College of Resource and Environmental Sciences, South China Agriculture University, Guangzhou 510642, China.
J Environ Manage. 2011 Oct;92(10):2708-13. doi: 10.1016/j.jenvman.2011.06.011. Epub 2011 Jul 16.
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 significantlyIncreases of 29.41%, 3.53% and 34.71% were observed after treatment with NaOH, alkaline residue and sodium lignosulphonate, respectively. Infrared spectroscopy showed that CO 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, -CH(3)- and -CH(2)-) (1450-1460 cm(-1)); Aliphatic C-H stretching in methyl and phenol OH (1370-1380 cm(-1)); CO 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 T1, T5 and T9, indicating reduced lignin contents and increased sugar contents after CDA treatment.
绿色植物废物的降解通常较为困难,且通常需要较长的成熟时间。在这项研究中,我们使用木质素、纤维素和半纤维素测定、扫描电子显微镜、红外光谱分析和 X 射线衍射分析来研究化学分解剂对绿色植物废物木质纤维素含量、结构和主要功能基团的影响,以及加速降解的机制。我们的结果表明,向榕叶下珠锯末中添加化学分解剂后,在 24 h 内木质素的含量降低了 0.53%-11.48%,纤维素的含量降低了 2.86%-7.71%,半纤维素的含量增加了 2.92%-33.63%。随着碱性残渣和木质素磺酸钠用量的增加,木质素含量降低。扫描电子显微镜显示,榕叶下珠锯末经化学分解剂处理后,木质纤维素管壁厚明显增加,经 NaOH、碱性残渣和木质素磺酸钠处理后分别增加了 29.41%、3.53%和 34.71%。红外光谱显示,CO 和芳香骨架伸缩吸收峰减弱,木质素的 C-H 振动吸收峰从面外位置 2 和 6(S 单元)(890-900 cm(-1)))得到增强,表明木质素含量降低。几个吸收峰[即 C-H 变形(甲基不对称,-CH(3)-和-CH(2)-)(1450-1460 cm(-1))]; 脂肪族 C-H 伸缩在甲基和酚羟基(1370-1380 cm(-1));CO 伸缩(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部分断裂。X 射线衍射分析表明,NaOH、碱性残渣和木质素磺酸钠可使榕叶下珠锯末的木质纤维素相对结晶度分别降低 2.64%、13.24%和 12.44%。C-H 振动吸收峰从面外位置 2 和 6(S 单元)来自糖端基碳原子的振动。由于木质素是一种酚类,而不是碳水化合物聚合物,因此在木质素含量较低时,该峰的相对吸收强度应更强。与 CK 相比,T1、T5 和 T9 处理的峰强度增加,表明 CDA 处理后木质素含量降低,糖含量增加。