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Lignocellulose

Lignocellulose is a complex structural material found in the cell walls of plants, composed primarily of cellulose, hemicellulose, and lignin.
It is an abundant and renewable natural resource with potential applications in biofuels, biochemicals, and other industrial processes.
Lignocellulosic biomass, such as agricultural residues, forestry waste, and dedicated energy crops, is a promising feedstock for the production of sustainable fuels and chemicals.
Optimizing the extraction, pretreatment, and conversion of lignocellulose is an active area of research, requirng reliable protocols and accurate comparisons to accelerate progress and improve reproducibility.

Most cited protocols related to «Lignocellulose»

Together with L.edodes, 26 fungal species assigned to Basidiomycota or Ascomycota were used in the phylogenetic analysis. The protein sequences of these 26 fungi were compared by BLASTP with e-value < 1e-5 and hit number < 500. Then, the BLASTP result was analyzed by OrthoMCL[73 (link)] with default parameters to get the orthologous genes, and 756 single-copy orthologous genes were determined. Multiple sequence alignments of these 756 genes were calculated by MAFFT v7.158b [74 (link)] software, and were combined into a long sequence for each species. Then, the conserved block regions of the alignment were picked out by Gblocks 0.91b with default parameters [75 (link)] of the software, and the final alignment length was 193323 aa. With the input of this alignment, phylogenetic tree was constructed by RAxML-8.0.26 [76 (link)] software with bootstrap 1000. Three fossil calibration points [77 (link)] were fixed in the molecule clock analysis: the most recent common ancestor (MRCA) of Coprinopsis cinerea, Laccaria bicolor and Schizophyllum commune were diverged at 122.74 MYA; the MRCA of Serpula lacrymans and Coniophora puteana were diverged at 104.23 MYA; the MRCA of Pichia stipitis, Aspergillus niger, Cryphonectria parasitica, Stagonospora nodorum and Trichoderma reesei were diverged at 517.55 MYA. Then, the divergence time of other nodes was calculated by r8s v1.80 [78 (link)] software with TN algorithm, PL method and the smoothing parameter value set to 1.8 through cross-validation. Based on the ultrametric tree, the orthologous gene family expansion was calculated by CAFE version 3 [25 (link)] software.
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Publication 2016
Amino Acid Sequence Anesthesia, Conduction Ascomycetes Aspergillus niger Basidiomycota Coniophora puteana Coprinus cinereus Cryphonectria parasitica Fungal Proteins Fungi Genes Laccaria bicolor Parastagonospora nodorum Scheffersomyces stipitis Schizophyllum commune Sequence Alignment Serpula lacrymans Trees Trichoderma reesei
The A. niger strains used were N402 [57] (link) and AB4.1 pyrG[7] (link) or as specified otherwise. Strains were maintained on potato dextrose agar (Oxoid). All AB4.1 cultures were supplemented by 10 mM uridine (Sigma). Cultures were incubated at 28°C until they had conidiated. Spores were harvested into 0.1% (v/v) Tween 20 (Sigma). ΔxlnR and ΔcreA strains are A. niger AB4.1 pyrG containing a deletion of the respective open reading frame. Strains were constructed using the method developed by Scherer and Davis. [58] (link) based on recombination between a plasmid containing the flanking region of the gene of interest and the chromosome. As a selection/counter-selection marker we used the gene coding for the orotidine-5-phosphate decarboxylase [59] (link) (pyrG, from Aspergillus oryzae). After transformation of A. niger, cells were selected for uridine prototrophy, confirming integration of the plasmid into the chromosome. After purification of the transformants, release of the selective pressure for the integrated plasmid was achieved by propagating the clones twice on potato dextrose agar containing 10 mM uridine. Selection for cells that had excised the plasmid from the chromosome was done by plating them on media containing 4 mM of 5-fluoro-orotic acid (Melford) and 1.6 mM uridine. Deletion of creA or xlnR was confirmed by PCR using internal and external oligonucleotide primers and by sequencing around the respective loci.
Liquid batch cultures were inoculated with spores to a final concentration of 106 spores/ml. A. niger was grown in 100 ml of minimal media [all l−1: NaNO3, 6 g; KCl, 0.52 g; MgSO4.7H2O, 0.52 g; KH2PO4, 1.52 g; Na2B4O7.10H2O, 0.008 mg; CuSO4.5H2O, 0.16 mg; FePO4.H2O, 0.16 mg; MnSO4.4H2O, 0.16 mg; NaMoO4.2H2O, 0.16 mg; ZnSO4, 1.6 mg] with the appropriate carbon source added to a final concentration of 1% (w/v) in 250 ml Erlenmeyer flasks at 28°C, shaken at 150 rpm. The standard time-course consisted of growth for 48 h in 1% (w/v) glucose media, after which mycelia were removed by filtration through Miracloth (Merck), washed thoroughly with media devoid of carbon source, and transferred to fresh media containing 1% (w/v) ball-milled wheat straw as sole carbon source. Incubation was continued for 24 h. Glucose was then added exogenously to a final concentration of 1% (w/v) and incubation continued for 5 hours. Figure 1 shows an image of a mycelial clump that was magnified using a Nikon SMZ1000 stereomicroscope and the picture taken using a Nikon 4500 camera.
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Publication 2012
Agar Aspergillus oryzae Batch Cell Culture Techniques Carbon Cells Chromosomes Clone Cells Deletion Mutation ferric phosphate Filtration Genes Glucose Mycelium Oligonucleotide Primers Orotic Acid Orotidine-5'-Phosphate Decarboxylase Plasmids Pressure Recombination, Genetic Solanum tuberosum Spores Strains Sulfate, Magnesium Triticum aestivum Tween 20 Uridine
The polysaccharides were extracted as the method from Peng et al. with minor modification [15 (link)]. The crude cell wall material was suspended in 0.5% (w/v) ammonium oxalate and heated for 1 h in a boiling water bath, and the supernatants were combined as total pectin. The remaining pellet was suspended in 4 M KOH containing 1.0 mg mL-1 sodium borohydride for 1 h at 25°C, and the combined supernatant was neutralized, dialyzed and lyophilized as hemicelluloses. The KOH non-extractable residue was further extracted with acetic-nitric acids for 1 h at 100°C and the remaining pellet was defined as crystalline cellulose. All samples were carried out in triplicate for wall fractionations.
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Publication 2012
Acetic Acids Ammonium Oxalate Bath Cellulose Cell Wall hemicellulose Pectins Polysaccharides Radiotherapy Dose Fractionations sodium borohydride
Carbohydrate-active enzymes (CAZymes) were classified separately by HMM search of dbCAN HMMs 4.0 [82 (link)] (default cutoff threshold) and BLASTP search of CAZy datebase [83 (link)] (evalue < = 1e-6 && covered fraction ratio > = 0.2, maximum hit number is 500). Then, according to the common results of these 2 methods, a series of more strict thresholds (BLASTP hit number and evalue, S19 Table) of each CAZyme family were determined by median values of 26 fungal genomes. Finally, the blastp results screened with the new threshold were added to the common results, to obtain the final CAZyme annotation. Therefore, the identification process used here is distinct from that employed by the CAZy system [83 (link)], suggesting the possibility of occasional discrepancies with previously published results. Lignocellulolytic Genes were identified mainly by the Swiss-Prot annotation with key words (S20 Table) among the CAZymes. Transcription factors were identified by a set of InterPro codes (S14 Table) which were collected according to TRANSFAC [84 (link)] and FTFD databases [85 (link)].
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Publication 2016
Carbohydrates Enzymes Genes Genome, Fungal Hypertelorism, Severe, With Midface Prominence, Myopia, Mental Retardation, And Bone Fragility Transcription Factor
Surface sediment samples of 2 g fine grained organic rich sandy mud were overlaid with 2 ml of the natural estuarine bottom water and were added to 20 ml sterile glass vials containing sterile oxygen sensor spots (PreSens Precision Sensing) with ca. 15 ml of oxygenated headspace. The oxygen sensor spot was positioned at the sediment – seawater interface to measure benthic O2 concentrations, and additional sensor spots were placed in the headspace of two flasks to measure gaseous O2 levels throughout the incubation. Lignocellulose was extracted from wheat stems as described previously (Crawford and Crawford, 1976), pulverized into powder and added to the sediment at a concentration of 5 mg per g sediment in triplicate. This concentration of organic matter is realistic for the sampled lagoon where average macrophyte biomass is 9 (+/−1.2) mg cm2 (Valiela et al., 1992) and carbon content in the upper meter of sediment is roughly 6% (Foster and Fulweiler, 2014). Separate vials that did not receive lignocellulose were also set up as controls. Vials were crimp sealed with 15 ml of headspace using sterile rubber stoppers and incubated in the dark at room temperature without shaking. Whole vials were taken (sacrificed) in triplicate for ITS1 and 16S rRNA gene sequencing at T0, 25%, 5% and 0% benthic O2 concentrations (a.s.) for treatments that received, or did not receive (control), lignocellulose. Samples for metatranscriptomics were taken only from the 25% benthic O2 concentrations. Sacrificing whole vials at each time point avoided the opening and re‐crimping of vials, which would have altered the O2 concentrations in the flasks. O2 was continuously measured several times throughout the day with the Fibox 4 using oxygen sensor spots (PreSens Precision Sensing). Replicates were then stored frozen (−20 °C) for downstream analyses.
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Publication 2018
Carbon Exanthema Freezing Gases Genes lignocellulose Oxygen Powder RNA, Ribosomal, 16S Rubber Stem, Plant Sterility, Reproductive Triticum aestivum

Most recents protocols related to «Lignocellulose»

Activated sludge used for lignocellulose incubations was divided into two groups. In the first group, 500 mL activated sludge was untreated while in the other group, activated sludge was amended with 2 mM ammonium acetate and 18 mM sodium acetate every 12 h as carbon, energy, and nitrogen source. Preliminary testing showed that this supplementation regime did not result in accumulation of either substrate. Particulate lignocellulose samples (0.2 g) were placed in nylon mesh bags with 50-µm pore size enabling passage of bacteria into the nylon bag while retaining the lignocellulose within. Nylon bags containing 0.2-g lignocellulose were incubated in activated sludge with and without nutrient amendment. At each time point (week 0, week 1, week 2), 1 mL activated sludge and 0.2-g lignocellulose samples were taken from reactors A, B, and C and stored at -20 °C for further analysis. A pH of approximately 8 (+ / -0.5 pH units) was maintained by adding 5-10 mL of 0.1 HCl every 2 to 3 days.
Publication 2024
The straw lignocellulose-degrading bacteria were isolated from soil samples collected at various sampling dates using the serial dilution plate method [25 (link)]. To initiate the isolation process, 1 g of soil obtained from the straw surface was thoroughly mixed and added to 9 mL of sterile water in a shaker set at 30 °C and 120 rpm for 20 min. Subsequently, the soil suspension was serially diluted and inoculated onto a straw agar medium consisting of 20 g/L of commercial straw powder (<1 mm) and 1 g/L of urea and adjusted to a pH of 7.0. Following a 7-day incubation period at 30 °C, single colonies were selected and cultured on the same medium to achieve purification. Genomic DNA extraction was performed employing a bacterial genomic DNA extraction kit (Tiangen Biochemical Technology Co. Ltd., Beijing, China). Bacteria and fungi were identified using the primers 27F/1492R and ITS1/ITS4, respectively. The obtained 16S rRNA and ITS gene sequences were compared using the Ezbiocloud and NCBI databases. After the removal of potential clonal duplicates, a total of 59 bacterial and 14 fungal strains were successfully isolated, and their glycerol stocks were prepared and stored at −80 °C.
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Publication 2024
R package SQMtools [64 (link)] was used to identify the taxonomic origin of genes related to lignocellulose degradation and nitrogen metabolism. Taxonomic information was extracted from the annotated dataset of each species using the subsetFun and subsetTax functions of SQMtools. Counts transformed into relative abundances were allocated to the corresponding substrates and bacterial phyla. Adjacency matrices were then generated and visualized using Circos webtool [65 (link)].
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Publication 2024
The organic matter (%) was quantified through the loss-on-ignition method by following Wu et al. [39] (link). This method involves preparing the sample, extracting organic matter, and quantifying it through techniques such as gravimetric analysis or spectroscopy. The content of lignocellulose in each treatment was estimated. For that, hemicellulose in soil was determined by separate determination of neutral detergent fibers (NDF) and acid detergent fibers (ADF) [40] (link). Lignin was determined as Klason lignin using 72% (v/v) sulfuric acid [41] (link), while cellulose content was measured at 620 nm using anthrone reagent [42] (link).
Publication 2024
Using cDNA obtained by reverse transcription as a template, RT-PCR amplification of xynF1 (NCBI ID: 4,980,082), abnC (NCBI ID: 4,979,546), cbhC (NCBI ID: 4,982,491), bglM (NCBI ID: 4,984,238), and eglD (NCBI ID: 4,988,091) was carried out using gene-specific primers. The PCR products were purified using the DNA Gel Extraction Kit (Sangon Biotech Co., Ltd., Shanghai, China), ligated into the One Step ZTOPO-Blunt/TA vector (Zhuangmeng Technology Co., Ltd., Beijing, China) and transformed into Escherichia coli DH5α. The clones were verified by DNA sequencing (Sangon Biotech Co., Ltd., Shanghai, China). Then, intron-spanning primers were designed for PCR validation based on the five lignocellulose-degrading enzyme genes xynF1, abnC, cbhC, bglM and eglD. The primers are listed in the Supplemental Table S1.
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Publication 2024

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Avicel PH-101 is a microcrystalline cellulose product manufactured by Merck Group. It is a white, odorless, and tasteless powder that is used as an excipient in the pharmaceutical and dietary supplement industries.
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Beechwood xylan is a type of hemicellulose extracted from the wood of beech trees. It is a complex polysaccharide composed of xylose units. Beechwood xylan is commonly used as a reference material in the analysis and characterization of plant cell wall components.
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Carboxymethylcellulose (CMC) is a water-soluble cellulose derivative. It is used as a thickening, suspending, and stabilizing agent in various laboratory applications.
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More about "Lignocellulose"

Lignocellulose is a complex and abundant natural material found in the cell walls of plants.
It is primarily composed of cellulose, hemicellulose, and lignin, making it a promising feedstock for biofuels, biochemicals, and other industrial applications.
Optimizing the extraction, pretreatment, and conversion of lignocellulosic biomass, such as agricultural residues, forestry waste, and dedicated energy crops, is an active area of research.
To accelerate progress and improve reproducibility, researchers often use standardized materials like Avicel PH-101 (a microcrystalline cellulose) and Beechwood xylan (a hemicellulose), as well as analytical tools like the MiSeq or HiSeq 2000/2500 platforms and the RNeasy Plant Mini Kit for RNA extraction.
Enzymatic hydrolysis with products like Cellic® CTec2 and chemical pretreatments using sodium hydroxide or carboxymethylcellulose (CMC) are also common approaches.
By leveraging AI-driven comparisons of protocols from literature, preprints, and patents using tools like PubCompare.ai, researchers can optimize their lignocellulose research, identify the most reliable and accurate methods, and enhance the reproducibility of their work.
This holistic approach can lead to breakthroughs in the sustainable production of fuels, chemicals, and other valuable products from this abundant and renewable natural resource.