1. 安徽师范大学 生命科学学院 安徽省重要生物资源保护与利用研究重点实验室,安徽,芜湖,241000
2. 南昌工程学院 江西省退化生态系统修复与流域生态水文重点实验室,江西,南昌,330099
纸质出版:2021
移动端阅览
魏倩, 周际海, 程双怀, 等. 黑麦草生长及根系形态对土壤Cd,Pb与石油污染的响应[J]. 水土保持通报, 2021,41(2):84-91.
Wei Qian, Zhou Jihai, Cheng Shuanghuai, et al. Response of Ryegrass Growth and Root Morphology to Soil Cd, Pb and Petroleum Pollution[J]. Bulletin of Soiland Water Conservation, 2021, 41(2): 84-91.
魏倩, 周际海, 程双怀, 等. 黑麦草生长及根系形态对土壤Cd,Pb与石油污染的响应[J]. 水土保持通报, 2021,41(2):84-91. DOI: 10.13961/j.cnki.stbctb.2021.02.011.
Wei Qian, Zhou Jihai, Cheng Shuanghuai, et al. Response of Ryegrass Growth and Root Morphology to Soil Cd, Pb and Petroleum Pollution[J]. Bulletin of Soiland Water Conservation, 2021, 41(2): 84-91. DOI: 10.13961/j.cnki.stbctb.2021.02.011.
[目的
]
研究不同污染条件下黑麦草生理指标的动态变化,为植物修复污染土壤提供初步理论基础。[方法
]
通过室内试验模拟不同类型的土壤污染。设置4个处理,未污染土壤+黑麦草(SH)、重金属污染土壤(500 mg/kg Pb
2+
和50 mg/kg Cd
2+
)+黑麦草(SGH)、石油污染土壤(1 000 mg/kg石油)+黑麦草(SPH)、石油和重金属复合污染土壤(500 mg/kg Pb
2+
,50 mg/kg Cd
2+
和1 000 mg/kg石油)+黑麦草(SPGH),采用WINRHIZO根系分析系统测量根系形态指标,用分光光度计测量叶片色素指标,研究不同类型土壤污染对黑麦草生长的影响。[结果
]
3种不同类型的污染土壤均不同程度地刺激了黑麦草根系的生长。与未污染处理相比,在20 d时,石油重金属复合处理下的黑麦草根系的根长、根表面积、根体积、根直径分别增加了88.10%,148.60%,221.90%,32.20%。与未污染相比,随着培养时间的增加各污染处理的地下生物量呈现出先增加后减少的趋势,地上生物量均低于未污染处理,且在第10,40,80 d时,复合污染处理的地上生物量最小,较未污染处理分别降低了34.68%,45.42%,58.05%。80 d时,重金属污染处理、石油污染处理和石油重金属复合污染处理的黑麦草叶绿素含量显著低于未污染处理,分别降低了26.84%,44.82%和47.02%。[结论
]
不同污染物都可以促进黑麦草根系形态发育,降低黑麦草的生物量及色素含量;石油重金属复合处理对黑麦草的生长影响最大,石油污染处理次之。基于不同污染物对黑麦草根系形态及生长影响的差异,在今后植物修复土壤污染过程中,可添加一些生长调节物质来缓解污染对植物的毒害作用,提高植物生物量及增强相关生理功能,提升污染土壤修复效果。
[Objective] The dynamic changes of physiological indexes of ryegrass under different pollution conditions were studied
in order to provide a preliminary theoretical basis for phytoremediation of contaminated soil.[Methods] Through indoor simulation of different types of soil pollution
4 treatments were set up
namely uncontaminated soil + ryegrass (SH) as contorl
heavy metal contaminated soil (500 mg/kg Pb2+
50 mg/kg Cd2+)+ ryegrass (SGH)
petroleum contaminated soil (1 000 mg/kg petroleum) + ryegrass (SPH)
petroleum and heavy metals combined contaminated soil (500 mg/kg Pb2+
50 mg/kg Cd2+
1 000 mg/kg petroleum) + ryegrass (SPGH). The root morphological index was measured by WINRHIZO root analysis system
and the pigment index of leaves was measured by spectrophotometer
to explore the influence of different types of soil pollution on the pigment content of ryegrass leaves.[Results] The root growth of ryegrass was stimulated by three different types of contaminated soil to varying degrees. Compared with control
on the 20 th day
the root length
root surface area
root volume
and root diameter of plant roots under the combined treatment of petroleum and heavy metals increased by 88.10%
148.60%
221.90%
and 32.20%
respectively. Compared with control
the underground biomass of each polluted treatment showed a trend of increasing firstly and then decreasing with the increase of cultivation time
while the above-ground biomass was always lower than that of control. Moreover
on the 10th
40th and 80th days
the abovementioned biomass of the combined pollutted treatment was the smallest
which significantly decreased by 34.68%
45.42% and 58.05% compared with that of the control. On the 80 th day
the chlorophyll content of ryegrass in heavy metal contaminated soil
petroleum contaminated soil and petroleum and heavy metals combined contaminated soil was significantly lower than that of control
which decreased by 26.84%
44.82% and 47.02%
respectively.[Conclusion] Different pollutions could promote the morphological changes of ryegrass root system
and reduce the biomass and pigment contents of ryegrass
among which the combined pollution with petroleum and heavy metals have the greatest influence on the growth of ryegrass
followed by the treatment with petroleum pollution. Based on the difference of physiological response of ryegrass root morphology and growth to different polluted soils
some regulatory substances can be added to alleviate the toxic effect of pollution on plants in the future during the phytoremediation of contaminated soils
increase the biomass of plants and enhance the related physiological functions to improve the efficiency of pollution remediation.
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