文章信息
- 马泽林, 刘家亨, 黄序, 财音青格乐, 朱宏吉.
- MA Ze-lin, LIU Jia-heng, HUANG Xu, CAIYIN Qing-gele, ZHU Hong-ji.
- 微生物利用木质纤维素的研究进展
- Research Progress on Utilization of Lignocellulosic Biomass by Microorganisms
- 中国生物工程杂志, 2017, 37(6): 124-133
- China Biotechnology, 2017, 37(6): 124-133
- http://dx.doi.org/DOI:10.13523/j.cb.20170618
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文章历史
- 收稿日期: 2017-03-20
- 修回日期: 2017-04-17
2. 系统生物工程教育部重点实验室 天津 300072;
3. 天津化学化工协同创新中心合成生物学平台 天津 300072;
4. 中粮营养健康研究院 北京 102209
2. Key Laboratory of Systems Bioengineering, Ministry of Education, Tianjin 300072, China;
3. Syn Bio Research Platform, Collaborative Innovation Center of Chemical Science and Engineering, Tianjin 300072, China;
4. China Oil & Foodstuffs Corporation(COFCO Nutrition and Health Research Institute, Beijing 102209, China
目前,工业上多以玉米、甘蔗等可食用生物质作为原料进行微生物发酵生产乙醇、乳酸及多元醇类等化学物质。这些化学物质的大量需求,造成了全球范围内粮食价格的上涨。为了避免未来发生人与化学品共同竞争食用生物质资源的问题,寻找可替代的,资源丰富的原材料是解决问题的关键[1]。木质纤维素广泛存在于林业及农业废弃物中,全球每年的木质纤维素产量约为100亿吨,我国每年可利用的木质纤维素也在7.5亿吨左右[2]。常见木质纤维素包括玉米秸秆、柳枝稷、甜菜浆、柑橘皮、木材及造纸废弃物等,是尤为丰富且价格低廉的可再生资源[3]。木质纤维素经糖化后的水解产物中含有葡萄糖、木糖及阿拉伯糖等大量的糖类[4-5],这些糖类可以作为微生物发酵生产化学品的碳源。利用可再生木质纤维素生物质资源制备化学品对我国可持续发展具有重要意义。然而,在微生物发酵木质纤维素的过程中,很多问题亟待解决:如木质纤维素预处理工艺、微生物对水解液中木糖的充分利用、碳代谢抑制影响微生物对复杂碳源的选择性利用及微生物对水解液中发酵抑制物的耐受性等问题。这些问题严重限制了木质纤维素大规模替代可食用生物质作为微生物发酵原料的发展[6-9]。本文综述了近年来国内外针对这几个关键问题的最新研究成果,能够为今后微生物高效利用木质纤维素为底物发酵生产化学品的大规模生产提供有价值的参考。
1 木质纤维素预处理工艺的研究木质纤维素的开发利用分为两步,首先木质纤维素被水解处理成可发酵糖类,糖类被微生物发酵后进一步转化为生物燃料和化学品。木质纤维素材料中聚合物的多样性导致每一种材料最后转化的糖类都有所不同,因此对于底物的选择是第一要素。其次,木质纤维素主要由纤维素,半纤维素和木质素组成,有效降解木质素的网状结构,破坏纤维素的结晶度能够提高水解效率[10-11],因此选择正确的预处理工艺尤为关键。目前木质纤维素常用的预处理方法可分为三大类,即物理法、化学法和生物法。物理法通常会用碾磨的方法来降低木质纤维素的颗粒大小和结晶度;化学法处理木质纤维素是通过添加化学溶剂来破坏纤维素半纤维素及木质素的结晶结构,使其发生化学反应降解,常见的化学法有酸处理,碱处理,臭氧分解,CO2处理及SO2催化蒸汽爆破等。生物法处理主要通过微生物对底物的氧化来去除木质素[12]。我们实验室[13]首次用酸法和碱法处理菌糠,并进一步提出了酸碱混合预处理的方法,有效降低了传统处理过程中造成的环境污染,同时提高了菌糠转化可发酵糖的经济性[14]。在很多情况下采用多种处理技术组合的方式来提高生物质转化效率,如稀酸-蒸汽爆破组合,微生物-蒸汽组合,微波辅助酸碱预处理等[15]。除此之外,等离子体处理法是一种新兴的处理技术,该技术利用电能形成高活性的离子化气体,破坏木质纤维素复杂的结构。与传统处理工艺相比,该技术操作方法简单,绿色环保,同时使后续的酶处理效率更高[16]。表 1介绍了常见的等离子体处理方法,根据处理介质的不同分为氮气(空气),臭氧和氩等离子体处理法。预处理后常用纤维素酶及半纤维素酶对木质纤维素进行酶解,得到多种糖类。针对不同处理及酶解过程产生的抑制物等影响因素,一般会选择分步糖化法或同步糖化发酵法作为木质纤维素处理及发酵过程的工艺方法,以降低木质纤维素的预处理和酶解过程产生的发酵抑制物对后续微生物发酵造成的影响[17]。
2 提高微生物木糖利用能力的研究
在木质纤维素中葡聚糖为主要多糖,占总糖含量的33%~51%(干重)。虽然不同木质纤维素中木聚糖含量多有不同,但是木聚糖的糖含量在总糖含量中的比重很高,如在软木中木聚糖含量约占10%[24-25],在硬木及农作物废弃物中约占25%[26-27]。因此,有效发酵木质纤维素水解液可以显著提高最终化学品的产量[24]。常见发酵木质纤维素的微生物有大肠杆菌Escherichia coli等细菌及酵母菌属如酿酒酵母Saccharomyces cerevisiae。木质纤维素水解液中的己糖如葡萄糖、半乳糖和甘露糖可以被菌株有效地代谢利用,而戊糖如木糖和阿拉伯糖等却很难被菌株利用,并且木糖是木质纤维素水解液中含量第二丰富的糖类,也是生物合成木糖醇等化学品的重要原料。因此,提高菌株对木糖的利用是很有必要的。
微生物代谢工程可以提高产品的产量及生物转化效率,并且微生物代谢工程生产化合物并不局限于利用原始菌株生产,通过对具有其他高耐受性,生长速度快等优势的菌株的生物合成途径进行设计和改造,能够使各种微生物都能利用廉价的木质纤维素原料生产高产量的生物燃料或其他有价值的化学品[28]。
2.1 木糖代谢途径改造对菌株原始的木糖代谢途径的深入研究可以更加有针对性地利用代谢工程的方法提高微生物对木糖的利用能力。如图 1所示,在酵母及丝状真菌中,进入胞内的木糖首先在木糖还原酶(xylose reductase,XR)的作用下转化为木糖醇,随后通过木糖醇脱氢酶(xylitol dehydrogenase,XDH)转化成木酮糖,最后经过木酮糖激酶(xylulokinase)的催化形成木酮糖-5-磷酸从而进入戊糖磷酸途径[29-30]。在大肠杆菌等常见细菌中,木糖可以直接经过木糖异构酶(xylose isomerase,XI)作用形成木酮糖后经过木酮糖激酶的催化作用形成木酮糖-5-磷酸进入戊糖磷酸途径。除此之外,在乳酸乳球菌Lactococcus lactis[31]中还存在有磷酸转酮酶途径,该途径中的木酮糖-5-磷酸裂解成甘油醛-3-磷酸和乙酰磷酸,继而进入糖酵解途径。关于优化木糖代谢相关途径以提高微生物对木糖的利用已经在工业菌株发酵木糖的研究中多有报道(表 2)。早在1988年,Chang等[32]就通过同源表达木酮糖激酶基因提高木酮糖进入戊糖磷酸途径以促进微生物对木糖的利用。近年来,也有报道通过提高戊糖磷酸途径中相关基因的表达量来增强木糖的代谢[33]。Jin等[34]研究了丙醇丁醇梭杆菌中分别编码转醛酶Tal、转酮醇酶TKL、5-磷酸核酮糖异构酶RPE和核糖-5-磷酸异构酶RPI的4个参与戊糖磷酸系统的关键基因,这些基因的过表达使重组菌株的木糖利用能力显著提高,并且比原始菌株的ABE(丙醇,丁醇,乙醇)产量提高42%。Zhou等[35]通过异源表达来自瘤胃壶菌中的木糖异构酶(XYLA)和树干毕赤酵母的木酮糖激酶(XYL3) 并强化非氧化戊糖磷酸途径,最终得到的菌株在厌氧条件下的生长率、木糖消耗率及乙醇产量均有明显提高。我们实验室目前研究通过表达木糖调控因子基因xylR提高乳酸乳球菌对木糖的利用能力,与原始菌株相比,最终工程菌的木糖消耗可以提高2.5倍。
2.2 非磷酸化途径改造
作为细胞代谢的中枢,三羧酸循环伴随着多种氨基酸和化学品的产生。传统意义上来说,碳代谢流进入三羧酸循环的途径包括糖酵解途径及戊糖磷酸途径,这两条途径的代谢过程包括十多步反应并且其调控方式非常复杂,如生产丁二醇就需要二十一步反应[36]。这些复杂的代谢过程会降低产物的产率,并且很难通过传统的代谢工程方法提高产量。研究发现有一条特殊的代谢途径可将木质纤维素水解液直接转化成2-酮戊二酸,与糖酵解途径及戊糖磷酸途径相比可减少六步反应。这种代谢途径为:木糖首先被木糖脱氢酶转化成木糖内酯,接着逐步转变成D-木糖酸、2-氢-3-氧-D-木糖酸、2, 5-二氧代戊酸甲酯和2-酮戊二酸。这种木糖氧化途径在1960年首次发现,也称作Weimberg代谢途径[37]。同时,阿拉伯糖也可通过类似的非磷酸化代谢途径转化成2-酮戊二酸,减少进入三羧酸循环的代谢步骤。由于这条途径不包括任何的磷酸化过程,故而可使能量得到更加有效的利用,且通过Weimberg代谢途径生产2-酮戊二酸的理论产量可达到100%,比戊糖磷酸途径产2-酮戊二酸的理论产量(83mol%)要高很多。Radek[38]等研究发现,谷氨酸棒状杆菌通过木糖异构酶途径利用木糖的过程中会产生CO2,造成碳源的浪费。为了避免这种资源浪费,研究外源引入新月丙杆菌中的Weimberg代谢途径,使得该重构菌株可以充分利用碳源生产木糖醇等物质。近年来,通过强化非磷酸化代谢途径以提高菌株利用木糖能力的研究有很多(表 2)。Liu等[39]重构了一条将木糖直接代谢转化成丁二醇的代谢通路,同时为了避免木糖磷酸化,将木糖进入戊糖磷酸途径的关键酶基因xylA敲除。最近,Tai等[40]首次构建一株利用非磷酸化途径同时代谢木质纤维素水解液中的木糖、阿拉伯糖及半乳糖醛酸酯的大肠杆菌,该菌株可生产多种化学物质如琥珀酸、戊烯二酸及谷氨酸等。
3 提高微生物的混糖发酵能力的研究木质纤维素水解液中含有多种己糖和戊糖,如葡萄糖、甘露糖、果糖、木糖和阿拉伯糖等。尽管木质纤维素类生物质具有多样性,木糖和葡萄糖仍然是木质纤维素水解液中最主要的糖类[41]。然而在葡萄糖存在的条件下,大多数微生物会选择将葡萄糖消耗后再继续利用其他糖类。这种调控作用被称为碳代谢抑制(CCR)。CCR是微生物普遍存在的一种全局性调控机制,决定了微生物对复杂碳源的选择性利用[42]。在酵母及不同细菌中的CCR机制完全不同,由于CCR系统的复杂性,构建一株有效利用木质纤维素水解液多种糖类的菌株仍然面临很多挑战(表二)。近年来研究发现,磷酸葡萄糖转移酶系统(PTS)在CCR系统中都起到了主要的作用[43],通过抑制PTS系统减少混糖发酵中的CCR的研究有很多。Jarmander等[44]在可以同时利用木糖与阿拉伯糖的大肠杆菌E. coli AF1000中引入ptsG突变基因以减弱PTS系统的活性,最终工程菌株可以同时利用葡萄糖、木糖和阿拉伯糖。研究表明,CCR通常通过Crp(cAMP受体蛋白),HPr和Mlc[45]诱导排斥进行调控,其中部分调控因子仍然与PTS系统相关,例如在大肠杆菌中Mlc的突变可以减少葡萄糖经过PTS系统的代谢活性,进一步降低了CCR[46]。而HPr基因突变的嗜热厌氧杆菌Thermoanaerobacterium saccharolyticum可同时利用混合糖[47]。同样,将大肠杆菌中的原始基因crp替换成不依赖cAMP基因的突变基因(crp*),在葡萄糖存在下,CRP*蛋白可以诱导xyl系列基因的表达,促使菌株在混糖发酵中提高对木糖的摄取及木糖醇的产量[48]。Groff等[49]对xyl系列基因的进一步研究表明,提高大肠杆菌中xylR的表达量可以缓解阿拉伯糖对木糖的抑制。Wu等[50]首次将厌氧菌丙醇丁醇梭菌Clostridium acetobutylicum CCR的代谢控制蛋白CCPA进行了优化筛选,将CCPA调控CCR依赖的302位缬氨酸替换成天冬酰胺可以缓解CCR的抑制,使菌株在混糖发酵时木糖的消耗由30%增长至90%。
糖在细胞膜上的运输是糖代谢的第一步。近年来对糖转运研究的不断深入,发现糖的转运吸收作用在微生物糖类代谢的过程中起到了关键作用[51]。并且,研究发现在某些条件下木糖的运输速率常常决定了木糖在细胞中代谢的快慢,而葡萄糖的存在会显著降低木糖转运的效果[52]。因此,在含有葡萄糖的混糖发酵过程中引入木糖转运蛋白可以有效避免微生物由于CCR造成的木糖利用率降低的问题。Hector等[53]在酵母中异源表达了拟南芥中的木糖转运蛋白,与原始菌株相比,工程菌在葡萄糖-木糖混糖发酵中对木糖的利用可以提高2.5倍。Khankal等[54]在大肠杆菌中引入了木糖特异性转运蛋白XylE或XylFGH,可以有效提高混糖发酵时对木糖的利用。在热带假丝酵母(Candida tropicalis)中同源表达木糖转运基因At5g17010可以提高对木糖的摄取进而使木糖醇的产量提高25%[55]。然而转运蛋白可能会由于发生错误折叠或不恰当转运使微生物同时利用木糖和葡萄糖的能力减弱,并且大多数糖类转运蛋白对葡萄糖亲和性比对木糖的亲和性要更高。因此,通过提高木糖转运能力实现微生物对于木质纤维素水解液中混糖的利用仍然是一个挑战。
4 提高微生物对木质纤维素水解液耐受能力的研究在木质纤维素的处理及酶解过程中会产生其他的物质。如木质纤维素类生物质在水解过程中半纤维素部分会乙酰化产生乙酸。在高温高压下,己糖脱去水分子转化成羟甲基糠醛(HMF),HMF会进一步降解形成乙酰丙酸和甲酸,同时,木糖被降解成糠醛,若木质纤维素处理的时间过长,糠醛会进一步转化成甲酸。已有研究表明这些物质会影响微生物的生理性质[56-57],如Heer等[58]研究发现HMF及糠醛的存在会降低微生物的生长速度,影响乙醇产量。这些抑制物的抑制作用影响微生物发酵的同时也降低了化学品的生产。
基因工程法改造菌株不仅可以优化代谢途径,也可以提高微生物对抑制物的耐受性。近年来很多研究利用基因工程法可有针对性地提高微生物对木质纤维素水解液中的耐受性(表 2)。Hasunuma等[59]在酿酒酵母中表达毕赤酵母中的转醛醇酶基因及乙醇脱氢酶基因,工程菌在含有70mmol/L糠醛存在的培养基中发酵的乙醇产量是原始菌株的2.3倍。Li等[60]选用可利用木糖的酵母菌在含有木质纤维素水解液中发酵产乙醇,并将对硝基苯酚磷酸酶基因敲除,使转醛醇酶基因过表达,敲除及过表达的协同作用使重构菌株不仅可以耐受三种弱酸的抑制,而且可以提高木糖醇的积累,并最终使乙醇的产量提高[61]。利用进化工程法提高菌株耐受性的研究近年来也日益增加,如Royce等[62]研究用进化工程法在额外添加辛酸的低pH培养基下驯化大肠杆菌MG1655,最终得到的工程菌株不仅对辛酸有耐受性,同时对己酸、癸酸、正丁醇及异丁醇等物质的耐受性均有所提高。Wallace-Salinas等[63]运用进化工程法将酵母在恒温30℃的木质纤维素水解液中进化,构建得到的工程菌株比原始菌株对HMF的耐受能力有明显提高。除上述方法外,近年来,原位抑制物去除方法(ISPR)的应用也较为广泛[64]。另外,也有专利报道表明提高对乙酸的摄取可以增强菌株在木质纤维素酶解液中的耐受性[65-66]。
5 结论与展望近年来微生物利用木质纤维素发酵生产化学品得到了广泛关注并取得了很大的研究进展。然而微生物大规模高效利用木质纤维素生产生物化学品仍然面临诸多挑战。木质纤维素的预处理过程会对后续的其他步骤产生重大影响,并且由于木质纤维素结构的紧密性使其比淀粉类生物质的处理过程要求更加严格。对于酶的选择,糖的产率与抑制物的产生之间的关系也需妥善处理。
微生物的代谢调节或转运蛋白调控会导致木质纤维素水解液中的多种糖类按照葡萄糖优先的原则被微生物消耗[82-83]。尽管近几年提高木糖利用的研究很多,木糖的利用速率仍然次于葡萄糖。因此研究解决微生物混糖发酵过程中的碳代谢抑制问题有很良好的应用前景。木质纤维素水解液中所含的多种抑制物会影响微生物的发酵结果。利用基因的协同作用虽然会提高菌株的耐受性,可是特定基因的过表达也会干扰其他物质的代谢。此外,在葡萄糖作为微生物发酵的主要碳源条件下,依赖ATP的耐受机制会更有效果,然而木质纤维素酶解液中较高的木糖与葡萄糖比例使得高效发酵也变得更加困难[84]。因此,微生物能够在含有高浓度抑制物的环境下有效利用己糖和戊糖作为碳源生产化学品是未来微生物能够大规模高效利用木质纤维素水解液的关键。
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