Abstract
Metabolic and genetic engineering and further other genomics, transcriptomics, and metabolomics tools still need to be further developed to provide more useful information and new ways on enhancing lipid production in oleaginous microorganisms, optimizing fatty acid (FA) profiles, enhancing lipid accumulation, and improving the use of low-cost raw materials as lignocellulosic hydrolysates. Several oleaginous organisms have been described as good lipid producers, being the fast ones the yeasts. However the kinetics for this production is much slower than that required for industrial processes, unless the products are sold at high competitive prices (fine chemicals, cosmetics, and food), covering the costs for the long residential bioreactor times.
Microalgal cultivation in heterotrophic systems is able to use organic carbon sources, sugars, or organic acids, and this cultivation mode offers some advantages over autotrophic cultivation including increased lipid productivity, besides good control of the cultivation process and low cost for harvesting the biomass, since higher cell density is obtained. However, the feasibility of large-scale cultures of microalgae in heterotrophic conditions is still limited by, among other things, the high cost of organic substrates used in this type of cultivation, unless urban/agricultural/industrial wastes are used as lignocellulose and wastewater and sewage are used as carbon or mineral sources.
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1 Introduction
Lignocellulosic biomass is the most abundant raw materials on Earth and is a promising alternative energy source due to their abundance and renewable characteristics. Agro-industrial residues such as sugarcane bagasse (SCB), wheat straw, rice straw, and corn stover represent feedstocks for their conversion into value-added products (Chandel et al. 2012).
Microbial oils, also called single cell oils (SCO), are produced by some oleaginous microorganisms, such as yeast, fungi, bacteria, and microalgae, which are able to accumulate more than 20 % lipids (dry mass) (Ageitos et al. 2011; Karatay and Dönmez 2011). Different lignocellulosic biomasses have been used for microbial oil production, such as wheat straw, corncobs, rice straw, and SCB. SCB seems to be the most promising and competitive in sugarcane-producing lands, due to the availability of large amounts stored in the sugarcane mills after crushing/pressing (Matos 2012). SCB may be an attractive and promising feedstock for microbial oil production to reduce the costs of culture medium, which conventionally hampers the economic feasibility of SCO as alternative feedstock for biodiesel production (Anschau et al. 2014; Tsigie et al. 2011).
Two problems influence SCO production on lignocellulosic hydrolysates. Few oleaginous microorganisms are able to use xylose for SCO production, and as xylose is the second most abundant component of lignocellulose hydrolysates, substantial amounts of feedstock can be lost. Several strains of oleaginous microorganisms have their growth inhibited by small molecules from lignocellulose hydrolysates. Fortunately, it has been observed that some oleaginous strains are able to metabolize xylose for SCO production, without being so much inhibited by the growth inhibitors (Anschau et al. 2014).
Zhao (2005) described the possibility of SCO production from lignocellulose hydrolysates, the biomass-to-biodiesel three-step plan: lignocellulose biomass depolymerization into fermentable sugars, their conversion into microbial lipids by oleaginous microorganisms, and the chemical transformation of their lipids into biodiesel.
2 The Lignocellulosic Biomass
Lignocellulose is a complex polymer of cellulose (40–80 %), hemicellulose (10–40 %), and lignin (5–25 %) (Chandel et al. 2012, Fig. 1). Cellulose, the main fraction of plant cell wall, is linear and crystalline and is a homopolymer of repeating units of glucose linked by β(1-4) glycosidic bonds. Hemicellulose is a highly branched heteropolymer composed of d-xylose, d-arabinose, d-glucose, d-galactose, and d-mannose (Fig. 2). Lignin, formed by polymerization of phenolic compounds, is hydrophobic in nature and is tightly bound to the cellulose and hemicellulose protecting them from microbial and chemical (Sarkar et al. 2012) and enzymatic action (Meng and Ragauskas 2014).
Xylose is the main carbohydrate present in the hemicellulose fraction (second most abundant component of lignocellulose, representing about 80 % of total sugars) (Girio et al. 2010). Potentially, the released carbohydrates, mono- and dimeric sugars, are substrates for the production of value-added products such as ethanol, xylitol, n-butanol, 2,3-butanediol, and lactic acid via microbial fermentation processes (Chandel et al. 2010, 2011, 2012).
The goal of pretreating vegetal biomasses is to remove or modify the lignin (delignification) and to reduce the crystallinity of cellulose (increasing the accessibility to enzymes, which convert carbohydrates into fermentable sugars). The pretreatment of lignocellulose is usually able to hydrolyze the hemicellulose fraction yielding xylose (mostly) and arabinose, mannose, galactose, and glucose in smaller relative concentrations, in addition to the small molecules, also known as microbial growth inhibitors (Meng and Ragauskas 2014; Girio et al. 2010).
There are different types of pretreatment methods such as steam explosion, gamma radiation, acid or alkali treatment, hydrothermal, ammonia, urea, hydrogen peroxide, solvents, milling, and fungal degradation (Girio et al. 2010; Chandel et al. 2010; Kumar et al. 2009; Moretti et al. 2014), being exclusively physical, chemical, physicochemical, biological, or a combination of mechanisms.
The choice of pretreatment depends on the biomass to be used, its composition, and by-products produced. Furthermore, pretreatments need to avoid sugar degradation and minimize the consequent formation of growth inhibitor molecules (Moretti et al. 2014) and significantly affect their costs.
Hydrochloric acid (HCl), phosphoric acid (H3PO4), and sulfuric acid (H2SO4) catalyze the hydrolysis of lignocellulosic materials and are used in two different combinations with the reactor’s temperature, high concentrations of acid and low temperatures or diluted acid concentrations and high temperatures. In our laboratory, we hydrolyzed the SCB with 1.5 % (w/v) H2SO4, solid-to-liquid ratio (1:10) at 120 °C, for 20 min (Fig. 3). Xylose was the major product released (14.3 g/L) by SCB hemicellulosic hydrolysate (H–H) due to its high content of xylan. In addition, glucose and arabinose were found in low concentrations (1.6 and 2.3 g/L, respectively). Glucose was released from the cellulose and hemicellulose fractions, and the arabinose was from the depolymerization of arabino-xylan (a hemicellulosic heteropolymer that contains more xylose than arabinose). Usually, hexose fermenter microorganisms are unable to metabolize pentose sugars and do not tolerate the growth inhibitors generated from the biomass pretreatment (Carvalheiro et al. 2008). The full use of H–H must be understood as a way to reduce waste and to increase the efficiency of conversion of raw material into final products, mainly when value-added products that are obtained improve the economics of the process.
During acid hydrolysis of lignocellulosics, toxic inhibitors to the fermenting microorganism are generated in addition to the sugar monomers. These inhibitors include phenolic compounds, furans (furfural and 5-hydroxymethylfurfural (5-HMF)), and weak acids (acetic acid, formic, levulinic) (Fig. 2). Furfural and 5-HMF are formed by degradation of pentoses and hexoses, respectively. However, the HMF concentration tends to be smaller than furfural due to limited degradation of hexoses in acid saccharification. Acetic acid is formed by hydrolysis of acetyl groups from lignocellulose, as a result of deacetylation of acetylated pentosans, and its generation is mainly dependent on the temperature and residence time of pretreatment with diluted acid (Chandel et al. 2012; Kumar et al. 2009). The formation of the growth inhibitors during the acid hydrolysis depends on multiple factors, including the nature and composition of the lignocellulose, cell wall composition, thermochemical conditions, and reaction time of the hydrolysis (Stoutenburg et al. 2011; Palmqvist and Hahn-Hägerdal 2000a, b). These toxic compounds may affect microbial metabolism hindering the fermentation process (Sangeeta et al. 2014). Their toxicity is the major limiting factor to the bioconversion of lignocellulose, and often they need to be removed from the H–H prior to the fermentation (Stoutenburg et al. 2011). Detoxification methods have been used to reduce the presence of growth inhibitors or to remove them in order to improve their fermentability and increase their biotechnological applications (Chandel et al. 2010; Palmqvist and Hahn-Hägerdal 2000a).
There are several detoxification methods such as physical, chemical, or biological and may be used individually or in combined form. These methods include activated charcoal treatment, neutralization, calcium hydroxide overliming, extraction with solvents, ion exchange resins, evaporation, membrane-mediated detoxification, enzymatic mediated using laccase, lignin peroxidase, in situ microbial detoxification, etc. (Ge et al. 2011; Chandel et al. 2012; Moretti et al. 2014), which will vary depending on the H–H, the type of microorganisms used in the fermentation, and their degree of tolerance to inhibitors. It is important to compare the different methods of treatment in order to select those that provide greater removal of inhibitors and lower reduction of sugar concentrations. For example, activated charcoal and alkali treatment with calcium oxide are chemical methods used to detoxify acid hydrolysates. Calcium oxide treatment causes precipitation of toxic compounds and instability of some inhibitors in high pH, removing furans and phenolic compounds efficiently with a marginal loss of sugars (Chandel et al. 2010). Activated carbon treatment by adsorption is capable of removing acetic acid, furans, phenolic and aromatic compounds, furfural, and HMF with high efficiency coupled with low cost (Chandel et al. 2010, 2011; Stoutenburg et al. 2011).
In our laboratory, we obtained a H–H with 3.6 g/L of acetic acid, 0.02 g/L of HMF, and 0.04 g/L of furfural. The pH was adjusted with CaO without marginal loss of sugars and slight reduction of inhibitors; therefore, the H–H detoxification was considered as unnecessary. The non-detoxified hydrolysate was used for lipid production by Lipomyces starkeyi without appreciable inhibition by the toxic compounds. Furthermore, the yeast consumed or bioreduced the inhibitors during fermentation suggesting that the strain could use these compounds as c Carbon and energy source. High tolerance of L. starkeyi is very interesting for the use of H–H since the detoxification step would not be required in the conditions tested.
Therefore, proper pretreatment methods can increase the relative concentrations of fermentable sugars after enzymatic saccharification, thereby improving the efficiency of the whole process. Enzymatic hydrolysis uses enzyme complexes to depolymerize complex carbohydrates into simple monomers and requires less energy and milder environmental conditions than acid hydrolysis. Enzymatic hydrolysis is carried out by cellulase and hemicellulase enzymes, which cleave the bonds of cellulose and hemicellulose, respectively. Enzymatic hydrolysis shows some advantages such as low toxicity and low corrosion compared to acid or alkaline hydrolysis and does not produce inhibitors (Sarkar et al. 2012). On the other hand, enzymes are costly, require longer time of hydrolysis, and have high loads which limit the economical feasibility of technological processes related to the lignocellulosic biomass. Therefore, an efficient pretreatment is to be selected to decrease cellulose crystallinity and to remove lignin to the maximum extent, so that hydrolysis time as well as cellulase loading will be minimized (Sarkar et al. 2012).
3 Microbial Oil Production from Lignocellulosic Biomass
3.1 Microbial Oil Production by Microalgae
Within the broad microbial diversity, microalgae have potential for lipid production, since many species can be induced to accumulate substantial quantities of lipids within the cell (Malcata 2011). The average lipid content of algal cells varies between 1 and 50 % of dry weight under certain conditions (Meng et al. 2009; Spolaore et al. 2006). Also already it has been known that microalgae could accumulate more lipids with stress treatments such as nitrogen deficiency (Illman et al. 2000). Coelho et al. (2014) working at fed-batch culture with Chlorella, during nitrogen-limited stage, obtained an increase of 38 % in lipid content (from 21 to 29 %) and 26 % in overall lipid productivity (from 1.25 to 1.58 g/L/day).
Microalgae are able to get energy from different metabolisms (Richmond and Qian 2004). In autotrophic metabolism, in the presence of light, organisms are able to convert CO2 and water into biomass. Already heterotrophic systems are a different approach to microalgal biomass production with elimination of light requirement and CO2 absorption.
In heterotrophic cultivation organic carbon sources are used, such as sugars or organic acids, as a source of carbon and energy. This cultivation mode offers several advantages over autotrophic cultivation including increased lipid productivity, besides good control of the cultivation process and low cost for harvesting the biomass because of higher cell density obtained in heterotrophic culture of microalgae. Cell densities as high as 80 g/L (Coelho and Franco 2013) and until 100 g/L (Zheng et al. 2013) have been achieved in heterotrophic systems using glucose as organic carbon source and different feeding strategies. The feasibility of large-scale cultures of microalgae in heterotrophic conditions is still limited by, among other things, the high cost of organic substrates used in this type of cultivation, unless wastes are used as carbon or mineral sources.
In heterotrophic culture, the biosynthesis of products is significantly influenced by medium nutrients, and carbon sources are the most important element for heterotrophic culture of microalgae in the production of lipids. Glucose is most commonly used as carbon source for heterotrophic cultures of microalgae, and far higher rates of growth are obtained with this substrate than with any other. Usually, glucose accounts for most of the medium cost of microalgal cultivation (it was estimated up to 80 %) (Li et al. 2007).
Corn powder hydrolysate has been used to replace glucose for developing a cheap medium for heterotrophic Chlorella protothecoides (Xu et al. 2006). Many additional options of organic carbon sources were tested for feasibility instead of glucose (Table 1).
Molasses, a by-product from sugar refinery, also can be a good alternative to glucose in promoting microalgal lipid accumulation. Vidotti et al. (2014) tested the hydrolyzed sugarcane molasses with two microalgal strains, and this substrate provided a similar cell growth as that observed when glucose was used in the cultivation of Chlorella vulgaris and Scenedesmus bijugatus.
Sugars released from lignocellulosic materials also are able to provide cheaper and sustainable carbon source for heterotrophic microalgal cultivation. However, besides the physical and chemical barriers already mentioned in this chapter, caused by the close association of the main components of lignocellulosic biomass, a variety of potential inhibitory degradation products are produced during pretreatment of lignocellulosic biomass, and all of these chemicals can potentially cause inhibition to algal growth (Liang 2013).
How microalgal species survive the presence of these toxic degradation by-products is unknown. In the literature, only the effect of acetate on microalgal growth has been evaluated (Perez-Garcia et al. 2011; Heredia-Arroyo et al. 2010, 2011; Yeh et al. 2012; Vidotti et al. 2013). Another important factor is the sugar composition present in the feedstock. As mentioned earlier, glucose is the most commonly used carbon source for heterotrophic cultures of microalgae, but microalgal species that can utilize xylose are few. At present, only one paper in the literature reported the xylose utilization by Chlorella strain, but only in the light or when glucose was present in the media (Hawkins 1999). On the other hand, Vidotti et al. (2014) tested xylose as carbon source for Chlorella vulgaris and Scenedesmus bijugatus; however none of the two strains were able to utilize this sugar.
To solve the xylose utilization issue, some directions can be taken: screening microalgal species that can grow on xylose as well as on glucose and genetically engineering strains to metabolize xylose. Moreover Liang (2013) mentions the possibility of coupling with other xylose utilizing microbial species, either yeast or bacteria in the same reactor or sequentially. In this way, glucose and xylose will both be consumed by different microorganisms, and different products can be resulted from the biomass hydrolysates. Recent research efforts have concentrated on the identification of microalgal strains capable of converting cellulosic feedstocks into oil (Chua and Somanchi 2012; Pourmir and Johannes 2011), but in light of the complexity involved in this application, few studies have been reported in the literature.
3.2 Microbial Oil Production by Bacteria
The advantages of using bacteria for lipid production are obvious since these microorganisms show usually higher growth rates than yeast and fungi and can be more easily genetically manipulated. Prokaryotes have fewer genes allocated all in one chromosome, and the lower complexity of genome demands less complexity of control mechanisms. However, while triacylglycerols (TAG) can be found in most eukaryotic organisms, they are rarely found in bacteria. Extractable lipids in bacteria are usually in the form of specialized lipids such as poly(3-hydroxybutiric acid) or other poly-hydroxyalkanoates. Only a few species of actinomycetes group such as Rhodococcus and Mycobacterium can synthesize and accumulate TAGs (Alvarez and Steinbuchel 2002). Among these, the genus Rhodococcus is frequently studied for its high capacity of accumulating lipids while growing in different substrates. Rhodococcus opacus PD630 is usually selected as the model microorganism for bacterial lipid accumulation. It was found to accumulate over 70 % of its cell dry weight (CDW) in FAs under nitrogen limitation condition (Alvarez et al. 2000) and grow at specific growth rates of 0.1–0.2 h−1 with glucose as carbon source (Xiong et al. 2012; Baboshin and Golovleva 2005).
Rhodococcus opacus PD630 was shown to grow well in the presence of lignocellulosic biomass pretreatment by-products such as furfural, 5-hydroxymethyl furfural (5-HMF), vanillin, vanillic acids, and trans-p-coumaric acid (TPCA), which are known for inhibiting microbial growth. In addition, the strain could use vanillin, vanillic acid, and TPCA for growth and lipid accumulation in the absence of other carbon sources (Table 2). Furfural and 5-HMF were also fully degraded but not as sole carbon sources. The strain could grow in corn stover, sorghum, and grass hydrolysates while accumulating TAGs (Wang et al. 2014).
Xylose is one of the substrates that cannot be metabolized by Rhodococcus species. However the metabolic pathway of d-xylose utilization was introduced into strains Rhodococcus opacus PD630 and Rhodococcus jostii RHA1. The heterogeneous expression of genes xylA (xylose isomerase) and xylB (xylulokinase) from Streptomyces lividans TK23 allowed the recombinant R. opacus PD630 and R. jostii RHA1 to grow on xylose and accumulate 68.3 and 52.5 % of lipids, respectively. However, the specific growth rate on xylose (0.07 h−1) was 63 % lower than the observed for glucose (0.19 h−1) (Xiong et al. 2012).
Regarding cellulose direct utilization, Rhodococcus opacus PD630 was engineered to express six cellulase genes from Cellulomonas fimi ATCC 484 (cenABC, cex, and cbhA) and Thermobifida fusca DSM43792 (cel6A) which enabled the strain to degrade cellulose into cellobiose. The modified strain was able to hydrolyze 9.3 % of cellulose provided, and a second strain engineered to utilize cellobiose could accumulate 15 % of lipids from the hydrolyzed cellulose (Hetzler et al. 2013).
Lignin is usually considered to be a bottleneck in lignocellulosic biomass bioconversion. It represents 10–25 % of lignocellulosic feedstocks, and few microorganisms are capable of metabolizing it, thus limiting its utilization as fuel for energy cogeneration or bioconversion through pyrolysis. Recently lignin model compounds (4-HBA, VanA, and SyrA) were found to be directly metabolized by R. opacus DSM1069 and PD630 to lipid production (11.44 and 18.22 % of dry cell weight, respectively) (Kosa and Ragauskas 2012).
3.3 Microbial Oil Production by Fungi
Filamentous fungi usually grow at lower growth rates, yields, and productivities than yeasts. However some of these organisms are capable of producing lipids containing more than 70 % of polyunsaturated fatty acids (PUFAs) such as arachidonic acid and γ-linolenic acid. The composition of the lipids produced depends directly on the culture medium composition and may change during cultivation.
It is well known that lipid synthesis and accumulation occur under nitrogen limitation conditions. Interestingly arachidonic acid synthesis seems to occur after carbon source starvation (Nie et al. 2013). However, under carbon-depleted conditions, the concentration of total FAs remains constant, but a rapid increase in arachidonic acid content is observed while at the same time other FAs such as oleic and stearic acids are consumed. It was suggested that saturated FAs and oleic acid are converted to linolenic and γ-linolenic acids and subsequently to arachidonic acid (Eroshin et al. 2002). However if no carbon limitation is induced, lipid composition is mainly composed by saturated and monounsaturated FAs as observed by Stressler et al. (2013) and Nie et al. (2013).
Strains of the genus Mortierella (Fig. 4) are regarded as some of the most productive organism for PUFA synthesis, with the capacity of accumulating 20–70 % of total lipids (Table 3) containing mostly PUFA (Sakuradani 2010). These fungi can grow at high growth rates of up to 0.566 h−1 when grown in non-limiting conditions and yield lipid productivities as high as 0.785 g/(L h) (Economou et al. 2011a).
Arachidonic acid is already commercially produced from Mortierella strains by Cargill Alking Bioengineering in Wuhan, China; by Nippon Suisan Kaisha in Tokyo, Japan; and by Martek Biosciences (DSM) in Columbia, USA (Tyburczy et al. 2011). These fungi are also one of the few highly productive oleaginous microorganisms that can grow well using xylose as sole carbon source (Huang et al. 2013).
Mortierella isabellina could grow on both C5 (arabinose, ribose, xylose, and mannose) and disaccharides (sucrose and cellobiose). When grown in the presence of model lignocellulosic inhibitor compounds, phenolic compounds were highly inhibitory, while furfural, 5-HMF, acetic acid, formic acid, and levulinic acid showed limited inhibition. Surprisingly acetic and formic acid improved lipid production by twofold as compared with that observed for the control. When grown on wheat straw, hydrolysate up to 53 % total lipids was obtained with a lipid yield of 16.8 % from the carbon sources (Zeng et al. 2013).
The oleaginous fungi Mucor circinelloides was grown on corn ethanol stillage resulting in 52 % total lipids. When the culture was supplemented with glycerol at the stationary phase, an increase of 46–61 % in lipid content was observed.
3.4 Microbial Oil Production by Yeast
Among fungi, oleaginous yeasts are distinguished by their capacity to accumulate high concentrations of lipids. Species such as Rhodosporidium toruloides and Lipomyces starkeyi have been found to accumulate lipids at around 60 and 70 % of dry cell weight (Shi et al. 2011). Microbial fermentation for producing biodiesel from lignocellulosic hydrolysates is receiving increasing attention; however, oleaginous yeasts that can utilize lignocellulosic hydrolysates are few (especially for acid lignocellulosic hydrolysates to accumulate lipids) and still at its initial stages (Table 4). Therefore, it is necessary to discover oleaginous strains that have high lipid yield on lignocellulosic biomass hydrolysates.
To date, SCO production from lignocellulosic biomass was usually carried out through a batch fermentation mode. It is possible that using a fed-batch or continuous fermentation mode could fulfill the high-cell-density cultivation on lignocellulosic hydrolysates, and this is undoubtedly beneficial for the industrialization of SCO production (Huang et al. 2013). Anschau et al. (2014) indicated the possibility of the transformation of lignocellulosic materials into biodiesel studying the lipid production by L. starkeyi DSM 70296 using different feeding strategies. Glucose and xylose were used for batch, fed-batch, repeated fed-batch, and continuous cultures, and hemicellulose hydrolysate (H–H) was tested at continuous culture. High cell mass (~85 g/L) and lipid (~40 g/L) concentrations were achieved through both fed-batch and repeated fed-batch cultivations using glucose:xylose (30:70), with a maximum specific growth rate of 0.07 h−1. The kinetic profile obtained from a continuous cultivation with H–H was similar to that obtained from cultivation in a synthetic medium. This may be explained by the fact that the hydrolysate contained some protein and microelements, which could promote the yeast growth and lipid accumulation. At a dilution rate of 0.03 h−1 with H–H, the cultivation yielded cell mass and lipid concentrations of 13.9 g/L and 3.7 g/L (26.7 %), with a maximum specific growth rate at batch step of 0.089 h−1. Arabinose was not consumed throughout the cultivation. The inhibitor concentrations (acetic acid, furfural, and HMF) were reduced during the batch stage and the first residence times of the continuous cultivation, indicating that this yeast can use these compounds as carbon sources. This is of particular interest because it is possible that L. starkeyi is highly tolerant to inhibitors, which may allow a broader study of H–H from SCB in fermentation processes. Continuous cultivations at 0.03 h−1 using glucose:xylose (30:70, w/w) and H–H from SCB presented the highest yields and productivities, indicating that this approach is the most appropriate for scale-up (Fig. 5).
The same strain (L. starkeyi DSM 70296) was adapted by evolutionary engineering in culture medium containing SCBH (H–H) (Aristizabal et al. 2012). The H–H was obtained after seven sequential extraction steps of bagasse previously pretreated by steam explosion. The yeast was adapted by evolutionary engineering in culture medium containing increasing concentrations of H–H. As a result, a yeast adapted to culture medium containing 30 % of H–H was obtained, which showed higher cell concentration (9.79 g/L) with lower lipid content (18.5 %) compared to not adapted strain (5.21 g/L of cells with 31.5 % of lipids) with a maximum specific growth rate of 0.039 h−1.
The possibility of utilizing detoxified sugarcane bagasse hydrolysate (DSCBH) was investigated as an alternative carbon source to culture Y. lipolytica Po1g for microbial oil and biodiesel production (Tsigie et al. 2011). Compared with (DSCBH) medium, growth in the non-detoxified sugarcane bagasse hydrolysate (NDSCBH) medium was limited because of the presence of inhibitors (furfural and HMF).
Cryptococcus curvatus has great potential in fermenting unconditioned hydrolysates of sweet sorghum bagasse (Liang et al. 2012). During yeast fermentation, glucose and xylose were consumed simultaneously, while cellobiose was released from the residual bagasse. Surprisingly, the cellobiose utilization rates were much higher than those on glucose and xylose. It seems that C. curvatus could engulf cellobiose rapidly, but then it had to spend more energy on digesting this disaccharide, which resulted in the lowest cell yield among all of the sugars tested.
Trichosporon fermentans was proved to be able to use sulfuric acid-treated sugarcane bagasse hydrolysate as substrate to grow and accumulate lipid (Huang et al. 2012b). Although the volumetric productivity of T. fermentans on bagasse hydrolysate is not as high as that of Y. lipolytica on industrial fats, the higher lipid concentration and moderate volumetric productivity make oleaginous yeast T. fermentans very promising for lipid production from abundant and inexpensive lignocellulosic materials. The effects of five representative aldehydes in lignocellulosic hydrolysates on the growth and the lipid accumulation of oleaginous yeast T. fermentans were also investigated (Huang et al. 2011). There was no relationship between the hydrophobicity and the toxicity of aldehyde, and 5-hydroxymethylfurfural was less toxic than aromatic aldehydes and furfural. Binary combination of aromatic aldehydes caused a synergistic inhibitory effect, but a combination of furan and aromatic aldehydes reduced the inhibition instead. Furthermore, the inhibition of aldehydes on cell growth was more dependent on inoculum size, temperature, and initial pH than that on lipid content.
The inhibitory effect of lignocellulose degradation products on the oleaginous yeast fermentation was carefully investigated by Chen et al. (2009). Preliminary screening was carried out in the minimum nutritious medium without adding any expensive complex ingredients and then was carried out in the lignocellulosic hydrolysate pretreated by dilute sulfuric acid. Seven typical lignocellulose degradation products formed in various pretreatments and hydrolysis processing were selected as the model inhibitors, including three organic acids, two furan compounds, and two phenol derivatives. The inhibition of the degradation compounds on the cell growth and the lipid productivity of the selected oleaginous yeasts were examined. Acetic acid, formic acid, furfural, and vanillin were found to be the strong inhibitors for the fermentation of oleaginous yeasts, while levulinic acid, 5-hydroxymethylfurfural, and hydroxybenzaldehyde were relatively weak inhibitors. T. cutaneum 2.1374 was found to be the most adopted strain to the lignocellulose degradation compounds.
In summary, these works showed the great potential of SCO production from lignocellulosic biomass. The use of lignocellulosic hydrolysates as substrates could serve as the basis for the industrialization of SCO production. However, many problems in this process still exist that must be solved.
4 Fatty Acid Composition in Microbial Lipids
Microbial oils may have great potential for biodiesel production due to FA composition. Microorganisms also produce edible oils rich in PUFA for dietary supplements and infant nutrition applications (Ratledge 2004; Cahoon and Schmid 2008). It is possible to observe that the FA profile produced by microorganisms is quite similar to vegetable oils (Table 5) and can thus be used as a substitute for biofuels.
According to Table 5, most PUFAs produced by fungi, algae, and bacteria have been proposed as producers of certain PUFAs. Yeasts are not potential producers of PUFAs. The number of unsaturations does not have an effect only on the values of viscosity and density of biodiesel but also on the oxidative stability (Lobo et al. 2009). Most biodiesel fuels present significant amounts of esters of oleic, linoleic, or linolenic acids, influencing the oxidative stability of the fuel (Knothe 2005). Biodiesel presents portability, greater renewability, higher combustion efficiency, lower sulfur and aromatic content, and higher cetane number than diesel oil (Balat 2011). It is recommended that these fuels meet the biodiesel standards of US ASTM D 6751 and European EN 14214 (Ashraful et al. 2014).
When the extraction process is used for oils, it seeks to achieve the following objectives: (1) to obtain a fat or oil uninjured and free from undesirable impurities, (2) obtain the best possible performance without changing the cost of litigation, and (3) produce a minimum of waste with the greatest possible value. The choice of the optimal extraction method for large-scale oil must meet certain criteria: the ease with which the cell breaks down, the cost of the method, rate of cell disruption, and so on (Hulteberg et al. 2008).
Tables 6 contains, respectively, the properties of FAMES collected from the literature and the results of the prediction of quality parameters of oleaginous yeast and microalgae (Lacerda et al. 2013) compared with the American, European, and Brazilian standards. The values of臒heat of combustion (HC),臒index of oxidative stability臒(OSI) and臒iodine value臒(II) are out of limits imposed by these standards, however, the values of density (ρ), viscosity (u)臒and臒cetane number臒(CN) are within it. Even though the indexes are slightly out of bounds, the biodiesel obtained from臒Chlorella vulgaris臒and臒Lipomyces starkeyi may still be used as fuel.
Biodiesel produced by Lipomyces starkeyi has the advantage of being deficient in of C18:3, which is limited to 12 % by EN 14214. Chlorella vulgaris has an advantage if compared to mitigation of carbon dioxide associated with the production of biofuel. In both cases, the FA profile showed compounds commonly found in biodiesel. The results of the prediction quality are classified into three available standards, demonstrating the potential of C. vulgaris and L. starkeyi oil as raw materials for biodiesel production (Lacerda et al. 2013).
Yeasts have several difficulties for lipid extraction, including the presence of a thick cell wall that renders the yeast cells resistant to many solvents, as well as the possible presence of lipases in their cell extracts, and most of the neutral lipids are intracellularly stored in lipid bodies. However, lipid bodies also contain other lipophilic compounds, in particular aromatic compounds, which are difficult to remove during lipid purification (Ageitos et al. 2011). Table 7 shows the profile of TAG for some lipid extraction methods from L. starkeyi.
Glycerides are desirable for biodiesel production mainly for alkaline transesterifications (Chisti 2007). Acylglycerols generally have a lower degree of unsaturation than other lipid fractions (i.e., polar lipids) and produce FAME with higher oxidation stability (Halim et al. 2012).
From a technological point of view, the TAG profile represents a key to the understanding of the several physical properties of an oil or fat. The ability to change the physical properties of fats has attracted great interest in recent years. Information on the TAG profile is needed to control these processes (Buchgraber et al. 2004).
The microbial oil production process requires four main steps: cell disruption, oil extraction, separation of value-added compounds (PUFAs), and esterification/cracking of lipids. The improvement of each of these steps demonstrates the use and application of these lipids for biofuels, food and cosmetic industries, jet fuels, health supplements, and PUFA.
5 Genetic and Metabolic Engineering to Enhance Microbial Lipids
In the last years metabolic and genetic engineering has established itself as an enabling technology for biofuel development. Those tools are able to modify microorganisms aiming to improve their natural features and even introduce new characteristics. Metabolic engineering emerged approximately 15 years ago as a distinct field that is differentiated from genetic engineering by its focus on the properties of biosynthetic and metabolic pathways in their entirety, instead of single genes and enzymes (Liang and Jiang 2013). Oleaginous microorganisms able to use lignocellulosic hydrolysates as some yeasts, molds, bacteria, and microalgae can be engineered to be a lipid platform production.
As was presented in this chapter, only few microorganisms are able to convert sugars, from lignocellulosic materials, into lipids. However, these native microorganisms, which are derived from environmental isolates, are often distinct from the microorganisms that are traditionally used and that have been proved to be effective in industrial processes. Furthermore, these isolated strains typically suffer from a lack of genetic and molecular biology traditional tools and therefore require much scientific investment to transform them into modifiable production platforms. Nevertheless, the innate capacity and potential of these cells—which may be able to use recalcitrant substrates or withstand toxic products—is immense (Alper and Stephanopoulos 2009).
To overcome this lack of traditional genetic and metabolic tools, that can be used to genetically manipulate those strains, other genetic approaches as site-direct and random mutagenesis, as made for yeast Lipomyces starkeyi (Tapia et al. 2012), which presented a productivity increase of 15.1 % in biomass and 30.7 % in lipid productivity, and microalga Isochrysis affinis galbana (Bougaran et al. 2012) resulted in a 1.8-fold increase for neutral lipid productivity, could be important to enhance their natural capacity to storage lipids. However, it is necessary to understand the metabolic pathways linked to lipid material metabolism, in order to select the genes and the best approach to metabolic engineering.
Oleaginous microorganisms do not have high oil levels under balanced nutrient conditions; however, when a given substrate is limiting—typically nitrogen—they channel carbon sources into lipid formation. It has been shown that phosphorus limitation has some advantages; for example, the nitrogen content of the substrate biomass does not influence lipid accumulation. FA synthesis is the first step of lipid accumulation. Subsequently, phospholipid (PL) and triacylglycerol (TAG) (also known as “neutral lipid”) synthesis results in membrane and reserve lipid accumulation, respectively. Conversion of these lipids into FA short-chain alcohol esters [mainly methanol (FAME) and ethanol (FAEE)] is the final step in biodiesel production (Kosa and Ragauskas 2011). The enzymes and steps that lead to TAG accumulation in eukaryotes and prokaryotes microorganism, using as carbon sources sugars from lignocellulosic biomass, are shown in Fig. 6.
The genetic engineering of oleaginous microorganism is focused in enhancing the FFA and TAG biosynthesis by overexpressing main enzymes linked to those metabolic routes, as ACC1, FAT, ME, and ACL (free FA biosynthesis) and GPAT, LPAT, GPD1, and GUT2 (TAG biosynthesis), or partially blocking competing pathways as lipolysis. Furthermore a multigene transgenic approach can be used in order overexpressing more than one key enzyme in the TAG pathway to enhance lipid biosynthesis as showed in Table 8.
Efficient fermentation of hemicellulosic sugars is critical for the bioconversion of lignocellulosics to lipids. While most hexoses are readily phosphorylated as soon as they enter the cell, hemicellulosic sugars must go through several biochemical steps before phosphorylation. Eukarya and bacteria use two distinct pathways each for the assimilation of d-xylose and l-arabinose (Van Vleet and Jeffries 2009) as showed in Fig. 7.
6 Future Perspectives
Only few studies about oleaginous microorganisms have used metabolic and genetic engineering tools to improve metabolism of sugars: oleaginous fungi (Mortierella isabellina) and yeasts (as Lipomyces starkeyi and Rhodotorula glutinis) have a good capacity to assimilate those sugars, and also, majority of autotrophic microalgae are used to accumulate lipids. The lack of traditional genetic and metabolic tools for those nonconventional species, as discussed before, also contributes to the small number of works in this area. However some studies have used heterologous pathways to introduce xylose assimilation capacity in wild strains that accumulate good amounts of lipids but are not able to metabolize xylose. Bacteria Rhodococcus sp., which is known as high lipid production strain, was engineered to express heterogeneously two well-selected genes, xylA, encoding xylose isomerase, and xylB, encoding xylulokinase from Streptomyces lividans TK23, under the control of the tac promoter with an Escherichia coli-Rhodococcus shuttle vector. Lipid produced from xylose by recombinants of R. jostii RHA1 and R. opacus PD630 carrying xylA and xylB represented up to 52.5 and 68.3 % of the CDW, respectively (Xiong et al. 2012). Microalgae are also engineered to metabolize xylose as described by Solazyme patent (Chua and Somanchi 2012).
Metabolic and genetic engineering and further other genomics, transcriptomics, and metabolomics tools provide more information and new ways on enhancing lipid production in oleaginous microorganisms, optimizing FA profiles, enhancing lipid accumulation, and improving the use of low-cost raw materials as lignocellulosic hydrolysates.
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Coradini, A.L.V. et al. (2015). Microorganism for Bioconversion of Sugar Hydrolysates into Lipids. In: Kamm, B. (eds) Microorganisms in Biorefineries. Microbiology Monographs, vol 26. Springer, Berlin, Heidelberg. https://doi.org/10.1007/978-3-662-45209-7_3
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