TWI648400B - Micractinium sp. and uses thereof - Google Patents
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Abstract
本發明係關於一種可在不同材質上生長形成生物膜,且產生高量三酸甘油酯之經分離微芒藻屬(Micractinium sp.)。本發明亦係關於該經分離微芒藻屬(Micractinium sp.)於生產生質燃料及食用油上之用途。 The present invention relates to a isolated Micractinium sp. which can grow on different materials to form a biofilm and produce a high amount of triglyceride. The invention also relates to the use of the isolated Micractinium sp. for producing biomass fuel and edible oil.
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本發明係關於新穎微芒藻屬(Micractinium sp.)分離株,該分離株可在不同材質上生長形成生物膜(biofilm),且可利用生物膜培養模式進行培養,以減少對水資源及土地的需求,並簡化採收流程,降低採收成本。該分離株可產生高量的三酸甘油酯(triacylglycerol),於培養時可吸收二氧化碳,可作為固碳之用,並具有高熱值、低灰分及低硫分等特性,可作為生產生質柴油及食用油的料源。 The invention relates to a novel Micractinium sp. isolate, which can grow on different materials to form a biofilm, and can be cultured by using a biofilm culture mode to reduce water resources and land. Demand and streamline the harvesting process and reduce harvesting costs. The isolate can produce high amount of triacylglycerol, can absorb carbon dioxide during culture, can be used as carbon fixation, and has high calorific value, low ash and low sulfur, and can be used as raw diesel. And the source of edible oil.
自18世紀工業革命以來,人類對石化能源的需求與日俱增,然而石化能源之天然蘊藏量有限,因此逐漸需要尋求新的替代能源。第一代生質能源係以甘蔗、甜菜、玉米、大豆等糧食作物做為原料,利用水解、發酵及轉酯化(transesterification)等技術來製造生質能源,但會造成農耕地需求上升、糧食作物價格上昂等問題;第二代生質能源係以稻桿、玉米桿、木屑及蔗渣等非糧食作物為原料,利用纖維素水解等技術來製造生質能源,但此類生質能源具有原料來源有限、處理成本過高等問題;第三代生質能原係起源於西元1970年能源危機爆發時,美國所推動的藻類生質柴油開發計畫,以藻類為主要原料,利用油脂萃取、氫化(hydrogenation)及轉酯化等技術來製造生質能源。 Since the industrial revolution of the 18th century, human demand for petrochemical energy has increased. However, the natural reserves of petrochemical energy are limited, so it is gradually necessary to seek new alternative energy sources. The first generation of biomass energy is based on sugarcane, sugar beet, corn, soybean and other food crops. It uses biomass, transesterification and other technologies to produce biomass energy, but it will increase the demand for agricultural land and food. The problem of crop prices is high; the second generation of biomass energy is based on non-food crops such as rice straw, corn stalks, wood chips and bagasse, using cellulite hydrolysis technology to produce biomass energy, but such biomass energy has The source of raw materials is limited and the cost of treatment is too high. The third generation of germplasm originated from the 1970 energy crisis. The algae biodiesel development plan promoted by the United States uses algae as the main raw material and extracts with oil. Hydrogenation and transesterification technologies are used to produce biomass energy.
微藻(microalgae)係屬於一種單細胞藻類,其細胞大小介於幾微米(μm)至幾百微米之間,一般無法以肉眼直接觀察,需利用顯微鏡輔助 觀察。微藻之分佈範圍非常廣泛,在淡水、海洋或潮濕的土壤中皆可發現其蹤跡,據估計,地球上大約有20萬至80萬種微藻,其中已發現並有記錄的僅約有3萬5千種,其生物多樣性非常複雜,無論是以基礎研究或是開發的角度而言,為一個幾乎未積極開發的領域。 Microalgae belongs to a kind of unicellular algae. Its cell size ranges from a few micrometers (μm) to several hundred micrometers. It is generally not directly visible to the naked eye. It needs microscopic assistance. Observed. The distribution of microalgae is very wide. It can be found in fresh water, ocean or wet soil. It is estimated that there are about 200,000 to 800,000 species of microalgae on the earth, of which only about 3 have been found and recorded. With 5,000 species, its biodiversity is very complex, from a basic research or development perspective to an area that is barely actively developed.
微藻具備生長速度快、二氧化碳利用率高、可高密度培養、受病菌污染機率較小及所需土地面積較小等優點,並可在短時間內蓄積大量的生物質(biomass),可作為生產生質柴油(biodiesel)、生物乙醇及生物氫等生質燃料(biofuel)的原料。此外,微藻可使用非農耕地、海水、生活廢水、農牧廢水及煙道氣等進行培養,大大減少了土地與淡水的需求,從而減少與糧食及經濟作物的資源競爭。加上其細胞結構簡單且缺乏細胞分化,相較於棕櫚、油菜、大豆及甘蔗等產油作物,其操作性較植物細胞更為簡易,且具有與植物相似的醣化後轉譯修飾機制以利細胞基因表現(Yen,H.W.et al.,Microalgae-based biorefinery-From biofuels to natural products.,Bioresour.Technol.,2013,135:166-174)。 Microalgae has the advantages of fast growth rate, high carbon dioxide utilization rate, high-density culture, low probability of contamination by pathogens and small required land area, and can accumulate a large amount of biomass (biomass) in a short period of time. Produces raw materials for biodiesel, bioethanol, and biofuel. In addition, microalgae can be cultivated using non-agricultural land, seawater, domestic wastewater, agricultural and animal husbandry wastewater, and flue gas, which greatly reduces the demand for land and fresh water, thereby reducing competition for resources with food and cash crops. In addition, its cell structure is simple and lacks cell differentiation. Compared with oil-producing crops such as palm, rapeseed, soybean and sugar cane, its operation is easier than that of plant cells, and it has a similar post-glycation translation modification mechanism to plants. gene expression (Yen, HW et al, Microalgae -based biorefinery-From biofuels to natural products, Bioresour.Technol, 2013,135:... 166-174).
目前,微藻生物質中所含的藻多醣、類胡蘿蔔素(carotenoid)、藻膽蛋白(phycobilin)、二十碳五烯酸(Eicosapentaenoic Acid(EPA))及二十二碳六烯酸(Docosahexaenoic acid(DHA))等,已被廣泛應用於醫療保健、美容、食品加工、水產養殖及生物能源等產業中(Spolaore,P.et al.,Commercial applications of microalgae.,J.Biosci.Bioeng.,2006,101:87-96)。 Currently, algae polysaccharides, carotenoids, phycobilins, Eicosapentaenoic Acid (EPA) and docosahexaenoic acid are contained in microalgal biomass. acid (DHA)), etc., have been widely used in health care, beauty, food processing, aquaculture and bio-energy industries (Spolaore, P. et al. , Commercial applications of microalgae., J.Biosci.Bioeng., 2006, 101: 87-96).
微藻所產的藻油主要由三酸甘油酯、各式脂肪酸及固醇類所組成,並可藉由氫化或轉酯化將其轉化為液態生物燃料。不同的藻種其藻油的組成成份比例亦不相同,因此,有研究指出微藻藻油的脂肪酸圖譜可作為篩選藻種的指標之一(Ramos,M.J.et al.,Influence of fatty acid composition of raw materials on biodiesel properties.,Bioresour. Technol.,2009,100:261-268)。然而,並非所有微藻所產的藻油皆適合用於製備生質燃料,其中所含脂肪酸的不飽和度(degree of unsaturation)及三酸甘油酯的比例,亦會影響該藻油是否適合用於製備生質燃料。有研究文獻指出單針藻(Monoraphidium contortum)(SAG 47.8)具備300mg/L/日的生質能產量,其藻體含油量佔藻體乾重的22.2%(w/w),藻油主要脂肪酸組成為C16:0到C18:1脂肪酸,可作為製造生質燃料的潛力藻株(Bogen,C.et al.,Identification of Monoraphidium contortum as a promising species for liquid biofuel production.Bioresour.Technol.,2013,133:622-626)。 The algae oil produced by microalgae is mainly composed of triglyceride, various fatty acids and sterols, and can be converted into liquid biofuel by hydrogenation or transesterification. Different algae species have different proportions of algae oil composition. Therefore, studies have indicated that the fatty acid profile of microalgae algae oil can be used as one of the indicators for screening algae species (Ramos, MJ et al ., Influence of fatty acid composition of Raw materials on biodiesel properties., Bioresour . Technol ., 2009, 100: 261-268). However, not all algae oil produced by microalgae is suitable for the preparation of biofuels. The degree of unsaturation of fatty acids and the ratio of triglycerides may also affect the suitability of the algae. For the preparation of biofuels. Studies have indicated that Monoraphidium contortum (SAG 47.8) has a biomass yield of 300 mg/L/day, and the algae oil content accounts for 22.2% (w/w) of the dry weight of algae. consisting of C16: 0 to C18:. 1 fatty acid, as a potential for producing biofuel algae strains (Bogen, C et al, Identification of Monoraphidium contortum as a promising species for liquid biofuel production Bioresour.Technol, 2013,... 133:622-626).
微藻的生長需仰賴光合作用的進行,故光、二氧化碳、水、氮、磷及鉀等係培養微藻所需之要素,其養殖方式包含自營、異營及混營培養等,自營培養係指微藻利用光源及無機碳(如二氧化碳)行光合作用得到生長所需之能量;異營培養係指微藻在無照光之條件下,利用培養基中的有機碳作為碳源(如醋酸鈉、葡萄糖)來生長;混營培養則係指微藻可同時進行自營及異營生長。一般而言,微藻之藻體量大約每6至72小時會增加1倍,微藻生長的速度越快,其可採收的頻率越高。然而,通常含油量較高的藻種生長速度較含油量較低的藻種來的慢,故需同時考量微藻的生長速度及含油量來篩選適宜用於製備生質燃料之藻種。此外,不同的培養方式及培養基成份對微藻生長速度、油脂的累積、產率及組成亦會產生不同程度的影響(Dhup,S.& Dhawan,V.,Effect of nitrogen concentration on lipid productivity and fatty acid composition of Monoraphidium sp.,Bioresour.Technol.,2014,152:572-575)。 The growth of microalgae depends on the photosynthesis. Therefore, light, carbon dioxide, water, nitrogen, phosphorus and potassium are the essential elements for cultivating microalgae. The breeding methods include self-operated, multi-operated and mixed culture, etc. Culture refers to the energy required for microalgae to grow by photosynthesis using a light source and inorganic carbon (such as carbon dioxide). The isoculture means that the microalgae use organic carbon in the medium as a carbon source (such as acetic acid under no light). Sodium, glucose) to grow; mixed culture refers to microalgae can carry out self-operated and hetero-growth at the same time. In general, the amount of algae in the microalgae increases approximately every 6 to 72 hours, and the faster the microalgae grows, the higher the frequency of harvesting. However, the growth rate of algae species with higher oil content is slower than that of algae species with lower oil content. Therefore, it is necessary to consider the growth rate and oil content of microalgae to select algae species suitable for preparing biomass fuel. In addition, different culture methods and medium components have different effects on the growth rate of microalgae, oil accumulation, yield and composition (Dhup, S. & Dhawan, V., Effect of nitrogen concentration on lipid productivity and fatty . acid composition of Monoraphidium sp, Bioresour.Technol , 2014,152:. 572-575).
目前以微藻作為生質燃料之原料,其生產成本與技術上仍有待克服與突破之處。以自營培養模式為例,微藻自營培養主要是將微藻懸浮培養於培養液中,然而目前現有的養殖技術仍無法將培養液中藻體 濃度提升至10g/L(1%)以上。此外,由於培養液中藻體濃度低且藻體細胞微小,導致在藻體回收乾燥時,需經由繁複的流程及設備才可將藻體與培養液分離,耗能費時且費用昂貴,使得藻體的回收成本可占微藻生質柴油全部生產成本的20~30%。 At present, microalgae is used as a raw material for biomass fuel, and its production cost and technology still have to be overcome and breakthrough. Taking the self-supporting culture model as an example, the self-cultivation of microalgae mainly involves the suspension culture of microalgae in the culture solution. However, the current culture technology still cannot transfer the algae in the culture solution. The concentration is increased to 10 g/L (1%) or more. In addition, because the concentration of algae in the culture solution is low and the cells of the algae are small, it is necessary to separate the algae from the culture solution through complicated processes and equipment when the algae is recovered and dried, which is time consuming and expensive, so that the algae The recovery cost of the body can account for 20~30% of the total production cost of the microalgae biodiesel.
微藻生物膜養殖系統係利用微藻可貼附生長於載體表面之養殖模式,最早係應用於1980年代處理工業廢水中的氮及磷(Przytocka-Jusiak M.et al.,Removal of nitrogen from industrial waste waters with the use of algal rotating disks and denitrification packed bed reactor.,Water Res.,1984,18:1077-1082)。該養殖模式因不需將微藻懸浮培養於培養液中,且藻體採收時可直接得到高濃度之藻泥,可簡化傳統上繁複的藻體採收流程,大幅地減少藻體回收之能耗及成本,為極具開發潛力的微藻養殖模式。例如,2010年Johnson等人開發將綠球藻(Chlorella sp.)培養於廢水中以保麗龍作為載體之微藻生物膜貼附養殖模式,發現貼附培養之綠球藻可移除廢水中60%以上的氮及磷,且藻體可以直接以刮取之方式進行採收(Johnson,M.B.& Wen,Z.,Development of an attached microalgal growth system for biofuel production,Appl.Microbiol.Biotechnol.,2010,82:525-534);2012年Ozkan等人以低能耗及低水需求量之微藻生物膜光反應器培養叢粒藻(Botryococcus braunii),發現與開放池養殖系統相比,其生物膜光反應器養殖過程減少45%之水需求量,並大幅降低將藻液中水體移除所需能耗的99.7%(Ozkan,A.et al.,Reduction of water and energy requirement of algae cultivation using an algae biofilm photobioreactor.,2012,Bioresour.Technol.,114:542-548);匈牙利MFKK工程公司自2012年開始推行ALGADISK計畫,目的在開發一種可模組化、易於放大、低運轉及低安裝成本的自動化微藻生物膜反應器,並於2014年由合作開發的匈牙利Bay-Bio研究所在研討會中發表,由微藻生物膜反 應器所直接採收之藻泥平均濃度可達100g/L(Sebestyén,P.et al.,Biomass and lipid production by microalgae in a new biofilm based photobioreactor.,presented at Young Biotechnologist National Conference,2014,Szeged),此濃度為一般懸浮微藻養殖濃度的10倍以上;以及2013年美國愛荷華大學Gross等人利用循環微藻生物膜(Revolving Algal Biofilm(RAB))生長系統培養小球藻(Chlorella vulgaris),發現相較於開放池養殖系統,RAB系統所採收之藻泥含水量約90.3%,接近傳統離心後所採收之藻泥含水量(約88.6%)。因此,微藻生物膜養殖模式可以直接刮取之方式重覆採收高濃度之藻泥,免除傳統沉降、絮凝及離心等採收流程,具備節省時間、空間以及減少水資源、採收成本及能源消耗等優勢。然而,上述RAB系統所採收之藻體油脂含量較開放池養殖系統減少約40%(w/w),且在ALGADISK計畫中所採收的藻體油脂含量亦較懸浮培養的藻體油脂含量少,兩種培養模式之油脂含量皆約為10%(w/w)(Gross,M.& Wen,Z.,Yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm(RAB)cultivation system,Bioresour.Technol.,2014,171:50-58;及Sebestyén,P.et al.,Biomass and lipid production by microalgae in a new biofilm based photobioreactor,presented at Young Biotechnologist National Conference,2014,Szeged)。顯示以微藻作為生質燃料之料源時,並非所有藻株皆適合以生物膜培養模式進行培養。 The microalgae biofilm culture system utilizes microalgae to attach to the culture mode that grows on the surface of the carrier. It was first applied to the treatment of nitrogen and phosphorus in industrial wastewater in the 1980s (Przytocka-Jusiak M. et al ., Removal of nitrogen from industrial Waste waters with the use of algal rotating disks and denitrification packed bed reactor., Water Res ., 1984, 18: 1077-1082). The culture mode does not need to suspend the microalgae in the culture solution, and the algae body can directly obtain the high concentration algae mud when harvesting, which can simplify the traditional complicated algae harvesting process and greatly reduce the algae recovery. Energy consumption and cost are micro-algae farming models with great development potential. For example, in 2010, Johnson et al. developed a microalgae biofilm attachment culture model in which Chlorella sp. was cultured in wastewater with styrofoam as a carrier, and it was found that the chlorella was attached to the cultured wastewater. More than 60% of nitrogen and phosphorus, and algae can be harvested directly by scraping (Johnson, MB & Wen, Z., Development of an attached microalgal growth system for biofuel production, Appl . Microbiol . Biotechnol ., 2010, 82:525-534); In 2012, Ozkan et al. cultured a microalgae biofilm photoreactor with low energy consumption and low water demand to culture Botryococcus braunii , and found that its biofilm light was compared with the open pond culture system. The reactor culture process reduces water requirements by 45% and significantly reduces the energy consumption required to remove water from algae (99.7%) (Ozkan, A. et al ., Reduction of water and energy requirement of algae cultivation using an algae) biofilm photobioreactor, 2012, Bioresour.Technol, 114 : 542-548); Hungary MFKK engineering company since 2012, launched ALGADISK project aimed at developing an modular, easy-to-zoom, low operation and low installation costs. Automated microalgae biofilm reactor, which was published in 2014 by the cooperative Bay-Bio Institute in Hungary, and the average concentration of algae collected directly from the microalgae biofilm reactor can reach 100g/L ( Sebestyén, P. et al ., Biomass and lipid production by microalgae in a new biofilm based photobioreactor., presented at Young Biotechnologist National Conference, 2014, Szeged), this concentration is more than 10 times the concentration of general suspended microalgae; and 2013 In the United States, the University of Iowa Gross et al. used the Revolving Algal Biofilm (RAB) growth system to culture Chlorella vulgaris , and found that the algae harvested by the RAB system compared to the open pond culture system. The moisture content of the mud is about 90.3%, which is close to the moisture content of the algae collected after the traditional centrifugation (about 88.6%). Therefore, the microalgae biofilm culture mode can directly harvest high-concentration algae mud by means of direct scraping, eliminating the traditional sedimentation, flocculation and centrifugation harvesting processes, saving time, space, and reducing water resources and harvesting costs. Advantages such as energy consumption. However, the content of algae oil recovered by the above RAB system is about 40% (w/w) lower than that of the open pond culture system, and the algae oil content collected in the ALGADISK plan is also higher than that of the suspension culture algae oil. The content of the oil in both culture modes is about 10% (w/w) (Gross, M. & Wen, Z., Yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm (RAB) cultivation system , Bioresour.Technol, 2014,171:... 50-58; and Sebestyén, P et al, Biomass and lipid production by microalgae in a new biofilm based photobioreactor, presented at Young Biotechnologist National Conference, 2014, Szeged). When microalgae is used as a source of biofuel, not all algae strains are suitable for cultivation in a biofilm culture mode.
以微藻作為生質燃料料源之另一優勢在於微藻的熱值(calorific value)含量高(大於25MJ/Kg),與發電廠(包含火力發電廠及汽電共生廠)所使用之燃煤相比,微藻的熱值約為煙煤(熱值23.94MJ/Kg)的1.044倍以上,約為亞煙煤(熱值20.58MJ/Kg)的1.215倍以上。換言之,若以25MJ/Kg之熱值含量計算,每1公噸藻體所產生之熱值相當 於1.044噸煙煤所產生之熱值,或1.215噸的亞煙煤所產生之熱值。若將微藻以生物膜培養模式進行培養,其採收之藻泥可利用廢熱進行後續的乾燥與焙燒,生產出生質煤炭(biocoal),可取代部份目前使用之燃煤,進而減少燃煤的使用量。 Another advantage of using microalgae as a source of biofuels is the high calorific value of microalgae (greater than 25 MJ/Kg), which is used in power plants (including thermal power plants and cogeneration plants). Compared with coal, the calorific value of microalgae is about 1.044 times higher than that of bituminous coal (heat value 23.94 MJ/Kg), which is about 1.215 times higher than that of sub-bituminous coal (heat value 20.58 MJ/Kg). In other words, if the calorific value of 25MJ/Kg is calculated, the calorific value produced per 1 metric ton of algae is equivalent. The calorific value produced by 1.044 tons of bituminous coal, or the calorific value produced by 1.215 tons of sub-bituminous coal. If the microalgae are cultured in a biofilm culture mode, the harvested algae can be subjected to subsequent drying and roasting using waste heat to produce biocoal, which can replace some of the currently used coal, thereby reducing coal combustion. The amount of use.
目前以微藻作為生質燃料之料源的相關研究,主要包含藻種開發/篩選、微藻養殖技術、藻體回收及生物質萃取等。在藻種開發及篩選方面,目前仍需要具有生長快速、生物質產率高、藻油含量高及藻體易於回收等特點的藻種作為製備微藻生質燃料的基礎。希冀藉由開發具潛力之藻種,以製備生質燃料或高價之活性物質,同時減緩二氧化碳的排放,達到環境保護與產業獲利雙贏之目標(Farrelly,D.J.et al.,Carbon sequestration and the role of biological carbon mitigation:A review.,Renewable and Sustainable Energy Reviews,2013,21:712-727)。 At present, the research on microalgae as a source of biofuels mainly includes algae development/screening, microalgae culture technology, algae recovery and biomass extraction. In the development and screening of algae species, algae species with rapid growth, high biomass yield, high algal oil content and easy recovery of algae are still needed as the basis for the preparation of microalgae biomass fuel. By developing potential algae species to prepare biofuels or high-priced active substances, and at the same time slowing carbon dioxide emissions, the company achieves the goal of environmental protection and industrial profitability (Farrelly, DJ et al ., Carbon sequestration and the role) Of biological carbon mitigation: A review., Renewable and Sustainable Energy Reviews, 2013, 21: 712-727).
本發明係於台灣嘉義阿里山山區採集到含微藻的土壤樣品後,以C培養基進行微藻的培養與分離,選取出可以生物膜培養模式進行培養、具高油脂含量及高熱值以及耐高溫之74C藻株,經鑑定該藻株屬於微芒藻屬(Micractinium)之微藻。經藻油含量、組成及藻體熱值、灰分、硫分含量等分析,發現74C藻株具有作為生質燃料及食用油之原料的潛力。此外,74C藻株可貼附生長於不同材質之載體表面上,形成生物膜;可藉由生物膜培養模式生產藻油,在藻體採收時僅需將載體表面之藻體刮取下來,即可得到高濃度之藻泥,可簡化微藻養殖過程中的採收流程,並降低生產成本。 The invention collects soil samples containing microalgae in the Alishan mountainous area of Chiayi, Taiwan, and cultures and separates the microalgae in C medium, and selects a culture mode capable of culture, high oil content, high calorific value and high temperature resistance. The 74C strain was identified as a microalgae of the genus Micractinium . Based on the analysis of algae oil content, composition and algae calorific value, ash content and sulfur content, 74C strains were found to have potential as raw materials for biofuels and edible oils. In addition, the 74C strain can be attached to the surface of the carrier of different materials to form a biofilm; the algae oil can be produced by the biofilm culture mode, and only the algae on the surface of the carrier can be scraped off when the algae is harvested. High concentration of algae mud can be obtained, which simplifies the harvesting process during microalgae cultivation and reduces production costs.
因此,本發明之一目的係提供一種經分離之微芒藻屬分離株,其中該微芒藻屬分離株包含SEQ ID NO:1所示之核苷酸序列的18S rDNA序列及SEQ ID NO:2所示之核苷酸序列的ITS區域序列。 Accordingly, it is an object of the present invention to provide an isolated M. genus isolate, wherein the M. genus isolate comprises the 18S rDNA sequence of the nucleotide sequence set forth in SEQ ID NO: 1 and SEQ ID NO: The ITS region sequence of the nucleotide sequence shown in 2.
本發明之另一目的係提供一種培養該經分離之微芒藻屬分離株以獲得微芒藻屬培養產物的方法。 Another object of the present invention is to provide a method of culturing the isolated M. genus isolate to obtain a culture product of Micromandala.
本發明之另一目的係提供一種由上述方法所獲得的微芒藻屬培養產物,其中該微芒藻屬培養產物可作為生產生質燃料及食用油的料源。 Another object of the present invention is to provide a culture product of Micromandala obtained by the above method, wherein the culture product of Micromania can be used as a source of raw fuel and edible oil.
本發明之另一目的係提供一種由上述微芒藻屬培養產物中獲得三酸甘油酯之方法。 Another object of the present invention is to provide a method for obtaining triglyceride from the above culture product of Micromonas.
本發明之另一目的係提供一種培養該經分離之微芒藻屬分離株以固定二氧化碳之方法。 Another object of the present invention is to provide a method of culturing the isolated Miscanthus isolate to immobilize carbon dioxide.
本發明在以下部分中詳細描述。本發明之其他特徵、目的及優點可易見於本發明之實施方式及申請專利範圍中。 The invention is described in detail in the following sections. Other features, objects, and advantages of the invention are apparent from the embodiments of the invention and the appended claims.
圖1為74C藻株的顯微鏡檢圖。圖1A為明視野觀察,藻細胞直徑約為3~6μm,顯微倍率1,000X;圖1B為以Nile Red染色,以螢光顯微鏡觀察,藻體內部有黃色之油滴分佈,顯微倍率1,000X。 Figure 1 is a microscopic examination of the 74C strain. Fig. 1A is a bright field observation, the diameter of the algae cells is about 3~6μm, and the microscopic magnification is 1,000X; Fig. 1B is stained by Nile Red, observed by a fluorescent microscope, and the yellow oil droplets are distributed inside the algae body, and the microscopic magnification is 1,000. X.
圖2為74C藻株18S rDNA及ITS區域序列的演化樹分析圖。 Figure 2 is an evolutionary tree analysis of the 18S rDNA and ITS region sequences of the 74C strain.
圖3為74C藻株之ITS區域序列之演化樹分析圖。 Figure 3 is an evolutionary tree analysis diagram of the ITS region sequence of the 74C strain.
圖4為74C藻株於不同培養溫度下(30℃、35℃、37℃及40℃)之生長情形。 Figure 4 shows the growth of 74C strains at different culture temperatures (30 ° C, 35 ° C, 37 ° C and 40 ° C).
圖5為74C藻株於不同培養pH值下(pH4、pH5.5、pH6.5、pH7.5 pH8.5及pH9.5)之生長情形。 Figure 5 shows the growth of 74C strains at different culture pH values (pH 4, pH 5.5, pH 6.5, pH 7.5 pH 8.5 and pH 9.5).
圖6為74C藻株在不同培養鹽度下(0%(w/v)、1.0%(w/v)、1.5%(w/v)、2.0%(w/v)、2.5%(w/v)、3.0%(w/v)及4.0%(w/v))之生長情形。 Figure 6 shows 74C strains at different culture salinities (0% (w/v), 1.0% (w/v), 1.5% (w/v), 2.0% (w/v), 2.5% (w/ v), 3.0% (w/v) and 4.0% (w/v) growth.
圖7為74C藻株生長於不同材質之貼附載體之貼附與產油情形。組別A為各種不同材質之貼附載體;組別B為74C藻株貼附於各載體之生 長情形;組別C為貼附於各載體之74C藻體的顯微鏡明視野觀察圖,顯微倍率為400X;組別D為貼附於各載體之74C藻體經Nile red染色後的螢光顯微鏡觀察圖,顯微倍率為400X。 Fig. 7 shows the attachment and oil production of the attached carrier of the 74C strain grown on different materials. Group A is a carrier attached to various materials; Group B is a 74C strain attached to each carrier. Long case; group C is a microscope bright field view of 74C algae attached to each carrier, the microscopic magnification is 400X; group D is the fluorescent light of 74C algae attached to each carrier after Nile red staining Microscopic observation, the microscopic magnification is 400X.
本發明可藉由下述實施方式中所揭示之各種發明態樣、實施例及表列之相關敘述所瞭解。除非在本文中另作定義,否則與本發明關聯使用之術語(包含技術及科學術語)應具有本發明所屬技術領域中具有通常知識者所瞭解之含義。且當可瞭解,除非本文中提供之定義另作說明,在任何潛在歧義之情況,術語之定義應與該等普遍使用之術語(如詞典中所定義)一致。可進一步瞭解者,本案所使用的術語僅係用作描述特定實施態樣之目的,而非用於限定。 The present invention can be understood from the various aspects of the invention, the embodiments and the description of the embodiments disclosed herein. Unless otherwise defined herein, terms (including technical and scientific terms) used in connection with the present invention shall have the meaning as understood by those of ordinary skill in the art. And, as will be appreciated, unless the definitions provided herein are otherwise specified, in the case of any potential ambiguity, the definition of terms should be consistent with such commonly used terms (as defined in the dictionary). It is to be understood that the terminology used herein is for the purpose of describing the particular embodiments
必須注意的是,除非有清楚的相反指示,於說明書或申請專利範圍使用之單數格式「一」、「一種」及「該」亦包含複數表示。因此,除非上下文另有需要,單數術語應包含複數,而複數術語亦包含單數。 It must be noted that the singular forms "a", "an" and "the" are used in the <RTIgt; Therefore, unless the context requires otherwise, the singular terms shall include the plural, and the plural terms also include the singular.
本發明的範圍以「自一『約』特定數值及/或至另一『約』特定數值」表示。當範圍藉上述方式表示時,其包含自一特定數值及/或至另一特定數值之範圍。同樣地,當數值可藉由術語「約」以表示近似值,將可了解其為一特定值的另一個態樣。可進一步了解,當提及有關其它端點及其他端點本身而言,每一範圍的兩端點皆為有意義的。根據本發明,「約」可表示±20%,較佳為±10%,更佳為±5%。 The scope of the present invention is expressed by "a particular value" and / or another "about" specific value. When the range is expressed in the above manner, it includes a range from a particular value and/or to another particular value. Similarly, when a value can be approximated by the term "about", it will be understood that it is another aspect of a particular value. It can be further appreciated that when referring to other endpoints and other endpoints themselves, the endpoints of each range are meaningful. According to the present invention, "about" can mean ± 20%, preferably ± 10%, more preferably ± 5%.
於本發明中,術語「經分離」或「分離」意謂使物質自其原始環境(若天然存在則為天然環境)中移出。術語"經分離"或"分離"並不一定指物質係經純化者。 In the present invention, the term "separated" or "isolated" means that the substance is removed from its original environment (or natural environment if it is naturally present). The term "isolated" or "isolated" does not necessarily mean that the material is purified.
本發明之一目的係提供一種微芒藻屬分離株,其中該微芒藻屬分離株包含SEQ ID NO:1所示之核苷酸序列的18S rDNA序列及SEQ ID NO:2所示之核苷酸序列的ITS區域序列。於本發明較佳實施態樣中,該微芒藻屬分離株為寄存於財團法人食品工業發展研究所且寄存編號為BCRC 980044之藻株,或為與寄存於財團法人食品工業發展研究所且寄存編號為BCRC 980044之藻株具有實質上完全相同識別特徵之變異株。 An object of the present invention is to provide a strain of Micromandala, wherein the strain of Micromania comprises the 18S rDNA sequence of the nucleotide sequence shown in SEQ ID NO: 1 and SEQ ID NO: The sequence of the ITS region of the nucleotide sequence shown in 2. In a preferred embodiment of the present invention, the microorganism is a strain deposited in the Food Industry Development Research Institute of the Corporation and registered as BCRC 980044, or is deposited with the Food Industry Development Research Institute. The strain with the accession number BCRC 980044 has a variant strain that has substantially identical identification characteristics.
上述術語「變異株」意謂涵蓋全體細胞遺傳組成已藉由如化學突變誘發、自發突變、遺傳工程、轉化或轉染而改變,以致影響其物理或生物化學特性之任何微芒藻屬藻株。然而,該變異株應具有寄存於財團法人食品工業發展研究所且寄存編號為BCRC 980044之微芒藻屬分離株的所有分類學識別特徵。 The term "variant strain" means any micromandala strain that covers all cytogenetic components that have been altered by chemical mutation induction, spontaneous mutation, genetic engineering, transformation or transfection, such that they affect their physical or biochemical properties. . However, the variant strain should have all taxonomic identification features deposited in the Institute of Food Industry Development and deposited under the registration number BCRC 980044.
於本發明中,術語「相似度」意謂兩個核酸序列間的相似程度。該兩個核酸序列之差異可出現於參考核苷酸序列之5'或3'末端位置處,或個別散布於參考序列中之核苷酸當中,或散布於參考序列內之一或多個鄰近基團中之彼等末端位置之間的任何地方。任何特定核酸分子是否與參考核苷酸序列具至少95%、96%、97%、98%、99%或100%相似度係指使用此項技術中所熟知之標準演算法在兩個分子之間所進行的比較,且可常規使用公開可用之電腦程式(諸如BLASTN演算法)來判定。 In the present invention, the term "similarity" means the degree of similarity between two nucleic acid sequences. The difference between the two nucleic acid sequences may occur at the 5' or 3' end position of the reference nucleotide sequence, or may be individually dispersed among the nucleotides in the reference sequence, or interspersed in one or more adjacent sequences within the reference sequence Anywhere between the end positions of the group. Whether any particular nucleic acid molecule has at least 95%, 96%, 97%, 98%, 99%, or 100% similarity to a reference nucleotide sequence refers to the use of standard algorithms well known in the art in two molecules The comparisons made between them can be determined conventionally using publicly available computer programs such as the BLASTN algorithm.
本發明之一目的係在於提供一種製備微芒藻屬培養產物之方法。於本發明之實施態樣中,該方法包含將本發明之微芒藻屬分離株接種於液態培養基中,在照光及通氣下進行培養以獲得該培養產物。於本發明之一較佳實施態樣中,該方法包含將本發明之微芒藻屬分離株與一或多種載體共同培養於液態培養基中,在照光及通氣下進行培養以獲得該培養產物,其中該微芒藻屬分離株與該一或多種載體係分別加入該液態培養基中,或先將該微芒藻屬分離株接種於該一或多種載體上後,再將經接種之載體置入該液態培養基中。 It is an object of the present invention to provide a method of preparing a culture product of Micromania. In an embodiment of the present invention, the method comprises inoculating the Miscanthus isolate of the present invention in a liquid medium, culturing under irradiation and aeration to obtain the culture product. In a preferred embodiment of the present invention, the method comprises culturing the microorganism of the present invention with one or more vectors in a liquid medium, and culturing under illumination and aeration to obtain the culture product. Wherein the Micromandala isolate and the one or more vector lines are separately added to the liquid medium, or the Micromandala isolate is first inoculated on the one or more carriers, and then the inoculated vector is placed. In the liquid medium.
於本發明中,術語「培養產物」意謂將微藻置於培養基中培養後,所獲得富含微藻細胞的產物。於本發明中,該培養產物中之微藻細胞可不必與培養基分離,且該培養產物可呈液態、固態或黏稠狀。 In the present invention, the term "culture product" means a product rich in microalgae cells obtained by culturing microalgae in a medium. In the present invention, the microalgae cells in the culture product may not necessarily be separated from the culture medium, and the culture product may be in a liquid state, a solid state or a viscous state.
於本發明中,用於培養微芒藻屬分離株之「培養基」可為任何容許微芒藻屬分離株生長、繁殖並製造三酸甘油酯及/或脂肪酸之水性培養基,例如C培養基[每100mL中包含15mg Ca(NO3)2˙4H2O、10mg KNO3、5mg β-甘油磷酸二鈉˙5H2O、4mg MgSO4˙7H2O、0.01μg維生素B12、0.01μg生物素(Biotin)、1μg噻胺HCl、0.3mL PIV微量元素溶液(每100mL中包含100mg Na2EDTA˙2H2O、19.6mg FeCl3˙6H2O、3.6mg MnCl2˙4H2O、1.04mg ZnCl2、0.4μg CoCl2˙6H2O、0.25μg Na2MoO4˙2H2O及水)、50mg Tris(hydroxymethyl)aminomethane及水]、BG-11培養基[每100mL包含1,500mg NaNO3、40mg K2HPO4、75mg MgSO4.7H2O、27.18mg CaCl2、6mg檸檬酸、6mg檸檬酸鐵銨、1mg Na2.Mg.EDTA.2H2O、20mg Na2CO3、2.86mg HBO3、1.181mg MnCl2˙4H2O、0.222mg ZnSO4˙7H2O、0.39mg Na2MoO4˙2H2O、0.0718mg CuSO4˙5H2O、0.049mg Co(NO3)2.6H2O及水],以及MA培養基[每100mL中包含10mg Ca(NO3)2˙4H2O、10mg KNO3、5mg NaNO3、4mg Na2SO4、5mg MgCl2˙6H2O、10mg β-甘油磷酸二鈉˙5H2O、0.5mg Na2EDTA˙2H2O、0.05mg FeCl3˙6H2O、0.5mg MnCl2˙4H2O、0.05mg ZnCl2、0.5mg CoCl2˙6H2O、0.08mg Na2MoO4˙2H2O、2mg H3BO3及50mg Bicine]。 In the present invention, the "medium" used for culturing the Miscanthus isolate may be any aqueous medium which allows the growth, propagation and production of triglycerides and/or fatty acids of the Miscanthus isolate, such as C medium [per 100mL contains 15mg Ca(NO 3 ) 2 ̇4H 2 O, 10mg KNO 3 , 5mg β-glycerophosphate disodium ̇5H 2 O, 4mg MgSO 4 ̇7H 2 O, 0.01μg vitamin B12, 0.01μg biotin (Biotin 1 μg of thiamine HCl, 0.3 mL of PIV trace element solution (containing 100 mg Na 2 EDTA ̇ 2H 2 O, 19.6 mg FeCl 3 ̇ 6H 2 O, 3.6 mg MnCl 2 ̇ 4H 2 O, 1.04 mg ZnCl 2 per 100 mL, 0.4 μg CoCl 2 ̇6H 2 O, 0.25 μg Na 2 MoO 4 ̇2H 2 O and water), 50 mg Tris (hydroxymethyl) aminomethane and water], BG-11 medium [containing 1,500 mg NaNO 3 , 40 mg K 2 HPO per 100 mL 4 , 75mg MgSO 4 . 7H 2 O, 27.18 mg CaCl 2 , 6 mg citric acid, 6 mg ammonium ferric citrate, 1 mg Na 2 . Mg. EDTA. 2H 2 O, 20 mg Na 2 CO 3 , 2.86 mg HBO 3 , 1.181 mg MnCl 2 ̇ 4H 2 O, 0.222 mg ZnSO 4 ̇7H 2 O, 0.39 mg Na 2 MoO 4 ̇ 2H 2 O, 0.0718 mg CuSO 4 ̇ 5H 2 O, 0.049 mg Co(NO 3 ) 2 . 6H 2 O and water], and MA medium [10 mg Ca(NO 3 ) 2 ̇ 4H 2 O, 10 mg KNO 3 , 5 mg NaNO 3 , 4 mg Na 2 SO 4 , 5 mg MgCl 2 ̇6H 2 O, 10 mg per 100 mL Β -glycerol phosphate disodium ̇5H 2 O, 0.5 mg Na 2 EDTA ̇ 2H 2 O, 0.05 mg FeCl 3 ̇6H 2 O, 0.5 mg MnCl 2 ̇4H 2 O, 0.05 mg ZnCl 2 , 0.5 mg CoCl 2 ̇6H 2 O, 0.08 mg Na 2 MoO 4 ̇ 2H 2 O, 2 mg H 3 BO 3 and 50 mg Bicine].
本發明中用於培養微芒藻屬分離株之條件意指如培養基之pH值、鹽度、培養溫度、照光、通氣條件及培養時間等條件,其可容許該微芒藻屬分離株生長、繁殖並製造三酸甘油酯及/或脂肪酸。本技術領域之人士可根據既有知識針對培養基的成分及培養條件作調整。 The condition for cultivating the Miscanthus isolate in the present invention means that the pH of the medium, the salinity, the culture temperature, the illumination, the aeration condition, and the culture time, etc., allow the growth of the Miscanthus isolate, Reproduction and manufacture of triglycerides and/or fatty acids. Those skilled in the art can adjust the composition and culture conditions of the medium based on prior knowledge.
於本發明之實施態樣中,用於培養微芒藻屬之培養基的pH值可為約pH2.5至約pH11.0(例如約pH2.5、約pH3.0、約pH3.5、約pH4.0、約pH4.5、約pH5.0、約pH5.5、約pH6.0、約pH6.5、約pH7.0、約pH7.5、約pH8.0、約pH8.5、約pH9.0、約pH9.5、約pH10.0、約pH10.5或約pH11.0),較佳為約pH4.0至約pH9.5。 In an embodiment of the present invention, the pH of the medium for culturing Micromandala may be from about pH 2.5 to about pH 11.0 (eg, about pH 2.5, about pH 3.0, about pH 3.5, about pH 4.0, about pH 4.5, about pH 5.0, about pH 5.5, about pH 6.0, about pH 6.5, about pH 7.0, about pH 7.5, about pH 8.0, about pH 8.5, about pH 9.0, about pH 9.5, about pH 10.0, about pH 10.5 or about pH 11.0), preferably from about pH 4.0 to about pH 9.5.
於本發明之實施態樣中,微芒藻屬培養溫度可為約15℃至約60℃(例如約15℃、約20℃、約25℃、約30℃、約35℃、約40℃、約45℃、約50℃、約55℃或約60℃),較佳為約20℃至約40℃;且照光量可為約100lux至約4,000lux,較佳為約2,000lux之亮度持續照光。 In an embodiment of the present invention, the micro-mandala culture temperature may be from about 15 ° C to about 60 ° C (eg, about 15 ° C, about 20 ° C, about 25 ° C, about 30 ° C, about 35 ° C, about 40 ° C, About 45 ° C, about 50 ° C, about 55 ° C or about 60 ° C), preferably about 20 ° C to about 40 ° C; and the amount of light can be from about 100 lux to about 4,000 lux, preferably about 2,000 lux of brightness continuous illumination .
於本發明之實施態樣中,可視需要調整培養微芒藻屬之培養基的鹽度。本文中所謂「鹽度」意旨溶解於培養基中之鹽類含量。本發明中培養基之鹽度可為0%(w/w)至約6.0%(w/w)(例如0%(w/w)、約0.5%(w/w)、約1.0%(w/w)、約1.5%(w/w)、約2.0%(w/w)、約2.5%(w/w)、約3.0%(w/w)、約3.5%(w/w)、約4.0%(w/w)、約4.5%(w/w)、約5.0%(w/w)、約5.5%(w/w)或約6.0%(w/w)),較佳為0%(w/w)至約4.0%(w/w)。 In the embodiment of the present invention, the salinity of the culture medium of the culture of Micromania can be adjusted as needed. As used herein, "salinity" means the salt content dissolved in the medium. The culture medium may have a salinity of from 0% (w/w) to about 6.0% (w/w) (e.g., 0% (w/w), about 0.5% (w/w), about 1.0% (w/). w), about 1.5% (w/w), about 2.0% (w/w), about 2.5% (w/w), about 3.0% (w/w), about 3.5% (w/w), about 4.0 % (w/w), about 4.5% (w/w), about 5.0% (w/w), about 5.5% (w/w) or about 6.0% (w/w), preferably 0% ( w/w) to about 4.0% (w/w).
於本發明中,術語「通氣」意旨於液體培養基中持續地通入含有二氧化碳之空氣,而通氣量可為約0.05vvm至約1vvm,較佳為約0.1vvm至約0.5vvm,最佳為約0.1vvm。該空氣中之二氧化碳的濃度可為約0.04%(v/v)至約20%(v/v),較佳為約0.1%(v/v)至約15%(v/v),更佳為約5%(v/v)至約10%(v/v)。 In the present invention, the term "ventilating" means continuously introducing air containing carbon dioxide into a liquid medium, and the aeration amount may be from about 0.05 vvm to about 1 vvm, preferably from about 0.1 vvm to about 0.5 vvm, most preferably about 0.1vvm. The concentration of carbon dioxide in the air may range from about 0.04% (v/v) to about 20% (v/v), preferably from about 0.1% (v/v) to about 15% (v/v), more preferably. It is from about 5% (v/v) to about 10% (v/v).
於本發明中,術語「載體」意指可供微芒藻屬貼附及/或固定於其表面上並生長之任何基質,其包括(但不限於)網狀物質(例如,纖維濾紙、棉布、麻布、濾布、木漿布、不織布、牛仔布、尼龍布、超細纖維織布及帆布)、泡棉(例如,聚乙烯醇(PVA)泡棉)或其任意的組合;該載體可呈任何形狀,包括(但不限於)片狀、球形、環狀、螺旋 體、正方體、長方體及多邊體。 In the present invention, the term "carrier" means any substrate which can be attached to and/or immobilized on the surface of the microorganism, including but not limited to a mesh material (for example, fiber filter paper, cotton cloth). , burlap, filter cloth, wood pulp cloth, non-woven fabric, denim, nylon cloth, microfiber woven fabric and canvas), foam (for example, polyvinyl alcohol (PVA) foam) or any combination thereof; In any shape, including but not limited to flakes, spheres, rings, spirals Body, cube, cuboid and polygon.
於本發明中,術語「生物膜」意指由本發明之微芒藻屬細胞所聚集而形成之膜狀群落。 In the present invention, the term "biofilm" means a membranous colony formed by aggregation of the cells of the Micromania of the present invention.
本發明製備微芒藻屬培養產物之方法中,可視需要包含分離該培養產物的步驟,而該分離步驟可為如離心、過濾、聚集凝結及/或將生物膜從載體上刮下收集等習知的方法步驟。 In the method for preparing a culture product of Micromandala according to the present invention, the step of isolating the culture product may be included as needed, and the separation step may be, for example, centrifugation, filtration, aggregation coagulation, and/or scraping of the biofilm from the carrier. Know the method steps.
本發明亦提供由上述方法所獲得之培養產物。本發明之培養產物中富含三酸甘油酯及/或脂肪酸,特別是三酸甘油酯,可作為製造生質燃料及食用油之料源。有研究指出,微藻在貼附生長下所產生之油脂量僅佔藻體乾重10%(w/w)以下,遠低於懸浮生長所產生之油脂量(Gross,M.& Wen,Z.,Yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm(RAB)cultivation system,Bioresour.Technol.,2014,171:50-58;及Sebestyén,P.et al.,Biomass and lipid production by microalgae in a new biofilm based photobioreactor,presented at Young Biotechnologist National Conference,2014,Szeged)。然而,本發明之微芒藻屬分離株於貼附培養下之藻乾含油量為52.08%(w/w),遠高於一般藻株於貼附培養下之藻乾含油量。 The present invention also provides a culture product obtained by the above method. The culture product of the present invention is rich in triglycerides and/or fatty acids, particularly triglycerides, and can be used as a source of raw fuel and edible oil. Studies have shown that the amount of oil produced by microalgae under attachment growth accounts for only 10% (w/w) of the dry weight of algae, which is much lower than the amount of oil produced by suspension growth (Gross, M. & Wen, Z ., yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm (RAB) cultivation system, Bioresour.Technol, 2014,171:... 50-58; and Sebestyén, P et al, Biomass and lipid production by microalgae In a new biofilm based photobioreactor, presented at Young Biotechnologist National Conference, 2014, Szeged). However, the oil content of the dried algae of the microorganism of the present invention is 52.08% (w/w), which is much higher than the oil content of the algal dry of the common algae strain under the attachment culture.
本文中之「三酸甘油酯」意旨具有1個甘油分子及3個脂肪酸分子之酯類化合物,其中該3個脂肪酸分子可具有完全相同、部份相同或完全相異之碳數及不飽和鍵。 As used herein, "triglyceride" means an ester compound having one glycerol molecule and three fatty acid molecules, wherein the three fatty acid molecules may have identical, partially identical or completely different carbon numbers and unsaturated bonds. .
本文中之「脂肪酸」意旨具有8至30個碳原子及0至6個不飽和鍵的羧酸化合物,其較佳為具有12至20個碳原子及0至5個不飽和鍵的羧酸化合物,更佳為具有16至18個碳原子及0至3個不飽和鍵的羧酸化合物。 The "fatty acid" herein means a carboxylic acid compound having 8 to 30 carbon atoms and 0 to 6 unsaturated bonds, preferably a carboxylic acid compound having 12 to 20 carbon atoms and 0 to 5 unsaturated bonds. More preferably, it is a carboxylic acid compound having 16 to 18 carbon atoms and 0 to 3 unsaturated bonds.
三酸甘油酯及脂肪酸之獲得可使用本技術領域所熟知的任何萃 取及分離方法,例如Folch等人(Folch,J.et al.,A simple method for the isolation and purification of total lipids from animal tissue.,J.Bio.Chem.,1957,23:497-509)、Balasubramanian等人(Balasubramanian S.et al.,Oil extraction from Scenedesmus obliquus using a continuous microwave system-design,optimization,and quality characterization.,Bioresour.Technol.,2011,102:3396-3403)及Sajilata等人(Sajilata M.G.et al.,Supercritical CO2 extraction of γ-linolenic acid(GLA)from Spirulina platensis ARM 740 using response surface methodology.,J.Food Eng.,2008,84:321-326)所述的方法。簡而言之,該方法可包含將微芒藻屬細胞以如研磨法或超音波法等方式擊碎,藉由適當的溶劑萃取微芒藻屬細胞中之三酸甘油酯及/或脂肪酸,再藉由如HPLC及/或離子交換樹脂的技術獲得三酸甘油酯及/或脂肪酸。 The triglyceride and the fatty acid can be obtained by any extraction and separation method well known in the art, for example, Folch, J. et al ., A simple method for the isolation and purification of total lipids from animal tissue. , J. Bio . Chem ., 1957, 23: 497-509), Balasubramanian S. et al ., Oil extraction from Scenedesmus obliquus using a continuous microwave system-design, optimization, and quality characterization., Bioresour. Technol ., 2011, 102: 3396-3403) and Sajilata et al . (Sajilata MG et al ., Supercritical CO 2 extraction of γ-linolenic acid (GLA) from Spirulina platensis ARM 740 using response surface methodology., J.Food Eng . , 2008, 84: 321-326). Briefly, the method may comprise crushing Microman's genus cells in a manner such as grinding or ultrasonication, and extracting triglycerides and/or fatty acids in Microman's cells by a suitable solvent. Triglycerides and/or fatty acids are then obtained by techniques such as HPLC and/or ion exchange resins.
本發明之微芒藻屬培養產物可經化學轉化(如氫化、轉酯化、水熱碳化(hydrothermal carbonisation)、發酵或裂解等)或萃取而成固態、液態或氣態之生質燃料,其包括(但不限於)生質柴油、生物甲醇、生物乙醇、生物丁醇、生物甲烷、生物氫或生質煤炭。 The culture product of the microorganism of the present invention can be chemically converted (such as hydrogenation, transesterification, hydrothermal carbonisation, fermentation or pyrolysis, etc.) or extracted into a solid, liquid or gaseous biomass fuel, including (but not limited to) biodiesel, biomethanol, bioethanol, biobutanol, biomethane, biohydrogen or biomass coal.
上述生質燃料之獲得可使用本技術領域所熟知的任何方法,諸如Tran D.T.等人(Tran D.T.et al.,Effect of solvents and oil content on direct transesterification of wet oil-bearing microalgal biomass of Chlorella vulgaris ESP-31 for biodiesel synthesis using immobilized lipase as the biocatalyst.,Bioresour.Technol.,2013,135:213-221)、Cheng H.H.等人(Cheng H.H.,et al.,Biological butanol production from microalgae-based biodiesel residues by Clostridium acetobutylicum.,Bioresour.Technol.,2015,184:379-385)、Sambusiti C.等人(Sambusiti C.,et al.,Algae as promising feedstocks for fermentative biohydrogen production according to a biorefinery approach:A comprehensive review.,Renew.Sust.Energ.Rev.,2015,44:20-36)及Heilmann S.M.等人(Heilmann S.M.et al.,Hydrothermal carbonization of microalgae.,Biomass.Bioenerg.,2010,34(6):875-882及Heilmann S.M.et al.,Hydrothermal carbonization of microalgae II.Fatty acid,char,and algal nutrient products.,Appl.Energ.,2011,88(10):3286-3290)所述之方法。 The above biomass fuel can be obtained by any method known in the art, such as Tran DT et al ., Effect of solvents and oil content on direct transesterification of wet oil-bearing microalgal biomass of Chlorella vulgaris ESP- 31 for biodiesel synthesis using immobilized lipase as the biocatalyst, Bioresour.Technol, 2013,135:.. 213-221), Cheng HH et al (Cheng HH, et al, Biological butanol production from microalgae-based biodiesel residues by Clostridium acetobutylicum. ., Bioresour.Technol., 2015, 184: 379-385), Sambusiti C., et al ., Algae as promising feedstocks for fermentative biohydrogen production according to a biorefinery approach: A comprehensive review., Renew .Sust.Energ.Rev ., 2015, 44: 20-36) and Heilmann SM et al ., Hydrothermal carbonization of microalgae., Biomass . Bioenerg ., 2010 , 34 (6): 875-882 and Heilmann SM et al ., Hydrothermal carbonization of microalgae II. Fatty acid, char, and algal nutrient products., Appl.Energ ., 201 1,88(10):3286-3290).
本文所述之所有公開案、專利及專利文獻均以全文引用的方式併入本文中。 All publications, patents and patent documents mentioned herein are hereby incorporated by reference in their entirety.
提供以下實例以輔助熟習此項技術者實施本發明。即使如此,不應將該等實例視為本發明之限制,因為本發明所屬技術領域中具有通常知識者在不背離本發明之精神或範疇的情況下對本文所討論之實施例進行的修改及變化,而仍屬於本發明之範圍。 The following examples are provided to assist those skilled in the art in practicing the invention. </ RTI> </ RTI> </ RTI> </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; </ RTI> <RTIgt; Changes are still within the scope of the invention.
1.C培養基 1.C medium
將Ca(NO3)2˙4H2O 15mg、KNO3 10mg、β-甘油磷酸二鈉˙5H2O 5mg、MgSO4˙7H2O 4mg、維生素B12 0.01μg、生物素(Biotin)0.01μg、噻胺(Thiamine)HCl 1μg、PIV微量金屬溶液0.3mL與Tris 50mg混合後將其體積補水至100mL,調整pH至7.5後進行高壓滅菌。若為1.5%(w/v)洋菜固體培養基則需加入15g的洋菜膠一同滅菌。 Ca(NO 3 ) 2 ̇4H 2 O 15 mg, KNO 3 10 mg, β-glycerophosphate disodium H5H 2 O 5 mg, MgSO 4 ̇7H 2 O 4 mg, vitamin B12 0.01 μg, biotin (Biotin) 0.01 μg, 1 μg of Thiamine HCl, 0.3 mL of a PIV trace metal solution and 50 mg of Tris were mixed, and the volume was hydrated to 100 mL, and the pH was adjusted to 7.5, followed by autoclaving. If it is 1.5% (w/v) acacia solid medium, it needs to be sterilized by adding 15g of vegetable gum.
PIV微量金屬溶液的配製為依序加入Na2EDTA˙2H2O 100mg、FeCl3˙6H2O 19.6mg、MnCl2˙4H2O 3.6mg、ZnCl2 1.04mg、CoCl2˙6H2O 0.4μg與Na2MoO4˙2H2O 0.25μg,隨後將其體積補水至100mL後進行高壓滅菌。 The PIV trace metal solution was prepared by sequentially adding Na 2 EDTA ̇2H 2 O 100 mg, FeCl 3 ̇6H 2 O 19.6 mg, MnCl 2 ̇4H 2 O 3.6 mg, ZnCl 2 1.04 mg, CoCl 2 ̇6H 2 O 0.4 μg. After autoclaving with Na 2 MoO 4 ̇2H 2 O 0.25 μg, the volume was then hydrated to 100 mL.
2.藻樣採集、分離及培養 2. Algae collection, separation and culture
取台灣嘉義阿里山山區之土壤樣品約10g置於50mL離心管中,並加入約30mL C培養基,於25℃下照光培養。培養期間以顯微鏡觀察是否有藻體生長,之後取出適量含藻體之培養液,將其轉至平板培養基,於25℃下照光培養。待藻體生長後取單一藻種將其於平板培養基中塗開,以上步驟需重覆至篩到單一藻體為止。平板培養則取單一藻落塗至C培養基平板上,於25℃下照光培養。大量培養則自平板培養基上刮取新鮮培養之單一藻體,添加至液態C培養基中(約800mL),使其培養液吸光值(OD682nm)約達0.1~0.15,並於25℃照光充氣培養,培養期約30天。 Approximately 10 g of the soil sample from the Alishan mountain area of Chiayi, Taiwan, was placed in a 50 mL centrifuge tube, and about 30 mL of C medium was added and cultured at 25 ° C. During the culture, the growth of the algae was observed by a microscope, and then an appropriate amount of the culture medium containing the algae was taken out, transferred to a plate medium, and cultured at 25 ° C. After the algae grows, a single algae species is taken and spread in the plate medium, and the above steps need to be repeated until the sieve is applied to the single algae body. For plate culture, a single algal was applied to a C medium plate and cultured at 25 ° C. In a large number of cultures, a freshly cultured single algae body is scraped from the plate medium and added to the liquid C medium (about 800 mL) to make the absorbance of the culture solution (OD 682 nm) about 0.1 to 0.15, and the aeration culture is carried out at 25 ° C. The culture period is about 30 days.
3.油脂染色分析 3. Oil staining analysis
將培養好的藻體取20μL與1μL Nile Red(於二甲基亞碸中0.1mg/mL)混合以進行油滴染色,染色後於室溫靜置10分鐘,再利用螢光顯微鏡進行觀察(Chen,W.et al.,A high throughput Nile red method for quantitative measurement of neutral lipids in microalgae.,J.Microbio.Methods,2009,77:41-47及Huang,G.H.,et al.,Rapid screening method for lipid production in alga based on Nile red fluorescence.,Biomass.Bioenerg.,2009,33:1386-1392)。 20 μL of the cultured algae was mixed with 1 μL of Nile Red (0.1 mg/mL in dimethyl sulfoxide) for oil droplet staining, and after staining, it was allowed to stand at room temperature for 10 minutes, and then observed with a fluorescence microscope ( Chen, W. et al ., A high throughput Nile red method for quantitative measurement of neutral lipids in microalgae ., J. Microbio. Methods, 2009, 77:41-47 and Huang, GH, et al ., Rapid screening method for Lipid production in alga based on Nile red fluorescence., Biomass . Bioenerg ., 2009 , 33 : 1386-1392).
4.藻種之分子鑑定 4. Molecular identification of algae species
自平板培養基上刮取適量之新鮮培養的藻體,將其收集在2mL微量離心管中,依照ZYMO RESEARCH的ZR Fungal/Bacterial DNA MiniPrepTM kit說明書操作取得基因體(genomic)DNA,並以NanoDrop(ND-1000分光光度計)檢測DNA濃度。 Scraped from the plate medium amount of freshly cultured algae, which was collected in a microcentrifuge tube 2mL acquires genome (genomic) DNA in accordance ZYMO RESEARCH ZR Fungal / Bacterial DNA MiniPrep TM kit manual operation, and to a NanoDrop ( ND-1000 spectrophotometer) detects DNA concentration.
將藻體基因體DNA作為PCR模板,以18S rRNA與ITS區域(包含內轉錄間隔區(internal transcribed spacer)1、5.8S核糖體RNA、內轉錄間隔區2與28S核糖體RNA的前端等序列)的相關引子組(http://biology.duke.edu/fungi/mycolab/primers.htm)來擴增其 基因片段。PCR反應溶液如下:適量的基因體DNA溶液作為PCR模板、10mM dNTP 3μL、10X PCR緩衝液4μL、10mM 5'端引子與3'端引子各0.5μL及Taq酵素5U。PCR反應條件為96℃,5分鐘;(96℃,30秒;50℃,20秒;72℃,3分鐘)共40次循環;72℃,10分鐘;最後保持在4℃。取5μL產物進行電泳跑膠分析。 The genomic DNA of the algae was used as a PCR template, and the 18S rRNA and ITS regions (including the internal transcribed spacer 1, the 5.8S ribosomal RNA, the internal transcribed spacer 2 and the front end of the 28S ribosomal RNA) A related primer set (http://biology.duke.edu/fungi/mycolab/primers.htm) to amplify its gene fragment. The PCR reaction solution was as follows: an appropriate amount of genome DNA was used as PCR template, 10mM dNTP 3μL, 10X PCR buffer 4μL, 10mM 5 'end of the primer and the 3' end of each primer and Taq enzyme 0.5μL 5U. The PCR reaction conditions were 96 ° C for 5 minutes; (96 ° C, 30 seconds; 50 ° C, 20 seconds; 72 ° C, 3 minutes) for a total of 40 cycles; 72 ° C, 10 minutes; and finally maintained at 4 ° C. 5 μL of the product was taken for electrophoresis.
將PCR產物純化後以適當引子(http://biology.duke.edu/fungi/mycolab/primers.htm)進行定序,將定序結果以Vector NTI Suite 9軟體(VNTI)與NCBI/Blastn(http://www.ncbi.nlm.nih.gov/BLAST/)進行序列重組與序列相似性比對分析。另,分別將定序所得的結果經NCBI/Blastn後所得相近的藻株與數個藻種中心較接近的藻株及藻屬列為比較範圍,進行演化樹分析,以MEGA 6.0做比對,接著利用最大概似法(Maximum Likelihood)以GTR+G+I的方式繪製演化樹,Bootstrap則為100次。 The PCR product was purified and sequenced with appropriate primers (http://biology.duke.edu/fungi/mycolab/primers.htm), and the sequencing results were made with Vector NTI Suite 9 software (VNTI) and NCBI/Blastn (http Sequence recombination and sequence similarity alignment analysis were performed at ://www.ncbi.nlm.nih.gov/BLAST/). In addition, the results obtained by sequencing were compared with the algae and algae which were obtained by NCBI/Blastn and the algae and algae which were close to several algal species centers. The evolution tree was analyzed and compared with MEGA 6.0. Then use the Maximum Likelihood to plot the evolution tree in GTR+G+I, with Bootstrap 100 times.
5.藻種培養特性分析 5. Analysis of culture characteristics of algae
5.1 培養溫度(耐熱溫度) 5.1 Culture temperature (heat resistant temperature)
將74C藻種於25℃環境下進行分離純化,之後於20℃下進行長期的繼代保存。為測試74C藻株在不同培養溫度下之生長耐受性,將適量藻體接種於多個C培養基平板上,並分別於30℃、35℃、37℃及40℃等不同溫度下進行照光培養,之後分別於培養第14天及第21天觀察藻體在不同溫度下之生長情形。 The 74C algae were isolated and purified at 25 ° C, and then subjected to long-term subculture at 20 ° C. In order to test the growth tolerance of 74C strains at different culture temperatures, appropriate algae were inoculated on multiple C medium plates and cultured at 30 ° C, 35 ° C, 37 ° C and 40 ° C, respectively. Then, the growth of the algal bodies at different temperatures was observed on the 14th day and the 21st day of the culture, respectively.
5.2 培養pH值 5.2 Culture pH
製備pH4~pH9.5之液態C培養基,分別取適量藻體接種於含有不同pH值之液態C培養基中,在25℃下進行照光培養,分別於培養第1天及第14天觀察藻體在不同pH值下之生長情 形。 The liquid C medium with pH 4~pH9.5 was prepared, and the appropriate amount of algae was inoculated into liquid C medium with different pH values. The light culture was carried out at 25 °C, and the algae were observed on the first and the 14th day of culture. Growth at different pH values shape.
5.3 培養鹽度(鹽度耐受性) 5.3 Culture salinity (salt tolerance)
製備含有0%(w/v)~4%(w/v)NaCl之液態C培養基,取適量藻體分別接種於各鹽度之液態培養基中,在25℃下進行照光培養,分別於培養第1天及第14天觀察藻體在不同鹽度下之生長情形。 Prepare a liquid C medium containing 0% (w/v) ~ 4% (w / v) NaCl, and take an appropriate amount of algae inoculated in liquid medium of each salinity, and illuminate at 25 ° C, respectively. The growth of algal bodies at different salinities was observed on day 1 and day 14.
5.4. 藻體貼附培養 5.4. Algae attachment culture
觀察74C藻株於8種不同材質之載體上之生長貼附情形。所測試之載體包含:(1)纖維濾紙;(2)棉布a;(3)濾布;(4)木漿布;(5)棉布b;(6)不織布;(7)牛仔布;及(8)碎花布。將不同載體分別與74C藻株置於含有50mL C培養基之250mL錐形瓶中,以75rpm之轉速共同振盪培養21天後,將載體取出觀察藻體之貼附情形,並將貼附於載體上之藻體以Nile red染色,室溫靜置10分鐘後,以螢光顯微鏡觀察。 The growth and attachment of the 74C strain on the carrier of 8 different materials was observed. The carrier tested comprises: (1) fiber filter paper; (2) cotton cloth a; (3) filter cloth; (4) wood pulp cloth; (5) cotton cloth b; (6) non-woven fabric; (7) denim; 8) Floral cloth. The different vectors and 74C strains were placed in a 250 mL Erlenmeyer flask containing 50 mL of C medium, and shake-cultured at 75 rpm for 21 days. The carrier was taken out to observe the attachment of the algae and attached to the carrier. The algae were stained with Nile red, allowed to stand at room temperature for 10 minutes, and observed under a fluorescent microscope.
6.藻體分析 6. Algal analysis
6.1 藻體含油量分析 6.1 analysis of algae oil content
收集藻體後將其冷凍乾燥成藻粉,秤取定量之藻粉,萃取其油脂。油脂萃取方法參考Folch等人的方法(Folch,J.et al.,A simple method for the isolation and purification of total lipids from animal tissue.,J.Bio.Chem.,1957,23:497-509)並經修飾來進行,其過程為將30mg冷凍乾燥的藻粉(A值)置入2mL微量離心管,加入約2.0mL氯仿/甲醇(v:v=2:1)與適量大顆玻璃珠,以撞擊式細胞破碎儀(Retsch® MM400)振盪約5分鐘,重複兩次。以10,000rpm離心5分鐘後,取出上清液並將其加入拋棄式15mL離心管中,隨即於2mL微量離心管內加入約2.0mL氯仿/甲醇(v:v=2:1),再以超音波振盪與離心處理,取出上清
液並將其加入另一拋棄式15mL離心管中,重複上述萃取離心步驟直到萃取液無色為止。於裝有萃取液的15mL離心管中加入等體積的145mM NaCl溶液後,以試管旋轉混合器混和均勻後,經離心管在4,500rpm下離心10分鐘。以玻璃吸管取下層液體到已秤重的玻璃瓶(B值)中。將此玻璃瓶內液體隔夜風乾再秤重(C值),計算藻乾含油量的百分比(D值)。藻乾含油量計算公式:
6.2 脂肪酸圖譜分析 6.2 Fatty acid map analysis
刮取適量乾燥藻體置於玻璃試管中,加入1mL溶液I(NaOH 45g、甲醇150mL及ddH2O 150mL),震散藻體。於100℃加熱5分鐘,再將所有藻體震散,繼續加熱25分鐘。加入2mL溶液II(6N HCl 325mL及甲醇200mL),於80℃加熱10分鐘,完成後迅速冷卻。再加入1.25mL溶液III(己烷200mL及三級丁基甲基醚200mL),緩慢混合10分鐘,以玻璃吸管尖吸取下層液體並丟棄。將上層液體加入3mL溶液IV(NaOH 10.8g及ddH2O 900mL),混合5分鐘後,吸取上層液體並將上層液體以GC/MS(HP 5973 GC/MS System)分析其脂肪酸含量。GC/MS分析方法參考2007年Valencia,I.等人的方法(Valencia,I.et al.,Development of dry fermented sausages rich in docosahexaenoic acid with oil from the microalgae Schizochytrium sp.:Influence on nutritional properties,sensorial quality and oxidation stability.,Food Chem.,2007,104:1087-1096)。GC/Mass分析條件為:毛細管管柱:SP-2560,75m x 0.18mm I.D.,0.14μm;注入口温度:250℃; 離子源温度:FID 250℃;管柱烘箱溫度:起始溫度140℃,保持5分鐘後以4℃/min之昇温速率昇温至240℃,保持2分鐘;載送氣體:氦;管柱流量:40cm/sec@175℃;待分析樣品注射體積:1μL;分流比:1/100;脂肪酸標準品:37-Component FAME Mix(Cat.18919-1AMP,Sigma-Aldrich)。 A proper amount of dry algae was scraped and placed in a glass test tube, and 1 mL of solution I (NaOH 45 g, methanol 150 mL, and ddH 2 O 150 mL) was added to shake the algae. Heat at 100 ° C for 5 minutes, then shake all the algae and continue heating for 25 minutes. 2 mL of Solution II (6N HCl 325 mL and methanol 200 mL) was added, and the mixture was heated at 80 ° C for 10 minutes, and then rapidly cooled. Further, 1.25 mL of Solution III (200 mL of hexane and 200 mL of tertiary butyl methyl ether) was added, and the mixture was slowly mixed for 10 minutes, and the lower layer liquid was sucked by a glass pipette tip and discarded. The upper liquid was added to 3 mL of solution IV (NaOH 10.8 g and ddH 2 O 900 mL), and after mixing for 5 minutes, the supernatant liquid was taken up and the upper layer liquid was analyzed for its fatty acid content by GC/MS (HP 5973 GC/MS System). GC/MS analysis method reference to the method of Valencia, I. et al ., 2007 (Valencia, I. et al ., Development of dry fermented sausages rich in docosahexaenoic acid with oil from the microalgae Schizochytrium sp.: Influence on nutritional properties, sensorial quality And oxidation stability., Food Chem ., 2007, 104: 1087-1096). The GC/Mass analysis conditions were: capillary column: SP-2560, 75m x 0.18mm ID, 0.14μm; inlet temperature: 250°C; ion source temperature: FID 250°C; column oven temperature: initial temperature 140°C, After 5 minutes, the temperature was raised to 240 ° C at a heating rate of 4 ° C / min for 2 minutes; carrier gas: helium; column flow: 40 cm / sec @ 175 ° C; sample to be analyzed injection volume: 1 μL; split ratio : 1 / 100; fatty acid standard: 37-Component FAME Mix (Cat. 18919-1 AMP, Sigma-Aldrich).
6.3 油脂組成分析 6.3 Analysis of oil composition
將6.1所萃取的藻油樣品以HPLC分析其油脂組成。HPLC分析條件:分離管柱為德國Merck公司製造之Silica gel(4.6mm id×250mm,顆粒大小5μm);沖提溶劑A為己烷;沖提溶劑B為己烷/乙酸乙酯/異丙醇(80:10:10(v/v));在0分鐘溶劑A/B為98:2(v/v),在8分鐘線性增加至溶劑A/B為50:50(v/v),在8.5分鐘線性增加至溶劑A/B為2:98(v/v),15分鐘維持相同梯度,20分鐘線性減少至溶劑A/B為98:2(v/v);流速:1.2mL/min;蒸發光散射檢測器(Evaporative Light Scattering Detector;ELSD)條件:氣體流量2.6L/min;蒸發器溫度為40℃(詹國靖等人,以甘油與植物油利用脂解酶之轉酯化反應生產1,3-雙醯甘油。台灣農業化學與食品科學,2010,45:19-25)。 The 1:1 extracted algal oil sample was analyzed for its oil composition by HPLC. HPLC analysis conditions: Separation column was Silica gel (4.6 mm id × 250 mm, particle size 5 μm) manufactured by Merck, Germany; solvent A was hexane; solvent B was hexane / ethyl acetate / isopropanol (80:10:10 (v/v)); solvent A/B was 98:2 (v/v) at 0 minutes, linearly increased to solvent A/B of 50:50 (v/v) at 8 minutes, Linear increase to 8.5 minutes at solvent A/B of 2:98 (v/v), maintaining the same gradient for 15 minutes, linear reduction to 20:00 for solvent A/B of 98:2 (v/v); flow rate: 1.2 mL/ Min; Evaporative Light Scattering Detector (ELSD) conditions: gas flow rate 2.6L / min; evaporator temperature is 40 ° C (Zhan Guojing et al, glycerol and vegetable oil using lipolytic enzymes to produce esterification reaction 1 , 3-biguanide glycerol. Taiwan Agricultural Chemistry and Food Science , 2010, 45: 19-25).
7.藻體貼附培養之生物質產率及產油效率分析 7. Analysis of biomass yield and oil production efficiency of algae-attached culture
將74C藻株以懸浮培養之方式大量培養後,將藻液濃度調整至其吸光值(OD682nm)為0.5,再取30mL藻液,以抽氣過濾的方式將藻體固定於乾燥並完成稱重的0.45μm之硝酸纖維/乙基纖維膜表面,製備2份固定化之藻體。製作1份空白組(含未進行貼附生長的藻體)直接進行冷凍乾燥,扣除濾紙乾重(WP)後,作為培養前之藻體乾重(WAI)。取經無菌處理過之吸水載體(如海棉、厚濾紙...等),置於無菌平板底部,加入適量液態C培養基使其維持濕潤,再將含固定化 藻體之濾紙平放至吸水載體上方,將平板置於夾鏈袋中防止水份蒸發流失,於30℃下進行24小時照光培養。培養14天後,將含固定化藻體之濾紙自平板中取出,以冷凍乾燥方式將藻體乾燥後,稱重,並扣除濾紙乾重,作為培養後之藻體乾重(WAF)。完成藻體稱重後,將藻體自載體表面刮下進行含油量分析,記錄貼附藻體含油量(OCA)。計算藻體生物質產率及油脂含量之計算公式為:PAB=(WAF-WAI)/A/T PAO=OCA×PAB After the 74C strain was cultured in a large amount in a suspension culture, the concentration of the algae solution was adjusted to an absorbance (OD 682 nm ) of 0.5, and then 30 mL of the algae solution was taken, and the algae body was fixed to dryness by air filtration and finished. On the surface of a 0.45 μm nitrocellulose/ethyl fiber membrane, 2 parts of immobilized algae were prepared. One blank group (including algae which had not been attached for growth) was directly subjected to freeze-drying, and the dry weight (W P ) of the filter paper was subtracted, and the dry weight (W AI ) of the algae before the culture was used. Take aseptically treated water-absorbing carrier (such as sponge, thick filter paper, etc.), place it on the bottom of the sterile plate, add appropriate amount of liquid C medium to keep it moist, and then place the filter paper containing immobilized algae on the water-absorbing carrier. On the top, the plate was placed in a zipper bag to prevent evaporation of water, and the light was cultured at 30 ° C for 24 hours. After 14 days of culture, the filter paper containing the immobilized algal body was taken out from the plate, and the algae body was dried by freeze-drying, weighed, and the dry weight of the filter paper was subtracted as the dry weight of the algae (W AF ) after the cultivation. After the algae body was weighed, the algae body was scraped off from the surface of the carrier to analyze the oil content, and the oil content (OC A ) of the attached algae body was recorded. The calculation formula for calculating the biomass yield and oil content of algae is: P AB = (W AF - W AI ) / A / TP AO = OC A × P AB
PAB:貼附培養之藻體生物質產率(g/m2/日) P AB : biomass yield of algae in attached culture (g/m 2 /day)
PAO:貼附培養之藻體油脂產率(g/m2/日) P AO : yield of algae oil in attached culture (g/m 2 /day)
WAF:藻體貼附培養後之乾重(g) W AF : dry weight of algae attached to culture (g)
WAI:藻體貼附培養前之乾重(g) W AI : dry weight of algae attached to culture (g)
A:藻體貼附培養之面積(m2) A: Area of algae attachment culture (m 2 )
T:藻體貼附培養之天數(日) T: days of algae attachment culture (day)
OCA:貼附培養之藻體含油量(%)(w/w) OC A : oil content (%) (w/w) of the cultured algae
8.藻體懸浮培養之生物質產率、產油效率分析及固碳效率分析 8. Biomass yield, oil production efficiency analysis and carbon sequestration efficiency analysis of algae suspension culture
將適量藻體放入含有1L之C培養基的1L血清瓶中,調整其培養液之吸光值(OD682nm)達約0.5後,先取50mL液,以抽氣過濾方式收集藻體,並將藻體冷凍、烘乾及秤重(作為藻體生長的起始點WAI)。之後置於二氧化碳固碳篩選平台,以體積為1L之藻液進行監測。固碳篩選平台以通氣量為0.1vvm持續通入5%(v/v)二氧化碳至潛力藻株之藻液中,再利用二氧化碳自動監測系統持續監測進流及出流之二氧化碳濃度(濃度單位為%,1%=10,000ppm),經由氣體濃度轉換公式之計算將二氧化碳濃度單位轉換為mg/m3,計算每日固定二氧化碳毫克數(Ya-jun H.,Brief Discussion on Conversion Coefficient between the Concentration Units ppm and mg/m3 of Nitrogen Oxides(NOX).,Sichuan Environment,2010,29(1):24-46)。30℃照光培養後,取50mL藻液(四重複,共取200mL液),以抽氣過濾方式收集藻體,並將藻體冷凍、烘乾及秤重(作為藻體生長的終點WAF)。另,完成藻體稱重後,將藻體自載體表面刮下進行藻乾含油量分析,記錄其藻乾含油量(OCA)。 Place an appropriate amount of algae in a 1 L serum bottle containing 1 L of C medium, adjust the absorbance (OD 682 nm ) of the culture solution to about 0.5, then take 50 mL of the solution, collect the algae by suction filtration, and add the algae. Freeze, dry and weigh (as the starting point for algae growth W AI ). After that, it was placed on a carbon dioxide carbon sequestration screening platform and monitored with a 1 L volume of algae solution. The carbon sequestration platform continuously feeds 5% (v/v) carbon dioxide into the algae liquid of the potential algae strain with aeration of 0.1vvm, and continuously monitors the influent and outflow carbon dioxide concentration by using the carbon dioxide automatic monitoring system (concentration unit is %, 1% = 10,000 ppm), convert the carbon dioxide concentration unit to mg/m 3 by calculation of the gas concentration conversion formula, and calculate the daily fixed carbon dioxide milligrams (Ya-jun H., Brief Discussion on Conversion Coefficient between the Concentration Units Ppm and mg/m 3 of Nitrogen Oxides (NO X )., Sichuan Environment, 2010, 29(1): 24-46). After incubation at 30 ° C, take 50 mL of algae solution (four replicates, take a total of 200 mL of liquid), collect the algae by suction filtration, and freeze, dry and weigh the algae (as the end point of algae growth W AF ) . In addition, after the algae body was weighed, the algae body was scraped off from the surface of the carrier to analyze the oil content of the algae, and the oil content (OC A ) of the algae was recorded.
二氧化碳氣體濃度轉換之計算公式:濃度(mg/m3)=濃度(ppm)×(分子量/22.4)×[273/(273+t)] Calculation formula for carbon dioxide gas concentration conversion: concentration (mg/m 3 ) = concentration (ppm) × (molecular weight / 22.4) × [273 / (273 + t)]
分子量(二氧化碳):44.01 Molecular weight (carbon dioxide): 44.01
t:測定溫度(30℃) t: measured temperature (30 ° C)
固碳效率計算公式:R=(Cin-Cout)×V×Q×T Formula for calculating carbon sequestration efficiency: R=(C in -C out )×V×Q×T
R:每日固定毫克數(mg) R: fixed milligrams per day (mg)
V:微藻培養體積(m3) V: microalgae culture volume (m 3 )
Q:氣體通氣量(vvm,volume per volume per minute) Q: gas permeation (vvm, volume per volume per minute)
T:每日通氣時間(分鐘) T: daily ventilation time (minutes)
Cin:二氧化碳進流濃度(mg/m3) C in : carbon dioxide influent concentration (mg/m 3 )
Cout:二氧化碳出流濃度(mg/m3) C out : carbon dioxide outflow concentration (mg/m 3 )
計算藻體生物質產率及產油效率之計算公式為:PAB=(WAF-WAI)/A/T PAO=OCA×PAB The formula for calculating the biomass yield and oil production efficiency of algae is: P AB =(W AF -W AI )/A/TP AO =OC A ×P AB
PAB:懸浮培養之藻體生物質產率(mg/L/日) P AB : algal biomass yield in suspension culture (mg/L/day)
PAO:懸浮培養之藻體油脂產率(mg/L/日) P AO : oil yield of algae in suspension culture (mg/L/day)
WAF:藻體懸浮培養後之乾重(mg) W AF : dry weight (mg) after suspension culture of algae
WAI:藻體懸浮培養前之乾重(mg) W AI : dry weight (mg) before suspension culture of algae
A:藻液體積(L) A: algal fluid volume (L)
T:藻體懸浮培養之天數(日) T: days of algae suspension culture (day)
OCA:懸浮培養之藻乾含油量(%)(w/w) OC A : Algae dry oil content in suspension culture (%) (w/w)
9.藻體熱值測定 9. Algae calorific value determination
將74C藻株大量培養後,將藻體收集凍乾後保存。將1g之凍乾藻體置於烘箱,以105℃烘乾2小時後,將烘乾之藻體置於乾燥器中冷卻至室溫後,以天秤記錄藻體烘乾後重量(WHD)。將烘乾後之藻體置入燃燒彈熱卡計內,再置於附有絕熱式燃燒彈夾套之水浴槽中,點火燃燒後,樣品所釋放之燃燒熱,將由外圍水浴槽吸收,紀錄水浴槽上昇之溫度,乘上水及燃燒彈熱卡計水當量之總和,乘上水之比熱,再除以WHD,即可求得樣品之熱值。 After the 74C strain was cultured in a large amount, the algal bodies were collected and lyophilized and stored. 1 g of freeze-dried algae was placed in an oven and dried at 105 ° C for 2 hours. After drying the dried algae in a desiccator and cooling to room temperature, the weight of the dried algae after drying (W HD ) was recorded on the scale. . The dried algae body is placed in a thermal bomb meter and placed in a water bath with an adiabatic incendiary bomb jacket. After ignition and combustion, the combustion heat released by the sample will be absorbed by the peripheral water bath. The temperature of the water bath rises, multiplied by the sum of water and the thermal charge of the incendiary bomb, multiplied by the specific heat of the water, and divided by W HD , the calorific value of the sample can be obtained.
10.藻體灰分測定 10. Algae ash determination
將74C藻株大量培養後,將藻體收集凍乾後保存。將1g之凍乾藻體置入坩鍋,並置於烘箱以105℃烘乾2小時後,將烘乾之藻體置於乾燥器中冷卻至室溫,以天秤記錄乾體烘乾後重量(WAD)。將去除水分之乾藻體樣品及坩鍋置於800±50℃之高溫爐中加熱燃燒3小時,降低爐溫至300℃,將坩鍋及樣品移入乾燥器中冷卻至室溫,秤量燃燒後之殘餘物重量(WASH),將WASH除以WAD即得藻體灰分含量。 After the 74C strain was cultured in a large amount, the algal bodies were collected and lyophilized and stored. 1 g of the freeze-dried algae body was placed in a crucible, and dried in an oven at 105 ° C for 2 hours. The dried algae body was placed in a desiccator and cooled to room temperature, and the weight of the dried body after drying was recorded by Libra ( W AD ). The dried algae sample and the crucible are removed and placed in a high temperature furnace at 800±50°C for 3 hours, the furnace temperature is lowered to 300° C., the crucible and the sample are transferred to a desiccator and cooled to room temperature. The weight of the residue (W ASH ), the W ASH is divided by W AD to obtain the algal ash content.
11.藻體硫分測定 11. Determination of sulfur content in algae
將74C藻體在高溫純氧之環境下燃燒,並將燃燒後所產生含有二氧化碳、水、氮化物及二氧化硫之混合氣體以氦氣輸送至銅還原管中,將氮化物還原成氮氣,其他氣體則依氣體吸附特性分別被不同吸附管中之填充物吸附。氮氣則直接由氦氣輸送至熱傳導偵檢器(Thermal conductivity detector;TCD)檢測其含量。不同的吸附管則以不同之脫附溫度加溫分別脫附出二氧化碳、水及二氧化硫,再將該等成分分別引入熱傳導偵檢器來檢測個別成分之含量,以求得硫之組成百分比。 The 74C algae body is burned in a high-temperature pure oxygen environment, and the mixed gas containing carbon dioxide, water, nitride and sulfur dioxide produced after combustion is sent to the copper reduction tube by helium gas, and the nitride is reduced to nitrogen gas, other gases. According to the gas adsorption characteristics, they are respectively adsorbed by the fillers in different adsorption tubes. Nitrogen is directly sent from the helium gas to the Thermal conductivity detector (TCD) to detect its content. Different adsorption tubes desorb carbon dioxide, water and sulfur dioxide separately at different desorption temperatures, and then the components are respectively introduced into a heat conduction detector to detect the content of individual components to obtain the composition percentage of sulfur.
於台灣嘉義阿里山山區的土壤樣品中分離純化得到74C藻株。以顯微鏡(1,000X)觀察其形態,發現74C藻株以非群聚之單一藻體存在,其中細胞壁外無剛毛狀突起,細胞呈圓形,依其藻體培養天數之不同,細胞直徑約為3~6μm(圖1A)。經Nile Red染色後,以螢光顯微鏡觀察到藻體內部有大量明顯且呈黃色之油滴分佈,顯示其藻體內可以蓄積油滴(圖1B)。 The 74C strain was isolated and purified from soil samples from the Alishan Mountains in Chiayi, Taiwan. The morphology was observed by microscope (1,000X), and it was found that the 74C strain was present in a non-clustered single algae body. There was no bristles outside the cell wall, and the cells were round. According to the number of days of algal culture, the cell diameter was about 3~6μm (Fig. 1A). After staining with Nile Red, a large number of distinct and yellow oil droplets were observed inside the algae by a fluorescence microscope, indicating that oil droplets could accumulate in the algae (Fig. 1B).
將74C藻株之18S rDNA及ITS區域進行DNA定序,分別得到長度1,744bp之18S rDNA序列(SEQ ID NO:1)及長度674bp之ITS序列(SEQ ID NO:2)。將該18S rDNA及ITS序列與NCBI的nr資料庫比對後,發現其與以下5株藻株之序列具最高相似度:(1)Micractinium sp.(Accession No.JX889639.1),相似度為99%;(2)Micractinium sp.CCAP 248/2(Accession No.FR865695.1),相似度為95%;(3)Micractinium pusillum(Accession No.FM205866.1),相似度為95%;(4)Micractinium sp.CCAP 248/7(Accession No.FM205835.1),相似度為95%;及(5)Micractinium pusillum(Accession No.FM205872.1),相似度為95%。 The 18S rDNA and ITS regions of the 74C strain were subjected to DNA sequencing to obtain an 18S rDNA sequence (SEQ ID NO: 1) of length 1,744 bp and an ITS sequence (SEQ ID NO: 2) of 674 bp in length. After comparing the 18S rDNA and ITS sequences with NCBI's nr database, it was found to have the highest similarity to the sequence of the following five strains: (1) Micractinium sp. (Accession No. JX889639.1), the similarity is 99%; (2) Micractinium sp. CCAP 248/2 (Accession No. FR865695.1), similarity is 95%; (3) Micractinium pusillum (Accession No. FM205866.1), similarity is 95%; (4 Micractinium sp. CCAP 248/7 (Accession No. FM205835.1) with a similarity of 95%; and (5) Micractinium pusillum (Accession No. FM205872.1) with a similarity of 95%.
將74C藻株的ITS序列(SEQ ID NO:2)與NCBI的nr資料庫進行比對後,則發現其與以下4株藻株之序列具最高相似度:(1)Chlorella sp.(Accession No.JQ315187.1),相似度為100%;(2)Micractinium sp.(Accession No.JX889639.1),相似度為99%;(3)Micractinium sp.CCAP 211/92(Accession No.FM205863.1),相似度為99%;及 (4)Micractinium sp.(Accession No.JQ710681.1),相似度為98%。 After comparing the ITS sequence of the 74C strain (SEQ ID NO: 2) with the NCBI nr database, it was found to have the highest similarity to the sequence of the following four strains: (1) Chlorella sp. (Accession No) .JQ315187.1), similarity is 100%; (2) Micractinium sp. (Accession No. JX889639.1), similarity is 99%; (3) Micractinium sp. CCAP 211/92 (Accession No. FM205863.1 ), the similarity is 99%; and (4) Micractinium sp. (Accession No. JQ710681.1), the similarity is 98%.
此外,將74C藻株的18S rDNA及ITS區域的DNA序列(全長)經NCBI/Blastn比對分析後,將所得相近的藻株與數個較接近的藻株及藻屬列進行演化樹分析,結果顯示74C被劃分歸屬於Micractinium sp.群組中(圖2)。而在ITS序列的演化樹比對分析中,顯示74C藻株亦被歸屬於Micractinium sp.群組中(圖3)。以上序列比對分析結果顯示,74C藻株可能屬於微芒藻屬(Micractinium)。 In addition, the 18S rDNA of the 74C strain and the DNA sequence (full length) of the ITS region were analyzed by NCBI/Blastn, and the obtained algal strains were analyzed with an evolutionary tree of several closely related algae and algae. The results show that 74C is assigned to the Micractinium sp. group (Fig. 2). In the evolution tree alignment analysis of the ITS sequence, it was shown that the 74C strain was also attributed to the Micractinium sp. group (Fig. 3). The above sequence alignment analysis showed that the 74C strain may belong to the genus Micractinium .
綜合其形態與分子鑑定之結果,初步鑑定74C藻株應屬於Micractinium sp.,且極可能為一新種,故命名為Micractinium sp.74C。 Based on the results of morphological and molecular identification, the 74C strain should be identified as Micractinium sp., and it is likely to be a new species, so it was named Micractinium sp.74C.
(1)培養溫度(耐熱溫度)測試 (1) Culture temperature (heat resistant temperature) test
圖4之結果顯示在30℃至40℃之培養溫度下,74C藻株於C培養基平板上可持續且明顯的生長。據此,74C藻株可生長於約20℃至約40℃之溫度範圍中,且可耐熱生長於約30℃至約40℃之溫度範圍中。 The results in Figure 4 show that the 74C strain was continuously and significantly grown on the C medium plate at a culture temperature of 30 °C to 40 °C. Accordingly, the 74C strain can be grown in a temperature range of from about 20 ° C to about 40 ° C and can be thermally resistant to growth in a temperature range of from about 30 ° C to about 40 ° C.
(2)培養基pH值測試 (2) Medium pH test
圖5之結果顯示74C藻株在pH4至pH9.5之液態C培養基中可持續且明顯的生長。據此,74C藻株可生長在約pH4至約pH9.5之環境中。 The results in Figure 5 show the sustainable and significant growth of the 74C strain in liquid C medium at pH 4 to pH 9.5. Accordingly, the 74C strain can be grown in an environment of from about pH 4 to about pH 9.5.
(3)培養基鹽度測試 (3) Medium salt test
圖6之結果顯示74C藻株在鹽度0%(w/v)至4.0%(w/v)之液態C培養基中,有持續且明顯的生長現象。因此,74C藻株可在0%(w/v)到至少約4.0%(w/v)之鹽度環境下生長。 The results in Fig. 6 show that the 74C strain has a sustained and significant growth phenomenon in liquid C medium having a salinity of 0% (w/v) to 4.0% (w/v). Thus, the 74C strain can be grown from 0% (w/v) to at least about 4.0% (w/v) salinity.
將74C藻株分別與以下8種不同材質之載體共同培養:(1)纖維濾紙、(2)棉布a、(3)濾布、(4)木漿布、(5)棉布b、(6)不織布、(7)牛仔布及(8)碎花布,以測試其貼附性。圖7之結果顯示,74C藻株可貼附 生長於(1)纖維濾紙、(5)棉布b、(6)不織布、(7)牛仔布及(8)碎花布等載體上,其中以(1)纖維濾紙及(8)碎花布的貼附效果最佳。此外,將貼附於各載體上之74C藻體以Nile red染色後,以螢光顯微鏡觀察,發現藻體內有大量的油滴分佈(圖7),故74C藻株極具產油潛力。 The 74C strains were separately cultured with the following carriers of 8 different materials: (1) fiber filter paper, (2) cotton cloth a, (3) filter cloth, (4) wood pulp cloth, (5) cotton cloth b, (6) Non-woven fabrics, (7) denim and (8) floral fabrics were tested for adhesion. The results in Figure 7 show that the 74C strain can be attached. It is grown on (1) fiber filter paper, (5) cotton cloth b, (6) non-woven fabric, (7) denim and (8) floral fabric, etc., among which (1) fiber filter paper and (8) floral cloth The best results are attached. In addition, the 74C algae attached to each carrier was stained with Nile red, and observed by a fluorescent microscope. It was found that there was a large amount of oil droplets distributed in the algae (Fig. 7), so the 74C strain had great potential for oil production.
分別將74C藻株以懸浮及貼附之方式培養,收集其藻體,將其冷凍乾燥成藻粉,秤取定量之藻粉並萃取其中之油脂,分析藻乾含油量、油脂成分及脂肪酸組成。結果顯示,懸浮培養下74C藻乾含油量為47.7%(w/w),貼附培養下74C藻乾含油量為52.08%(w/w)。相較於一般藻株在貼附培養時其藻乾含油量會較懸浮培養時下降至10%以下的情況(Gross,M.& Wen,Z.,Yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm(RAB)cultivation system,Bioresour.Technol.,2014,171:50-58),貼附培養之74C藻乾含油量反而高於懸浮培養之藻乾含油量,此特性顯示74C藻株更適合以貼附方式培養。 The 74C strain was cultured in suspension and attached, and the algae was collected, freeze-dried into algal flour, the quantitative algae powder was weighed and the oil was extracted, and the oil content, oil composition and fatty acid composition of the algae were analyzed. . The results showed that the oil content of 74C algae in suspension culture was 47.7% (w/w), and the oil content of 74C algae in the attached culture was 52.08% (w/w). Compared with the general algae strain, the algae dry oil content in the attachment culture is reduced to less than 10% compared with the suspension culture (Gross, M. & Wen, Z., Yearlong evaluation of performance and durability of a pilot-scale Revolving Algal Biofilm (RAB) cultivation system, Bioresour . Technol ., 2014 , 171:50-58), the oil content of 74C algae in the attached culture is higher than that in the suspension culture, and this characteristic shows that the 74C strain is more Suitable for cultivating by attachment.
表一之油脂組成結果顯示,74C藻株於懸浮培養及貼附培養下的油脂成分組成並無顯著差異,主要以三酸甘油酯(TAG)為主,含量達99.81~99.89%(w/w),其餘則包含少量的1,3-雙醯基甘油酯(1,3-DAG,佔總油脂含量的0.08~0.17%(w/w))及1,2-雙醯基甘油酯(1,2-DAG,佔總油脂含量的0.01~0.02%(w/w)),此組成成分適合作為生質燃料的料源。 The results of oil composition in Table 1 showed that there was no significant difference in the composition of oil and fat in 74C strains under suspension culture and attachment culture, mainly based on triglyceride (TAG), with a content of 99.81~99.89% (w/w). ), the rest contains a small amount of 1,3-bisguanidinoglyceride (1,3-DAG, 0.08~0.17% (w/w) of total oil content) and 1,2-bis-decyl glyceride (1 , 2-DAG, accounting for 0.01~0.02% (w/w) of the total oil content, this component is suitable as a source of biofuel.
表二之脂肪酸組成結果顯示,懸浮培養及貼附培養下之74C藻體脂肪酸組成主要為C16及C18脂肪酸,其中各脂肪酸組成比例相似,C16、C18:1及C18:2脂肪酸含量較高。此外,經計算後,74C藻體所含油脂的不飽和度(DU)為109~116,符合歐盟所定之生質柴油標準值(DU值須小於137)(Ramos,M.J.,et al.,Influence of fatty acid composition of raw materials on biodiesel properties.Bioresour.Technol.,2009,100:261-268)。據此,74C藻株不論以懸浮或貼附方式 培養皆適合作為提煉生質燃料的料源。此外,根據74C藻株所產油脂中脂肪酸之組成及三酸甘油酯之含量,其亦適合作為食用油之料源。 The fatty acid composition results in Table 2 showed that the fatty acid composition of 74C algae in suspension culture and attachment culture was mainly C16 and C18 fatty acids, and the composition ratio of each fatty acid was similar, and the C16, C18:1 and C18:2 fatty acids were higher. In addition, after calculation, the unsaturation (DU) of the oil contained in 74C algae is 109~116, which is in line with the European standard for biodiesel (DU value must be less than 137) (Ramos, MJ, et al ., Influence . of fatty acid composition of raw materials on biodiesel properties Bioresour.Technol, 2009,100:. 261-268). Accordingly, the 74C strain is suitable as a source of refining biomass fuel, whether it is cultured in suspension or attached. In addition, according to the composition of the fatty acid in the oil produced by the 74C strain and the content of the triglyceride, it is also suitable as a source of edible oil.
將74C藻株以纖維濾紙貼附培養,於30℃下24小時照光培養,收集藻體,計算其載體表面之藻體生物質產率及產油效率,其結果顯示以實驗室規模貼附培養下之74C藻體生物質產率最高可達6.7g/m2/日,而產油效率可達1.44g/m2/日。其產油效率高於利用循環微藻生物膜生長系統(RAB)所培養之小球藻株(產油效率為0.27g/m2/日)。 The 74C strain was affixed with fiber filter paper, cultured at 30 ° C for 24 hours, and the algae were collected to calculate the algal biomass yield and oil production efficiency on the surface of the carrier. The results showed that the culture was attached to the laboratory scale. The yield of 74C algae biomass is up to 6.7g/m 2 /day, and the oil production efficiency can reach 1.44g/m 2 /day. The oil production efficiency is higher than that of the chlorella strain cultivated by the circulating microalgae biofilm growth system (RAB) (oil production efficiency is 0.27 g/m 2 /day).
利用二氧化碳固碳效率評估平台進行74C藻株的固碳能力測試,以通氣量為0.1vvm持續通入5%(v/v)二氧化碳至藻液中,再利用二氧化碳自動監測系統持續監測進流及出流之二氧化碳濃度(濃度單位為%,1%=10,000ppm),計算每日固定二氧化碳毫克數。以30℃懸浮培養後,收集藻體分析,結果顯示74C藻體生物質產率、油脂產率及固碳效率分別為100.4mg/L/日、45.7mg/L/日及508mg/L/日。 The carbon sequestration efficiency of the 74C strain was tested using a carbon dioxide carbon sequestration efficiency evaluation platform, and 5% (v/v) carbon dioxide was continuously supplied to the algae solution at a ventilation rate of 0.1 vvm, and the inflow was continuously monitored using an automatic carbon dioxide monitoring system. The concentration of carbon dioxide in the outflow (concentration in %, 1% = 10,000 ppm), and the number of milligrams of fixed carbon dioxide per day is calculated. After suspension culture at 30 ° C, the collected algal body analysis showed that the 74C algal biomass yield, oil yield and carbon sequestration efficiency were 100.4 mg / L / day, 45.7 mg / L / day and 508 mg / L / day, respectively. .
將74C藻株大量培養後,收集藻體,冷凍乾燥成藻粉,秤取定量之藻粉並量測其熱值、灰分及硫分。表三之結果顯示藻粉熱值達25.41MJ/Kg,灰分及硫分含量則分別為2.07%(w/w)及0.362%(w/w)。此外,相較於目前發電廠所使用之燃煤煙煤及亞煙煤,74C藻株的灰分及硫分僅為發電廠燃煤採購標準的13.8%(w/w)及32.9%(w/w)。而相較於雜草、豆桿或稻草等生質燃料(王岱淇及馮丁樹,農產品廢棄物焚化物性之研究,農業機械學刊,1993,2:1-11),74C藻株不僅熱值含量高,亦具有較低之灰分含量。以上結果可證明,74C藻株亦可作為一優質生質燃料(如生質煤炭)的料源,且可大幅減少污染物生成以減少環境污染。 After the 74C strain was cultured in large amounts, the algal bodies were collected, freeze-dried to algal flour, and the quantitative algal flour was weighed and the calorific value, ash and sulfur were measured. The results in Table 3 show that the algae powder has a calorific value of 25.41 MJ/Kg, and the ash and sulfur contents are 2.07% (w/w) and 0.362% (w/w), respectively. In addition, compared with the coal-fired bituminous coal and sub-bituminous coal used in the current power plants, the ash and sulfur content of the 74C strain are only 13.8% (w/w) and 32.9% (w/w) of the coal-fired coal procurement standards. . Compared with biomass fuels such as weeds, bean stems or straw (Wang Yuqi and Feng Dingshu, research on incineration of agricultural wastes, Journal of Agricultural Machinery, 1993, 2:1-11), 74C strains have high calorific value. It also has a lower ash content. The above results prove that the 74C strain can also be used as a source of high-quality biomass fuel (such as raw coal), and can significantly reduce the generation of pollutants to reduce environmental pollution.
本發明首先發現經初步鑑定為Micractinium sp.之微芒藻屬分離株74C。該藻株可生長在溫度約20℃至約40℃、約pH4至約pH9及鹽度0%(w/v)到至少約4%(w/v)之環境中,且具備良好的貼附特性,可貼附生長於不同材質之載體上。此外,74C藻株在懸浮培養下之藻乾含油量為47.7%(w/w),在貼附培養下所形成之生物膜中的藻乾含油量為52.08%(w/w),其反而高於懸浮培養之藻乾含油量。在貼附培養下,74C藻體之生物質產率及產油效率分別為6.7g/m2/日及1.44g/m2/日;而在懸浮培養下,74C藻體之生物質產率、油脂產率及固碳效率分別為100.4mg/L/日、45.7mg/L/日及508mg/L/日。此外,不論是以懸浮培養或貼附培養之方式培養,74C藻體三酸甘油酯含量佔油脂總含量的99%(w/w)以上,其中脂肪酸組成以C16及C18脂肪酸為主,脂肪酸不飽和度為109~116。進一步分析發現,74C藻體具備生物炭特性,其熱值為25.41MJ/Kg,灰分及硫分含量分別為2.07%(w/v)及0.362%(w/v)。上述結果顯示,74C藻株(Micractinium sp.)具有形成生物膜之特性,可以貼附培養之模式來培養;具有高優質之藻油組成,可作為生產生質柴油及食用油之料源;具有固碳之能力,可減少環境中之二氧化碳達到環境減廢之作用;並因為具有低灰分及低硫分之特 性,可作為生質燃料的料源,並可大幅減少污染物生成以降低環境污染。 The present invention firstly found a micromania sp. isolate 74C which was initially identified as Micractinium sp. The strain can be grown in an environment having a temperature of from about 20 ° C to about 40 ° C, from about pH 4 to about pH 9 and from 0% (w/v) to at least about 4% (w/v), with good adhesion. Features can be attached to carriers grown on different materials. In addition, the oil content of the dried algae of the 74C strain in suspension culture was 47.7% (w/w), and the oil content of the algae in the biofilm formed by the attachment culture was 52.08% (w/w), which instead Higher than the oil content of the algae in suspension culture. Under the attachment culture, the biomass yield and oil production efficiency of 74C algae were 6.7g/m 2 /day and 1.44g/m 2 /day, respectively, while the biomass yield of 74C algae in suspension culture The oil yield and carbon sequestration efficiency were 100.4 mg/L/day, 45.7 mg/L/day and 508 mg/L/day, respectively. In addition, regardless of whether it is cultured by suspension culture or attachment culture, the content of triglyceride in 74C is more than 99% (w/w) of the total content of oil and fat, and the fatty acid composition is mainly C16 and C18 fatty acids, and fatty acids are not. The saturation is 109~116. Further analysis showed that the 74C algae had biochar characteristics, and its calorific value was 25.41 MJ/Kg, and the ash and sulfur contents were 2.07% (w/v) and 0.362% (w/v), respectively. The above results show that the 74C strain ( Micractinium sp.) has the characteristics of forming a biofilm and can be cultured in a mode of cultivation; it has a high-quality algae oil composition and can be used as a source of raw diesel oil and edible oil; The ability to fix carbon can reduce the role of carbon dioxide in the environment to reduce environmental pollution; and because of its low ash and low sulfur content, it can be used as a source of biofuels and can significantly reduce pollutant generation to reduce environmental pollution. .
國內寄存資訊 Domestic deposit information
財團法人食品工業發展研究所,2017年1月24日,BCRC 980044。 Food Industry Development Institute, January 24, 2017, BCRC 980044.
國外寄存資訊 Foreign deposit information
中國,中國典型培養物保藏中心,2016年12月12日,CCTCC M 2016743。 China, China Type Culture Collection, December 12, 2016, CCTCC M 2016743.
<110> 財團法人食品工業發展研究所 <110> Food Industry Development Research Institute
<120> 微芒藻屬(MICRACTINIUM SP.)及其用途 <120> MICRACTINIUM SP. and its use
<130> 294 <130> 294
<160> 2 <160> 2
<170> PatentIn version 3.5 <170> PatentIn version 3.5
<210> 1 <210> 1
<211> 1744 <211> 1744
<212> DNA <212> DNA
<213> 微芒藻屬(Micractinium sp.) <213> Micractinium sp.
<220> <220>
<221> 18S rDNA <221> 18S rDNA
<222> (1)..(1744) <222> (1)..(1744)
<400> 1 <400> 1
<210> 2 <210> 2
<211> 728 <211> 728
<212> DNA <212> DNA
<213> 微芒藻屬(Micractinium sp.) <213> Micractinium sp.
<220> <220>
<221> ITS <221> ITS
<222> (1)..(728) <222> (1)..(728)
<400> 2 <400> 2
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GenBank: JX889639.1, https://www.ncbi.nlm.nih.gov/nuccore/429489009,2012/12/17. |
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