Phenotypic Observation of Canada Asiatica in Different Invasive Areas of Yunnan

doi:10.11924/j.issn.1000-6850.casb2023-0570

Abstract

Abstract:

This study aimed to clarify the ecological adaptability of Solidago canadensis L. in 11 different occurrence areas in Yunnan Province. The plant traits and differences were observed under common garden conditions, respectively. The results showed that the further growth and reproduction characteristics of Solidago canadensis L. occurring in different invasive regions differed significantly under common garden conditions, in which the variation of root sprouting trait index reached 54.23%, and the variation of stem diameter, leaf width and leaf shape indexes ranged from 23.63%-26.31%. Among the biomass allocation ratios, the plant with the highest percentage of flower biomass allocation was from Qiubei County of Wenshan Prefecture, the plant with the highest percentage of leaf biomass allocation was from Xishan District of Kunming, the plant with the highest percentage of culm biomass allocation was from Panlong District of Kunming, and the plant with the highest percentage of root biomass allocation was also from Panlong District of Kunming. In the further determination of the four enzyme activities of POD, SOD, CAT and MDA, the plant populations from 11 different invasive regions and habitats showed significant differences, among which those from Qiubei point and Panlong point were the most prominent. In the cluster analysis, it was found that the leaves in the plant traits showed certain variability, but in the bias correlation analysis of climatic factors, the climatic factors in the original place had less influence on Solidago canadensis L. The results of the study showed that the plant traits of Solidago canadensis L. were basically stable and consistent, but the phenotypes in different invasive areas had some differences and plasticity due to the different environmental conditions. The results of this study lay an important scientific foundation for clarifying the ecological adaptability of the Solidago canadensis L. in Yunnan Province, and provide a scientific basis for early warning, monitoring and preventing the expansion of this invasive plant.

Key words: Solidago canadensis L., botanical trait, plant plasticity, enzymatic activity, common garden experiment

FAN Zewen, ZHENG Fengping, YANG Yunhai, YANG Shaosong, ZHANG Fudou, SHEN Shicai, XU Gaofeng, ZHANG Zhiyan, CHUAN Li, CUI Yuchen. Phenotypic Observation of Canada Asiatica in Different Invasive Areas of Yunnan[J]. Chinese Agricultural Science Bulletin, 2024, 40(17): 127-134.

Figures/Tables 6

References 40

[1]	WILLIAMSON M, FITTER A. The varying success of invaders[J]. Ecology, 1996, 77(6):1661-1666.
[2]	CLAUDIO VALLADARES-PADUA C. Importance of knowledge-intensive economic development to conservation of biodiversity in developing countries[J]. Conservation biology, 2006, 20(3):700-701.
[3]	王宁, 李卫芳, 周兵, 等. 中国入侵克隆植物入侵性、克隆方式及地理起源[J]. 生物多样性, 2016, 24(1):12-19. doi: 10.17520/biods.2015190
[4]	陈慧丽, 李玉娟, 李博, 等. 外来植物入侵对土壤生物多样性和生态系统过程的影响[J]. 生物多样性, 2005, 13(6):555-565. doi: 10.1360/biodiv.050058
[5]	周雨露, 李凌云, 高俊琴, 等. 种间竞争对入侵植物和本地植物生长的影响[J]. 生态学杂志, 2016, 35(6):1504-1510.
[6]	万凌云. 入侵植物加拿大一枝黄花(Solidago canadensis L.)的磷资源竞争策略[D]. 镇江: 江苏大学, 2019.
[7]	WEBER E. Current and potential ranges of three cxotic goldenrods (Solidago) in Europe[J]. Conservation biology, 2001, 15(1):122-128.
[8]	李振宇, 解焱. 中国外来入侵种[M]. 北京: 中国林业出版社,2002:170
[9]	王培蕾. 入侵植物加拿大一枝黄花的入侵起源与亲缘关系研究[D]. 上海: 上海师范大学, 2016.
[10]	雷军成, 徐海根. 基于MaxEnt的加拿大一枝黄花在中国的潜在分布区预测[J]. 生态与农村环境学报, 2010, 26(2):137-141.
[11]	綦顺英, 宫志锋, 杨宇航, 等. 加拿大一枝黄花入侵对地上植被及土壤种子库的影响[J]. 安徽农业大学学报, 2022, 49(3):476-482.
[12]	胡嘉贝, 沈佳. 泉州地区生物入侵现状与防范对策[J]. 山西农业科学, 2012, 40(7):775-778,799.
[13]	VILA M, ESPINAR J L, HEJDA M, et al. Ecological impacts of invasive alien plants:ameta-analysis of their effects on species, communities and ecosystems[J]. Ecology letters, 2011, 14(7):702-708.
[14]	郭水良. 加拿大一枝黄花的生态位及其入侵对植物群落的影响[J]. 生物数学学报, 2005, 20(1):91-96.
[15]	WANG CY, JIANG K, LIU J, et al. Moderate and heavy Solidago Canadensis L. invasion are associated with decreased taxonomic diversity but increased functional diversity of plant communities in East China[J]. Ecological engineering, 2018, 112(3):55-64.
[16]	金红玉, 肖顺勇, 游芳. 典型药剂对不同留茬高度加拿大一枝黄花的防效[J]. 植物保护, 2019, 45(4):271-281.
[17]	HULME P E. Phenotypic plasticity and plant invasions: Is it all jack?[J]. Function ecology, 2008,22:3-7.
[18]	SCHOEPPNER N M, RELYEA R A. Phenotipic plasticity in response to fine-grained environmental variation in predation[J]. Functional ecology, 2009,23:587-594.
[19]	LAVERGNE S, MOLOFSKY J. Increased genetic variation and evolutionary potential drive the success of an invasive grass[J]. Proceedings of the National Academy of sciences of the United States of America, 2007,104:3883-3888.
[20]	徐汝梅. 生物入侵—理论与实践[M]. 北京: 科学出版社,2004:16-19.
[21]	GENG Y P, PAN X Y, XU C Y, et al. Phenotypic plasticity rather than locally adapted ecotypes allows the invasive alligator weed to colonize a wide range of habitats[J]. Biological invasions, 2007, 9(3):245-256.
[22]	马俊改, 石福臣. 养分条件对互花米草表型可塑性的影响[J]. 生态学杂志, 2011, 30(3):459-463.
[23]	SCHLICHTING, CARL D, LEVIN, DONALD A. Phenotypic plasticity: An evolving plant character[J]. Biological journal of the linnean society, 1986, 29(1):37-47.
[24]	HUEY, RAYMOND B, GILCHRIST, et al. Rapid evolution of a geographic cline in size in an introduced fly[J]. Science, 2000, 287(5451):308-309. pmid: 10634786
[25]	NIINEMETS U, VALLADARES F, CEULEMANS R. Leaf-level phenotypic variability and plasticity of invasive Rhododendron ponticum and non-invasive Ilex aquifolium co-occurring at two contrasting European sites[J]. Plant, cell and environment, 2003, 26(6):941-956.
[26]	郭水良, 方芳. 入侵植物加拿大一枝黄花对环境的生理适应性研究[J]. 植物生态学报, 2003, 27(1):47-52. doi: 10.17521/cjpe.2003.0007
[27]	杨如意, 昝树婷, 唐建军. 加拿大一枝黄花的入侵机理研究进展[J]. 生态学报, 2011, 31(4):1185-1194.
[28]	FENG Y L, LEI Y B, WANG R F, et al. Evolutionary tradeoffs for nitrogen allocation to photosynthesis versus cell walls in an invasive plant[J]. Proceedings of the National Academy of Sciences of the United States of America, 2009,106:1853-1856.
[29]	王姝, 周道玮. 植物表型可塑性研究进展[J]. 生态学报, 2017, 37(24):8161-8169.
[30]	DIAZ S, CABIDO M, CASANOVES F. Plant functional traits and environmental filters at a regional scale[J]. Journal of vegetation science, 1998,9:113-122.
[31]	VAN K M, WEBER E, FISCHER M. A meta-analysis of trait differences between invasive and non-invasive plant species[J]. Ecology letter, 2010,13:235-245.
[32]	COUTTS S R, VAN KLINKEN R D, YOKMIZO H, et al. What are the key drivers of spread in invasive plants: Dispersal, demography of landscape: and how can we use this knowledge to aid management?[J]. Biological invasions, 2011,13:1649-1661.
[33]	GALLAGHER R V, RANDALL R P, LEISHMAN M R. Trait differences between naturalized and invasive plant species independent of residence time and phylogeny[J]. Conservation biology, 2014,29:360-369.
[34]	ABHILASHA D. AND JOSHI J. Enhanced fitness due higher fecundity, increased defence against a specialist and tolerance towards a generalist herbivore in an invasive annual plant[J]. Journal plant ecology, 2009,2:77-86.
[35]	DAWSON W, BURSLEM D F R P, HULME P E. Factors explaining alien plant invasion success in a tropical ecosystem differ at each stage of invasion[J]. Journal of ecology, 2009, 97(4):657-665.
[36]	FLORY L S, CLAY K. Effects of roads and forest successional age on experimental plant invasions[J]. Biological conservation, 2009, 142(11):2531-2537.
[37]	PETR PYšEK, MARTIN KřIVáNEK, VOjTěCH J. Planting intensity, residence time, and species traits determine invasion success of alien woody species[J]. Ecology, 2009, 90(10):2734-2744. pmid: 19886483
[38]	MASON ROBERT AB, COOKE JULIA, MOLES ANGELA T, LEISHMAN Michelle R. Reproductive output of invasive versus native plants[J]. Global ecology and biogeography, 2008, 17(5):633-640.
[39]	张震, 曹亚蒙, 钟耀华, 等. 加拿大一枝黄花在安徽合肥的入侵生态因子分析[J]. 生物安全学报, 2019, 28(2):133-139.
[40]	葛结林, 熊高明, 毛江涛, 等. 加拿大一枝黄花在江南休闲旅游乡村的入侵特征及其影响因素[J]. 中国生态农业学报,2023:1-11.

编号	采集地址	生境	海拔/m	经度(E)/°	纬度(N)/°
KPZ	昆明市盘龙区庄科村	路边荒地	1941	102.8701547	25.2361231
KX	昆明市西山区碧鸡街道	人工林	1857	102.6534609	24.9153123
KJ	昆明市晋宁区昆阳兴旺环湖路	路边荒地	1864	102.600477	24.684998
KC	昆明市呈贡区捞鱼河湿地公园	人工林	1840	102.7751749	24.8260382
KPA	昆明市盘龙区阿子营	湿地	2035	102.7735417	24.347415
KL	昆明市禄劝县转龙镇	沟渠	1952	102.8747267	24.887353
KPD	昆明市盘龙区甸尾村	人工林	1921	102.8634683	24.212613
LJ	曲靖市罗平县江边村	沟渠	1456	104.29342	24.933336
LS	曲靖市罗平县江召公路	路边荒地	1467	104.3042066	24.853715
WP	文山州丘北县普者黑国家湿地公园	公园绿化	1449	104.140338	24.09644
LH	曲靖市罗平县罗平花海驿栈	农田	1470	104.3332316	24.903108

编号	采集地址	生境	海拔/m	经度(E)/°	纬度(N)/°
KPZ	昆明市盘龙区庄科村	路边荒地	1941	102.8701547	25.2361231
KX	昆明市西山区碧鸡街道	人工林	1857	102.6534609	24.9153123
KJ	昆明市晋宁区昆阳兴旺环湖路	路边荒地	1864	102.600477	24.684998
KC	昆明市呈贡区捞鱼河湿地公园	人工林	1840	102.7751749	24.8260382
KPA	昆明市盘龙区阿子营	湿地	2035	102.7735417	24.347415
KL	昆明市禄劝县转龙镇	沟渠	1952	102.8747267	24.887353
KPD	昆明市盘龙区甸尾村	人工林	1921	102.8634683	24.212613
LJ	曲靖市罗平县江边村	沟渠	1456	104.29342	24.933336
LS	曲靖市罗平县江召公路	路边荒地	1467	104.3042066	24.853715
WP	文山州丘北县普者黑国家湿地公园	公园绿化	1449	104.140338	24.09644
LH	曲靖市罗平县罗平花海驿栈	农田	1470	104.3332316	24.903108

编号	株高/cm	茎杆直径/cm	根萌芽	叶长/cm	叶宽/cm	叶形指数
KPZ	108.50±24.10b	0.68±0.13b	15.00±0.71a	13.10±2.75ab	2.54±0.67ab	5.33±1.19abc
KX	121.68±9.65ab	0.84±0.11ab	7.00±1.00c	14.66±2.63ab	2.18±0.59ab	6.91±1.16ab
KJ	103.22±21.33b	0.72±0.19b	3.80±0.45e	11.86±1.31ab	2.18±0.47ab	5.63±1.32abc
KC	113.68±16.68ab	0.74±0.17b	5.20±0.84d	13.26±1.44ab	2.46±0.49ab	5.64±1.63abc
KPA	131.10±15.13ab	0.72±0.08b	5.40±0.55d	11.78±0.9ab	1.70±0.35b	7.12±1.27a
KL	116.38±23.56ab	0.72±0.16b	3.40±0.55ef	12.70±4.16ab	2.66±1.00ab	5.04±1.29bc
KPD	116.56±10.88ab	1.06±0.30a	6.80±0.84c	16.06±3.31a	3.06±0.91a	5.44±1.34abc
LJ	143.60±16.12a	1.00±0.12a	3.40±0.55ef	13.08±2.18ab	2.38±0.22ab	5.50±0.82abc
LS	116.02±12.41ab	1.00±0.07a	8.20±0.45b	13.96±1.75ab	2.30±0.51ab	6.29±1.48abc
WP	98.62±35.52b	0.69±0.24b	2.80±0.84f	11.50±2.35b	2.62±0.38ab	4.41±0.76c
LH	128.52±24.11ab	0.90±0.14ab	8.00±1.00b	13.96±1.93ab	2.58±0.57ab	5.59±1.12abc
平均值	117.99±22.19	0.83±0.21	6.27±3.40	13.27±2.54	2.42±0.64	5.72±1.35
可塑性指数PI_v	0.605	0.596	0.819	0.528	0.660	0.384
变异系数CV/%	18.80	24.86	54.23	19.17	26.31	23.63

编号	株高/cm	茎杆直径/cm	根萌芽	叶长/cm	叶宽/cm	叶形指数
KPZ	108.50±24.10b	0.68±0.13b	15.00±0.71a	13.10±2.75ab	2.54±0.67ab	5.33±1.19abc
KX	121.68±9.65ab	0.84±0.11ab	7.00±1.00c	14.66±2.63ab	2.18±0.59ab	6.91±1.16ab
KJ	103.22±21.33b	0.72±0.19b	3.80±0.45e	11.86±1.31ab	2.18±0.47ab	5.63±1.32abc
KC	113.68±16.68ab	0.74±0.17b	5.20±0.84d	13.26±1.44ab	2.46±0.49ab	5.64±1.63abc
KPA	131.10±15.13ab	0.72±0.08b	5.40±0.55d	11.78±0.9ab	1.70±0.35b	7.12±1.27a
KL	116.38±23.56ab	0.72±0.16b	3.40±0.55ef	12.70±4.16ab	2.66±1.00ab	5.04±1.29bc
KPD	116.56±10.88ab	1.06±0.30a	6.80±0.84c	16.06±3.31a	3.06±0.91a	5.44±1.34abc
LJ	143.60±16.12a	1.00±0.12a	3.40±0.55ef	13.08±2.18ab	2.38±0.22ab	5.50±0.82abc
LS	116.02±12.41ab	1.00±0.07a	8.20±0.45b	13.96±1.75ab	2.30±0.51ab	6.29±1.48abc
WP	98.62±35.52b	0.69±0.24b	2.80±0.84f	11.50±2.35b	2.62±0.38ab	4.41±0.76c
LH	128.52±24.11ab	0.90±0.14ab	8.00±1.00b	13.96±1.93ab	2.58±0.57ab	5.59±1.12abc
平均值	117.99±22.19	0.83±0.21	6.27±3.40	13.27±2.54	2.42±0.64	5.72±1.35
可塑性指数PI_v	0.605	0.596	0.819	0.528	0.660	0.384
变异系数CV/%	18.80	24.86	54.23	19.17	26.31	23.63

编号	POD/(U/g)	SOD/(U/g)	MDA/(U/g)	CAT/[U/(g min)]
KPZ	173.67	263.23	2.79	13.61
KX	175.30	78.61	3.16	8.46
KJ	167.31	62.75	2.06	4.61
KC	167.13	55.49	1.52	9.06
KPA	163.00	150.61	2.52	6.08
KL	180.43	159.52	1.37	10.84
KPD	214.72	105.03	0.72	8.40
LJ	185.68	108.49	0.54	8.04
LS	174.34	86.70	2.46	5.60
WP	173.37	102.01	1.21	8.08
LH	190.00	217.98	2.82	4.19