Chin J Plant Ecol ›› 2020, Vol. 44 ›› Issue (12): 1236-1246.DOI: 10.17521/cjpe.2020.0059
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WEI Xue-Ying1, YE Yu-Shi1, LIN Xi-Po2, CUI Yu-Wen1, ZENG Fei-Yan1, WANG Fa-Guo1,*()
Received:
2020-03-09
Accepted:
2020-09-10
Online:
2020-12-20
Published:
2021-04-01
Contact:
WANG Fa-Guo
About author:
*(wangfg@scib.ac.cn)Supported by:
WEI Xue-Ying, YE Yu-Shi, LIN Xi-Po, CUI Yu-Wen, ZENG Fei-Yan, WANG Fa-Guo. Population status and conservation of an extremely small population species Euryodendron excelsum[J]. Chin J Plant Ecol, 2020, 44(12): 1236-1246.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2020.0059
Fig. 1 Sampled sites during investigation of Euryodendron excelsum. 1, Helu Village in Bajia Town; 2, Muli Village in Bajia Town; 3, Chengdong Village in Bajia Town; 4, Village forest of Chengdong Village in Bajia Town; 5, Chongtian Village in Bajia Town; 6, Shanhou of Zhongtian Village in Bajia Town; 7, Shima of Zhongtian Village in Bajia Town; 8, Tangyong of Zhongtian Village in Bajia Town; 9, Banbei Village in Sanjia Town; 10, Shijiao of Gaowu Village in Bajia Town; 11, Chaliao of Lianhe Village in Bajia Town; 12, Sanye of Gaowu Village in Bajia Town; 13, Zhugen of Chengdong Village in Bajia Town; 14, Zhongtian of Chengdong Village in Bajia Town.
生活型 Life form | 类别 Category | 物种 Species | 德氏多度 Drude abundance |
---|---|---|---|
乔木 Arbor | 优势种 Dominant species | 阴香 Cinnamomum burmannii | cop3 |
粉箪竹 Bambusa chungii | cop1 | ||
卫矛叶蒲桃 Syzygium euonymifolium | sol | ||
龙眼 Dimocarpus longan | sp | ||
伴生种 Companion species | 假苹婆 Sterculia lanceolata | sp | |
车筒竹 Bambusa sinospinosa | cop1 | ||
楝 Melia azedarach | sol | ||
破布叶 Microcos paniculata | sp | ||
鹅掌柴 Schefflera heptaphylla | cop1 | ||
华润楠 Machilus chinensis | un | ||
杉木 Cunninghamia lanceolata | sol | ||
灌木 Shrub | 优势种 Dominant species | 九里香 Murraya exotica | sol |
九节 Psychotria asiatica | cop2 | ||
赪桐 Clerodendrum japonicum | sp | ||
对叶榕 Ficus hispida | cop1 | ||
黄椿木姜子 Litsea variabilis | cop1 | ||
八角枫 Alangium chinense | sol | ||
伴生种 Companion species | 紫玉盘 Uvaria macrophylla | sp | |
大罗伞树 Ardisia hanceana | sp | ||
小花山小橘 Glycosmis parviflora | sp | ||
大青 Clerodendrum cyrtophyllum | sol | ||
猴耳环 Archidendron clypearia | sp | ||
粗叶榕 Ficus hirta | sol | ||
草本 Herb | 优势种 Dominant species | 假蒟 Piper sarmentosum | sp |
热亚海芋 Alocasia macrorrhizos | cop1 | ||
半边旗 Pteris semipinnata | cop1 | ||
伴生种 Companion species | 火炭母 Polygonum chinense | un | |
欧洲凤尾蕨 Pteris cretica | sol | ||
淡竹叶 Lophatherum gracile | sol | ||
华南毛蕨 Cyclosorus parasiticus | sol | ||
牛白藤 Hedyotis hedyotidea | sol | ||
玉叶金花 Mussaenda pubescens | sol |
Table 1 Species recorded with the field measurement method in the distributional range of Yangchun Euryodendron excelsum population
生活型 Life form | 类别 Category | 物种 Species | 德氏多度 Drude abundance |
---|---|---|---|
乔木 Arbor | 优势种 Dominant species | 阴香 Cinnamomum burmannii | cop3 |
粉箪竹 Bambusa chungii | cop1 | ||
卫矛叶蒲桃 Syzygium euonymifolium | sol | ||
龙眼 Dimocarpus longan | sp | ||
伴生种 Companion species | 假苹婆 Sterculia lanceolata | sp | |
车筒竹 Bambusa sinospinosa | cop1 | ||
楝 Melia azedarach | sol | ||
破布叶 Microcos paniculata | sp | ||
鹅掌柴 Schefflera heptaphylla | cop1 | ||
华润楠 Machilus chinensis | un | ||
杉木 Cunninghamia lanceolata | sol | ||
灌木 Shrub | 优势种 Dominant species | 九里香 Murraya exotica | sol |
九节 Psychotria asiatica | cop2 | ||
赪桐 Clerodendrum japonicum | sp | ||
对叶榕 Ficus hispida | cop1 | ||
黄椿木姜子 Litsea variabilis | cop1 | ||
八角枫 Alangium chinense | sol | ||
伴生种 Companion species | 紫玉盘 Uvaria macrophylla | sp | |
大罗伞树 Ardisia hanceana | sp | ||
小花山小橘 Glycosmis parviflora | sp | ||
大青 Clerodendrum cyrtophyllum | sol | ||
猴耳环 Archidendron clypearia | sp | ||
粗叶榕 Ficus hirta | sol | ||
草本 Herb | 优势种 Dominant species | 假蒟 Piper sarmentosum | sp |
热亚海芋 Alocasia macrorrhizos | cop1 | ||
半边旗 Pteris semipinnata | cop1 | ||
伴生种 Companion species | 火炭母 Polygonum chinense | un | |
欧洲凤尾蕨 Pteris cretica | sol | ||
淡竹叶 Lophatherum gracile | sol | ||
华南毛蕨 Cyclosorus parasiticus | sol | ||
牛白藤 Hedyotis hedyotidea | sol | ||
玉叶金花 Mussaenda pubescens | sol |
Fig. 2 General situation of the habitat of Euryodendron excelsum. A, Chengdong Village in Bajia Town. B, Zhugen of Chengdong Village in Bajia Town. C, Zhongtian of Chengdong Village in Bajia Town. D, Shijiao of Gaowu Village in Bajia Town. E, Sanye of Gaowu Village in Bajia Town. F, Chaliao of Lianhe Village in Bajia Town. G, Helu Village in Bajia Town. H, Muli Village in Bajia Town. I, Shanhou of Zhongtian Village in Bajia Town. J, Shima of Zhongtian Village in Bajia Town. K, Tangyong of Zhongtian Village in Bajia Town. L, Banbei Village in Sanjia Town. M, Chengdong Village in Bajia Town. N, Chongtian Village in Bajia Town. O, Banbei Village in Sanjia Town.
编号 Number | 地点 Place | 生境 Habitat | 乔木层盖度 Coverage of arbor layer | 海拔 Altitude (m) | 人为干扰 Human disturbance | 干扰原因 Cause of interference | 成株 Adult plant | 幼树 Sapling | 幼苗 Seedling |
---|---|---|---|---|---|---|---|---|---|
1 | 八甲镇合路村 Helu Village in Bajia Town | 村边林 Village forest | 50 | 52 | 弱 Weak | 1 | 0 | 10 | |
2 | 八甲镇木力村 Muli Village in Bajia Town | 村边林 Village forest | 65 | 68 | 中 Middle | 2 | 0 | 3 | |
3 | 八甲镇澄垌村 Chengdong Village in Bajia Town | 田野 Field | 45 | 42 | 中 Middle | 阴蔽 Shading | 0 | 0 | 10 |
4 | 八甲镇澄垌村 Chengdong Village in Bajia Town | 村边林 Village forest | 60 | 42 | 中 Middle | 断梢 Branches broken | 2 | 2 | 20 |
5 | 八甲镇澄垌村冲田 Chongtian of Chengdong Village in Bajia Town | 村边林 Village forest | 70 | 30 | 中 Middle | 8 | 0 | 20 | |
6 | 八甲镇中田村山喉 Shanhou of Zhongtian Village in Bajia Town | 村边林 Village forest | 30 | 72 | 弱 Weak | 1 | 4 | 28 | |
7 | 八甲镇中田村师马 Shima of Zhongtian Village in Bajia Town | 村边 Near the village | 65 | 42 | 强 Strong | 栽培 Cultivation | 1 | 3 | 10 |
8 | 八甲镇中田村塘涌 Tangyong of Zhongtian Village in Bajia Town | 村边 Village | 20 | 30 | 强 Strong | 断梢 Branches broken | 0 | 2 | 0 |
9 | 三甲镇湴背村 Banbei Village in Sanjia Town | 村边风水林 Fengshui woods near village | 80 | 44 | 强 Strong | 盗挖 Stolen | 16 | 5 | 40 |
10 | 八甲镇高屋村石角 Shijiao of Gaowu Village in Bajia Town | 村边林 Village forest | 60 | 42 | 强 Strong | 1 | 0 | 2 | |
11 | 八甲镇联合村茶嘹 Chaliao of Lianhe Village in Bajia Town | 村边林 Village forest | 70 | 33 | 中 Middle | 断梢 Branches broken | 2 | 3 | 7 |
12 | 八甲镇高屋村三叶 Sanye of Gaowu Village in Bajia Town | 村边林 Village forest | 75 | 65 | 中 Middle | 阴蔽 Shading | 1 | 0 | 8 |
13 | 八甲镇澄垌村竹根 Zhugen of Chengdong Village in Bajia Town | 屋后风水林 Fengshui woods behind house | 80 | 32 | 中 Middle | 2 | 0 | 10 | |
14 | 八甲镇澄垌村中田 Zhongtian of Chengdong Village in Bajia Town | 村边林 Village forest | 65 | 46 | 中 Middle | 3 | 0 | 8 |
Table 2 General situation of habitat and quantity of each locality of Euryodendron excelsum
编号 Number | 地点 Place | 生境 Habitat | 乔木层盖度 Coverage of arbor layer | 海拔 Altitude (m) | 人为干扰 Human disturbance | 干扰原因 Cause of interference | 成株 Adult plant | 幼树 Sapling | 幼苗 Seedling |
---|---|---|---|---|---|---|---|---|---|
1 | 八甲镇合路村 Helu Village in Bajia Town | 村边林 Village forest | 50 | 52 | 弱 Weak | 1 | 0 | 10 | |
2 | 八甲镇木力村 Muli Village in Bajia Town | 村边林 Village forest | 65 | 68 | 中 Middle | 2 | 0 | 3 | |
3 | 八甲镇澄垌村 Chengdong Village in Bajia Town | 田野 Field | 45 | 42 | 中 Middle | 阴蔽 Shading | 0 | 0 | 10 |
4 | 八甲镇澄垌村 Chengdong Village in Bajia Town | 村边林 Village forest | 60 | 42 | 中 Middle | 断梢 Branches broken | 2 | 2 | 20 |
5 | 八甲镇澄垌村冲田 Chongtian of Chengdong Village in Bajia Town | 村边林 Village forest | 70 | 30 | 中 Middle | 8 | 0 | 20 | |
6 | 八甲镇中田村山喉 Shanhou of Zhongtian Village in Bajia Town | 村边林 Village forest | 30 | 72 | 弱 Weak | 1 | 4 | 28 | |
7 | 八甲镇中田村师马 Shima of Zhongtian Village in Bajia Town | 村边 Near the village | 65 | 42 | 强 Strong | 栽培 Cultivation | 1 | 3 | 10 |
8 | 八甲镇中田村塘涌 Tangyong of Zhongtian Village in Bajia Town | 村边 Village | 20 | 30 | 强 Strong | 断梢 Branches broken | 0 | 2 | 0 |
9 | 三甲镇湴背村 Banbei Village in Sanjia Town | 村边风水林 Fengshui woods near village | 80 | 44 | 强 Strong | 盗挖 Stolen | 16 | 5 | 40 |
10 | 八甲镇高屋村石角 Shijiao of Gaowu Village in Bajia Town | 村边林 Village forest | 60 | 42 | 强 Strong | 1 | 0 | 2 | |
11 | 八甲镇联合村茶嘹 Chaliao of Lianhe Village in Bajia Town | 村边林 Village forest | 70 | 33 | 中 Middle | 断梢 Branches broken | 2 | 3 | 7 |
12 | 八甲镇高屋村三叶 Sanye of Gaowu Village in Bajia Town | 村边林 Village forest | 75 | 65 | 中 Middle | 阴蔽 Shading | 1 | 0 | 8 |
13 | 八甲镇澄垌村竹根 Zhugen of Chengdong Village in Bajia Town | 屋后风水林 Fengshui woods behind house | 80 | 32 | 中 Middle | 2 | 0 | 10 | |
14 | 八甲镇澄垌村中田 Zhongtian of Chengdong Village in Bajia Town | 村边林 Village forest | 65 | 46 | 中 Middle | 3 | 0 | 8 |
Fig. 3 Height (H) and diameter at breast height (DBH) class of Euryodendron excelsum population. St, wild E. excelsum population (including Sanjia Town and Bajia Town); Sa, wild E. excelsum population of Bajia Town; Ss, wild E. excelsum population of Sanjia Town. I, the seedling I stage, 0 < H ≤ 100.0 cm; II, the seedling II stage, H > 100.0 cm, DBH < 3.0 cm; III, the sapling stage, 3.0 cm ≤ DBH < 9.0 cm; IV, the small tree I stage, 9.0 cm ≤ DBH < 15.0 cm; V, the small tree II stage, 15.0 cm ≤ DBH < 21.0 cm; VI, the middle tree I stage, 21.0 cm ≤ DBH < 27.0 cm; VII, the middle tree II stage, 27.0 cm ≤ DBH < 33.0 cm; VIII, the adult tree I stage, 33.0 cm ≤ DBH < 39.0 cm; IX, the adult tree II stage, 39.0 cm ≤ DBH < 45.0 cm; X, the big tree stage, DBH ≥ 45.0 cm.
大小级 Size stage | 划分标准 Division standard | ax | lx | dx | qx | Lx | Tx | kx | ex | lnlx |
---|---|---|---|---|---|---|---|---|---|---|
I (St) | 0 ≤ H ≤ 100 | 97 | 1 000 | 185. | 0.19 | 1 814 | 1 855 | 0.21 | 1.86 | 6.91 |
II (St) | H > 100, DBH < 3.0 | 79 | 814 | 618 | 0.76 | 1 010 | 1 051 | 1.43 | 1.29 | 6.70 |
III (St) | DBH [3.0, 9.0) | 19 | 196 | 123 | 0.63 | 268 | 309 | 1.00 | 1.58 | 5.28 |
IV (St) | DBH [9.0, 15.0) | 7 | 72 | -20 | -0.29 | 164 | 206 | -0.25 | 2.86 | 4.28 |
V (St) | DBH [15.0, 21.0) | 9 | 93 | 30 | 0.33 | 154 | 195 | 0.41 | 2.11 | 4.53 |
VI (St) | DBH [21.0, 27.0) | 6 | 62 | -41 | -0.67 | 164 | 206 | -0.51 | 3.33 | 4.12 |
VII (St) | DBH [27.0, 33.0) | 10 | 103 | 92 | 0.90 | 113 | 154 | 2.30 | 1.50 | 4.64 |
VIII (St) | DBH [33.0, 39.0) | 1 | 10 | -20 | -2.00 | 41 | 82 | -1.10 | 8.00 | 2.33 |
IX (St) | DBH [39.0, 45.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
X (St) | ≥ 45.0 | 4 | 41 | NA | NA | 41 | 364 | 3.72 | 8.83 | 3.72 |
I (Sa) | 0 ≤ H ≤ 100 | 80 | 1 000 | 453 | 0.45 | 1 546 | 1 587 | 0.60 | 1.59 | 6.91 |
II (Sa) | H > 100, DBH < 3.0 | 53 | 546 | 402 | 0.74 | 690 | 731 | 1.33 | 1.34 | 6.30 |
III (Sa) | DBH [3.0, 9.0) | 14 | 144 | 123 | 0.86 | 164 | 206 | 1.95 | 1.43 | 4.97 |
IV (Sa) | DBH [9.0, 15.0) | 2 | 21 | -10 | -0.50 | 51 | 92 | -0.41 | 4.50 | 3.03 |
V (Sa) | DBH [15.0, 21.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
VI (Sa) | DBH [21.0, 27.0) | 4 | 41 | -30 | -0.75 | 113 | 154 | -0.56 | 3.75 | 3.72 |
VII (Sa) | DBH [27.0, 33.0) | 7 | 72 | 61 | 0.86 | 82 | 123 | 1.95 | 1.71 | 4.28 |
VIII (Sa) | DBH [33.0, 39.0) | 1 | 10 | -20 | -2.00 | 41 | 82 | -1.10 | 8.00 | 2.33 |
IX (Sa) | DBH [39.0, 45.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
X (Sa) | ≥ 45.0 | 4 | 41 | NA | NA | 41 | 364 | 3.72 | 8.83 | 3.72 |
I (Ss) | 0 ≤ H ≤ 100 | 24 | 1 000 | 835 | 0.31 | 1 164 | 1 206 | 1.80 | 1.21 | 6.91 |
II (Ss) | H > 100, DBH < 3.0 | 16 | 165 | 113 | 0.84 | 216 | 257 | 1.16 | 1.56 | 6.91 |
III (Ss) | DBH [3.0, 9.0) | 5 | 52 | 0 | 0.69 | 103 | 144 | 0.00 | 2.80 | 5.11 |
IV (Ss) | DBH [9.0, 15.0) | 5 | 52 | -10 | 0.00 | 113 | 154 | -0.18 | 3.00 | 3.94 |
V (Ss) | DBH [15.0, 21.0) | 6 | 62 | 41 | -0.20 | 82 | 123 | 1.10 | 2.00 | 3.94 |
VI (Ss) | DBH [21.0, 27.0) | 2 | 21 | -10 | 0.67 | 51 | 92 | -0.41 | 4.50 | 4.12 |
VII (Ss) | DBH [27.0, 33.0) | 3 | 31 | 3.03 |
Table 3 Standard life table of Euryodendron excelsum population in Yangchun City
大小级 Size stage | 划分标准 Division standard | ax | lx | dx | qx | Lx | Tx | kx | ex | lnlx |
---|---|---|---|---|---|---|---|---|---|---|
I (St) | 0 ≤ H ≤ 100 | 97 | 1 000 | 185. | 0.19 | 1 814 | 1 855 | 0.21 | 1.86 | 6.91 |
II (St) | H > 100, DBH < 3.0 | 79 | 814 | 618 | 0.76 | 1 010 | 1 051 | 1.43 | 1.29 | 6.70 |
III (St) | DBH [3.0, 9.0) | 19 | 196 | 123 | 0.63 | 268 | 309 | 1.00 | 1.58 | 5.28 |
IV (St) | DBH [9.0, 15.0) | 7 | 72 | -20 | -0.29 | 164 | 206 | -0.25 | 2.86 | 4.28 |
V (St) | DBH [15.0, 21.0) | 9 | 93 | 30 | 0.33 | 154 | 195 | 0.41 | 2.11 | 4.53 |
VI (St) | DBH [21.0, 27.0) | 6 | 62 | -41 | -0.67 | 164 | 206 | -0.51 | 3.33 | 4.12 |
VII (St) | DBH [27.0, 33.0) | 10 | 103 | 92 | 0.90 | 113 | 154 | 2.30 | 1.50 | 4.64 |
VIII (St) | DBH [33.0, 39.0) | 1 | 10 | -20 | -2.00 | 41 | 82 | -1.10 | 8.00 | 2.33 |
IX (St) | DBH [39.0, 45.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
X (St) | ≥ 45.0 | 4 | 41 | NA | NA | 41 | 364 | 3.72 | 8.83 | 3.72 |
I (Sa) | 0 ≤ H ≤ 100 | 80 | 1 000 | 453 | 0.45 | 1 546 | 1 587 | 0.60 | 1.59 | 6.91 |
II (Sa) | H > 100, DBH < 3.0 | 53 | 546 | 402 | 0.74 | 690 | 731 | 1.33 | 1.34 | 6.30 |
III (Sa) | DBH [3.0, 9.0) | 14 | 144 | 123 | 0.86 | 164 | 206 | 1.95 | 1.43 | 4.97 |
IV (Sa) | DBH [9.0, 15.0) | 2 | 21 | -10 | -0.50 | 51 | 92 | -0.41 | 4.50 | 3.03 |
V (Sa) | DBH [15.0, 21.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
VI (Sa) | DBH [21.0, 27.0) | 4 | 41 | -30 | -0.75 | 113 | 154 | -0.56 | 3.75 | 3.72 |
VII (Sa) | DBH [27.0, 33.0) | 7 | 72 | 61 | 0.86 | 82 | 123 | 1.95 | 1.71 | 4.28 |
VIII (Sa) | DBH [33.0, 39.0) | 1 | 10 | -20 | -2.00 | 41 | 82 | -1.10 | 8.00 | 2.33 |
IX (Sa) | DBH [39.0, 45.0) | 3 | 31 | -10 | -0.33 | 72 | 113 | -0.29 | 3.67 | 3.43 |
X (Sa) | ≥ 45.0 | 4 | 41 | NA | NA | 41 | 364 | 3.72 | 8.83 | 3.72 |
I (Ss) | 0 ≤ H ≤ 100 | 24 | 1 000 | 835 | 0.31 | 1 164 | 1 206 | 1.80 | 1.21 | 6.91 |
II (Ss) | H > 100, DBH < 3.0 | 16 | 165 | 113 | 0.84 | 216 | 257 | 1.16 | 1.56 | 6.91 |
III (Ss) | DBH [3.0, 9.0) | 5 | 52 | 0 | 0.69 | 103 | 144 | 0.00 | 2.80 | 5.11 |
IV (Ss) | DBH [9.0, 15.0) | 5 | 52 | -10 | 0.00 | 113 | 154 | -0.18 | 3.00 | 3.94 |
V (Ss) | DBH [15.0, 21.0) | 6 | 62 | 41 | -0.20 | 82 | 123 | 1.10 | 2.00 | 3.94 |
VI (Ss) | DBH [21.0, 27.0) | 2 | 21 | -10 | 0.67 | 51 | 92 | -0.41 | 4.50 | 4.12 |
VII (Ss) | DBH [27.0, 33.0) | 3 | 31 | 3.03 |
Fig. 4 Standard survival curve of Euryodendron excelsum population. lx, proportion organisms surviving from the beginning of the life table to age x. Sa, wild E. excelsum population of Bajia Town; Ss, wild E. excelsum population of Sanjia Town; St, wild E. excelsum population (including Sanjia Town and Bajia Town). I-X see Fig. 3.
Fig. 5 Killing power and life expectancy curve of Euryodendron excelsum population. Sa-ex, life expectancy at age x of wild E. excelsum (only including Bajia Town); Sa-kx, specific mortality of wild E. excelsum (only including Bajia Town); Sa-qx, mortality rate of wild E. excelsum (only including Bajia Town); St-ex, life expectancy at age x of wild E. excelsum (including Sanjia Town and Bajia Town); St-kx, specific mortality of wild E. excelsum (including Sanjia Town and Bajia Town); St-qx, mortality rate of wild E. excelsum (including Sanjia Town and Bajia Town). I-X see Fig. 3.
Fig. 6 Killing power and life expectancy curve of Euryodendron excelsum population of Sanjia town. ex, life expectancy at age x; kx, specific mortality; qx, mortality rate. I-VI see Fig. 3.
[1] | Cai F, Song YC (1997). A study on the structure and dynamics of Schima superba population on Wuyi Mountain. Acta Phytoecologica Sinica, 21, 138-149. |
[ 蔡飞, 宋永昌 (1997). 武夷山木荷种群结构和动态的研究. 植物生态学报, 21, 138-149.] | |
[2] | Chen XD (1998). A study on the method of quantitative analysis for plant population and community structural dynamics. Acta Ecologica Sinica, 18, 214-217. |
[ 陈晓德 (1988). 植物种群与群落结构动态量化分析方法研究. 生态学报, 18, 214-217.] | |
[3] | Chen YZ, Ma XQ, Feng LZ, Zheng QR (2006). The population life table and periodic fluctuation of Cinnamomun micranthum, an endangered plant. Acta Ecologica Sinica, 26, 4267-4272. |
[ 陈远征, 马祥庆, 冯丽贞, 郑群瑞 (2006). 濒危植物沉水樟的种群生命表和谱分析. 生态学报, 26, 4267-4272.] | |
[4] | Cui L, Su Y (2015). SSR markers for a critically endangered species Euryodendron excelsum and a distantly related species Ternstroemia gymnanthera(Ternstroemiaceae). Biochemical Systematics and Ecology, 58, 288-292. |
[5] | He H, Wang YH (2001). The existing circumstance and the biological characteristic research of Euryodendron excelsum H. T. Chang, the paticular genera in China. Journal of Yunnan University (Natural Sciences Edition), 23(S1), 52-55. |
[ 何瀚, 王跃华 (2001). 中国特有属猪血木的生存现状及生物学特性研究. 云南大学学报(自然科学版), 23(S1), 52-55.] | |
[6] | Hilton TC (2000). IUCN Red List of Threatened Species. IUCN Publication Service Unit, Cambridge. 21. |
[7] | Kang HJ, Chen ZL, Liu P, Hao CY, Wei FM (2007). The population structure and distribution pattern of Emmenopterys henryi in Dapanshan natural reserve of Zhejiang Province. Acta Ecologica Sinica, 27, 389-396. |
[ 康华靖, 陈子林, 刘鹏, 郝朝运, 韦福民 (2007). 大盘山自然保护区香果树种群结构与分布格局. 生态学报, 27, 389-396.] | |
[8] | Li XK, Su ZM, Xiang WS, Ning SJ, Tang RQ, Ou ZL, Li RT (2002). Study on the structure and spatial pattern of the endangered plant population of Abies yuanbaoshanensis. Acta Ecologica Sinica, 22, 2246-2253. |
[ 李先琨, 苏宗明, 向悟生, 宁世江, 唐润琴, 欧祖兰, 李瑞棠 (2002). 濒危植物元宝山冷杉种群结构与分布格局. 生态学报, 2246-2253.] | |
[9] | Leak WB (1975). Age distribution in virgin red spruce and northern hardwoods. Ecology, 56, 1451-1454. |
[10] | Li B (2000). General Ecology . Higher Education Press, Beijing. 43-49. |
[ 李博 (2000). 普通生态学. 高等教育出版社, 北京. 43-49.] | |
[11] | Li XBY, Fu L, Wang FG, Xing FW (2017). Michelia guangdongensis (Magnoliaceae), an endangered plant species with extremely small population, should be evaluated as CR C2a (i); D. Biodiversity Science, 25, 91-93. |
[ 李西贝阳, 付琳, 王发国, 邢福武 (2017). 极小种群植物广东含笑应当被评估为极危等级. 生物多样性, 25, 91-93.] | |
[12] | Luo XY, Tang GD, Xu H, Zhuang XY, Zheng WJ, Zeng M (2005). Genetic diversity of three endemic and endangered species of the family Theaceae in Guangdong, China. Biodiversity Science, 13, 112-121. |
[ 罗晓莹, 唐光大, 许涵, 庄雪影, 郑文经, 曾明 (2005). 山茶科3种中国特有濒危植物的遗传多样性研究. 生物多样性, 13, 112-121.] | |
[13] | Ran Q, Wei HY, Zhao ZF, Zhang QZ, Liu J, Gu W (2019). Impact of climate change on the potential distribution and habitat fragmentation of the relict plant Cathaya argyrophylla Chun et Kuang. Acta Ecologica Sinica, 39, 2481-2493. |
[ 冉巧, 卫海燕, 赵泽芳, 张权中, 刘静, 顾蔚 (2019). 气候变化对孑遗植物银杉的潜在分布及生境破碎度的影响. 生态学报, 39, 2481-2493.] | |
[14] | Shen SK, Hu XL, Wang YH (2008a). Ornithochory of Euryodendron excelsum and its significance in conservation biology. Guihaia, 28, 650-654. |
[ 申仕康, 胡晓立, 王跃华 (2008a). 鸟类对猪血木种子的散布及在其保护中的意义. 广西植物, 28, 650-654.] | |
[15] | Shen SK, Ma HY, Liu XY, Wang YH (2007). The endangered causes and preserving strategies for Euryodendron excelsum, a plant endemic to China. Ecology and Environment, 16, 1819-1823. |
[ 申仕康, 马海英, 刘湘永, 王跃华 (2007). 中国特有植物猪血木的濒危原因及保护对策. 生态环境, 16, 1819-1823.] | |
[16] | Shen SK, Ma HY, Wang YH, Wang BY, Shen GZ (2008b). The structure and dynamics of natural population of the endangered plant Euryodendron excelsum H. T. Chang. Acta Ecologica Sinica, 28, 2404-2412. |
[ 申仕康, 马海英, 王跃华, 王博轶, 申国柱 (2008b). 濒危植物猪血木(Euryodendron excelsum H. T. Chang)自然种群结构及动态. 生态学报, 28, 2404-2412.] | |
[17] |
Su YJ, Wang T, Sun YF, Ye HG (2009). High ISSR variation in 14 surviving individuals of Euryodendron excelsum(Ternstroemiaceae) endemic to China. Biochemical Genetics, 47, 56-65.
DOI URL PMID |
[18] | Tao DL, Xu ZB, Li X (1985). Experimental study on the effect of dead and living ground covers on the natural regeneration of Pinus koraiensis Sieb. et Zucc. associated tree species. Acta Phytoecologica et Geobotanica Sinica, 9, 47-58. |
[ 陶大立, 徐振邦, 李昕 (1985). 死、活地被物对红松伴生树种天然更新影响的实验研究. 植物生态学报, 9, 47-58.] | |
[19] | Wang T, Su YJ, Ye HG, Ouyang PY, Jiang Y, Sun YF, Chen GP, Deng F, Zhang HD (2005). Genetic differentiation and conservation of 14 surviving individuals of Euryodendron excelsum endemic to China. Acta Scientiarum Naturalium Universitatis Sunyatseni, 44, 68-72. |
[ 王艇, 苏应娟, 叶华谷, 欧阳蒲月, 江宇, 孙宇飞, 陈国培, 邓锋, 张宏达 (2005). 中国特有极度濒危植物猪血木的保护遗传学研究. 中山大学学报(自然科学版), 44, 68-72.] | |
[20] |
Wang XG, Wu CZ, He DJ, Liao CZ, Cheng Y, Feng L (2004). Life table and spectral analysis of endangered plant Taxus chinensis var. mairei population. Journal of Applied Ecology, 15, 201-204.
URL PMID |
[ 王新功, 吴承祯, 何东进, 廖成章, 程煜, 封磊 (2004). 濒危植物南方红豆杉种群生命表及谱分析. 应用生态学报, 15, 201-204.]
PMID |
|
[21] | Wang YH, Cao LM, He H, Hu XL (2002). Cutting propagation of the endangered species Euryodendron excelsum H. T. Chang from Theaceae. Journal of Yunnan University (Natural Science Edition), 24, 227-228. |
[ 王跃华, 曹丽敏, 何瀚, 胡晓立 (2002). 山茶科濒危植物猪血木(Euryodendron excelsum H. T. Chang)的扦插繁殖. 云南大学学报(自然科学版), 24, 227-228.] | |
[22] | Wang YH, Shen SK, Shen GZ, Wang BY, Hu XL, Wang M, Liu XY (2016). Pollination biology of endangered Euryodendron excelsum. Journal of West China Forestry Science, 36(4), 11-15. |
[ 王跃华, 申仕康, 申国柱, 王博轶, 胡晓立, 王敏, 刘湘永 (2007). 濒危植物猪血木的传粉生物学特性研究. 西部林业科学, 36(4), 11-15.] | |
[23] | Wang Z, Hu ZY, Huang L (2015). Development and characterization of genomic microsatellite markers inApterosperma oblata (Theaceae) and cross-amplification in Euryodendron excelsum (Ternstroemiaceae). Conservation Genetics Resources, 7, 119-120. |
[24] | Wei KH, Liang Lin Y, Li LX, Hu Y, Liao JH, Gao WY (2019). Conservation research of Bletilla striata. Modern Chinese Medicine, 21, 689-693. |
[ 韦坤华, 梁莹, 林杨, 李林轩, 胡营, 缪剑华, 高文远 (2019). 白及的保育研究. 中国现代中药, 21, 689-693.] | |
[25] | Xiao SL, Fu MY, Yang K, Chen XH (2019). Population structure and quantitative dynamics of an extremely small population, Michelia wilsonii. Acta Botanica Boreali- Occidentalia Sinica, 39, 1279-1288. |
[ 肖书礼, 付梦媛, 杨科, 陈小红 (2019). 极小种群野生植物峨眉含笑的种群结构与数量动态. 西北植物学报, 39, 1279-1288.] | |
[26] | Ye HG, Wang FG, Zhou LX, Ye YS, Huang S (2002). Euryodendron excelsum, a endangered tree of Theaceae. Plant Journal, (4), 3. |
[ 叶华谷, 王发国, 周联选, 叶育石, 黄仕 (2002). 山茶科濒危树种猪血木. 植物杂志, (4), 3.] | |
[27] | Ren Z, Chen L, Peng H (2016). Orophea yunnanensis should be listed as a plant species with extremely small population. Biodiversity Science, 24, 358-359. |
[ 任喆, 陈丽, 彭华 (2016). 云南澄广花应该作为极小种群植物加强保护. 生物多样性, 24, 358-359.] |
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