7种杨树铅抗性和积累能力的比较研究

doi:10.12302/j.issn.1000-2006.202103020

国家林草科技领军期刊
中国精品科技期刊
中国高校百佳科技期刊
江苏省新闻出版政府奖期刊奖
RCCSE林学权威期刊（A+）
CSCD核心期刊
Scopus数据库收录期刊
中文核心期刊
SCD核心期刊

作者加群：102861116

微信公众号：南京林业大学学报

高级检索

南京林业大学学报（自然科学版） ›› 2021, Vol. 45 ›› Issue (3): 61-70.doi: 10.12302/j.issn.1000-2006.202103020

7种杨树铅抗性和积累能力的比较研究

石文广¹(), 李靖², 张玉红¹^,³, 雷静品¹, 罗志斌¹^,^*()

1.林木遗传育种国家重点实验室,国家林业和草原局森林培育重点实验室,中国林业科学研究院林业研究所,北京 100091
2.南京林业大学轻工和食品学院,江苏南京 210037
3.和瑞基因科技有限公司,北京 100102

收稿日期:2021-03-09 修回日期:2021-04-06 出版日期:2021-05-30 发布日期:2021-05-31
通讯作者: 罗志斌
基金资助:
中国林业科学研究院中央级公益性科研院所基本科研业务费专项资金(CAFYBB2018GD001);中国林业科学研究院中央级公益性科研院所基本科研业务费专项资金(CAFYBB2019ZA001-1);中国林业科学研究院中央级公益性科研院所基本科研业务费专项资金(CAFYBB2018SY005)

A comparative study on lead tolerance and accumulation of seven poplar species

SHI Wenguang¹(), LI Jing², ZHANG Yuhong¹^,³, LEI Jingpin¹, LUO Zhibin¹^,^*()

1. State Key Laboratory of Tree Genetics and Breeding, Key Laboratory of Silviculture of National Forestry and Grassland Administration, Research Institute of Forestry, Chinese Academy of Forestry, Beijing 100091, China
2. College of Light Industry and Food Engineering, Nanjing Forestry University, Nanjing 210037, China
3. Berry Oncology Technology Co., Ltd., Beijing 100102, China

Received:2021-03-09 Revised:2021-04-06 Online:2021-05-30 Published:2021-05-31
Contact: LUO Zhibin

摘要/Abstract

摘要：

【目的】通过对比研究不同种杨树的铅(Pb)抗性和Pb积累能力,筛选具有修复Pb污染土壤潜力的杨树树种。【方法】选取7种速生杨树,用8 mmol/L Pb处理6周,分析7种杨树Pb抗性和积累能力。【结果】Pb胁迫导致7种杨树净光合速率、气孔导度和蒸腾速率降低,抑制了7种杨树的高生长和径向生长,其中欧洲黑杨、群众杨和青杨的光合和生长对Pb胁迫较敏感,美洲黑杨敏感性较低。Pb胁迫导致7种杨树生物量显著降低,其中欧美杨根生物量降低最多(50.31%),欧洲黑杨(31.99%)和群众杨(22.26%)木材生物量降低最显著,欧美杨(12.67%)和群众杨(19.54%)皮生物量降低最显著,灰杨叶生物量降低最多(35.44%)。7种杨树的总生物量在Pb胁迫下出现明显降低,其中灰杨降幅最大(29.03%),欧洲黑杨降幅最小(12.02%)。相应地,7种杨树Pb抗性指数大小顺序依次为:欧洲黑杨(88.09%)>银腺杨(82.98%)≈美洲黑杨(80.70%)>欧美杨(79.86%)>青杨(76.79%)>群众杨(72.78%)≈灰杨(70.35%)。7种杨树吸收和转运Pb的能力存在较大差异。美洲黑杨根中的Pb含量最高,达2 906.10 mg/kg;灰杨木材、皮和叶中的Pb含量较高,分别达46.55、44.39和325.90 mg/kg。美洲黑杨根和整株Pb积累量最大,分别为4.20和5.06 mg/株;灰杨地上部分Pb积累量最大,为1.21 mg/株。美洲黑杨的根富集系数最大,达6.70;灰杨地上部分富集系数最大,为0.43。灰杨的Pb转运系数显著高于其他杨树,达0.16;欧洲黑杨的转运系数最低,仅为0.02。【结论】7种杨树的Pb抗性和Pb积累能力存在明显差异,其中欧洲黑杨Pb抗性最强、美洲黑杨根吸收Pb的能力最强,可能在Pb污染土壤的植物固定和生态恢复方面具有较大潜力;灰杨转运Pb能力最强,地上部分Pb积累能力最强,可能在Pb污染土壤的植物提取方面具有较大潜力。

关键词: 杨树, 植物修复, Pb胁迫, 光合作用, 生物量, Pb积累, 土壤重金属污染

Abstract:

【Objective】In this study, we aimed to find the promising poplar species for the remediation of lead (Pb)-contaminated soil by comparing the lead (Pb) resistance and accumulation of different poplar species. 【Method】Seven fast-growing poplar species were exposed to 8 mmol/L Pb(NO₃)₂ for 6 weeks to analyze their capacities for Pb tolerance and accumulation. 【Result】The net photosynthetic rate, stomatal conductance and transpiration rate were significantly reduced in the leaves of Pb-exposed poplar plants compared to those under the controlled condition. Thus, the axial and radial growth of poplar plants were inhibited by Pb exposure. The photosynthesis and growth of Populus nigra, P. × popularis and P. cathayana were more sensitive, and those of P. deltoides were less sensitive to Pb exposure than the other poplar species. The biomass of Pb-treated poplar plants was declined in comparison with that of poplar plants under the controlled condition. The greatest reduction in root biomass was found in P. × euramericana (50.31%); the significant decreases in wood biomass were found in P. nigra (31.99%) and P. × popularis (22.26%); the significant decreases in bark biomass were found in P. × euramericana (12.67%) and P. × popularis (19.54%); the greatest reduction in leaf biomass was found in P. × canescens (35.44%). The total biomass of the seven poplar species decreased significantly under Pb stress. The largest decrease was found in P. × canescens (29.03%), and the smallest reduction was found in P. nigra (12.02%). Correspondingly, the tolerance index of the seven poplar species was decreased in the order: P. nigra (88.09%) > P. alba × P. glandulosa (82.98%) ≈ P. deltoides (80.70%) > P. × euramericana (79.86%) > P. cathayana (76.79%) > P. × popularis (72.78%) ≈ P. × canescens (70.35%). Significant differences in absorption and transport of Pb were found among poplar species. P. deltoides displayed the highest Pb concentration in the roots (2 906.10 mg/kg). P. × canescens showed the highest concentrations of Pb in the wood (46.55 mg/kg), bark (44.39 mg/kg) and leaves (325.90 mg/kg). The total Pb amount in the roots (4.20 mg/plant) and whole plant (5.06 mg/plant) of P. deltoides and those in the aerial part (1.21 mg/plant) of P. × canescens were the largest among the seven poplar species. P. deltoides showed the highest bio-concentration factor of roots (6.70) and P. × canescens displayed the highest bio-concentration factor of the aboveground tissue (0.43). Meanwhile, P. × canescens displayed the highest translocation factor (0.16), and P. nigra showed the lowest translocation factor (0.02). 【Conclusion】Significant differences in Pb tolerance and accumulation were found among the seven poplar species. Among which, P. nigra and P. deltoides displayed the strongest abilities for Pb tolerance and absorption, respectively, and thus both species may have great potentials for phytostabilization and ecological restoration of Pb-polluted soil. P. × canescens showed the strongest ability to transport Pb to the aboveground tissues, and thus it may have a great potential for phytoextraction of Pb in contaminated soil.

Key words: Populus spp., phytoremediation, Pb stress, photosynthesis, biomass, Pb accumulation, soil heavy metal pollution

中图分类号:

S718
X53

石文广,李靖,张玉红,等. 7种杨树铅抗性和积累能力的比较研究[J]. 南京林业大学学报（自然科学版）, 2021, 45(3): 61-70.

SHI Wenguang, LI Jing, ZHANG Yuhong, LEI Jingpin, LUO Zhibin. A comparative study on lead tolerance and accumulation of seven poplar species[J].Journal of Nanjing Forestry University (Natural Science Edition), 2021, 45(3): 61-70.DOI: 10.12302/j.issn.1000-2006.202103020.

图/表 6

图1

表2

图2

图3

图4

表3

参考文献 43

[1]	ZULFIQAR U, FAROOQ M, HUSSAIN S, et al. Lead toxicity in plants:impacts and remediation[J]. J Environ Manage, 2019,250:109557.DOI: 10.1016/j.jenvman.2019.109557. doi: 10.1016/j.jenvman.2019.109557
[2]	环境保护部和国土资源部. 全国土壤污染状况调查公报[EB/OL]. [2014-04-07]. http://www.mee.gov.cn/gkml/sthjbgw/qt/201404/t20140417_270670.htm.
[3]	NEEDLEMAN H. Lead poisoning[J]. Annu Rev Med, 2004,55(1):209-222.DOI: 10.1146/annurev.med.55.091902.103653. doi: 10.1146/annurev.med.55.091902.103653
[4]	SARWAR N, IMRAN M, SHAHEEN M R, et al. Phytoremediation strategies for soils contaminated with heavy metals:modifications and future perspectives[J]. Chemosphere, 2017,171:710-721.DOI: 10.1016/j.chemosphere.2016.12.116. doi: 10.1016/j.chemosphere.2016.12.116
[5]	GERHARDT K E, GERWING P D, GREENBERG B M. Opinion:taking phytoremediation from proven technology to accepted practice[J]. Plant Sci, 2017,256:170-185.DOI: 10.1016/j.plantsci.2016.11.016. doi: 10.1016/j.plantsci.2016.11.016
[6]	STOBRAWA K, LORENC-PLUCINSKA G. Thresholds of heavy-metal toxicity in cuttings of European black poplar (Populus nigra L.) determined according to antioxidant status of fine roots and morphometrical disorders[J]. Sci Total Environ, 2008,390(1):86-96.DOI: 10.1016/j.scitotenv.2007.09.024. doi: 10.1016/j.scitotenv.2007.09.024
[7]	DURAND T C, HAUSMAN J F, CARPIN S, et al. Zinc and cadmium effects on growth and ion distribution in Populus tremula × Populus alba[J]. Biol Plant, 2010,54(1):191-194.DOI: 10.1007/s10535-010-0033-z. doi: 10.1007/s10535-010-0033-z
[8]	HE J, MA C, MA Y, et al. Cadmium tolerance in six poplar species[J]. Environ Sci Pollut Res Int, 2013,20(1):163-174.DOI: 10.1007/s11356-012-1008-8. doi: 10.1007/s11356-012-1008-8
[9]	SHI W G, LIU W, YU W, et al. Abscisic acid enhances lead translocation from the roots to the leaves and alleviates its toxicity in Populus × canescens[J]. J Hazard Mater, 2019,362:275-285.DOI: 10.1016/j.jhazmat.2018.09.024. doi: 10.1016/j.jhazmat.2018.09.024
[10]	SCARACIA-MUGNOZZA G E, CEULEMANS R, HEILMAN P E, et al. Production physiology and morphology of Populus species and their hybrids grown under short rotation.II.Biomass components and harvest index of hybrid and parental species clones[J]. Can J For Res, 1997,27(3):285-294.DOI: 10.1139/x96-180. doi: 10.1139/x96-180
[11]	PIETROSANTI L, MATTEUCCI G, PIETRINI F, et al. Hydrological control and phytoremediation by poplar and willow clones in a contamineted industrial site in Venice lagoon [C]// KALOGERAKIS N, FAVA F, BANWART S A. Crete: Proceedings of the Forth European Bioremediation Conference, 2008.
[12]	MCGRATH S P, DUNHAM S J, CORRELL R L. Potential for phytoextraction of zinc and cadmium from soils using hyperaccumulator plants[M]//Phytoremediation of Contaminated Soil and Water:CRC Press, 2020: 109-128. DOI: 10.1201/9780367803148-6.
[13]	POLLE A, DOUGLAS C. The molecular physiology of poplars:paving the way for knowledge-based biomass production[J]. Plant Biol (Stuttg), 2010,12(2):239-241.DOI: 10.1111/j.1438-8677.2009.00318.x. doi: 10.1111/j.1438-8677.2009.00318.x
[14]	HU Y, NAN Z, SU J, et al. Heavy metal accumulation by poplar in calcareous soil with various degrees of multi-metal contamination:implications for phytoextraction and phytostabilization[J]. Environ Sci Pollut Res Int, 2013,20(10):7194-7203.DOI: 10.1007/s11356-013-1711-0. doi: 10.1007/s11356-013-1711-0
[15]	PIETRINI F, ZACCHINI M, IORI V, et al. Screening of poplar clones for cadmium phytoremediation using photosynjournal,biomass and cadmium content analyses[J]. Int J Phytoremediation, 2009,12(1):105-120.DOI: 10.1080/15226510902767163. doi: 10.1080/15226510902767163
[16]	MIGEON A, RICHAUD P, GUINET F, et al. Hydroponic screening of poplar for trace element tolerance and accumulation[J]. Int J Phytoremediation, 2012,14(4):350-361.DOI: 10.1080/15226514.2011.620651. doi: 10.1080/15226514.2011.620651
[17]	BENYÓ D, HORVÁTH E, NÉMETH E, et al. Physiological and molecular responses to heavy metal stresses suggest different detoxification mechanism of Populus deltoides and P.×canadensis[J]. J Plant Physiol, 2016,201:62-70.DOI: 10.1016/j.jplph.2016.05.025. doi: 10.1016/j.jplph.2016.05.025
[18]	AS E, TABARI KOUCHAKSARAEI M, BAHRAMIFAR N, et al. Gas exchange responses of two poplar clones (Populus euramericana (Dode) Guinier 561/41 and Populus nigra Linnaeus 63/135) to lead toxicity[J]. J For Sci, 2016,62(9):422-428.DOI: 10.17221/91/2016-jfs. doi: 10.17221/JFS
[19]	HAN S H, KIM D H, LEE J C. Effects of the ectomycorrhizal fungus Pisolithus tinctorius and Cd on physiological properties and Cd uptake by hybrid poplar Populus alba × Glandulosa[J]. J Ecol Environ, 2011,34(4):393-400.DOI: 10.5141/jefb.2011.041. doi: 10.5141/JEFB.2011.041
[20]	CAO X, JIA J B, LI H, et al. Photosynjournal,water use efficiency and stable carbon isotope composition are associated with anatomical properties of leaf and xylem in six poplar species[J]. Plant Biol (Stuttg), 2012,14(4):612-620.DOI: 10.1111/j.1438-8677.2011.00531.x. doi: 10.1111/j.1438-8677.2011.00531.x
[21]	HE J, QIN J, LONG L, et al. Net cadmium flux and accumulation reveal tissue-specific oxidative stress and detoxification in Populus × canescens[J]. Physiol Plant, 2011,143(1):50-63.DOI: 10.1111/j.1399-3054.2011.01487.x.
[22]	ZHOU JT, WAN H X, HE J L, et al. Integration of cadmium accumulation,subcellular distribution,and physiological responses to understand cadmium tolerance in apple rootstocks[J]. Front Plant Sci, 2017,8:966.DOI: 10.3389/fpls.2017.00966. doi: 10.3389/fpls.2017.00966
[23]	WAN H, DU J, HE J, et al. Copper accumulation,subcellular partitioning and physiological and molecular responses in relation to different copper tolerance in apple rootstocks[J]. Tree Physiol, 2019,39(7):1215-1234.DOI: 10.1093/treephys/tpz042. doi: 10.1093/treephys/tpz042
[24]	KUMAR A, PRASAD M N V. Plant-lead interactions:transport,toxicity,tolerance,and detoxification mechanisms[J]. Ecotoxicol Environ Saf, 2018,166:401-418.DOI: 10.1016/j.ecoenv.2018.09.113. doi: 10.1016/j.ecoenv.2018.09.113
[25]	SHARMA P, DUBEY R S. Lead toxicity in plants[J]. Braz J Plant Physiol, 2005,17(1):35-52.DOI: 10.1590/s1677-04202005000100004. doi: 10.1590/S1677-04202005000100004
[26]	ALKHATIB R, MHEIDAT M, ABDO N, et al. Effect of lead on the physiological,biochemical and ultrastructural properties of Leucaena leucocephala[J]. Plant Biol, 2019,21(6):1132-1139.DOI: 10.1111/plb.13021. doi: 10.1111/plb.v21.6
[27]	PAJEVIC S, BORISEV M, NIKOLIC N, et al. Phytoremediation capacity of poplar (Populus spp.) and willow (Salix spp.) clonesin relation to photosynjournal[J]. Arch Biol Sci, 2009,61(2):239-247.DOI: 10.2298/abs0902239p. doi: 10.2298/ABS0902239P
[28]	ROMANOWSKA E, WRÓBLEWSKA B, DROAK A, et al. High light intensity protects photosynthetic apparatus of pea plants against exposure to lead[J]. Plant Physiol Biochem, 2006,44(5/6):387-394.DOI: 10.1016/j.plaphy.2006.06.003. doi: 10.1016/j.plaphy.2006.06.003
[29]	SHA S, CHENG M H, HU K J, et al. Toxic effects of Pb on Spirodela polyrhiza (L.):subcellular distribution,chemical forms,morphological and physiological disorders[J]. Ecotoxicol Environ Saf, 2019,181:146-154.DOI: 10.1016/j.ecoenv.2019.05.085. doi: 10.1016/j.ecoenv.2019.05.085
[30]	RADOJCIC REDOVNIKOVIC I, DE MARCO A, PROIETTI C, et al. Poplar response to cadmium and lead soil contamination[J]. Ecotoxicol Environ Saf, 2017,144:482-489.DOI: 10.1016/j.ecoenv.2017.06.011. doi: 10.1016/j.ecoenv.2017.06.011
[31]	SALEHI A, TABARI KOUCHAKSARAEI M, MOHAMMADI GOLTAPEH E, et al. Effect of mycorrhizal inoculation on black and white poplar in a lead-polluted soil[J]. J For Sci, 2016,62:223-228.DOI: 10.17221/23/2016-jfs. doi: 10.17221/JFS
[32]	SZUBA A, KARLINSKI L, KRZESŁOWSKA M, et al. Inoculation with a Pb-tolerant strain of Paxillus involutus improves growth and Pb tolerance of Populus × canescens under in vitro conditions[J]. Plant Soil, 2017,412(1/2):253-266.DOI: 10.1007/s11104-016-3062-3. doi: 10.1007/s11104-016-3062-3
[33]	CHEN L, GAO S, ZHU P, et al. Comparative study of metal resistance and accumulation of lead and zinc in two poplars[J]. Physiol Plant, 2014,151(4):390-405.DOI: 10.1111/ppl.12120.
[34]	DOS SANTOS UTMAZIAN M N, DE WIESHAMMER G, VEGA R, et al. Hydroponic screening for metal resistance and accumulation of cadmium and zinc in twenty clones of willows and poplars[J]. Environ Pollut, 2007,148(1):155-165.DOI: 10.1016/j.envpol.2006.10.045. doi: 10.1016/j.envpol.2006.10.045
[35]	SHI WG, ZHOU J, LI J, et al. Lead exposure-induced defense responses result in low lead translocation from the roots to aerial tissues of two contrasting poplar species[J]. Environ Pollut, 2021,271:116346.DOI: 10.1016/j.envpol.2020.116346. doi: 10.1016/j.envpol.2020.116346
[36]	MUTHUSARAVANAN S, SIVARAJASEKAR N, VIVEK J S, et al. Phytoremediation of heavy metals:mechanisms,methods and enhancements[J]. Environ Chem Lett, 2018,16(4):1339-1359.DOI: 10.1007/s10311-018-0762-3. doi: 10.1007/s10311-018-0762-3
[37]	BALDANTONI D, CICATELLI A, BELLINO A, et al. Different behaviours in phytoremediation capacity of two heavy metal tolerant poplar clones in relation to iron and other trace elements[J]. J Environ Manag, 2014,146:94-99.DOI: 10.1016/j.jenvman.2014.07.045. doi: 10.1016/j.jenvman.2014.07.045
[38]	PILIPOVIC A, ZALESNY R S, RONCEVIC S, et al. Growth,physiology,and phytoextraction potential of poplar and willow established in soils amended with heavy-metal contaminated,dredged river sediments[J]. J Environ Manage, 2019,239:352-365.DOI: 10.1016/j.jenvman.2019.03.072. doi: 10.1016/j.jenvman.2019.03.072
[39]	LEBRUN M, MIARD F, NANDILLON R, et al. Influence of biochar particle size and concentration on Pb and as availability in contaminated mining soil and phytoremediation potential of poplar assessed in a mesocosm experiment[J]. Water Air Soil Pollut, 2020,232(1):1-21.DOI: 10.1007/s11270-020-04942-y. doi: 10.1007/s11270-020-04943-x
[40]	KOMÁREK M, TLUSTOS P, SZÁKOVÁ J, et al. The use of maize and poplar in chelant-enhanced phytoextraction of lead from contaminated agricultural soils[J]. Chemosphere, 2007,67(4):640-651.DOI: 10.1016/j.chemosphere.2006.11.010. doi: 10.1016/j.chemosphere.2006.11.010
[41]	LIPHADZI M S, KIRKHAM M B, MANKIN K R, et al. EDTA-assisted heavy-metal uptake by poplar and sunflower grown at a long-term sewage-sludge farm[J]. Plant Soil, 2003,257(1):171-182.DOI: 10.1023/A:1026294830323. doi: 10.1023/A:1026294830323
[42]	KACALKOVA L, TLUSTOS P, SZAKOVA J. Chromium, nickel, cadmium, and lead accumulation in maize, sunflower, willow, and poplar[J]. 2014. 23(3):753-761.
[43]	MA C, CHEN Y, DING S, et al. Sulfur nutrition stimulates lead accumulation and alleviates its toxicity in Populus deltoides[J]. Tree Physiol, 2018,38(11):1724-1741.DOI: 10.1093/treephys/tpy069.

树种 species	Pb处理/ (mmol·L^-1) Pb treaments	地径/mm ground diameter
树种 species	Pb处理/ (mmol·L^-1) Pb treaments	0 d	7 d	14 d	21 d	28 d	35 d		42 d
Pc	0	2.45±0.11 a	2.63±0.10 a	2.89±0.14 a	3.15±0.17 a	3.77±0.16 a		4.09±0.26 a		4.48±0.27 a
Pc	8	2.95±0.13 b	3.29±0.09 b	3.55±0.09 b	3.78±0.12 b	4.21±0.18 b		4.29±0.18 a		4.39±0.25 a
Pd	0	3.70±0.06 cd	4.02±0.07 cd	4.37±0.14 c	4.87±0.10 de	5.12±0.04 def		5.44±0.08 cd		5.75±0.08 de
Pd	8	3.90±0.14 de	4.21±0.20 cde	4.51±0.16 cd	4.84±0.15 de	5.11±0.07 def		5.39±0.11 cd		5.58±0.12 cd
Pe	0	4.76±0.14 f	5.06±0.18 f	5.46±0.17 e	5.80±0.16 f	6.14±0.18 i		6.42±0.14 g		6.70±0.15 g
Pe	8	4.74±0.14 f	5.01±0.11 f	5.37±0.17 e	5.64±0.16 f	5.85±0.14 hi		6.11±0.15 fg		6.38±0.16 fg
Pg	0	3.52±0.22 c	3.92±0.17 cd	4.36±0.15 c	4.96±0.14 de	5.40±0.21 fg		5.71±0.18 de		6.08±0.18 ef
Pg	8	3.75±0.14 cde	4.16±0.05 cde	4.65±0.07 cd	5.03±0.04 de	5.34±0.07 fg		5.58±0.09 de		5.68±0.07 de
Pn	0	3.79±0.05 cde	4.11±0.09 cde	4.58±0.13 cd	4.80±0.14 de	5.17±0.41 defg		5.46±0.52 cde		5.81±0.56 def
Pn	8	3.73±0.04 cde	3.86±0.08 c	3.95±0.07 b	4.17±0.06 c	4.52±0.02 bc		4.74±0.05 b		5.01±0.04 b
Pp	0	3.98±0.07 de	4.34±0.10 e	4.74±0.11 d	5.07±0.10 e	5.53±0.13 gh		5.90±0.10 ef		6.25±0.07 f
Pp	8	3.87±0.08 de	4.10±0.08 cde	4.46±0.09 cd	4.72±0.08 d	4.86±0.06 cde		5.07±0.09 bc		5.17±0.08 bc
Pz	0	4.05±0.03 e	4.42±0.07 e	4.71±0.17 cd	5.04±0.14 de	5.37±0.12 fg		5.71±0.22 def		5.97±0.20 def
Pz	8	4.04±0.12 e	4.22±0.12 de	4.44±0.13 cd	4.66±0.09 d	4.72±0.05 cd		5.03±0.06 bc		5.17±0.05 bc

树种 species	Pb积累量/(mg·株^-1) total Pb amount				富集系数 BCF		转运系数 TF
树种 species	根 roots	木材 wood	树皮 bark	叶 leaves	根 roots	地上部分 aboveground part	转运系数 TF
Pc	0.92±0.16 a	0.11±0.02 d	0.06±0.01 b	1.04±0.10 e	2.70±0.04 b	0.43±0.02 e	0.16±0.01 f
Pd	4.20±0.45 c	0.08±0.01 c	0.06±0.01 b	0.72±0.05 c	6.70±0.26 e	0.20±0.00 d	0.03±0.00 ab
Pe	1.20±0.08 a	0.08±0.01 bc	0.04±0.00 a	0.60±0.03 c	1.73±0.06 a	0.13±0.01 b	0.08±0.00 e
Pg	1.58±0.04 a	0.06±0.00 ab	0.08±0.00 c	0.89±0.03 d	4.48±0.16 d	0.21±0.00 d	0.05±0.00 cd
Pn	2.92±0.56 b	0.04±0.00 a	0.03±0.00 a	0.20±0.04 a	3.41±0.35 c	0.07±0.01 a	0.02±0.01 a
Pp	2.59±0.27 b	0.05±0.00 a	0.03±0.00 a	0.47±0.03 b	3.95±0.03 d	0.16±0.00 c	0.04±0.00 bc
Pz	1.40±0.16 a	0.04±0.00 a	0.06±0.00 b	0.22±0.01 a	1.76±0.10 a	0.10±0.00 a	0.06±0.00 d

7种杨树铅抗性和积累能力的比较研究

A comparative study on lead tolerance and accumulation of seven poplar species

RichHTML

PDF

可视化

摘要/Abstract

引用本文

使用本文

图/表 6

参考文献 43

相关文章 15

编辑推荐

Metrics

本文评价

作者

读者

审稿

[1]	周友锋, 谢秉楼, 李明诗. 基于随机森林协同克里金法的区域森林地上生物量制图——以粤北森林为例[J]. 南京林业大学学报（自然科学版）, 2024, 48(1): 169-178.
[2]	董玉洁, 毛岭峰, 张敏, 鲁旭东, 吴秀萍. 华东地区亚热带典型常绿阔叶林地上生物量与环境因子的关系[J]. 南京林业大学学报（自然科学版）, 2024, 48(1): 74-80.
[3]	颜铮明, 阮宏华, 廖家辉, 石珂, 倪娟平, 曹国华, 沈彩芹, 丁学农, 赵小龙, 庄鑫. 不同林龄杨树人工林地表甲虫群落多样性特征[J]. 南京林业大学学报（自然科学版）, 2023, 47(6): 236-242.
[4]	李建新, 徐森, 杨丽婷, 陈双林, 郭子武. 毛竹林下多花黄精构件生物量分配特征的年际效应[J]. 南京林业大学学报（自然科学版）, 2023, 47(5): 121-128.
[5]	熊燕飞, 陈跃锋, 毛志强, 曹杏红, 叶语涵, 张建坤. 空气甲醛污染的植物修复机制[J]. 南京林业大学学报（自然科学版）, 2023, 47(4): 1-12.
[6]	王露露, 耿兴敏, 宦智群, 许世达, 赵晖. 1-MCP预处理对杜鹃花高温胁迫下光合特性及相关基因表达的影响[J]. 南京林业大学学报（自然科学版）, 2023, 47(4): 103-113.
[7]	何潇, 雷相东, 段光爽, 丰庆荣, 张逸如, 冯林艳. 气候变化对落叶松人工林生物量生长的影响模拟[J]. 南京林业大学学报（自然科学版）, 2023, 47(3): 120-128.
[8]	孙宇, 李凤日, 谢龙飞, 董利虎. 基于林分及地形因子的落叶松人工林林分生物量模型构建[J]. 南京林业大学学报（自然科学版）, 2023, 47(3): 129-136.
[9]	唐依人, 贾炜玮, 王帆, 孙毓蔓, 张颖. 基于TLS辅助的长白落叶松一级枝条生物量模型构建[J]. 南京林业大学学报（自然科学版）, 2023, 47(2): 130-140.
[10]	高羽, 李静, 刘洋, 乌雅瀚, 巩家星, 辛启睿. 结构方程模型在兴安落叶松林生长中的应用[J]. 南京林业大学学报（自然科学版）, 2023, 47(1): 38-46.
[11]	刘亚梅, 刘盛全, 周亮, 胡建军, 赵自成, 郑向丽. 8个杨树无性系/品种木材解剖特征及其径向变异模式[J]. 南京林业大学学报（自然科学版）, 2023, 47(1): 234-240.
[12]	王大卫, 沈文星. 中国主要树种人工乔木林碳储量测算及固碳潜力分析[J]. 南京林业大学学报（自然科学版）, 2022, 46(5): 11-19.
[13]	张庆源, 田野, 王淼, 翟政, 周诗朝. 美洲黑杨与青杨杂交F₁代苗期表型性状的分化及其类型划分[J]. 南京林业大学学报（自然科学版）, 2022, 46(5): 40-48.
[14]	夏捷, 陈胜, 吴一凡, 张玮, 谢锦忠. 种植竹荪后毛竹林土壤微生物生物量和微生物熵的动态变化[J]. 南京林业大学学报（自然科学版）, 2022, 46(4): 127-134.
[15]	赵爽, 王邵军, 杨波, 左倩倩, 曹乾斌, 王平, 张路路, 张昆凤, 樊宇翔. 西双版纳热带森林碳循环中土壤呼吸对次生演替的响应[J]. 南京林业大学学报（自然科学版）, 2022, 46(2): 12-18.