- Open Access
Detection of carbohydrate-active enzymes and genes in a spent engine oil-perturbed agricultural soil
Bulletin of the National Research Centre volume 42, Article number: 10 (2018)
The purpose of this study is to decipher the diverse carbohydrate metabolism pathways in a spent engine oil-perturbed agricultural soil, enunciate the carbohydrate-active enzymes and genes involved in the process, taxonomically classify the annotated enzymes and genes, and highlight the importance of the study for ecological and biotechnological processes.
Functional analysis of the metagenome of spent engine oil (SEO)-contaminated agricultural soil (AB1) using the Kyoto Encyclopedia of Genes and Genomes (KEGG) GhostKOALA, Cluster of Orthologous Groups (COG) of proteins, the Carbohydrate-Active Enzymes (CAZy) database, and the NCBI’s conserved domain database (CDD) revealed extensive metabolism of carbohydrates via diverse carbohydrate-active enzymes and genes. Enzymes and genes annotated for glycolysis/gluconeogenesis pathway, citric acid (TCA) cycle, pentose phosphate pathway, and pyruvate metabolism, among others, were detected, and these were not detected in the original agricultural soil (1S). Analysis of carbohydrate-active enzymes, using the CAZy database, showed 45 CAZy families with preponderance of glycoside hydrolases (GHs, 46.7%), glycosyltransferases (GTs, 24.4%), and carbohydrate-binding modules (CBMs, 15.5%). Taxonomic classification of the annotated enzymes and genes for carbohydrate metabolism using the GhostKOALA and CAZy databases revealed the predominance of the phylum Proteobacteria with the representative genera Pseudomonas (18%), Sphingobium (13.5%), and Sphingomonas (4.5%), respectively. Biotechnologically important enzymes such as xylanases, endoglucanases, α- and β-glucosidases and glycogen debranching enzymes were also retrieved from the metagenome.
This study revealed the presence of diverse carbohydrate-active enzymes and genes mediating various carbohydrate metabolism pathways in the SEO-perturbed soil metagenome. It also reveals the detection of biotechnologically important enzymes with potentials for industrial use.
Hydrolysis of carbohydrates by microorganisms is a combination of diverse biochemical processes responsible for their formation, degradation, and transformation. The metabolic pathways used and the metabolites produced are determined exclusively by the enzyme machinery of the microbial community in such environment (Ley et al. 2008; Xia et al. 2015).
Complex carbohydrates found in nature are catalyzed by a range of enzymes involved in their assembly (glycosyltransferases, GTs) and their breakdown (glycoside hydrolases, GHs; polysaccharide lyases, PLs; carbohydrate esterases, CEs; auxiliary activities, AAs), collectively called carbohydrate-active enzymes (CAZymes). In addition, the carbohydrate-binding modules (CBMs) assist in hydrolysis of polysaccharides by bringing the biocatalyst into close contact with its recalcitrant substrate (Lombard et al. 2014).
Glycoside hydrolases (GHs) are enzymes that cleave glycosidic bonds in glycosides, glucan, and glycoconjugates. Their industrial and biotechnological importance is not in doubt as they play key roles in the development of biofuels (cellulases, xylanases, etc.) and disease research (Yuzwa et al. 2008; Abbott et al. 2009; Wilson 2009). They also play crucial role in global carbon cycling by allowing microorganisms in the soil to breakdown plant cells, releasing CO2 aerobically and various fermentation products anaerobically (Bardgett et al. 2008). Glycosyltransferases (GTs) represent a subclass of enzymes that catalyze the synthesis of glycosidic linkages by the transfer of a sugar residue from a donor substrate to an acceptor. They play key roles in biosynthesis pathways of oligo- and polysaccharides, as well as protein glycosylation and formation of valuable natural products (Lairson et al. 2008; Schmid et al. 2016). The carbohydrate esterases (CEs) involve enzymes that catalyze the de-O or de-N-acylation to remove the ester embellishments from carbohydrates (Cantarel et al. 2009). The range of biological and biotechnological applications of CEs is diverse. For example, majority of CE families include members that catalyze the removal of acylated moieties of polysaccharides, which enhance their degradation and facilitate access of glycoside hydrolases, thus assisting in biomass saccharification and generation of renewable biofuels, sustainable materials, and green chemicals (Christov and Prior 1993; Gupta and Verma 2015). Furthermore, several CE families have been reported to contain enzyme targets for drug design and considerable potentials in biomedical applications (Nakamura et al. 2017).
In recent years, our understanding of microbial metabolism has been enhanced considerably by the application of next-generation sequencing (NGS) techniques. NGS-based metagenomics allows the study of microbial communities without prior culturing or marker gene amplification. This provides a relatively unbiased view of not only the microbial community structure but also the metabolic pathways of the community.
Hydrocarbon pollution generally imposed significant stress on microbial community in soil. As hydrocarbons are weak in nutrients consisting mostly of carbon and hydrogen, there is significant pressure on the microbial community to utilize stored and easily metabolized carbon sources as sources of energy to drive metabolism and biosynthetic processes (Demoling et al. 2007).
Previously, we have investigated the effects of SEO perturbation on the microbial community structure and functions of an agricultural soil using Illumina NGS sequencing technique. The study particularly showed the dominance of hydrocarbonoclastic organisms due to the SEO contamination and preponderance of functional genes related to hydrocarbon degradation, heavy metal tolerance and detoxification, oxidative stress, response to nutrient starvation, and many others (Salam et al. 2017). However, a curious observation is the detection of huge array of carbohydrate metabolism pathways mediated by carbohydrate-active enzymes and genes in the SEO-perturbed agricultural soil not detected in the original agricultural soil. These observations spur investigations into these unusual findings and the possible roles played by SEO presence and degradation.
Site description, microcosm set up, and determination of residual hydrocarbons
Soil samples were collected from an agricultural farm at Atere, Ilorin, Nigeria. The coordinates of the sampling site were latitude 8° 29′ 11.54″ N and longitude 4° 29′ 30.11″ E. The soil, which is dark-brown in color, is used to plant majorly maize and vegetables. Soil microcosm (agricultural soil, 1S; agricultural soil + SEO, AB1) set up, and incubation conditions have been described previously (Salam et al. 2017). Similarly, the physicochemical properties, the residual spent engine oil (SEO), and its various constituents as well as the heavy metal content of the soil microcosms have been reported previously (Salam et al. 2017).
DNA extraction, library construction, sequencing, and metagenome properties
Genomic DNA used for metagenomic analysis was extracted directly from soil microcosms. Genomic DNA were extracted from the sieved soil samples (0.25 g) using ZYMO soil DNA extraction Kit (Model D 6001, Zymo Research, USA) following the manufacturer’s instructions. Genomic DNA concentration and quality was ascertained using NanoDrop spectrophotometer and electrophoresed on a 0.9% (w/v) agarose gel, respectively.
Shotgun metagenomics of 1S and AB1 microcosms was prepared using the Illumina Nextera XT sample processing kit and sequenced on a MiSeq. Genomic DNA (50 ng) were fragmented and tagmented, and unique indexes were added using reduced-cycle PCR amplification consisting 8 cycles of 95 °C for 30 s, 55 °C for 30 s, and 72 °C for 30 s, and a final extension at 72 °C for 5 min before cooling to 4 °C. Constructed metagenomic libraries were purified with Agencourt AMPure XP beads and quantified with Quant-iT PicoGreen assay kit. The library size and quality were validated on Agilent Technologies 2100 Bioanalyzer. Libraries were normalized, pooled in equal volumes, and run on a 600 cycles MiSeq Reagent kit v3 (Illumina Inc., San Diego, CA). All samples were multiplexed and sequenced in a single lane on the MiSeq using 2 × 300 bp paired-end sequencing, which generates 20 Mb of data for each sample. Sequence reads were generated in < 65 h, while image analysis and base calling were performed directly on MiSeq. The sequences of IS and AB1 metagenomes were deposited on the MG-RAST server with the IDs 4,704,688.3 and 4,704,689.3, respectively.
Sequences generated from the microcosm set up were assembled individually by VelvetOptimiser v2.2.5, and the contigs generated were fed into the MG-RAST metagenomic analysis pipeline. The sequences were assembled into 2389 and 2948 unique contigs for soil microcosms 1S and AB1 with a total of 611,018 and 761,383 bp, an average length of 255 ± 63 and 258 ± 62 bp, and the GC content of 56 ± 4 and 62 ± 5%, respectively. After dereplication and quality control by the MG-RAST, the total number of sequence reads in AB1 metagenome reduced to 2828 sequence reads with 711,035 bp, an average length of 251 ± 54 bp, and a GC content of 62 ± 5% (Salam et al. 2017).
Functional analyses of metagenomic read for carbohydrate metabolism
Gene calling was performed on the AB1 contigs using FragGeneScan (Rho et al. 2010) to predict open reading frames (ORFs), which were functionally annotated using KEGG GhostKOALA, the Clusters of Orthologous Groups of proteins (COG) (Tatusov et al. 2001), the Carbohydrate-Active Enzymes (CAZy) database, and the NCBI’s conserved domain database (CDD; Marchler-Bauer et al. 2015). In GhostKOALA, each query gene is assigned a taxonomic category according to the best-hit gene in the Cd-hit cluster supplemented version of the non-redundant pangenome dataset (Kanehisa et al. 2016). In addition, the ORFs were functionally annotated and assigned to the COG database that compares protein sequences encoded in complete genomes, representing major phylogenetic lineage. The CAZymes Analysis Toolkit (CAT) (Park et al. 2010) was also used to detect the carbohydrate-active enzymes in AB1 metagenome using a sequence similarity-based annotation. This is based on the similarity search of the protein sequences in AB1 sequence reads against the entire non-redundant sequences of the carbohydrate-active enzymes (CAZy) database (Park et al. 2010; Lombard et al. 2014). Sequence reads annotated for carbohydrate metabolism in AB1 metagenome was further elucidated using the NCBI’s conserved domain database (CDSEARCH/cdd v 3.15) using the default blast search parameters. The CDD is a protein annotation resource that consists of a collection of well-annotated multiple sequence alignment models for ancient domains and full-length proteins.
Functional analyses of AB1 metagenome using GhostKOALA, COG, CAZy, and NCBI CDD databases revealed the presence of various carbohydrate metabolism pathways such as glycolysis/gluconeogenesis, citric acid (TCA) cycle, pentose phosphate pathway, and several others as well as carbohydrate-active enzymes (Table 1 and Table 2). It is instructive to note that only four genes encoding four different enzymes (β-glucuronidase, ribulose-5-phosphate 4-epimerase, 4-alpha-glucanotransferase, pyruvate dehydrogenase (quinone)) for carbohydrate metabolism were detected in 1S microcosm (Additional file 1).
Functional characterization of AB1 metagenome using GhostKOALA and COG revealed 13 enzymes annotated for glycolysis/gluconeogenesis (Fig. 1). Interestingly, only three of the enzymes are glycolytic enzymes, though aldehyde dehydrogenase (EC: 220.127.116.11) a superfamily having glyceraldehyde-3-phosphate dehydrogenase as member was detected. These are glucokinase (EC: 18.104.22.168), glucose-6-phosphate isomerase (EC: 22.214.171.124), and phosphoglycerate kinase (EC: 126.96.36.199). Similarly, three gluconeogenic enzymes were also detected in AB1 metagenome. These are pyruvate carboxylase (EC: 188.8.131.52), fructose 1,6-bisphosphatase I (EC: 184.108.40.206), and glucose-6-phosphate isomerase, respectively.
The remaining six enzymes annotated for glycolysis/gluconeogenesis falls into two categories. Enzymes that catalyze the feeder pathways for glycolysis include phosphoglucomutase (EC: 220.127.116.11), and phosphomannomutase (EC: 18.104.22.168). The second category is enzymes that catalyze pyruvate, the metabolic product of glycolysis. These are pyruvate dehydrogenase E1 (EC: 22.214.171.124) and E2 (EC: 126.96.36.199) components, alcohol dehydrogenase (EC: 188.8.131.52), and acetyl-CoA synthetase (EC: 184.108.40.206), which catalyze the conversion of acetate to acetyl-CoA, respectively (Table 1, Fig. 1).
Taxonomic affiliation of the functional genes/enzymes annotated for glycolysis/gluconeogenesis revealed that the organisms belong to the phylum Proteobacteria. The class γ-Proteobacteria predominates, constituting 40% of the taxonomic affiliations with members such as Pseudomonas, Stenotrophomonas, and Thioploca. This is closely followed by α-Proteobacteria, contributing 33.3% of the organisms annotated with representatives such as Caulobacter, Acidiphilium, and Methylobacterium. β-Proteobacteria contributes 26.7% of the organisms annotated with members such as Achromobacter and Massilia (Table 1).
Citric acid (TCA) cycle
Functional characterization of AB1 metagenome revealed eight (8) enzymes annotated for citric acid (TCA cycle) (Fig. 2). Aside from detection of pyruvate dehydrogenase E1 (EC: 220.127.116.11) and E2 (EC: 18.104.22.168) dihydrolipollysine-residue acetyltransferase components, which catalyze the starting point of the TCA cycle, seven (7) other major enzymes of the citric acid cycle were detected in AB1 metagenome. These are aconitate hydratase (EC: 22.214.171.124), 2-oxoglutarate (α-ketoglutarate) dehydrogenase (EC: 126.96.36.199), and succinyl-CoA:acetate-CoA transferase (EC:188.8.131.52). Others include succinate dehydrogenase (EC: 184.108.40.206), fumarate reductase (EC: 220.127.116.11), fumarate hydratase (EC: 18.104.22.168), and malate dehydrogenase (EC: 22.214.171.124), respectively.
Taxonomic affiliation of the functional genes/enzymes annotated for TCA cycle revealed that the microorganisms belong to the phylum Proteobacteria. α-Proteobacteria predominates with 50% of the taxonomic affiliations. The representative genera include Novosphingobium, Sphingobium, and Azorhizobium. This is followed by γ-Proteobacteria (35.7%) with representative genera such as Steroidobacter, Xanthomonas, and Stenotrophomonas. β-Proteobacteria contributes 14.3% of the organisms annotated with members such as Thauera and Candidatus Symbiobacter, respectively (Table 1).
Pentose phosphate pathway (PPP)
Functional analysis of AB1 metagenome revealed ten (10) enzymes annotated for the pentose phosphate pathway (Fig. 3). Out of these, four enzymes glucose 6-phosphate isomerase, phosphomannomutase, phosphoglucomutase, and fructose 1,6-bisphosphatase are glycolytic/gluconeogenic enzymes, with possible roles in the generation of glucose-6-phosphate, the starting substrate in pentose phosphate pathway. The remaining six (6) enzymes are PPP enzymes. These include glucose 6-phosphate dehydrogenase (EC: 126.96.36.199), 6-phosphogluconolactonase (EC: 188.8.131.52), and 6-phosphogluconate dehydrogenase (EC: 184.108.40.206). Others include ribulose phosphate 3-epimerase (EC: 220.127.116.11), xylulose 5-phosphate phosphoketolase (EC: 18.104.22.168), fructose 6-phosphate phosphoketolase (EC: 22.214.171.124), and ribokinase (EC: 126.96.36.199), which phosphorylate ribose to ribose-5-phosphate.
Taxonomic affiliation of the annotated PPP enzymes revealed that the phylum Proteobacteria dominates (62.5%) with representative members from α-(Brevundimonas, Sinorhizobium, Ensifer), β-(Achromobacter), and γ-Proteobacteria (Xanthomonas, Methylophaga, Colwellia, etc.) classes. Other phyla detected are Nitrospirae (Nitrospira), Cyanobacteria (Pseudanabaena), and Firmicutes (Symbiobacterium) each constituting 12.5% of the taxonomic affiliation (Table 1).
Starch and sucrose metabolism
Functional characterization of AB1 metagenome detected 18 enzymes annotated for starch and sucrose metabolism (Fig. 4). These include α-glucosidase (EC: 188.8.131.52), β-glucosidase (EC: 184.108.40.206), and trehalose 6-phosphate synthase (EC: 220.127.116.11). Others include trehalase (EC: 18.104.22.168), maltose α-d-glucosyltransferase (EC: 22.214.171.124), α-amylase (EC: 126.96.36.199), and UDP-glucuronate decarboxylase (EC: 188.8.131.52). Furthermore, various enzymes participating in cellulose and hemicellulose degradation and D-xylose degradation as well as starch and glycogen debranching enzymes among others were detected in AB1 metagenome (Table 1).
Taxonomic characterization of the annotated enzymes/genes for starch and sucrose metabolism revealed the dominance of Protebacteria phylum (91%) with representative members from α-(Sphingobium, Agrobacterium, Beijerinckia, Methylocella, etc.), β-(Paraburkholderia, Achromobacter), γ-(Citrobacter, Azotobacter, Pseudomonas, etc.), and δ-Proteobacteria (Desulfurivibrio) classes. Acidobacteria (9%) is the other phylum detected with representative members such as Acidobacterium and Terriglobus (Table 1).
Functional characterization of the AB1 metagenome revealed 13 enzymes annotated for pyruvate metabolism (Fig. 5). These include Acetyl-CoA synthetase (EC: 184.108.40.206), pyruvate dehydrogenase E1 (EC: 220.127.116.11) and E2 (EC: 18.104.22.168) components, and acetyl-CoA carboxylase (EC: 22.214.171.124). Others include succinyl-CoA:acetate-CoA transferase (EC:126.96.36.199), l-lactate dehydrogenase (EC: 188.8.131.52), pyruvate dehydrogenase (quinone) (EC: 184.108.40.206), and glyoxylate/hydroxypyruvate reductase A (EC: 220.127.116.11 18.104.22.168). Furthermore, other pyruvate metabolism enzymes and enzyme participating in L-leucine biosynthesis such as isopropylmalate synthase are also annotated (Table 1).
Taxonomic affiliation of the annotated enzymes revealed that the microorganisms belong to the phylum Proteobacteria with representative members of α-(Acidiphilium, Paracoccus, Novosphingobium, etc.), and γ-Proteobacteria (Dyella, Steroidobacter, Frateuria, etc.) constituting 80% of the genera while the remaining 20% belong to β-Proteobacteria (Thauera, Comamonas, etc.). Other functionally annotated carbohydrate metabolic pathways detected in AB1 metagenome are listed in Table 1.
Annotation of AB1 metagenome for carbohydrate-active enzymes
Functional characterization of AB1 metagenome for carbohydrate-active enzymes using the CATS system revealed 89 sequences with 45 CAZy families (Table 2). Majority (21; 46.7%) of the carbohydrate-active enzymes belong to GH (glycoside hydrolase) families. Aside GH families, other carbohydrate-active enzyme families detected are GTs (glycosyltransferases; 11, 24.4%), and the CBMs (carbohydrate-binding modules; 7, 15.5%). Furthermore, CEs (carbohydrate esterases) and the AAs (auxiliary activities) were also detected. Of these, the predominant CAZy families detected in AB1 metagenome are GT2 (10%), GH1 (7.9%), GH3 (6.7%), GH13 (6.7%), and GT51 (6.7%), respectively. Taxonomic characterization of the CAZy families showed the preponderance of Pseudomonas (18%), Sphingobium (13.5%), Terriglobus (5.6%), and Sphingomonas species (4.5%), respectively.
This study was necessitated by the surprise detection of diverse carbohydrate metabolism pathways in SEO-perturbed soil not detected in the original agricultural soil. This might be attributed to the stress imposed by SEO contamination of the agricultural soil. The stress may force the microbial community to catabolize the energy-rich stored carbohydrates such as cellulose, starch, glycogen, and others to easily metabolized carbohydrate such as glucose as sources of carbon and energy to drive metabolic processes (Demoling et al. 2007). This assertion is strengthened by the fact that most of the carbohydrate-active enzymes detected in AB1 microcosm performed catabolic functions, breaking down stored carbohydrates to easily metabolizable monomers.
The AA (auxiliary activities) families detected in AB1 microcosm are AA3, AA5, and AA6, respectively. AA3 belong to the glucose-methanol-choline (GMC) oxidoreductases family. The functions of the enzymes include cellulose, hemicellulose, and lignin biodegradation (CDH), oxidative dehydrogenation of several aromatic and aliphatic polyunsaturated alcohols leading to concomitant reduction of O2 to H2O2 (AO), and oxidation of the hydroxyl group at the C1 position of sugars (GOX) (Eriksson et al. 1986; Kremer and Wood 1992; Martinez et al. 2005; Hernández-Ortega et al. 2012). Also retrieved from AB1 microcosm is AA5 with galactose oxidase, N-acetylneuraminic acid mutarotase, and cell envelope biogenesis protein, OmpA as representatives (Table 2). Galactose oxidases (GAO) are copper-containing enzymes that catalyze the oxidation of a primary alcohol and reduction of O2 to H2O2 (Whittaker 2003). The enzyme catalyzes the oxidation of a wide range of carbohydrates (including galactose) and primary alcohols into the corresponding aldehydes, with the reduction of O2 into H2O2 (Levasseur et al. 2013).
The detection of NAD(P)H-dependent oxidoreductases as representative enzymes of AA6 family is not surprising as all experimentally characterized proteins of AA6 family are 1,4-benzoquinone reductases, a member of NAD(P)H-dependent oxidoreductases. 1,4-Benzoquinone reductase is an intracellular enzyme that catalyzes the reduction of methoxylated lignin-derived quinones to hydroquinones via a ping-pong steady state kinetic mechanism (Brock and Gold 1996; Akileswaran et al. 1999).
A carbohydrate-binding module (CBM) is a contiguous amino acid sequence within a carbohydrate-active enzyme with a discrete fold having carbohydrate-binding activity (Shoseyov et al. 2006). CBMs contribute in the binding of the target substrates to carbohydrate-degrading enzymes, and its catalytic modules is widely believed to perform three general roles defined as a proximity effect, a targeting function, and a disruptive function (Din et al. 1994; Bolam et al. 1998; Ali et al. 2001; Boraston et al. 2004; Herve et al. 2010). In this study, seven (7) CBM families namely CBM 2, 6, 13, 32, 34, 48, and 50 were detected in AB1 microcosm. CBM2 has polyisoprenoid-binding protein Yce1 as its representative. The primary function of CBM2 is to bind cellulose or xylan and bring it to proximity of cellulose- and xylan-degrading enzymes. Polyisoprenoid-binding proteins could be involved in substrate oxidation in order to facilitate the breakdown of the plant cell wall.
CBM13, classified as type-C CBM, with a pocket-like sugar-binding site generally recognizes one or two monosaccharide units within a polysaccharide (Fujimoto 2013). It shows specificity for the backbone of xylan, but it is found not only in xylanases (EC 22.214.171.124), but also in other GHs, several lyases, and glycosyltransferases (Fujimoto 2013). The detected CBM50 have two representatives, N-acetylmuramoyl-l-alanine amidase and bifunctional metallophosphatase/5′-nucleotidase. N-Acetylmuramoyl-l-alanine amidase is an autolysin that hydrolyzes the amide bond between N-acetylmuramoyl and l-amino acids in certain cell wall glycopeptides. The enzyme cleaves the septum to release daughter cells after cell division (Herbold and Glaser 1975; Ward et al. 1982). Bifunctional metallophosphatase/5′-nucleotidase (EC 126.96.36.199) catalyzes the degradation of periplasmic UDP-glucose to uridine, glucose-1-phosphate, and inorganic phosphate. Other CBMs detected in combination with GHs are CBM32, CBM64, and CBM48, which played prominent roles in facilitating the degradation of the complex carbohydrates by bringing the substrates in close contact to the enzymes.
The carbohydrate esterases (CEs) are widely used as biocatalysts in industrial processes and biotechnology (Jaeger and Reetz 1998; Bornscheuer 2002; Jaeger and Eggert 2002). In this study, only three (3) CE families—CE4, CE9, CE10—were detected in AB1 microcosm. However, the CE10 family has been nullified since most of its members appeared to be esterases active against non-carbohydrate substrates (Nakamura et al. 2017). In AB1 microcosm, CE4 is represented by polysaccharide deacetylase (Table 2), the general name given to members belonging to this family. Polysaccharide deacetylases catalyze the N- or O-deacetylation of xylan (Aspinall 1959), chitin (Tsigos et al. 2000), and peptidoglycans (Johannsen 1993). In AB1 microcosm, CE9 is represented by N-acetylglucosamine-6-phosphate deacetylase (EC 188.8.131.52) (Table 2). This enzyme is involved in the first step in the biosynthesis of amino sugar nucleotides. It catalyzes the hydrolysis of the N-acetyl group of N-acetylglucosamine-6-phosphate to yield glucosamine-6-phosphate and acetate (Vincent et al. 2004; Ferreira et al. 2006; Nakamura et al. 2017).
Glycoside hydrolases (GHs) are a widespread group of enzymes, which hydrolyze the glycosidic bond between two or more carbohydrates or between a carbohydrate and a non-carbohydrate moiety. In this study, 21 GH families were detected in AB1 microcosm. Six of these families (GH1, 10, 51, 53, 72, 79) belong to the GH-A clan (type I classical (β/α)8 glycosidases) (Naumoff 2011). GH1 is represented in AB1 microcosm by mannose-6-phosphate isomerase (catalyze the interconversion of fructose-6-phosphate and mannose-6-phosphate), polysaccharide biosynthesis protein (implicated in the production of polysaccharides), and glucokinase (catalyze the phosphorylation of glucose to glucose-6-phosphate). Others include dTDP-4-dehydrorhamnose reductase (catalyze the reduction of dTDP-6-deoxy-l-lyxo-4-hexulose to dTDP-l-rhamnose, the precursor of l-rhamnose, a component of the lipopolysaccharide core and several O antigen polysaccharides) and UDP-glucose-4-epimerase (facilitate the interconversion of UDP-glucose and UDP-galactose, which are precursors of glucose- and galactose-containing exopolysaccharides (EPS)) (Rahim et al. 2000; Fortina et al. 2003; Yoo et al. 2011).
The detection of endo-1,4-β-xylanase as the representative of GH10 in AB1 microcosm further affirms extensive deconstruction of complex plant polysaccharide in the agricultural soil in spite of spent engine oil contamination. The enzyme degrades the linear polysaccharide beta-1,4-xylan into xylose, thereby breaking down hemicellulose, one of the major components of plant cell walls (Beg et al. 2001). Functionally, similar to endo-1,4-β-xylanase are the alpha-N-arabinofuranosidase and alpha-l-arabinofuranosidase annotated for GH51, which act on alpha-l-arabinofuranosides, alpha-l-arabinans containing (1,3) and/or (1,5)-linkages, arabinoxylans, and arabinogalactans resulting in degradation of lignocelluloses (Numan and Bhosle 2006). The sole representative of GH53 in AB1 microcosm is diguanylate cyclase, which catalyzes the breakdown of guanosine triphosphate to diphosphate and cyclic di-3′,5′-guanylate (cyclic di-GMP). Cyclic di-GMP is an important messenger known for the control of cellulose biosynthesis as well as other diverse bacterial cellular functions such as virulence, motility, bioluminescence, adhesion, secretion, community behavior, biofilm formation, and cell differentiation (Hecht and Newton 1995; Galperin et al. 2001; D’Argenio and Miller 2004; Whiteley and Lee 2015).
The deconstruction of complex carbohydrates (e.g., cellulose, starch, glycogen, and xylan), mostly by microorganisms, releases short metabolizable oligosaccharides to the environment. This contributes to the functioning of an ecosystem and is essential for global carbon cycling (Berlemont and Martiny 2016). The detection of diverse complex carbohydrate deconstruction enzymes spanning several GH families such as GH13 (GH-H clan), GH31 (GH-D clan), GH3, GH37, and 63 (GH-G clan), and GH8 (GH-M clan) reflects the importance of these enzymes to the AB1 ecosystem and global carbon cycling. The short metabolizable oligosaccharides generated are fed into the central carbohydrate metabolic pathways, which not only generate energy yielding products but also produce precursor metabolites for other pathways (Neidhardt et al. 1990; Noor et al. 2010).
The facts elucidated in the preceding paragraph underscore the importance of these pathways in the normal functioning of the AB1 soil microcosm ecosystem in spite of spent engine oil contamination. The precursor metabolites are the source materials for all biomass components made by the microbial community in the microcosm: amino acids, RNA and DNA molecules, lipids, lipopolysaccharides, and peptidoglycan monomers. The cells cannot do without these components. Thus, there is a dire need for activation of enzyme machinery needed for these essential pathways.
Glycosyltransferases (GTs) are enzymes that catalyze the synthesis of glycosidic linkages by the transfer of a sugar residue from a donor substrate to an acceptor (Lairson et al. 2008; Ardèvol and Rovira 2015). The structure of GTs adopts one of threefold, namely GT-A, GT-B, and GT-C (Gloster 2014). In this study, the GT2 family represents the GT-A fold (inverting). Enzymes/proteins annotated for GT2 family in AB1 microcosm are glucan glucosyltransferase H, sensor histidine kinase, cellulose synthase catalytic subunit (UDP-forming), cysteine-tRNA ligase, non-ribosomal peptide synthetase, and DNA-binding response regulator. These enzymes are involved in biosynthesis of osmoregulated periplasmic glucans, signal transduction pathways upstream of many processes including various metabolic, virulence and homeostatic pathways, synthesis of cellulose, cysteine metabolism, aminoacyl-tRNA biosynthesis, among others (Wolanin et al. 2002; Strieker et al. 2010; Fuhs et al. 2015; Fuhs and Hunter 2017).
Of the eleven (11) GT families retrieved from AB1 microcosm, seven (7) belong to the GT-B fold. They are GT1, GT20, GT28, GT4, GT41, GT5, and GT9. Aside from GT20, GT4, and GT5 having retaining functions, the others possess inverting functions (Schmid et al. 2016). The enzymes annotated for the GT families in GT-B and GT-C (GT83) folds perform diverse functions in AB1 microcosm. This include glycan biosynthesis (GT20), peptidoglycan biosynthesis and maintenance of the rod cell shape and elongation of the lateral wall of the cell (GT28), lipopolysaccharide biosynthesis and bacterial outer membrane biogenesis (GT4, GT9), and lipopolysaccharide metabolism and cell wall/membrane/envelope biogenesis (GT83) (Henriques et al. 1998; van Heijenoort 2001; Bretscher et al. 2005).
It is noteworthy that most of the enzymes/genes annotated for AB1 microcosm using the CAZy database were also detected using the GhostKOALA, COG, and NCBI’s CDD databases. This further affirms the importance of using diverse metagenomic analysis tools to characterize environmental metagenomes. The deployment of these tools allows for unbiased and comprehensive detection and elucidation of targeted genes and enzymes.
Taxonomic classification of the AB1 sequences annotated for enzymes/genes involved in carbohydrate metabolism revealed the preponderance of Proteobacteria phylum. This is not surprising as the phylum is a compendium of members that are metabolically diverse with ability to utilize a wide range of organic and inorganic compounds and of living under diverse environmental conditions. The dominance of Pseudomonas species may be attributed to its metabolic versatility and genetic plasticity. The genus is reputed to possess remarkable nutritional versatility with majority growing on more than 50 different substrates, some on more than 100 employing various pathways (Stanier et al. 1966; Palleroni and Doudoroff 1972; Palleroni 1993). Their ability to thrive in habitats with temperature range of 4–42 °C, a pH between 4 and 8, and containing simple or complex organic compounds explains their ubiquity, survivability, and dominance in diverse soil environments (Moore et al. 2006). Furthermore, the detection of various carbohydrate-active enzymes and genes cutting across various phyla and not limited to related phylogenetic groups is a clear indication of involvement of lateral and horizontal gene transfer within the microbial community.
In summary, while the effects of SEO contamination on the microbial community structure and function in AB1 microcosm are profound, the microbial community maintains essential metabolic and cellular processes. The stress imposed on the agricultural soil by SEO contamination allowed the shift of the microbial community to utilization of stored and easily metabolized carbohydrates. The deconstruction of complex carbohydrate compounds in the soil liberates metabolizable oligosaccharides, which generates products (via diverse metabolic pathways) that are precursor metabolites for the biosynthesis of nucleotides, amino acids, lipids, lipopolysaccharides, and peptidoglycan monomers needed as building blocks and cellular constituents. Assemblage of complex carbohydrates through enzymatic formation of glycosidic linkages mediated by glycosyltransferases assists in construction of new cells and its constituents while the detection of industrial and biotechnologically important enzymes such as xylanases, endoglucanases, and α- and β-glucosidases revealed the soil as important reservoir of these enzymes. The use of various metagenomics analysis tools enunciated in this study not only reveal the diverse carbohydrate metabolic pathways in AB1 microcosm but also enrich our understanding of the various carbon fluxes in SEO-contaminated agricultural soil.
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Salam, L.B. Detection of carbohydrate-active enzymes and genes in a spent engine oil-perturbed agricultural soil. Bull Natl Res Cent 42, 10 (2018). https://doi.org/10.1186/s42269-018-0013-6
- Spent engine oil
- Agricultural soil
- Soil microcosm
- Illumina sequencing
- Carbohydrate metabolism
- Carbohydrate-active enzymes
- Microbial enzymes and genes