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Accelerating the degradation of green plant waste with chemical decomposition agents

机译:使用化学分解剂促进绿色植物废物的降解

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College of Resource and Environmental Sciences, South China Agriculture University, Guangzhou 510642, China ,Guangzhou Institute of Landscape Gardening, Guangzhou 510170, China;Guangzhou Institute of Landscape Gardening, Guangzhou 510170, China;Guangzhou Institute of Landscape Gardening, Guangzhou 510170, China;College of Resource and Environmental Sciences, South China Agriculture University, Guangzhou 510642, China ;Guangzhou Institute of Landscape Gardening, Guangzhou 510170, China;Guangzhou Institute of Landscape Gardening, Guangzhou 510170, China;%Degradation of green plant waste is often difficult, and excess maturity times are typically required. In this study, we used lignin, cellulose and hemicellulose assays; scanning electron microscopy; infrared spectrum analysis and X-ray diffraction analysis to investigate the effects of chemical decomposition agents on the lignocellulose content of green plant waste, its structure and major functional groups and the mechanism of accelerated degradation. Our results showed that adding chemical decomposition agents to Ficus microcarpa var. pusillifolia sawdust reduced the contents of lignin by 0.53%—11.48% and the contents of cellulose by 2.86%-7.71%, and increased the contents of hemicellulose by 2.92%-33.63% after 24 h. With increasing quantities of alkaline residue and sodium lignosulphonate, the lignin content decreased. Scanning electron microscopy showed that, after F. microcarpa var. pusillifolia sawdust was treated with chemical decomposition agents, lignocellulose tube wall thickness increased sig-nificantlylncreases of 29.41%, 3.53% and 34.71% were observed after treatment with NaOH, alkaline residue and sodium lignosulphonate, respectively. Infrared spectroscopy showed that C=O and aromatic skeleton stretching absorption peaks were weakened and the C-H vibrational absorption peak from out-of-plane in positions 2 and 6 (S units) (890-900 cm"1) was strengthened after F. microcarpa var. pusillifolia sawdust was treated with chemical decomposition agents, indicating a reduction in lignin content. Several absorption peaks [i.e., C-H deformations (asymmetry in methyl groups, -CH3- and -CH2-) (1450 -1460 cm"1); Aliphatic C-H stretching in methyl and phenol OH (1370-1380 cm"1); C=O stretching (cellulose and hemicellulose) (1040-1060 cm"1)] that indicate the presence of a chemical bond between lignin and cellulose was reduced, indicating that the chemical bond between lignin and cellulose had been partially broken. X-ray diffraction analysis showed that NaOH, alkaline residue and sodium lignosulphonate can reduce the relative crystallinity of lignocellulose in F. microcarpa var. pusillifolia by 2.64%, 13.24%, 12.44%, respectively. The C-H vibrational absorption peak from out-of-plane in positions 2 and 6 (S units) comes from the vibration of the sugar anomeric carbon. Because lignin is a phenolic, not carbohydrate polymer, the relative absorption intensity of this peak should be stronger at lower lignin contents. Compared to CK, the peak intensities increased in treatments Tl, T5 and T9, indicating reduced lignin contents and increased sugar contents after CDA treatment.
机译:华南农业大学资源与环境学院,广州510642,广州园林学院,广州510170;广州园林学院,广州510170;广州园林学院,广州510170;华南农业大学资源与环境科学学院,广州510642;广州园林绿化学院,广州510170;广州园林绿化学院,广州510170;绿色植物废弃物的降解通常很困难,并且通常需要过多的成熟时间。在这项研究中,我们使用了木质素,纤维素和半纤维素检测方法。扫描电子显微镜;红外光谱和X射线衍射分析,研究化学分解剂对绿色植物废料中木质纤维素含量,其结构和主要官能团以及加速降解机理的影响。我们的结果表明,将化学分解剂添加到无花果榕中。 24小时后,木屑木屑使木质素含量降低了0.53%-11.48%,纤维素含量降低了2.86%-7.71%,半纤维素含量提高了2.92%-33.63%。随着碱性残渣和木质素磺酸钠含量的增加,木质素含量下降。扫描电子显微镜显示,在小果番荔枝变种之后。用化学分解剂处理过的大叶锯末木屑,用NaOH,碱性残留物和木质素磺酸钠处理后,木质纤维素管壁厚度分别增加了29.41%,3.53%和34.71%。红外光谱分析表明,小果木薯后,C = O和芳香族骨架拉伸吸收峰减弱,位置2和6(S单位)(890-900 cm” 1)的面外CH振动吸收峰增强​​。用化学分解剂处理过的变质朴木屑木屑,表明木质素含量降低,有几个吸收峰(即CH形变(甲基,-CH3-和-CH2-不对称)(1450 -1460 cm“ 1;在甲基和苯酚OH(1370-1380 cm“ 1)中的脂肪族CH拉伸; C = O拉伸(纤维素和半纤维素)(1040-1060 cm” 1)]表明木质素和纤维素之间存在化学键,表明木质素和纤维素之间的化学键已被部分破坏。 X射线衍射分析表明,NaOH,碱性残留物和木质素磺酸钠可以降低小果木纤维中木质纤维素的相对结晶度。脓疱分别为2.64%,13.24%,12.44%。位置2和6(S单位)的面外C-H振动吸收峰来自于糖异头碳的振动。由于木质素是酚类而非碳水化合物聚合物,因此在较低的木质素含量下,该峰的相对吸收强度应更强。与CK相比,在处理T1,T5和T9中峰强度增加,表明CDA处理后木质素含量降低和糖含量升高。

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