浙江农业学报 ›› 2023, Vol. 35 ›› Issue (3): 647-657.DOI: 10.3969/j.issn.1004-1524.2023.03.18
肖小兰1(
), 张浩1, 付传僡2, 刘皓1, 阮文权1,*(
)
收稿日期:2022-03-15
出版日期:2023-03-25
发布日期:2023-04-07
作者简介:肖小兰(1986—),女,江西吉安人,博士,助理研究员,主要从事固体废弃物资源化利用研究。E-mail: 516140212@qq.com
通讯作者:
*阮文权,E-mail: wqruan@jiangnan.edu.cn
基金资助:
XIAO Xiaolan1(
), ZHANG Hao1, FU Chuanhui2, LIU Hao1, RUAN Wenquan1,*(
)
Received:2022-03-15
Online:2023-03-25
Published:2023-04-07
摘要:
于餐厨有机浆液厌氧沼渣和黑水虻虫粪共堆肥的高温期筛选嗜热菌,通过酶活分析,优选能够高效降解有机物的菌株复配成嗜热菌剂进行接种,考查接种嗜热菌剂后沼渣和虫粪共堆肥的效果。结果表明,本研究共筛选得到4株细菌和4株真菌,其中,属于地衣芽孢杆菌(Bacillus licheniformis)和空气芽孢杆菌(Bacillus aerius)的细菌菌株具有较高的糖化酶、纤维素酶、漆酶、脲酶、蛋白酶和木聚糖酶活性,属于疏绵状嗜热丝孢菌(Thermomyces lanuginosus)和烟曲霉(Aspergillus fumigatus)的真菌菌株具有较高的纤维素酶和漆酶活性。将上述4种菌株复配并接种于沼渣和虫粪共堆肥后,与不接种的空白组相比,高温期延长了2 d,有机质降解率、种子发芽指数、腐殖质含量和胡富比分别由12.09%、85.98%、107.95 g·kg-1、2.67提高到15.08%、90.77%、117.40 g·kg-1、3.01。此外,接种嗜热菌剂后,堆肥第5天的厚壁菌门(Firmicutes)和放线菌门(Actinobacteria)的相对丰度分别提高到76.84%和18.12%,而酵母菌目(Saccharomycetales)的相对丰度下降到1.70%。综上,接种嗜热菌剂可延长堆肥高温期,降低植物毒性,促进腐殖化进程,优化微生物群落结构,提高堆肥质量和效率。
中图分类号:
肖小兰, 张浩, 付传僡, 刘皓, 阮文权. 嗜热菌筛选及其促进沼渣和虫粪共堆肥的效果[J]. 浙江农业学报, 2023, 35(3): 647-657.
XIAO Xiaolan, ZHANG Hao, FU Chuanhui, LIU Hao, RUAN Wenquan. Screening thermophiles to promote co-composting of biogas residue and black soldier fly larval frass[J]. Acta Agriculturae Zhejiangensis, 2023, 35(3): 647-657.
| 原料 Raw material | 含水率 Moisture content/% | 总碳 Total C/ (g·kg-1) | 总氮 Total N/ (g·kg-1) | C/N | pH | P2O5/ (g·kg-1) | K2O/ (g·kg-1) |
|---|---|---|---|---|---|---|---|
| 沼渣Biogas residue | 89.16±0.52 | 274.4±4.8 | 40.7±1.0 | 6.52±0.01 | 8.51±0.12 | 68.6±2.4 | 40.6±2.6 |
| 虫粪Larval frass | 59.88±0.25 | 336.9±14.5 | 39.9±1.1 | 8.12±0.20 | 9.12±0.12 | 65.4±1.9 | 64.3±5.3 |
| 水稻秸秆Rice straw | 12.15±0.06 | 396.6±14.6 | 12.0±0.7 | 32.65±0.69 | — | 2.9±0.8 | 94.4±2.9 |
表1 堆肥原料的基础理化性质
Table 1 Basic properties of raw materials for composting
| 原料 Raw material | 含水率 Moisture content/% | 总碳 Total C/ (g·kg-1) | 总氮 Total N/ (g·kg-1) | C/N | pH | P2O5/ (g·kg-1) | K2O/ (g·kg-1) |
|---|---|---|---|---|---|---|---|
| 沼渣Biogas residue | 89.16±0.52 | 274.4±4.8 | 40.7±1.0 | 6.52±0.01 | 8.51±0.12 | 68.6±2.4 | 40.6±2.6 |
| 虫粪Larval frass | 59.88±0.25 | 336.9±14.5 | 39.9±1.1 | 8.12±0.20 | 9.12±0.12 | 65.4±1.9 | 64.3±5.3 |
| 水稻秸秆Rice straw | 12.15±0.06 | 396.6±14.6 | 12.0±0.7 | 32.65±0.69 | — | 2.9±0.8 | 94.4±2.9 |
图4 堆肥过程中腐殖质(a)、富里酸(b)、胡敏酸(c)含量和胡富比(d)的变化
Fig.4 Dynamics of humic substance (a), fulvic aic (b), humic acid (c) contents and ration of humic acid to fluvic acid (HA/FA) (d) during composting
图5 堆肥原料(a)、空白组堆肥最终产品(b)、接种组堆肥最终产品(c)的三维荧光光谱 EX,激发波长;EM,发射波长。
Fig.5 Three dimensional fluorescence spectra raw material (a), final composting product in blank group(b) and final composting product in inoculation group (c) EX, Excitation wavelength; EM, Emission wavelength
图6 堆肥过程中门水平细菌(a)和目水平真菌(b)相对丰度的变化 B和I分别代表空白组和接种组;5、15和30分别代表第5、15、30天的堆肥样品。
Fig.6 Changes of relative abundance of bacteria at phylum level (a) and fungi at order level (b) during composting B and I represent the blank group and inoculation group, respectively. 5,15, 30 represent composting samples on 5, 15, 30 d, respectively.
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