植物生态学报 ›› 2010, Vol. 34 ›› Issue (6): 678-686.DOI: 10.3773/j.issn.1005-264x.2010.06.007 cstr: 32100.14.j.issn.1005-264x.2010.06.007
收稿日期:2009-11-02
接受日期:2010-01-25
出版日期:2010-11-02
发布日期:2010-06-01
作者简介:* E-mail: gqyan@126.comReceived:2009-11-02
Accepted:2010-01-25
Online:2010-11-02
Published:2010-06-01
摘要:
以我国二级濒危保护植物翅果油(Elaeagnus mollis)为供试植物, 通过温室盆栽试验, 研究接种丛枝菌根真菌对翅果油树幼苗根际土壤微生态环境的影响。试验设计分4个组: 摩西球囊霉(Glomus mosseae)单独接种组(GM)、脆无梗囊霉(Acaulospora delicata)单独接种组(AD)、混合接种组(GM + AD)、不接种的对照组(CK)。测定了菌根侵染率、生物量、根际微生物数量、土壤pH值、土壤酶活性及其对N、P营养的影响等指标。结果显示: 菌根真菌对3个接种组均有侵染, 其中, GM + AD的侵染率最大(90.5%), 生态学效应最好; 与对照组相比, 接种组的生物量均明显提高(p < 0.05), 其中GM + AD组生物量显著增加, 是CK组的2.2倍; AM菌根对根部微生物种群数量产生一定的影响, 主要是使根面上的细菌、放线菌、固氮菌的数量显著增加(p < 0.05); AM菌根使根际pH值降低, 与菌根侵染率呈显著负相关关系(p < 0.05); 接种组根际土壤磷酸酶、脲酶、蛋白酶的活性增加, 根际土壤的磷酸酶、蛋白酶的活性增加量与菌根侵染率呈极显著相关关系(p < 0.01); 接种组的根际土壤中, 可直接被植物吸收利用的N、P元素出现富集现象, 与菌根侵染率呈显著相关关系(p < 0.05)。研究表明: 丛枝菌根的形成改善了翅果油树幼苗的微生态环境, 提高了根际土壤肥力。
袁丽环, 闫桂琴. 丛枝菌根化翅果油树幼苗根际土壤微环境. 植物生态学报, 2010, 34(6): 678-686. DOI: 10.3773/j.issn.1005-264x.2010.06.007
YUAN Li-Huan, YAN Gui-Qin. Rhizospheric soil of seedlings of Elaeagnus mollis colonized by arbuscular mycorrhizal fungi. Chinese Journal of Plant Ecology, 2010, 34(6): 678-686. DOI: 10.3773/j.issn.1005-264x.2010.06.007
| 处理 Treatment | 苗高 Height of seedlings (cm) | 地径 Diameter at ground (cm) | 生物量 Biomass | 菌根侵染率 Colonization rate (%) | |||
|---|---|---|---|---|---|---|---|
| 根干重 Dry weight of roots (g) | 茎干重 Dry weight of stems (g) | 叶干重 Dry weight of leaves (g) | 全株干重 Whole plant dry weight (g) | ||||
| GM | 14.85 ± 1.82a | 0.26 ± 0.04b | 1.08 ± 0.08a | 1.02 ± 0.09a | 1.04 ± 0.08a | 3.14 ± 0.75b | 72.5 ± 7.28b |
| AD | 14.73 ± 1.89a | 0.25 ± 0.02b | 0.72 ± 0.09b | 0.67 ± 0.07b | 0.70 ± 0.07b | 2.09 ± 0.84c | 42.4 ± 4.41c |
| GM + AD | 15.01 ± 1.54a | 0.29 ± 0.03a | 1.20 ± 0.08a | 1.11 ± 0.06a | 1.07 ± 0.09a | 3.38 ± 0.96a | 90.5 ± 9.25a |
| CK | 13.17 ± 1.85b | 0.18 ± 0.02c | 0.48 ± 0.07c | 0.58 ± 0.04c | 0.49 ± 0.05c | 1.55 ± 0.63d | 0 |
表1 丛枝菌根对翅果油树幼苗生长的影响(平均值±标准误差, n = 10)
Table 1 Effects of arbuscular mycorrhiza on the seedling growth of Elaeagnus mollis (mean ± SE, n = 10)
| 处理 Treatment | 苗高 Height of seedlings (cm) | 地径 Diameter at ground (cm) | 生物量 Biomass | 菌根侵染率 Colonization rate (%) | |||
|---|---|---|---|---|---|---|---|
| 根干重 Dry weight of roots (g) | 茎干重 Dry weight of stems (g) | 叶干重 Dry weight of leaves (g) | 全株干重 Whole plant dry weight (g) | ||||
| GM | 14.85 ± 1.82a | 0.26 ± 0.04b | 1.08 ± 0.08a | 1.02 ± 0.09a | 1.04 ± 0.08a | 3.14 ± 0.75b | 72.5 ± 7.28b |
| AD | 14.73 ± 1.89a | 0.25 ± 0.02b | 0.72 ± 0.09b | 0.67 ± 0.07b | 0.70 ± 0.07b | 2.09 ± 0.84c | 42.4 ± 4.41c |
| GM + AD | 15.01 ± 1.54a | 0.29 ± 0.03a | 1.20 ± 0.08a | 1.11 ± 0.06a | 1.07 ± 0.09a | 3.38 ± 0.96a | 90.5 ± 9.25a |
| CK | 13.17 ± 1.85b | 0.18 ± 0.02c | 0.48 ± 0.07c | 0.58 ± 0.04c | 0.49 ± 0.05c | 1.55 ± 0.63d | 0 |
图1 翅果油树接种丛枝菌根真菌后土壤微生物数量的变化(微生物数量单位: × 106·g-1) (n = 10)。 AD、CK、GM和GM + AD同表1。
Fig. 1 Effects of Elaeagnus mollis inoculated by arbuscular mycorrhizal fungi on soil microbial quantity (microbe quantity unit: ×106·g-1) (n = 10). AD, CK, GM and GM + AD see Table 1.
图2 不同处理的翅果油树苗木根部pH值比较(n = 10)。 AD、CK、GM和GM + AD同表1。
Fig. 2 Comparison of pH in the roots of different treated Elaeagnus mollis seedings (n = 10). AD, CK, GM and GM + AD see Table 1.
| 处理Treatment | 磷酸酶 Phosphatase (Phenol mg·g-1·d-1) | 蛋白酶 Protease (NH2-N mg·g-1·d-1) | 脲酶 Urease (NH3-N mg·g-1·d-1) | |||
|---|---|---|---|---|---|---|
| 碱性磷酸酶 Alkaline phosphatase | 中性磷酸酶 Neutral phosphatase | 酸性磷酸酶 Acid phosphatase | 磷酸酶总量 Total phosphatase | |||
| GM | 2.018a | 1.487b | 0.445b | 3.950a | 0.814 5ab | 1.252a |
| AD | 1.998ab | 1.201b | 0.431b | 3.630b | 0.756 1b | 0.854b |
| GM + AD | 2.019a | 1.521b | 0.554a | 4.094a | 1.002 8a | 1.326a |
| CK | 1.667b | 1.141b | 0.235c | 3.043b | 0.605 8b | 0.523c |
表2 翅果油树接种丛枝菌根真菌后根际土壤酶活性的变化(平均值±标准误差, n = 10)
Table 2 Effects of Elaeagnus mollis inoculated by arbuscular mycorrhizal fungi on the soil enzyme activity in the rhizosphere (mean ± SE, n = 10)
| 处理Treatment | 磷酸酶 Phosphatase (Phenol mg·g-1·d-1) | 蛋白酶 Protease (NH2-N mg·g-1·d-1) | 脲酶 Urease (NH3-N mg·g-1·d-1) | |||
|---|---|---|---|---|---|---|
| 碱性磷酸酶 Alkaline phosphatase | 中性磷酸酶 Neutral phosphatase | 酸性磷酸酶 Acid phosphatase | 磷酸酶总量 Total phosphatase | |||
| GM | 2.018a | 1.487b | 0.445b | 3.950a | 0.814 5ab | 1.252a |
| AD | 1.998ab | 1.201b | 0.431b | 3.630b | 0.756 1b | 0.854b |
| GM + AD | 2.019a | 1.521b | 0.554a | 4.094a | 1.002 8a | 1.326a |
| CK | 1.667b | 1.141b | 0.235c | 3.043b | 0.605 8b | 0.523c |
图3 翅果油树根部土壤全氮和水解氮比较(n = 10)。 AD、CK、GM、GM + AD, 同表1。
Fig. 3 Compaison of soil total N and hydrolysable N in the Elaeagnus mollis roots (n = 10). AD, CK, GM, GM + AD, see Table 1.
图4 翅果油树根部土壤全磷和速效磷比较(平均值±标准误差, n = 10)。 AD、CK、GM、GM + AD, 同表1。
Fig. 4 Comparison of soil total P and available P in Elaeagnus mollis roots (mean ± SE, n = 10). AD, CK, GM, GM + AD, see Table 1.
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