewater with a ratio of BG-11;
S103,利用有机溶剂提取S102得到的培养液中藻细胞内的脂质。S103, using an organic solvent to extract the lipids in the algal cells in the culture solution obtained in S102.
作为优选实施例,本发明实施例提供的利用回用废水提高微藻脂质产量的方法,具体包括以下步骤:As a preferred embodiment, the method for improving the lipid yield of microalgae by utilizing recycled wastewater provided in the embodiment of the present invention specifically includes the following steps:
(1)回用废水的收集:以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后即为回用废水;其中,微藻为纤维藻Ankistrodesmus sp.EHY。(1) Collection of reused wastewater: the BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase and settled for two days. The supernatant was poured off, the remaining algal cells were mixed as seed solution, and the collected supernatant was reused after suction filtration; wherein, the microalgae was Ankistrodesmus sp.EHY.
(2)回用废水配比BG-11培养微藻:将回用废水配比新鲜的BG-11作为混合培养基,混合培养基中回用废水浓度为30~60%;重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) Microalgae cultivation with recycled wastewater ratio BG-11: The recycled wastewater is formulated with fresh BG-11 as a mixed medium, and the concentration of recycled wastewater in the mixed medium is 30-60%; the first stage of resuspension The seed solution was placed in a 1L column photobioreactor to ensure that the microalgae inoculation amount was about 0.9g/L, 10% CO2 and air mixed gas was continuously introduced, and the temperature was 25°C and the light intensity was Cultivated at 7000-8000 lux to obtain the final culture medium.
(3)利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:将由步骤b得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量;有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;石英砂的质量为干藻粉质量的2倍。(3) Use an organic solvent to extract the lipids in the algal cells in the culture solution obtained in step (2): the final culture solution obtained in step b was centrifuged at 5000 r/min for 5 min, and the algal cells were collected in a centrifuge tube at -80°C Freeze overnight, freeze-dried for 24 hours in a freeze dryer, weighed, then weighed 0.2 g of dry algal powder, added quartz sand, ground and mixed, then added organic solvent and repeated extraction until the algal body turned white, and the organic phase was collected by centrifugation. Lipid, the lipid content of microalgae algal powder was measured by gravimetric method; the organic solvent was chloroform-methanol solution, and the volume ratio of chloroform and methanol in the chloroform-methanol solution was 2:1; the mass of quartz sand was the mass of dry
二、应用实施例。为了证明本发明的技术方案的创造性和技术价值,该部分是对权利要求技术方案进行具体产品上或相关技术上的应用实施例。2. Application examples. In order to prove the creativity and technical value of the technical solution of the present invention, this part is an application example of the technical solution in the claims on specific products or related technologies.
实施例1:Example 1:
本发明实施例提供的回用废水浓度为30%的情况下,检测、分析微藻生物量和脂质含量,具体步骤如下:When the concentration of the reused wastewater provided by the embodiment of the present invention is 30%, the specific steps of detecting and analyzing the biomass and lipid content of microalgae are as follows:
(1)回用废水的收集:以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒出上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后即为回用废水;(1) Collection of reused wastewater: the BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase and settled for two days. Pour out the supernatant, mix the remaining algal cells as seed solution, and the collected supernatant is reused wastewater after suction filtration;
(2)30%的回用废水培养微藻:利用30%的回用废水配比新鲜的BG-11作为混合培养基,重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) 30% recycled wastewater to cultivate microalgae: use 30% recycled wastewater to mix fresh BG-11 as a mixed medium, and resuspend the first-stage seed solution into a 1L column photobioreactor , ensure that the microalgae inoculum amount is about 0.9g/L, continuously feed 10% CO2 and air mixed gas, and place it at a temperature of 25 °C and a light intensity of 7000-8000 lux to cultivate to obtain the final culture solution.
利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:利用有机溶剂提取步骤(2)藻细胞内的油脂:其中有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;将由步骤(2)得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入0.4g石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量。其生物量为4.44g L-1,较对照组有小幅度提高,但无显著性差异;油脂含量为49.28%,油脂产率为243.38mg L-1d-1(见图2A~图2B),分别比单独BG-11组增加了8.93%和10.66%。Utilize the organic solvent to extract the lipid in the algal cell in the culture solution obtained in the step (2): use the organic solvent to extract the oil in the algal cell in the step (2): wherein the organic solvent is a chloroform-methanol solution, and the chloroform and chloroform in the chloroform-methanol solution are The volume ratio of methanol was 2:1; the final culture solution obtained in step (2) was centrifuged at 5000 r/min for 5 min, the algal cells were collected in a centrifuge tube, frozen at -80°C overnight, and then weighed after being lyophilized by a freeze dryer for 24 hours. Then weigh 0.2g of dry algal powder, add 0.4g of quartz sand and grind and mix, then add an organic solvent and repeat the extraction until the algal body turns white, and the organic phase is collected by centrifugation to obtain total lipids, and the microalgae are measured by gravimetric method. Lipid content of algal flour. The biomass was 4.44g L -1 , slightly higher than the control group, but there was no significant difference; the oil content was 49.28%, and the oil yield was 243.38mg L -1 d -1 (see Figure 2A to Figure 2B ) , increased by 8.93% and 10.66%, respectively, compared with the BG-11 group alone.
实施例2:Example 2:
本发明实施例提供的回用废水浓度为40%的情况下,检测、分析微藻生物量和脂质含量,具体步骤如下:When the concentration of the reused wastewater provided in the embodiment of the present invention is 40%, the specific steps of detecting and analyzing the biomass and lipid content of microalgae are as follows:
(1)回用废水的收集:以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后即为回用废水;(1) Collection of reused wastewater: the BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase and settled for two days. Pour off the supernatant, mix the remaining algal cells as seed liquid, and the collected supernatant is reused wastewater after suction filtration;
(2)40%的回用废水培养微藻:利用40%的回用废水配比新鲜的BG-11作为混合培养基,重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) 40% recycled wastewater to cultivate microalgae: use 40% recycled wastewater to mix fresh BG-11 as a mixed medium, and resuspend the first-stage seed solution into a 1L column photobioreactor , ensure that the microalgae inoculum amount is about 0.9g/L, continuously feed 10% CO2 and air mixed gas, and place it at a temperature of 25 °C and a light intensity of 7000-8000 lux to cultivate to obtain the final culture solution.
利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:利用有机溶剂提取步骤(2)藻细胞内的油脂:其中有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;将由步骤(2)得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入0.4g石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量。其生物量为4.33g L-1,与对照组无显著性差异;油脂含量为52.01%,油脂产率为250.72mg L-1d-1(见图2A~图2B),分别比单独BG-11组提高了14.95%和14.00%。Utilize the organic solvent to extract the lipid in the algal cell in the culture solution obtained in the step (2): use the organic solvent to extract the oil in the algal cell in the step (2): wherein the organic solvent is a chloroform-methanol solution, and the chloroform and chloroform in the chloroform-methanol solution are The volume ratio of methanol was 2:1; the final culture solution obtained in step (2) was centrifuged at 5000 r/min for 5 min, the algal cells were collected in a centrifuge tube, frozen at -80°C overnight, and then weighed after being lyophilized by a freeze dryer for 24 hours. Then weigh 0.2g of dry algal powder, add 0.4g of quartz sand and grind and mix, then add an organic solvent and repeat the extraction until the algal body turns white, and the organic phase is collected by centrifugation to obtain total lipids, and the microalgae are measured by gravimetric method. Lipid content of algal flour. Its biomass was 4.33 g L -1 , which had no significant difference with the control group; the oil content was 52.01%, and the oil yield was 250.72 mg L -1 d -1 (see Figure 2A to Figure 2B ), which were higher than those of BG-1 alone. Group 11 improved by 14.95% and 14.00%.
实施例3:Example 3:
本发明实施例提供的回用废水浓度为50%的情况下,检测、分析微藻生物量和脂质含量,具体步骤如下:When the concentration of the reused wastewater provided in the embodiment of the present invention is 50%, the specific steps of detecting and analyzing the biomass and lipid content of microalgae are as follows:
(1)回用废水的收集:以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后即为回用废水;(1) Collection of reused wastewater: the BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase and settled for two days. Pour off the supernatant, mix the remaining algal cells as seed liquid, and the collected supernatant is reused wastewater after suction filtration;
(2)50%的回用废水培养微藻:利用50%的回用废水配比新鲜的BG-11作为混合培养基,重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) 50% recycled wastewater to cultivate microalgae: use 50% recycled wastewater to mix fresh BG-11 as a mixed medium, and resuspend the first-stage seed solution into a 1L column photobioreactor , ensure that the microalgae inoculum amount is about 0.9g/L, continuously feed 10% CO2 and air mixed gas, and place it at a temperature of 25 °C and a light intensity of 7000-8000 lux to cultivate to obtain the final culture solution.
利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:利用有机溶剂提取步骤(2)藻细胞内的油脂:其中有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;将由步骤(2)得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入0.4g石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量。其生物量为3.69g L-1,仅为对照组的84.67%;油脂含量为50.64%,比对照组增加了11.94%,但由于其生长受到抑制,其油脂产率仅为197.70mg L- 1d-1(见图2A~图2B)。Utilize the organic solvent to extract the lipid in the algal cell in the culture solution obtained in the step (2): use the organic solvent to extract the oil in the algal cell in the step (2): wherein the organic solvent is a chloroform-methanol solution, and the chloroform and chloroform in the chloroform-methanol solution are The volume ratio of methanol was 2:1; the final culture solution obtained in step (2) was centrifuged at 5000 r/min for 5 min, the algal cells were collected in a centrifuge tube, frozen at -80°C overnight, and then weighed after being lyophilized by a freeze dryer for 24 hours. Then weigh 0.2g of dry algal powder, add 0.4g of quartz sand and grind and mix, then add an organic solvent and repeat the extraction until the algal body turns white, and the organic phase is collected by centrifugation to obtain total lipids, and the microalgae are measured by gravimetric method. Lipid content of algal flour. The biomass was 3.69g L -1 , which was only 84.67% of the control group; the oil content was 50.64%, an increase of 11.94% compared with the control group, but its oil yield was only 197.70mg L - 1 due to its growth inhibition. d -1 (see Figures 2A to 2B).
实施例4:Example 4:
本发明实施例提供的回用废水浓度为50%的情况下,检测、分析微藻生物量和脂质含量,具体步骤如下:When the concentration of the reused wastewater provided in the embodiment of the present invention is 50%, the specific steps of detecting and analyzing the biomass and lipid content of microalgae are as follows:
(1)回用废水的收集:以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液,收集的上清液经抽滤后即为回用废水;(1) Collection of reused wastewater: the BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late logarithmic growth phase and settled for two days. Pour off the supernatant, mix the remaining algal cells as seed liquid, and the collected supernatant is reused wastewater after suction filtration;
(2)60%的回用废水培养微藻:利用60%的回用废水配比新鲜的BG-11作为混合培养基,重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) 60% recycled wastewater to cultivate microalgae: use 60% recycled wastewater to mix fresh BG-11 as a mixed medium, and resuspend the first-stage seed solution into a 1L column photobioreactor , ensure that the microalgae inoculum amount is about 0.9g/L, continuously feed 10% CO2 and air mixed gas, and place it at a temperature of 25 °C and a light intensity of 7000-8000 lux to cultivate to obtain the final culture solution.
利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:利用有机溶剂提取步骤(2)藻细胞内的油脂:其中有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;将由步骤(2)得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入0.4g石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量。其生物量为3.04g L-1,仅达到对照组的69.56%;油脂含量为48.64%,比对照组增加了11.94%,其生长受到明显抑制,其油脂产率仅为143.24mg L-1d-1,显著低于对照组(见图2A~图2B)。Utilize the organic solvent to extract the lipid in the algal cell in the culture solution obtained in the step (2): use the organic solvent to extract the oil in the algal cell in the step (2): wherein the organic solvent is a chloroform-methanol solution, and the chloroform and chloroform in the chloroform-methanol solution are The volume ratio of methanol was 2:1; the final culture solution obtained in step (2) was centrifuged at 5000 r/min for 5 min, the algal cells were collected in a centrifuge tube, frozen at -80°C overnight, and then weighed after being lyophilized by a freeze dryer for 24 hours. Then weigh 0.2g of dry algal powder, add 0.4g of quartz sand and grind and mix, then add an organic solvent and repeat the extraction until the algal body turns white, and the organic phase is collected by centrifugation to obtain total lipids, and the microalgae are measured by gravimetric method. Lipid content of algal flour. The biomass was 3.04g L -1 , which only reached 69.56% of the control group; the oil content was 48.64%, an increase of 11.94% compared with the control group, its growth was significantly inhibited, and its oil yield was only 143.24 mg L -1 d -1 , significantly lower than the control group (see Figure 2A-2B).
三、实施例相关效果的证据。本发明实施例在研发或者使用过程中取得了一些积极效果,和现有技术相比的确具备很大的优势,下面内容结合试验过程的数据、图表等进行描述。3. Evidence of the relevant effects of the embodiment. The embodiments of the present invention have achieved some positive effects in the process of research and development or use, and indeed have great advantages compared with the prior art.
对比例:Comparative ratio:
本发明对比例提供的在单独BG-11培养条件下,检测、分析微藻生物量和脂质含量,具体步骤如下:The comparative example of the present invention provides detection and analysis of microalgae biomass and lipid content under separate BG-11 culture conditions, and the specific steps are as follows:
(1)以葡萄糖为碳源的BG-11培养基在500mL三角瓶中兼养培养纤维藻,待微藻生长至对数生长期后期,沉降两日后,在超净台中倒掉上清液,混合剩余的藻细胞作为种子液;(1) The BG-11 medium with glucose as the carbon source was cultured in a 500mL Erlenmeyer flask, and the microalgae were grown to the late stage of the logarithmic growth phase. Mix the remaining algal cells as seed solution;
(2)利用BG-11培养微藻:利用新鲜的BG-11重悬浮第一阶段的种子液至1L的柱式光生物反应器中,确保微藻接种量约为0.9g/L,连续通入10%的CO2和空气混合气体,并置于温度为25℃、光照强度为7000~8000lux下培养,得到最终的培养液。(2) Use BG-11 to cultivate microalgae: Use fresh BG-11 to resuspend the seed solution of the first stage into a 1L column type photobioreactor to ensure that the microalgae inoculation amount is about 0.9g/L, and the continuous flow of A mixture of 10% CO 2 and air was introduced, and cultured at a temperature of 25° C. and a light intensity of 7000-8000 lux to obtain the final culture solution.
利用有机溶剂提取步骤(2)得到的培养液中藻细胞内的脂质:利用有机溶剂提取步骤(2)藻细胞内的油脂:其中有机溶剂为氯仿-甲醇溶液,氯仿-甲醇溶液中氯仿与甲醇的体积比为2:1;将由步骤(2)得到的最终的培养液经5000r/min离心5min,收集藻细胞于离心管中,-80℃冷冻过夜,利用冻干机冻干24h后称重,而后称取0.2g干藻粉,加入0.4g石英砂并研磨混匀,再加入有机溶剂重复抽提至藻体发白,离心收集有机相即得总脂质,利用重量法测得微藻藻粉的脂质含量。其生物量为4.37g L-1,油脂含量为45.24%,油脂产率为219.93mg L-1d-1(见图2A~图2B)。Utilize the organic solvent to extract the lipid in the algal cell in the culture solution obtained in the step (2): use the organic solvent to extract the oil in the algal cell in the step (2): wherein the organic solvent is a chloroform-methanol solution, and the chloroform and chloroform in the chloroform-methanol solution are The volume ratio of methanol was 2:1; the final culture solution obtained in step (2) was centrifuged at 5000 r/min for 5 min, the algal cells were collected in a centrifuge tube, frozen at -80°C overnight, and then weighed after being lyophilized by a freeze dryer for 24 hours. Then weigh 0.2g of dry algal powder, add 0.4g of quartz sand and grind and mix, then add an organic solvent and repeat the extraction until the algal body turns white, and the organic phase is collected by centrifugation to obtain total lipids, and the microalgae are measured by gravimetric method. Lipid content of algal flour. The biomass was 4.37 g L -1 , the oil content was 45.24%, and the oil yield was 219.93 mg L -1 d -1 (see Figures 2A and 2B).
本发明结合兼养-光自养两阶段培养模式,在光自养培养阶段,40%的回用废水可显著提高微藻的脂质含量和脂质产率,通过此培养方法,既实现了藻细胞中脂质的快速合成,同时降低了淡水的使用和微藻培养的成本,为利用废水培养微藻和回用费用的处理提供了新的研究方向。The invention combines the facultative-photoautotrophic two-stage cultivation mode, and in the photoautotrophic cultivation stage, 40% of the reused wastewater can significantly improve the lipid content and lipid yield of the microalgae. The rapid synthesis of lipids in algal cells reduces the use of fresh water and the cost of microalgae cultivation, and provides a new research direction for the use of wastewater to cultivate microalgae and the treatment of recycling costs.
以上所述,仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,凡在本发明的精神和原则之内所作的任何修改、等同替换和改进等,都应涵盖在本发明的保护范围之内。The above are only specific embodiments of the present invention, but the protection scope of the present invention is not limited to this. Any person skilled in the art is within the technical scope disclosed by the present invention, and all within the spirit and principle of the present invention Any modifications, equivalent replacements and improvements made within the scope of the present invention should be included within the protection scope of the present invention.
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