生态环境学报 ›› 2026, Vol. 35 ›› Issue (8): 1256-1266.DOI: 10.16258/j.cnki.1674-5906.2026.08.009
王湘阳1,2,3(
), 李晨华1,2, 梁萌1,2,3, 刘燕1,2,*(
)
收稿日期:2025-12-22
修回日期:2026-05-20
接受日期:2026-05-27
出版日期:2026-08-18
发布日期:2026-08-17
通讯作者:
E-mail: 作者简介:王湘阳(2000年生),女,硕士研究生,研究方向为干旱区土壤与微生物生态。E-mail: wangxiangyang23@mails.ucas.ac.cn
基金资助:
Wang Xiangyang1,2,3(
), Li Chenhua1,2, Liang Meng1,2,3, Liu Yan1,2,*(
)
Received:2025-12-22
Revised:2026-05-20
Accepted:2026-05-27
Online:2026-08-18
Published:2026-08-17
摘要:
【目的】旨在研究灰漠土开垦与长期施肥模式下土壤化学性质和固氮微生物nifH基因群落多样性的响应特征。【方法】选择中国科学院阜康荒漠生态站长期施肥试验地(自1990年至今)的9个处理:不施肥(CK)、化肥(PK、NK、NP、N2P2、NPK、N2P2K)、化肥配施有机肥(NPKR(R:150kg秸秆)、NPKM(M:农家肥)),与同一毗邻荒漠(包含裸地、草本与灌木覆被),探究荒漠开垦过程中土壤固氮微生物nifH基因群落的多样性变化。【结果】与荒漠土壤相比,开垦后的所有处理中,土壤变形菌门的相对丰度显著减少,尤其是α变形菌纲,CK、NPKR和NPKM处理的降幅最大(79.40%-81.93%)。蓝细菌门相对丰度显著增加,NP、N2P2、NPK、N2P2K和NPKR增幅最大(233.18%-354.81%)。开垦与长期施肥显著增加了土壤固氮微生物nifH基因群落多样性指数(Shannon);土壤电导率和有机碳是固氮微生物nifH基因群落分异的最大影响因子。【结论】荒漠开垦和长期施肥显著增加了nifH基因多样性,开垦与施肥后的固氮微生物nifH基因群落与荒漠中裸地、草本覆被具有最大微生物群落分异,与灌木覆被的微生物群落结构相近。氮磷肥施用对于加强土壤有机碳固持、提升固氮微生物nifH基因群落多样性及其贡献率具有正向作用。
中图分类号:
王湘阳, 李晨华, 梁萌, 刘燕. 灰漠土开垦与长期施肥对土壤nifH基因多样性的影响[J]. 生态环境学报, 2026, 35(8): 1256-1266.
Wang Xiangyang, Li Chenhua, Liang Meng, Liu Yan. Effects of Grey Desert Soil Cultivation and Long-Term Fertilization on the Diversity of Soil nifH Genes[J]. Ecology and Environmental Sciences, 2026, 35(8): 1256-1266.
| 理化性质和基因拷贝数 | 开垦 | 施肥 | |||
|---|---|---|---|---|---|
| F值 | p值 | F值 | p值 | ||
| pH | 138.43 | *** | 24.55 | *** | |
| 电导率/(mS·cm−1) | 2230 | *** | 132.2 | *** | |
| 全氮质量分数/(g·kg−1) | 9.96 | ** | 26.53 | *** | |
| 全磷质量分数/(g·kg−1) | 87.06 | *** | 8.11 | *** | |
| 土壤有机碳质量分数/(g·kg−1) | 17.66 | *** | 16.76 | *** | |
| 土壤容重/(g·cm−3) | 42.37 | *** | 11.53 | *** | |
| nifH基因拷贝数/μL−1 | 18178 | *** | 2523 | *** | |
表1 开垦和施肥对土壤理化性质和基因拷贝数的双因素方差分析结果
Table 1 Two-way ANOVA results for the effects of cultivation and fertilization on soil physicochemical properties and nifH gene copy numbers
| 理化性质和基因拷贝数 | 开垦 | 施肥 | |||
|---|---|---|---|---|---|
| F值 | p值 | F值 | p值 | ||
| pH | 138.43 | *** | 24.55 | *** | |
| 电导率/(mS·cm−1) | 2230 | *** | 132.2 | *** | |
| 全氮质量分数/(g·kg−1) | 9.96 | ** | 26.53 | *** | |
| 全磷质量分数/(g·kg−1) | 87.06 | *** | 8.11 | *** | |
| 土壤有机碳质量分数/(g·kg−1) | 17.66 | *** | 16.76 | *** | |
| 土壤容重/(g·cm−3) | 42.37 | *** | 11.53 | *** | |
| nifH基因拷贝数/μL−1 | 18178 | *** | 2523 | *** | |
| 施肥处理 | pH | 电导率/(mS·cm−1) | 全氮质量分数/(g·kg−1) | 全磷质量分数/(g·kg−1) | 土壤有机碳质量分数/(g·kg−1) | 土壤容重/(g·cm−3) |
|---|---|---|---|---|---|---|
| Bd | 8.67±0.06c | 10.38±0.76a | 0.31±0.03e | 0.58±0.04cd | 3.94±0.41e | 1.16±0.02cde |
| Gd | 9.14±0.06a | 4.17±0.61d | 0.38±0.05de | 0.45±0.05d | 3.99±0.34e | 1.10±0.03e |
| Sd | 8.82±0.04b | 5.28±0.35c | 0.77±0.05a | 0.64±0.06bcd | 7.97±0.89a | 1.13±0.02de |
| Desert | 8.84±0.06b | 7.75±0.63b | 0.40±0.04cde | 0.55±0.05cd | 4.56±0.38de | 1.13±0.02de |
| CK | 9.00±0.06a | 0.55±0.06e | 0.46±0.04cd | 0.85±0.06abc | 4.47±0.54de | 1.37±0.05ab |
| PK | 8.70±0.03bc | 0.60±0.06e | 0.52±0.04bc | 1.03±0.11a | 4.76±0.35de | 1.50±0.10a |
| NK | 8.80±0.05bc | 0.41±0.06e | 0.41±0.06cde | 0.84±0.07abc | 4.69±0.34de | 1.30±0.11bcd |
| NP | 8.70±0.04bc | 0.35±0.05e | 0.44±0.06cde | 0.52±0.04cd | 5.33±0.86cde | 1.42±0.04ab |
| N2P2 | 8.50±0.03d | 0.41±0.05e | 0.45±0.05cd | 1.12±0.19a | 5.78±0.14bcd | 1.28±0.05bcde |
| NPK | 8.80±0.03bc | 0.34±0.03e | 0.41±0.03cde | 0.97±0.13ab | 5.31±0.68cde | 1.34±0.12abc |
| N2P2K | 8.70±0.04bc | 0.33±0.02e | 0.65±0.07ab | 1.12±0.18a | 6.30±0.32bc | 1.37±0.04ab |
| NPKR | 8.80±0.03bc | 0.29±0.04e | 0.51±0.03cd | 0.96±0.15ab | 6.31±0.49bc | 1.13±0.03de |
| NPKM | 8.70±0.05bc | 0.33±0.04e | 0.70±0.06a | 1.14±0.17a | 7.13±0.42ab | 1.14±0.05de |
表2 灰漠土开垦与长期施肥对表层土壤(0-20 cm)理化性质的影响
Table 2 Effects of long-term fertilization on physical and chemical properties of surface soil(0?20 cm)under cultivation of grey desert soil
| 施肥处理 | pH | 电导率/(mS·cm−1) | 全氮质量分数/(g·kg−1) | 全磷质量分数/(g·kg−1) | 土壤有机碳质量分数/(g·kg−1) | 土壤容重/(g·cm−3) |
|---|---|---|---|---|---|---|
| Bd | 8.67±0.06c | 10.38±0.76a | 0.31±0.03e | 0.58±0.04cd | 3.94±0.41e | 1.16±0.02cde |
| Gd | 9.14±0.06a | 4.17±0.61d | 0.38±0.05de | 0.45±0.05d | 3.99±0.34e | 1.10±0.03e |
| Sd | 8.82±0.04b | 5.28±0.35c | 0.77±0.05a | 0.64±0.06bcd | 7.97±0.89a | 1.13±0.02de |
| Desert | 8.84±0.06b | 7.75±0.63b | 0.40±0.04cde | 0.55±0.05cd | 4.56±0.38de | 1.13±0.02de |
| CK | 9.00±0.06a | 0.55±0.06e | 0.46±0.04cd | 0.85±0.06abc | 4.47±0.54de | 1.37±0.05ab |
| PK | 8.70±0.03bc | 0.60±0.06e | 0.52±0.04bc | 1.03±0.11a | 4.76±0.35de | 1.50±0.10a |
| NK | 8.80±0.05bc | 0.41±0.06e | 0.41±0.06cde | 0.84±0.07abc | 4.69±0.34de | 1.30±0.11bcd |
| NP | 8.70±0.04bc | 0.35±0.05e | 0.44±0.06cde | 0.52±0.04cd | 5.33±0.86cde | 1.42±0.04ab |
| N2P2 | 8.50±0.03d | 0.41±0.05e | 0.45±0.05cd | 1.12±0.19a | 5.78±0.14bcd | 1.28±0.05bcde |
| NPK | 8.80±0.03bc | 0.34±0.03e | 0.41±0.03cde | 0.97±0.13ab | 5.31±0.68cde | 1.34±0.12abc |
| N2P2K | 8.70±0.04bc | 0.33±0.02e | 0.65±0.07ab | 1.12±0.18a | 6.30±0.32bc | 1.37±0.04ab |
| NPKR | 8.80±0.03bc | 0.29±0.04e | 0.51±0.03cd | 0.96±0.15ab | 6.31±0.49bc | 1.13±0.03de |
| NPKM | 8.70±0.05bc | 0.33±0.04e | 0.70±0.06a | 1.14±0.17a | 7.13±0.42ab | 1.14±0.05de |
图1 灰漠土表层土壤(0-20 cm)不同处理固氮微生物(nifH)门的相对丰度 Bd:荒漠裸地土壤;Gd:荒漠草本植被覆盖土壤;Sd:荒漠灌木植被覆盖土壤。右下角小图为毗邻荒漠3中植被覆盖样本的门水平固氮微生物nifH基因相对丰度。Desert:根据植被样方调查结果,Bd、Gd、Sd面积占比分别为55%、30%、15%,根据这个结果加权得到3种样本类型各项测定指标的加权平均值用以表征毗邻荒漠(Desert)。下同
Figure 1 Relative abundance of nitrogen-fixing microbial (nifH) phyla in the surface soil (0?20 cm) of gray desert soil under different treatments
图2 灰漠土表层土壤(0-20 cm)四类变形菌纲的相对丰度 不同字母代表显著性差异。Desert:根据植被样方调查结果,Bd、Gd、Sd面积占比分别为55%、30%、15%,根据这个结果加权得到3种样本类型各项测定指标的加权平均值用以表征毗邻荒漠(Desert)。下同
Figure 2 Relative abundance of the four classes of Proteobacteria in the surface soil layer (0?20 cm) of the grey desert soil
| 分类 | Bd | Gd | Sd | Desert | CK | PK | NK | NP | N2P2 | NPK | N2P2K | NPKR | NPKM | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 门 | Proteobacteria | a | abc | cde | ab | de | abcde | bcde | bcde | cde | abcd | de | e | e |
| Cyanobacteria | f | ab | f | ef | de | ef | cde | a | bc | ab | bcd | ab | de | |
| Verrucomicrobia | b | b | ab | b | ab | a | ab | ab | ab | ab | ab | ab | ab | |
| Actinobacteria | a | ab | ab | ab | ab | ab | ab | b | ab | ab | b | ab | b | |
| Gemmatimonadetes | a | a | a | a | a | a | a | a | a | a | a | a | a | |
| Firmicutes | b | b | ab | b | ab | a | b | ab | ab | ab | ab | b | a | |
| others | a | b | a | ab | ab | b | ab | b | b | b | ab | b | b | |
| unidentified | cdef | f | a | cdef | ab | bcde | abcd | def | abcd | ef | abc | abc | a | |
| 属 | Azoarcus | c | c | c | c | c | a | c | bc | bc | bc | b | bc | c |
| Klebsiella | b | b | b | b | b | b | ab | b | b | a | b | b | b | |
| Nostoc | e | cde | e | de | cde | cd | de | bc | cde | a | de | ab | cd | |
| Leptolyngbya | c | c | c | c | bc | bc | bc | a | a | a | a | b | bc | |
| Azospirillum | a | a | b | a | b | b | b | b | b | b | b | b | b | |
| Azotobacter | d | d | cd | d | b | bc | bcd | a | bc | d | d | bcd | cd | |
| others | a | a | a | a | a | a | a | a | a | a | a | a | a | |
| unidentified | cde | cde | a | bcde | ab | abcde | abcd | de | abcde | e | abc | abcd | a | |
附表1 门、属水平微生物相对丰度显著性对照表
Supplementary table Table of significance of microbial relative abundance at phylum and genus levels
| 分类 | Bd | Gd | Sd | Desert | CK | PK | NK | NP | N2P2 | NPK | N2P2K | NPKR | NPKM | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 门 | Proteobacteria | a | abc | cde | ab | de | abcde | bcde | bcde | cde | abcd | de | e | e |
| Cyanobacteria | f | ab | f | ef | de | ef | cde | a | bc | ab | bcd | ab | de | |
| Verrucomicrobia | b | b | ab | b | ab | a | ab | ab | ab | ab | ab | ab | ab | |
| Actinobacteria | a | ab | ab | ab | ab | ab | ab | b | ab | ab | b | ab | b | |
| Gemmatimonadetes | a | a | a | a | a | a | a | a | a | a | a | a | a | |
| Firmicutes | b | b | ab | b | ab | a | b | ab | ab | ab | ab | b | a | |
| others | a | b | a | ab | ab | b | ab | b | b | b | ab | b | b | |
| unidentified | cdef | f | a | cdef | ab | bcde | abcd | def | abcd | ef | abc | abc | a | |
| 属 | Azoarcus | c | c | c | c | c | a | c | bc | bc | bc | b | bc | c |
| Klebsiella | b | b | b | b | b | b | ab | b | b | a | b | b | b | |
| Nostoc | e | cde | e | de | cde | cd | de | bc | cde | a | de | ab | cd | |
| Leptolyngbya | c | c | c | c | bc | bc | bc | a | a | a | a | b | bc | |
| Azospirillum | a | a | b | a | b | b | b | b | b | b | b | b | b | |
| Azotobacter | d | d | cd | d | b | bc | bcd | a | bc | d | d | bcd | cd | |
| others | a | a | a | a | a | a | a | a | a | a | a | a | a | |
| unidentified | cde | cde | a | bcde | ab | abcde | abcd | de | abcde | e | abc | abcd | a | |
图3 灰漠土表层土壤(0-20 cm)不同处理固氮微生物(nifH)属的相对丰度
Figure 3 Relative abundance of nitrogen-fixing microbial (nifH) genera in the surface soil layer (0?20 cm) of the grey desert soil under different treatments
图4 开垦与长期施肥对固氮微生物(nifH)群落Alpha多样性的影响
Figure 4 The effects of land reclamation and long-term fertilization on the Alpha diversity of the nitrogen-fixing microorganism community (nifH)
图5 开垦与长期施肥对固氮微生物(nifH)群落Beta多样性的影响 Bd:荒漠裸地土壤;Gd:荒漠草本植被覆盖土壤;Sd:荒漠灌木植被覆盖土壤
Figure 5 The impact of land reclamation and long-term fertilization on the Beta diversity of nitrogen-fixing microorganisms communities (nifH)
图7 灰漠土开垦与施肥对土壤理化性质和固氮微生物(nifH)群落在属水平上的冗余分析 图(a)为对TOP20固氮微生物nifH基因群落与环境因子及施肥处理的冗余分析;图(b)为对环境因子与施肥处理的距离冗余分析。Bd:荒漠裸地土壤;Gd:荒漠草本植被覆盖土壤;Sd:荒漠灌木植被覆盖土壤。Desert:根据植被样方调查结果,Bd、Gd、Sd面积占比分别为55%、30%、15%,根据这个结果加权得到3种样本类型各项测定指标的加权平均值用以表征毗邻荒漠(Desert)。图(a)中字母代表属水平上TOP 20的固氮微生物nifH基因
Figure 7 RDA showing the effects of cultivation and fertilization on soil physicochemical properties and nitrogen-fixing microbial communities (nifH) (genus level) in grey desert soils
| 环境因子 | 解释率 | 贡献率 | 伪F值 | p值 |
|---|---|---|---|---|
| pH | 2.6 | 9.0 | 3.7 | 0.0058 |
| EC | 37.5 | 60.0 | 20.4 | 0.002 |
| TN | 3.7 | 5.9 | 2.6 | 0.044 |
| TP | 3.5 | 5.6 | 2.7 | 0.042 |
| SOC | 8.5 | 13.7 | 5.2 | 0.0014 |
| SBD | 3.6 | 5.7 | 2.6 | 0.046 |
表3 前向选择结果
Table 3 Forward selection results
| 环境因子 | 解释率 | 贡献率 | 伪F值 | p值 |
|---|---|---|---|---|
| pH | 2.6 | 9.0 | 3.7 | 0.0058 |
| EC | 37.5 | 60.0 | 20.4 | 0.002 |
| TN | 3.7 | 5.9 | 2.6 | 0.044 |
| TP | 3.5 | 5.6 | 2.7 | 0.042 |
| SOC | 8.5 | 13.7 | 5.2 | 0.0014 |
| SBD | 3.6 | 5.7 | 2.6 | 0.046 |
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