
珍稀濒危植物堇叶紫金牛种群结构及动态分析
马丹丹, 库伟鹏, 夏国华, 毛洁莹, 薛建辉
南京林业大学学报(自然科学版) ›› 2021, Vol. 45 ›› Issue (3) : 159-164.
珍稀濒危植物堇叶紫金牛种群结构及动态分析
Structure and dynamics of rare and endangered plant Ardisia violacea natural population
【目的】堇叶紫金牛(Ardisia violacea)为中国特有的珍稀濒危植物,目前报道仅在台湾、浙江、安徽有零星分布。研究其种群结构和动态,旨在为维持堇叶紫金牛种群及其生存群落的发展提供一定的科学依据,也为探索堇叶紫金牛种群及群落的保护、更新和生态恢复奠定理论基础。【方法】以2018年新发现的堇叶紫金牛最北分布点杭州市临安区清凉峰镇顺溪坞的种群为研究对象,通过编制静态生命表和生殖力表,绘制种群年龄结构图、存活曲线和死亡率、消亡率曲线图,进行种群结构和动态分析。【结果】①种群内低龄级[DB(基径)≤1.4 mm]植株数最为丰富,中龄级(1.4<DB≤1.8 mm)和高龄级(DB>1.8 mm)植株数较少,表现为增长型种群。②存活曲线趋向于Deevey-Ⅱ型,种群各龄级有相近的死亡率。③未来外部干扰下的数量动态指数Vpi'=0.008 8>0,种群增长速度较为缓慢,且对外界干扰比较敏感。【结论】样地内堇叶紫金牛种群整体呈低增长型发展趋势,生理寿命约4.0 a,种群规模相对稳定。
【Objective】 Ardisia violacea, a rare and endangered plant endemic to China, has been found only in Taiwan, Zhejiang and Anhui Provinces. The purpose of this study is to provide a scientific basis for maintaining the development of the Ardisia violacea population and ensuring the survival of the community as well as to lay a theoretical foundation for the protection, regeneration and ecological restoration of the population and community. 【Method】The population of Ardisia violacea in Shunxiwu of Lin’an District, Hangzhou City, Zhejiang Province was newly discovered in 2018; the northernmost region where Ardisia violacea is distributed was taken as the study area for this study. The sample square survey method was adopted. The sample areas were divided into sample squares of 20 m× 20 m, and then each sample square was further divided into 16 small squares of 5 m × 5 m. For each individual plant, we recorded species name, height, basal diameter (Db), crown width and coverage; habitat factors were recorded, including altitude, latitude, longitude, slope direction, slope, forest canopy density, soil type and vegetation community. The population structure and dynamics of Ardisia violacea were analyzed by compiling the static life table and fertility table, drawing the population age structure diagram, survival curve, mortality curve and extinction rate curve. 【Result】 ① In the population, plants in the low age class (DB≤ 1.4 mm) were the most abundant, while the middle age class (1.4 < DB ≤ 1.8 mm) and the old age class (DB > 1.8 mm) were the least abundant, which shows that this population is growing. ② The survival curve tended to Deevey-Ⅱ, and the population had similar mortality rates at all ages. ③ Under future external interference, Vpi'=0.008 8 > 0, the population growth rate is likely to be slower and sensitive to external disturbances. 【Conclusion】The whole population of Ardisia violacea in the sample plot showed a trend of low growth, a physiological life span of about 4.0 years, and the population size was relatively stable.
堇叶紫金牛 / 种群结构 / 静态生命表 / 存活曲线 / 生殖力
Ardisia violacea / population structure / static life table / survival curve / fertility
[1] |
韩路, 王家强, 王海珍, 等. 塔里木河上游胡杨种群结构与动态[J]. 生态学报, 2014,34(16):4640-4651.
|
[2] |
江波, 周先容, 尚进, 等. 中国特有植物巴山榧树的种群结构与动态[J]. 生态学报, 2018,38(3):1016-1027.
|
[3] |
|
[4] |
张若蕙. 浙江珍稀濒危植物[M]. 杭州: 浙江科学技术出版社, 1994: 315-318.
|
[5] |
方云亿. 浙江植物志:第5卷[M]. 杭州: 浙江科学技术出版社, 1989: 31.
|
[6] |
马凯, 夏国华, 闫道良, 等. 珍稀濒危植物堇叶紫金牛生存群落结构特征及物种多样性[J]. 浙江农林大学学报, 2012,29(4):498-509.
|
[7] |
张云, 夏国华, 马凯, 等. 遮阴对堇叶紫金牛光合特性和叶绿素荧光参数的影响[J]. 应用生态学报, 2014,25(7):1940-1948.
|
[8] |
代英超, 徐奎源, 马凯, 等. 珍稀濒危植物堇叶紫金牛对持续干旱的生理响应[J]. 生态学报, 2015,35(9):2955-2959.
|
[9] |
孙英坤, 胡绍庆, 庞基良, 等. 珍稀濒危物种堇叶紫金牛高效快繁体系的建立[J]. 植物学报, 2017,52(6):764-773.
筛选堇叶紫金牛(Ardisia violacea)野生优株, 以其当年新发带休眠腋芽茎段为外植体, 通过启动培养、丛生芽诱导增殖、壮苗培养、生根培养和炼苗移栽等过程建立其组培快繁技术体系。研究结果表明, 最佳启动培养基为MS+0.80 mg·L<sup>-1</sup> KT+0.10 mg·L<sup>-1</sup> NAA+0.10 mg·L<sup>-1</sup> IBA, 腋芽萌发率达92.60%; 最佳丛生芽诱导增殖培养基为MS1+0.50 mg·L<sup>-1</sup> TDZ+0.10 mg·L<sup>-1</sup> NAA, 平均增殖系数达8.60; 最佳壮苗培养基为MS+1.00 mg·L<sup>-1</sup> KT+0.50 mg·L<sup>-1 </sup>NAA; 最佳生根培养基为1/2MS+2.00 mg·L<sup>-1</sup> IBA+1.00 mg·L<sup>-1</sup> NAA+1.00 mg·L<sup>-1</sup> AC, 平均生根率达98.70%; 采用松鳞和泥炭(2:1, v/v)作为炼苗基质, 炼苗成活率可达85.30%。实验成功建立了堇叶紫金牛高效组培快繁技术体系, 经验证该体系能够满足规模化生产的需求。
|
[10] |
吴明开, 沈志君, 刘海, 等. 梵净山自然保护区珙桐天然种群生命表与生存分析[J]. 生态学杂志, 2012,31(6):1419-1424.
|
[11] |
|
[12] |
李先琨, 苏宗明, 向悟生, 等. 濒危植物元宝山冷杉种群结构与分布格局[J]. 生态学报, 2002,22(12):2245-2253.
|
[13] |
宋萍, 洪伟, 吴承祯, 等. 珍稀濒危植物桫椤种群结构与动态研究[J]. 应用生态学报, 2005,16(3):413-418.
|
[14] |
申仕康, 马海英, 王跃华, 等. 濒危植物猪血木(Euryodendron excelsum H.T. Chang)自然种群结构及动态[J]. 生态学报, 2008,28(5):2404-2412.
|
[15] |
江洪. 云杉种群生态学[M]. 北京: 中国林业出版社, 1992.
|
[16] |
解婷婷, 苏培玺, 周紫鹃, 等. 荒漠绿洲过渡带沙拐枣种群结构及动态特征[J]. 生态学报, 2014,34(15):4272-4279.
|
[17] |
陈晓德. 植物种群与群落结构动态量化分析方法研究[J]. 生态学报, 1999,18(2):214-217.
|
[18] |
郝红敏, 路荣, 贾超, 等. 水蚀风蚀交错带黑沙蒿灌丛斑块种群结构及动态特征研究[J]. 西北植物学报, 2017,37(4):773-781.
|
[19] |
黄红兰, 张露, 郭晓燕, 等. 九连山毛红椿种群的结实特性及其生殖力[J]. 林业科学, 2013(7):170-174.
|
[20] |
高俊香, 梅盛龙, 鲁小珍, 等. 凤阳山自然保护区麂角杜鹃种群结构与分布[J]. 南京林业大学学报(自然科学版), 2009,33(2):35-38.
|
[21] |
兰国玉, 陈伟, 周小飞. 海南霸王岭青梅林群落特征研究[J]. 西北植物学报, 2007,27(9):1861-1868.
|
[22] |
魏琦, 楼炉焕, 冷建红, 等. 毛枝连蕊茶群落结构与物种多样性[J]. 浙江农林大学学报, 2011,28(4):634-639.
|
[23] |
许恒, 刘艳红. 极小种群梓叶槭种群结构及动态特征[J]. 南京林业大学学报(自然科学版), 2019,43(2):47-54.
|
/
〈 |
|
〉 |