To explore the remediation of Liquidambar formosana Hance to lead-contaminated soil and provide scientific reference for the promotion of planting maple in contaminated heavy metals
annual L. formosana Hance seedlings were used as test materials
the physiological characteristics and accumulation characteristics of L. formosana Hance seedlings under 6 Pb2+ concentrations (0
100
300
500
800
and 1 000 mg/kg) were studied. The principal component analysis method was used to screen the 12 physiological indexes of L. formosana Hance and evaluate the tolerance. The results showed that with the increase of Pb2+ concentration
the biomass
soluble sugar content
soluble protein content
free proline content
superoxide dismutase (SOD)
and peroxidase (POD) of L. formosana seedling leaves showed a upward-downward trend
which indicate a "low promotes high suppression" effect. The content of malondialdehyde (MAD) showed an upward trend. Both chlorophyll a and chlorophyll b showed a downward trend
but the downward trend of chlorophyll a was not significant. Net photosynthetic rate (Pn)
stomatal conductance (Gs)
CO2 concentration (Ci)
and transpiration rate (Tr) all showed an upward-downward trend. The lead content in the underground part of L. formosana>the lead content in the above-ground part
the transfer coefficient was the largest at T2 and T3
and the enrichment coefficient was negatively correlated with the stress concentration. The results of principal component analysis showed that the cumulative contribution rate of the two principal components extracted was as high as 92.462%
indicating that these two principal components can reflect most of the information. Free proline
net photosynthetic rate
stoma conductance
intercellular CO2 concentration
transpiration speed
and SOD activity were the simplified 6 indexes. The principal component scores showed that the lead tolerance of L. formosana seedlings is ranked as T3>T4>T2>T1>T5>T6. Comprehensively
the L. formosana Hance seedlings have certain tolerance
enrichment
and transfer ability to heavy metal lead
and this study provide theoretical basis for introducing L. formosana Hance to areas with heavy metal pollution and alleviating soil heavy metal pollution.
关键词
Keywords
references
Wang J, Zhang C B, Jin Z X. The distribution and phytoavailability of heavy metal fractions in rhizosphere soils of paulowniu fortunei (seem) hems near a Pb/Zn smelter in Guangdong, PR China[J].Geoderma,2009,148(3):299-306.
Pourrut B, Shahid M, Dumat C, et al. Lead uptake, toxicity, and detoxification in plants[J].Reviews of Environmental Contamination and Toxicology,2011,213:113-136.
秦惠生.铅的环境毒理学[J].环境科学研究,1979(增刊2):86-100.
Hanumanth K G, Pramoda K J. Heavy metal lead in fluative toxicity and its assessment in phytoremediating plants:A review[J].Springer International Publishing,2015,226(10):324-334.
Ariagada C A, Herrera M A, Ocampo J A. Contribution of arbuscularmycorrhizal and saprobe fungi to the tolerance of Eucalyplus globulus to Pb[J].Water Air and Soil Pollution,2005,166(14):31-47.
Baker A J M. Accumulators and excluders -strategies in the response of plants to heavy metals[J].Journal of Plant Nutrition,1981,3(1/4):643-654.
McGrath S P, Lombi E, Gray C W, et al. Field evaluation of Cd and Zn phytoextraction potential by the hyperaccumulators Thlaspi caerulescens and Arabidopsis haller[J].Environmental Pollution,2006,141(1):115-125.