丛枝菌根真菌(AMF)作为植物萃取重金属的缓冲剂。在原油污染的土壤上生长

O. Okon, J. Okon, G.D.O. Eneh
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The shoot length, petiole length, number of nodes, leaf area and percentage germination ofC. maximawere significantly (p=0.05) reduced in uninoculated crude oil treatment (C+ M-), unpolluted mycorrhizal inoculated treatments (C-M+) showed remarkable response in growth parameters above the control (C-M-), while the polluted and inoculated treatment (C+ M+) showed significant (p=0.05) increase in growth parameters when compared to the polluted uninoculated treatment (C+ M-). Heavy metals analysis revealed a significant (p=0.05) difference in the heavy metal accumulation ofC. maxima. The heavy metals analyzed in this study are present thus inC. maxima; Zn>Cu>Cr>Pb>Cd. Crude oil polluted uninoculated treatment (C+ M-) recorded the highest concentrations of heavy metals than crude oil polluted inoculated (R. irregularis) treatment (C+ M+). Mycorrhizal inoculated unpolluted treatment (C-M+) and unpolluted uninoculated treatment (C-M-) indicated the lowest heavy metal concentrations. 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引用次数: 2

摘要

研究了在原油污染土壤(C)中接种根状菌根(Rhizophagus irregularis)真菌(M)对大葫芦(cucurbita maxima)生长的影响,并对土壤中重金属(Zn、Cu、Cr、Cd和Pb)进行缓冲。试验设4个土壤处理,每个处理3个重复,分别为C+ M-、C+ M+、C-M+和C-M-(无油对照和接种对照)。对芽长、叶柄长、节数、叶面积和发芽率进行了比较。未接种原油处理(C+ M-)的最大值显著(p=0.05)降低,未污染菌根接种处理(C-M+)的生长参数高于对照(C-M-)的响应显著(p=0.05),而污染和接种处理(C+ M+)的生长参数与未接种处理(C+ M-)相比显著(p=0.05)增加。重金属分析显示,c的重金属积累量有显著差异(p=0.05)。最大值。因此,本研究分析的重金属存在inC.最大值;锌>铜>铬>铅> Cd。原油污染未接种处理(C+ M-)的重金属浓度高于原油污染接种处理(C+ M+)。菌根接种未污染处理(C-M+)和未污染未接种处理(C-M-)的重金属浓度最低。接种withR。不规则性显著(p=0.05)降低c对重金属的吸收。在这项研究中观察到。此外,原油对AMF根定植的负面影响。maximabyR。污染处理和接种处理均存在不规律性。HM通常积聚在土壤表层,因此可以通过根系被植物吸收,这是HM的主要入口,最终影响不同的生理过程。AM真菌可以影响土壤中重金属的化学性质,影响寄主植物对重金属的吸收和在植物不同部位的分配,从而影响植物的生长和生物修复过程,因此AM真菌是缓解重金属胁迫的合适缓冲剂。最大值。
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Arbuscular Mycorrhizal Fungi (AMF) as Buffer for Heavy Metals Phytoextraction by Cucurbita maxima Duch. Grown on Crude Oil Contaminated Soil
This study evaluated the influence of Arbuscular Mycorrhizal (Rhizophagus irregularis) fungi inoculation (M) on the growth ofCucurbita maximaand as a buffer against phytoextraction of selected heavy metals (HM) (Zn, Cu, Cr, Cd and Pb) from a soil contaminated with crude oil (C). The experiment was set up using four soil treatments, each with three replicates C+ M-, C+ M+, C-M+ and C-M- (control without oil and inoculum). The shoot length, petiole length, number of nodes, leaf area and percentage germination ofC. maximawere significantly (p=0.05) reduced in uninoculated crude oil treatment (C+ M-), unpolluted mycorrhizal inoculated treatments (C-M+) showed remarkable response in growth parameters above the control (C-M-), while the polluted and inoculated treatment (C+ M+) showed significant (p=0.05) increase in growth parameters when compared to the polluted uninoculated treatment (C+ M-). Heavy metals analysis revealed a significant (p=0.05) difference in the heavy metal accumulation ofC. maxima. The heavy metals analyzed in this study are present thus inC. maxima; Zn>Cu>Cr>Pb>Cd. Crude oil polluted uninoculated treatment (C+ M-) recorded the highest concentrations of heavy metals than crude oil polluted inoculated (R. irregularis) treatment (C+ M+). Mycorrhizal inoculated unpolluted treatment (C-M+) and unpolluted uninoculated treatment (C-M-) indicated the lowest heavy metal concentrations. Inoculation withR. irregularissignificantly (p=0.05) reduced heavy metals uptake byC. maximaas observed in this study. Also, the negative effect of crude oil on AMF root colonization ofC. maximabyR. irregulariswas observed in polluted and inoculated treatment. HM often accumulate in the top layer of soil, therefore, are available for uptake by plants via roots, which is a major entry point of HM that ultimately affects different physiological processes. AM fungi can impinge on the chemical properties of heavy metals in the soil, their absorption by the host plant, and their allocation to different plant parts, affecting plant growth and the bioremediation process, thus making the AM fungi a suitable buffer for mitigating heavy metal stress onC. maxima.
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