南京林业大学学报(自然科学版) ›› 2024, Vol. 48 ›› Issue (6): 102-110.doi: 10.12302/j.issn.1000-2006.202212029
张苗1(), 阮宏华1,*(
), 沈彩芹2, 丁学农2, 曹国华2
收稿日期:
2022-12-05
修回日期:
2023-03-23
出版日期:
2024-11-30
发布日期:
2024-12-10
通讯作者:
*阮宏华(hhruan@njfu.edu.cn),教授。作者简介:
张苗(1097380894@qq.com)。
基金资助:
ZHANG Miao1(), RUAN Honghua1,*(
), SHEN Caiqin2, DING Xuenong2, CAO Guohua2
Received:
2022-12-05
Revised:
2023-03-23
Online:
2024-11-30
Published:
2024-12-10
摘要:
【目的】探讨长期施用不同浓度沼液对杨树(Populus spp.)人工林土壤碳、氮、磷组分含量的影响,为科学施用沼液,改善杨树人工林土壤质量,促进杨树人工林可持续发展提供理论依据。【方法】以苏北沿海地区杨树人工林为研究对象,试验采用随机区组设计,设置了4种沼液施用处理,分别为对照(0 m3/hm2, CK)、低浓度(125 m3/hm2, L)、中浓度(250 m3/hm2, M)和高浓度(375 m3/hm2, H),自2012年开始每年定期在杨树人工林中施用。采用连续土钻法采集不同土壤深度0~20 cm(表层),≥20~40 cm(中层)和≥40~60 cm(深层)土壤样品,研究施用不同浓度沼液对杨树人工林不同土层土壤碳、氮、磷主要组分含量及其计量比的影响。【结果】施用沼液显著增加了表层土壤(0~20 cm)有机碳(SOC)、可溶性有机碳(DOC)、土壤微生物生物量碳(MBC)、土壤总氮(TN)、土壤微生物生物量氮(MBN)、土壤全磷(TP)、土壤有效磷(AP)含量,显著降低了表层土壤碳氮质量比(C/N)和土壤微生物生物量碳氮比(MBC/MBN);同时施加沼液也显著增加了≥20~40 cm土层土壤DOC、TP含量。而在深层土壤(≥40~60 cm)中,施加沼液对土壤C、N、P各项指标均无显著影响。沼液显著降低了各土层土壤pH。【结论】沼液作为一种优质的速效有机肥料,能显著增加表层土壤C、N、P等速效养分,对深层土壤无显著影响。同时,施用适量沼液也可以降低沿海盐碱地土壤pH,以及土壤C/N,对改善土壤肥力有一定的作用,但过度施加是否会引起土壤磷素淋洗、氮淋溶风险而造成生态环境污染还有待进一步研究。
中图分类号:
张苗,阮宏华,沈彩芹,等. 长期施用沼液对杨树人工林土壤碳氮磷及其计量比的影响[J]. 南京林业大学学报(自然科学版), 2024, 48(6): 102-110.
ZHANG Miao, RUAN Honghua, SHEN Caiqin, DING Xuenong, CAO Guohua. Effects of long-term application of biogas slurry on soil carbon, nitrogen, phosphorus and their metering ratio in poplar plantations[J].Journal of Nanjing Forestry University (Natural Science Edition), 2024, 48(6): 102-110.DOI: 10.12302/j.issn.1000-2006.202212029.
表1
沼液处理组间杨树人工林土壤C、N、P化学计量指标相关系数"
指标 index | pH | 含水率 moisture content | DOC | SOC | MBC | TN | MBN | TP | AP | C/N |
---|---|---|---|---|---|---|---|---|---|---|
含水率moisture content | -0.347** | |||||||||
DOC | -0.404** | 0.574** | ||||||||
SOC | -0.466** | 0.583** | 0.871** | |||||||
MBC | -0.313** | 0.514** | 0.805** | 0.826** | ||||||
TN | -0.322** | 0.559** | 0.915** | 0.774** | 0.714** | |||||
MBN | -0.422** | 0.577** | 0.906** | 0.888** | 0.854** | 0.824** | ||||
TP | -0.460** | 0.441** | 0.595** | 0.675** | 0.644** | 0.504** | 0.687** | |||
AP | -0.481** | 0.220* | 0.302** | 0.390** | 0.316** | 0.228* | 0.359** | 0.402** | ||
C/N | 0.246* | -0.320** | -0.641** | -0.448** | -0.407** | -0.780** | -0.511** | -0.171 | -0.107 | |
MBC/MBN | 0.126 | -0.373** | -0.363** | -0.283** | -0.105 | -0.353** | -0.425** | -0.221* | -0.09 | 0.305** |
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