生态环境学报 ›› 2026, Vol. 35 ›› Issue (4): 619-629.DOI: 10.16258/j.cnki.1674-5906.2026.04.012
邵玉蝶1,2(
), 朱学昊1,2, 吴河源1,2, 刘京1,2, 毛艳玲1,2, 杨文浩1,2,*(
)
收稿日期:2025-06-30
修回日期:2025-12-16
接受日期:2026-01-26
出版日期:2026-04-18
发布日期:2026-04-14
通讯作者:
*E-mail: 作者简介:邵玉蝶(2001年生),女,硕士研究生,主要研究方向为土壤重金属污染植物修复研究。E-mail: 52308031068@fafu.edu.cn
基金资助:
SHAO Yudie1,2(
), ZHU Xuehao1,2, WU Heyuan1,2, LIU Jing1,2, MAO Yanling1,2, YANG Wenhao1,2,*(
)
Received:2025-06-30
Revised:2025-12-16
Accepted:2026-01-26
Online:2026-04-18
Published:2026-04-14
摘要:
为探究外源硅(Si)对东南景天(Sedum alfredii Hance)吸收和富集镉(Cd)的影响及其相关生理和根际机制,设置3个Si处理水平(0、100、200 mg·kg−1),植物生长5个月后收获并测定土壤和植物相关指标。结果表明,土壤施用外源Si能显著提高根际蔗糖酶、酸性磷酸酶和脲酶活性,根际土壤中碱解氮(AN)、有效磷(AP)和速效钾(EK)含量显著提高,溶解性有机碳、氮(DOC与DON)含量也呈上升趋势。土壤全Cd含量由14.49 mg·kg−1降至11.41 mg·kg−1,而速效Cd含量则从2.21 mg·kg−1上升至2.69 mg·kg−1。与对照相比,施加外源Si后,东南景天株高增加4.1%-8.8%,地上部鲜质量和干质量分别提高34.2%-76.7%和38.5%-76.9%。当Si施用量达200 mg·kg−1时,叶绿素a、b含量均达最大值,较对照组显著增加35.9%和30.3%。叶片抗氧化酶超氧化物歧化酶(SOD)和对照相比显著升高,过氧化氢酶(CAT)和过氧化物酶(POD)活性分别达到2511.3、707.2和3.65 U·g−1。植物螯合素(PC)含量增至2008.4 pg·g−1,较对照提高11.3%,而丙二醛(MDA)含量显著降低32.8%。与对照相比,Si处理显著提高植株Cd积累能力,地上部Cd积累量分别增加38.3%和101.4%,根部Cd积累量分别提高31.0%和83.7%。综上,外源Si的施用促进土壤养分释放,促进东南景天生长发育,缓解Cd毒害,并显著提高其对Cd的吸收富集能力。
中图分类号:
邵玉蝶, 朱学昊, 吴河源, 刘京, 毛艳玲, 杨文浩. 硅对东南景天吸收和富集镉的影响及其机制研究[J]. 生态环境学报, 2026, 35(4): 619-629.
SHAO Yudie, ZHU Xuehao, WU Heyuan, LIU Jing, MAO Yanling, YANG Wenhao. Research on the Effects and Mechanisms of Exogenous Silicon on Cadmium Uptake and Accumulation in Sedum alfredii Hance[J]. Ecology and Environmental Sciences, 2026, 35(4): 619-629.
| 指标 | pH (土水比=1꞉2.5) | 碱解氮质量 分数/ (mg·kg−1) | 有效磷质量 分数/ (mg·kg−1) | 速效钾质量 分数/ (mg·kg−1) | 总Cd质量 分数/ (mg·kg−1) | 有效态Cd质量 分数/ (mg·kg−1) | 有效Si质量 分数/ (mg·kg−1) | 总Cu质量 分数/ (mg·kg−1) | 总Zn质量 分数/ (mg·kg−1) | 总Pb质量 分数/ (mg·kg−1) |
|---|---|---|---|---|---|---|---|---|---|---|
| 测定值 | 4.95 | 81.73 | 16.76 | 91.20 | 14.49 | 2.21 | 126.59 | 96.81 | 1068.55 | 697.46 |
表1 供试土壤基本理化性质
Table 1 Basic physical and chemical properties of the test soil
| 指标 | pH (土水比=1꞉2.5) | 碱解氮质量 分数/ (mg·kg−1) | 有效磷质量 分数/ (mg·kg−1) | 速效钾质量 分数/ (mg·kg−1) | 总Cd质量 分数/ (mg·kg−1) | 有效态Cd质量 分数/ (mg·kg−1) | 有效Si质量 分数/ (mg·kg−1) | 总Cu质量 分数/ (mg·kg−1) | 总Zn质量 分数/ (mg·kg−1) | 总Pb质量 分数/ (mg·kg−1) |
|---|---|---|---|---|---|---|---|---|---|---|
| 测定值 | 4.95 | 81.73 | 16.76 | 91.20 | 14.49 | 2.21 | 126.59 | 96.81 | 1068.55 | 697.46 |
| 处理 | 鲜质量/(g·plant−1) | 干质量/(g·plant−1) | 根长/ cm | 株高/ cm | |||
|---|---|---|---|---|---|---|---|
| 地上部 | 根部 | 地上部 | 根部 | ||||
| CK | 0.73± 0.09c | 0.20± 0.01b | 0.13± 0.01c | 0.06± 0.01b | 3.81± 0.20b | 13.75± 0.45c | |
| Si100 | 0.98± 0.09b | 0.21± 0.01b | 0.18± 0.02b | 0.07± 0.01b | 4.10± 0.14b | 14.32± 0.29b | |
| Si200 | 1.29± 0.12a | 0.28± 0.02a | 0.23± 0.02a | 0.11± 0.01a | 4.40± 0.28a | 14.96± 0.22a | |
表2 不同Si处理对东南景天生物量的影响
Table 2 Effects of different Si treatments on biomass of S. alfredii
| 处理 | 鲜质量/(g·plant−1) | 干质量/(g·plant−1) | 根长/ cm | 株高/ cm | |||
|---|---|---|---|---|---|---|---|
| 地上部 | 根部 | 地上部 | 根部 | ||||
| CK | 0.73± 0.09c | 0.20± 0.01b | 0.13± 0.01c | 0.06± 0.01b | 3.81± 0.20b | 13.75± 0.45c | |
| Si100 | 0.98± 0.09b | 0.21± 0.01b | 0.18± 0.02b | 0.07± 0.01b | 4.10± 0.14b | 14.32± 0.29b | |
| Si200 | 1.29± 0.12a | 0.28± 0.02a | 0.23± 0.02a | 0.11± 0.01a | 4.40± 0.28a | 14.96± 0.22a | |
| 处理 | SOD活性/(U∙g−1) | CAT活性/(U∙g−1) | POD活性/(U∙g−1) |
|---|---|---|---|
| CK | 1347.9±57.6c | 489.8±18.9c | 2.52±0.03c |
| Si100 | 2370.7±51.7b | 671.1±7.3b | 3.48±0.04b |
| Si200 | 2511.3±20.5a | 707.2±15.6a | 3.65±0.09a |
表3 不同Si处理对东南景天叶片抗氧化酶的影响
Table 3 Effects of different Si treatments on antioxidant enzymes in S. alfredii leaves
| 处理 | SOD活性/(U∙g−1) | CAT活性/(U∙g−1) | POD活性/(U∙g−1) |
|---|---|---|---|
| CK | 1347.9±57.6c | 489.8±18.9c | 2.52±0.03c |
| Si100 | 2370.7±51.7b | 671.1±7.3b | 3.48±0.04b |
| Si200 | 2511.3±20.5a | 707.2±15.6a | 3.65±0.09a |
| 处理 | 碱解氮质量分数/ (mg∙kg−1) | 有效磷质量分数/ (mg∙kg−1) | 速效钾质量分数/ (mg∙kg−1) | pH |
|---|---|---|---|---|
| CK | 112.53±0.53b | 24.64±2.51c | 92.96±1.08b | 4.94±0.05a |
| Si100 | 118.77±2.25a | 28.18±1.05b | 93.70±0.82ab | 4.92±0.02a |
| Si200 | 120.05±1.85a | 33.24±2.25a | 94.80±0.43a | 4.92±0.02a |
表4 不同Si处理对土壤理化性质的影响
Table 4 Effects of different Si treatments on soil physical and chemical properties
| 处理 | 碱解氮质量分数/ (mg∙kg−1) | 有效磷质量分数/ (mg∙kg−1) | 速效钾质量分数/ (mg∙kg−1) | pH |
|---|---|---|---|---|
| CK | 112.53±0.53b | 24.64±2.51c | 92.96±1.08b | 4.94±0.05a |
| Si100 | 118.77±2.25a | 28.18±1.05b | 93.70±0.82ab | 4.92±0.02a |
| Si200 | 120.05±1.85a | 33.24±2.25a | 94.80±0.43a | 4.92±0.02a |
| 处理 | 蔗糖酶活性/ (μg∙g−1∙24 h−1) | 酸性磷酸酶活性/ (μg∙g−1∙2 h−1) | 脲酶活性/ (μg∙g−1∙24 h−1) |
|---|---|---|---|
| CK | 158.42±5.05b | 206.02±8.25b | 165.43±3.43b |
| Si100 | 322.69±6.92a | 240.39±4.60a | 173.03±9.77ab |
| Si200 | 330.33±7.29a | 248.03±7.10a | 178.14±9.23a |
表5 不同Si处理对土壤酶活性的影响
Table 5 Effects of different Si treatments on soil enzyme activities
| 处理 | 蔗糖酶活性/ (μg∙g−1∙24 h−1) | 酸性磷酸酶活性/ (μg∙g−1∙2 h−1) | 脲酶活性/ (μg∙g−1∙24 h−1) |
|---|---|---|---|
| CK | 158.42±5.05b | 206.02±8.25b | 165.43±3.43b |
| Si100 | 322.69±6.92a | 240.39±4.60a | 173.03±9.77ab |
| Si200 | 330.33±7.29a | 248.03±7.10a | 178.14±9.23a |
图8 不同Si处理对东南景天根际土壤总Cd含量和有效态Cd含量的影响
Figure 8 Effects of different Si treatments on total Cd content and available Cd content in the rhizosphere soil of S. alfredii
图9 不同Si处理对东南景天富集系数及转运系数的影响 富集系数=植株镉含量/土壤镉含量;转运系数=植株地上部镉含量/植株地下部镉含量
Figure 9 Effects of different Si treatments on the Bioaccumulation factor and Translocation factor of S. alfredii
图10 东南景天生理与土壤理化性质的相关性分析 1:鲜质量;2:叶绿素总量;3:MDA;4:PCs;5:SOD;6:CAT;7:POD;8:pH;9:AP;10:EK;11:AN;12:DOC;13:DON;14:NH4+-N;15:NO3?-N;16:磷酸酶;17:蔗糖酶;18:脲酶。*表示在p<0.05水平显著相关,**和***分别表示在p<0.01和p<0.001水平上极显著相关
Figure 10 Correlation analysis between physiological properties and soil physical and chemical properties of S. alfredii
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