植物生态学报 ›› 2012, Vol. 36 ›› Issue (6): 491-503.DOI: 10.3724/SP.J.1258.2012.00491
收稿日期:
2012-01-04
接受日期:
2012-03-09
出版日期:
2012-01-04
发布日期:
2012-06-04
通讯作者:
高润梅
作者简介:
*(E-mail:sxndgrm@163.com)
GAO Run-Mei*(), SHI Xiao-Dong, GUO Yue-Dong
Received:
2012-01-04
Accepted:
2012-03-09
Online:
2012-01-04
Published:
2012-06-04
Contact:
GAO Run-Mei
摘要:
稳定性是植物群落结构与功能的综合特征。该文运用模糊综合评判理论评价了山西文峪河上游13种河岸林群落的稳定性。基于群落整体稳定性和结构稳定性的考虑, 选取乔木层优势树种更新潜力、物种多样性、Godron指数、立地质量和保护程度等5项特征指标, 通过计算各群落5项指标隶属度的平均值来评价群落稳定性。研究结果表明, 多数群落的稳定性隶属度介于0.40-0.60, 属于低山森林演替系列的青杨辽东栎(Populus cathayana + Quercus wutaishanica)混交林和油松白桦(Pinus tabulaeformis + Betula platyphylla)混交林的稳定性居中; 中高山森林演替系列中, 群落稳定性随着演替的进展而增加, 青杨(Populus cathayana)林结构简单, 稳定性最低, 青杄(Picea wilsonii)林接近演替顶极, 稳定性最高; 但并非只有近演替顶极的群落是稳定的, 客观存在的各种林冠干扰和河岸生境的高度异质性也使得白杄杨桦(Picea meyeri + Populus cathayana + Betula platyphylla)混交林、落叶松白杄(Larix principis-rupprechtii + Picea meyeri)混交林和落叶松青杄(Larix principis- rupprechtii + Picea wilsonii)混交林有较高的稳定性。
高润梅, 石晓东, 郭跃东. 山西文峪河上游河岸林群落稳定性评价. 植物生态学报, 2012, 36(6): 491-503. DOI: 10.3724/SP.J.1258.2012.00491
GAO Run-Mei, SHI Xiao-Dong, GUO Yue-Dong. Community stability evaluation of riparian forest of the upper reaches of Wenyuhe in Shanxi, China. Chinese Journal of Plant Ecology, 2012, 36(6): 491-503. DOI: 10.3724/SP.J.1258.2012.00491
群落类型 Community type | 海拔 Elevation (m) | 坡度 Slope (°) | 坡向 Slope aspect (°) | 郁闭度 Canopy coverage | 样地数量 Plot number |
---|---|---|---|---|---|
1 青杨林 PCS | 1 680 | 0-2 | 275 | 0.40-0.45 | 3 |
2 青杨辽东栎混交林 PQM | 1 818-1 935 | 0-16 | 110-243 | 0.36-0.40 | 3 |
3 青杨白桦混交林 PBM | 1 830-1 869 | 0-8 | 197-297 | 0.45-0.48 | 6 |
4 杨桦落叶松混交林 PBL | 1 940-2 144 | 22-40 | 180-299 | 0.44-0.50 | 6 |
5 青杨白杄混交林 PPM | 1 818-1 935 | 2-15 | 60-168 | 0.50-0.53 | 3 |
6 杨桦青杄混交林 PBP | 1 935-2 099 | 8-25 | 60-197 | 0.48-0.55 | 6 |
7 油松白桦混交林 TBM | 1 780-1 820 | 17-25 | 290-310 | 0.60-0.70 | 5 |
8 落叶松辽东栎混交林 LQM | 1 820-1 950 | 23-25 | 310-330 | 0.60-0.63 | 5 |
9 落叶松青杨混交林 LPM | 1 980-2 135 | 15-36 | 241-304 | 0.60-0.68 | 4 |
10 白杄杨桦混交林 PPB | 1 895-1 935 | 0-15 | 110-164 | 0.68-0.71 | 3 |
11 落叶松白杄混交林 LMM | 1 785-2 030 | 4-27 | 142-224 | 0.75-0.78 | 3 |
12 落叶松青杄混交林 LWM | 1 950-2 250 | 18-33 | 221-327 | 0.68-0.72 | 6 |
13 青杄林 PWS | 2 020-2 270 | 0-10 | 22-83 | 0.75-0.80 | 3 |
表1 河岸林13个群落的环境概况
Table 1 Environment situations of 13 riparian forest communities
群落类型 Community type | 海拔 Elevation (m) | 坡度 Slope (°) | 坡向 Slope aspect (°) | 郁闭度 Canopy coverage | 样地数量 Plot number |
---|---|---|---|---|---|
1 青杨林 PCS | 1 680 | 0-2 | 275 | 0.40-0.45 | 3 |
2 青杨辽东栎混交林 PQM | 1 818-1 935 | 0-16 | 110-243 | 0.36-0.40 | 3 |
3 青杨白桦混交林 PBM | 1 830-1 869 | 0-8 | 197-297 | 0.45-0.48 | 6 |
4 杨桦落叶松混交林 PBL | 1 940-2 144 | 22-40 | 180-299 | 0.44-0.50 | 6 |
5 青杨白杄混交林 PPM | 1 818-1 935 | 2-15 | 60-168 | 0.50-0.53 | 3 |
6 杨桦青杄混交林 PBP | 1 935-2 099 | 8-25 | 60-197 | 0.48-0.55 | 6 |
7 油松白桦混交林 TBM | 1 780-1 820 | 17-25 | 290-310 | 0.60-0.70 | 5 |
8 落叶松辽东栎混交林 LQM | 1 820-1 950 | 23-25 | 310-330 | 0.60-0.63 | 5 |
9 落叶松青杨混交林 LPM | 1 980-2 135 | 15-36 | 241-304 | 0.60-0.68 | 4 |
10 白杄杨桦混交林 PPB | 1 895-1 935 | 0-15 | 110-164 | 0.68-0.71 | 3 |
11 落叶松白杄混交林 LMM | 1 785-2 030 | 4-27 | 142-224 | 0.75-0.78 | 3 |
12 落叶松青杄混交林 LWM | 1 950-2 250 | 18-33 | 221-327 | 0.68-0.72 | 6 |
13 青杄林 PWS | 2 020-2 270 | 0-10 | 22-83 | 0.75-0.80 | 3 |
群落类型 Community type | 幼苗 Seedling (%) | 标准值 Standard value | 幼树 Sapling (%) | 标准值 Standard value | 平均值 Mean |
---|---|---|---|---|---|
1 青杨林 PCS | 49.22 | 500.46 | 2.03 | 26.43 | 263.44 |
2 青杨辽东栎混交林 PQM | 44.81 | 455.62 | 76.80 | 1 000.00 | 727.81 |
3 青杨白桦混交林 PBM | 21.94 | 223.08 | 48.17 | 627.21 | 425.15 |
4 杨桦落叶松混交林 PBL | 1.33 | 13.52 | 17.53 | 228.26 | 120.89 |
5 青杨白杄混交林 PPM | 2.45 | 24.91 | 39.54 | 514.84 | 269.88 |
6 杨桦青杄混交林 PBP | 41.58 | 422.78 | 10.61 | 138.15 | 280.46 |
7 油松白桦混交林 TBM | 69.47 | 706.35 | 58.20 | 757.81 | 732.08 |
8 落叶松辽东栎混交林 LQM | 10.46 | 106.35 | 15.69 | 204.30 | 155.33 |
9 落叶松青杨混交林 LPM | 2.52 | 25.62 | 17.65 | 229.82 | 127.72 |
10 白杄杨桦混交林 PPB | 69.47 | 706.35 | 15.98 | 208.07 | 457.21 |
11 落叶松白杄混交林 LMM | 98.35 | 1 000.00 | 42.18 | 549.22 | 774.61 |
12 落叶松青杄混交林 LWM | 66.41 | 675.24 | 35.98 | 468.49 | 571.87 |
13 青杄林 PWS | 52.23 | 531.06 | 19.03 | 247.79 | 389.42 |
表2 乔木层优势树种更新潜力特征
Table 2 Regeneration potential characteristics of dominant tree species of tree layer
群落类型 Community type | 幼苗 Seedling (%) | 标准值 Standard value | 幼树 Sapling (%) | 标准值 Standard value | 平均值 Mean |
---|---|---|---|---|---|
1 青杨林 PCS | 49.22 | 500.46 | 2.03 | 26.43 | 263.44 |
2 青杨辽东栎混交林 PQM | 44.81 | 455.62 | 76.80 | 1 000.00 | 727.81 |
3 青杨白桦混交林 PBM | 21.94 | 223.08 | 48.17 | 627.21 | 425.15 |
4 杨桦落叶松混交林 PBL | 1.33 | 13.52 | 17.53 | 228.26 | 120.89 |
5 青杨白杄混交林 PPM | 2.45 | 24.91 | 39.54 | 514.84 | 269.88 |
6 杨桦青杄混交林 PBP | 41.58 | 422.78 | 10.61 | 138.15 | 280.46 |
7 油松白桦混交林 TBM | 69.47 | 706.35 | 58.20 | 757.81 | 732.08 |
8 落叶松辽东栎混交林 LQM | 10.46 | 106.35 | 15.69 | 204.30 | 155.33 |
9 落叶松青杨混交林 LPM | 2.52 | 25.62 | 17.65 | 229.82 | 127.72 |
10 白杄杨桦混交林 PPB | 69.47 | 706.35 | 15.98 | 208.07 | 457.21 |
11 落叶松白杄混交林 LMM | 98.35 | 1 000.00 | 42.18 | 549.22 | 774.61 |
12 落叶松青杄混交林 LWM | 66.41 | 675.24 | 35.98 | 468.49 | 571.87 |
13 青杄林 PWS | 52.23 | 531.06 | 19.03 | 247.79 | 389.42 |
群落类型 Community type | 层次 Layer | S | D | H | JD | JH | 平均值 Mean |
---|---|---|---|---|---|---|---|
1 青杨林 PCS | 乔木 Tree | 347.83 | 56.34 | 72.85 | 98.90 | 177.78 | 613.78 |
灌木 Shrub | 301.89 | 780.22 | 520.16 | 969.39 | 968.75 | ||
草本 Herb | 966.67 | 1 000.00 | 996.89 | 948.98 | 1 000.00 | ||
2 青杨辽东栎混交林 PQM | 乔木 Tree | 638.26 | 802.82 | 682.12 | 934.07 | 955.56 | 849.27 |
灌木 Shrub | 805.28 | 923.08 | 846.77 | 948.98 | 927.08 | ||
草本 Herb | 589.00 | 947.37 | 801.24 | 979.59 | 957.89 | ||
3 青杨白桦混交林 PBM | 乔木 Tree | 565.22 | 816.90 | 655.63 | 923.08 | 944.44 | 827.33 |
灌木 Shrub | 498.11 | 890.11 | 709.68 | 979.59 | 979.17 | ||
草本 Herb | 746.67 | 957.89 | 847.83 | 969.39 | 926.32 | ||
4 杨桦落叶松混交林 PBL | 乔木 Tree | 521.74 | 732.39 | 576.16 | 857.14 | 877.78 | 781.25 |
灌木 Shrub | 498.11 | 824.18 | 629.03 | 918.37 | 906.25 | ||
草本 Herb | 753.33 | 936.84 | 822.98 | 959.18 | 905.26 | ||
5 青杨白杄混交林 PPM | 乔木 Tree | 986.09 | 1 000.00 | 966.89 | 945.05 | 933.33 | 920.69 |
灌木 Shrub | 679.25 | 934.07 | 810.48 | 979.59 | 958.33 | ||
草本 Herb | 766.67 | 968.42 | 913.04 | 979.59 | 989.47 | ||
6 杨桦青杄混交林 PBP | 乔木 Tree | 579.13 | 845.07 | 695.36 | 956.04 | 966.67 | 822.54 |
灌木 Shrub | 452.83 | 780.22 | 592.74 | 908.16 | 906.25 | ||
草本 Herb | 855.67 | 978.95 | 894.41 | 989.80 | 936.84 | ||
7 油松白桦混交林 TBM | 乔木 Tree | 913.04 | 873.24 | 768.21 | 857.14 | 800.00 | 947.44 |
灌木 Shrub | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | ||
草本 Herb | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | ||
8 落叶松辽东栎混交林 LQM | 乔木 Tree | 1 000.00 | 901.41 | 847.68 | 857.14 | 811.11 | 915.02 |
灌木 Shrub | 867.92 | 978.02 | 927.42 | 989.80 | 979.17 | ||
草本 Herb | 866.67 | 957.89 | 866.46 | 969.39 | 905.26 | ||
9 落叶松青杨混交林 LPM | 乔木 Tree | 638.26 | 901.41 | 754.97 | 978.02 | 1 000.00 | 839.93 |
灌木 Shrub | 471.70 | 868.13 | 677.42 | 979.59 | 979.17 | ||
草本 Herb | 791.67 | 926.32 | 819.88 | 938.78 | 873.68 | ||
10 白杄杨桦混交林 PPB | 乔木 Tree | 986.09 | 1056.34 | 1 000.00 | 1 000.00 | 966.67 | 900.90 |
灌木 Shrub | 603.77 | 912.09 | 758.06 | 969.39 | 947.92 | ||
草本 Herb | 666.67 | 947.37 | 813.66 | 959.18 | 926.32 | ||
11 落叶松白杄混交林 LMM | 乔木 Tree | 579.13 | 774.65 | 642.38 | 912.09 | 933.33 | 824.49 |
灌木 Shrub | 503.40 | 901.10 | 721.77 | 989.80 | 989.58 | ||
草本 Herb | 766.67 | 947.37 | 841.61 | 959.18 | 905.26 | ||
12 落叶松青杄混交林 LWM | 乔木 Tree | 869.57 | 929.58 | 847.68 | 923.08 | 900.00 | 868.54 |
灌木 Shrub | 503.40 | 868.13 | 693.55 | 959.18 | 958.33 | ||
草本 Herb | 911.00 | 947.37 | 863.35 | 959.18 | 894.74 | ||
13 青杄林 PWS | 乔木 Tree | 695.65 | 830.99 | 728.48 | 857.14 | 888.89 | 812.23 |
灌木 Shrub | 704.15 | 912.09 | 798.39 | 948.98 | 927.08 | ||
草本 Herb | 866.67 | 789.47 | 692.55 | 806.12 | 736.84 |
表4 群落物种多样性指数的标准值
Table 4 Standard value of species diversity index of community
群落类型 Community type | 层次 Layer | S | D | H | JD | JH | 平均值 Mean |
---|---|---|---|---|---|---|---|
1 青杨林 PCS | 乔木 Tree | 347.83 | 56.34 | 72.85 | 98.90 | 177.78 | 613.78 |
灌木 Shrub | 301.89 | 780.22 | 520.16 | 969.39 | 968.75 | ||
草本 Herb | 966.67 | 1 000.00 | 996.89 | 948.98 | 1 000.00 | ||
2 青杨辽东栎混交林 PQM | 乔木 Tree | 638.26 | 802.82 | 682.12 | 934.07 | 955.56 | 849.27 |
灌木 Shrub | 805.28 | 923.08 | 846.77 | 948.98 | 927.08 | ||
草本 Herb | 589.00 | 947.37 | 801.24 | 979.59 | 957.89 | ||
3 青杨白桦混交林 PBM | 乔木 Tree | 565.22 | 816.90 | 655.63 | 923.08 | 944.44 | 827.33 |
灌木 Shrub | 498.11 | 890.11 | 709.68 | 979.59 | 979.17 | ||
草本 Herb | 746.67 | 957.89 | 847.83 | 969.39 | 926.32 | ||
4 杨桦落叶松混交林 PBL | 乔木 Tree | 521.74 | 732.39 | 576.16 | 857.14 | 877.78 | 781.25 |
灌木 Shrub | 498.11 | 824.18 | 629.03 | 918.37 | 906.25 | ||
草本 Herb | 753.33 | 936.84 | 822.98 | 959.18 | 905.26 | ||
5 青杨白杄混交林 PPM | 乔木 Tree | 986.09 | 1 000.00 | 966.89 | 945.05 | 933.33 | 920.69 |
灌木 Shrub | 679.25 | 934.07 | 810.48 | 979.59 | 958.33 | ||
草本 Herb | 766.67 | 968.42 | 913.04 | 979.59 | 989.47 | ||
6 杨桦青杄混交林 PBP | 乔木 Tree | 579.13 | 845.07 | 695.36 | 956.04 | 966.67 | 822.54 |
灌木 Shrub | 452.83 | 780.22 | 592.74 | 908.16 | 906.25 | ||
草本 Herb | 855.67 | 978.95 | 894.41 | 989.80 | 936.84 | ||
7 油松白桦混交林 TBM | 乔木 Tree | 913.04 | 873.24 | 768.21 | 857.14 | 800.00 | 947.44 |
灌木 Shrub | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | ||
草本 Herb | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | 1 000.00 | ||
8 落叶松辽东栎混交林 LQM | 乔木 Tree | 1 000.00 | 901.41 | 847.68 | 857.14 | 811.11 | 915.02 |
灌木 Shrub | 867.92 | 978.02 | 927.42 | 989.80 | 979.17 | ||
草本 Herb | 866.67 | 957.89 | 866.46 | 969.39 | 905.26 | ||
9 落叶松青杨混交林 LPM | 乔木 Tree | 638.26 | 901.41 | 754.97 | 978.02 | 1 000.00 | 839.93 |
灌木 Shrub | 471.70 | 868.13 | 677.42 | 979.59 | 979.17 | ||
草本 Herb | 791.67 | 926.32 | 819.88 | 938.78 | 873.68 | ||
10 白杄杨桦混交林 PPB | 乔木 Tree | 986.09 | 1056.34 | 1 000.00 | 1 000.00 | 966.67 | 900.90 |
灌木 Shrub | 603.77 | 912.09 | 758.06 | 969.39 | 947.92 | ||
草本 Herb | 666.67 | 947.37 | 813.66 | 959.18 | 926.32 | ||
11 落叶松白杄混交林 LMM | 乔木 Tree | 579.13 | 774.65 | 642.38 | 912.09 | 933.33 | 824.49 |
灌木 Shrub | 503.40 | 901.10 | 721.77 | 989.80 | 989.58 | ||
草本 Herb | 766.67 | 947.37 | 841.61 | 959.18 | 905.26 | ||
12 落叶松青杄混交林 LWM | 乔木 Tree | 869.57 | 929.58 | 847.68 | 923.08 | 900.00 | 868.54 |
灌木 Shrub | 503.40 | 868.13 | 693.55 | 959.18 | 958.33 | ||
草本 Herb | 911.00 | 947.37 | 863.35 | 959.18 | 894.74 | ||
13 青杄林 PWS | 乔木 Tree | 695.65 | 830.99 | 728.48 | 857.14 | 888.89 | 812.23 |
灌木 Shrub | 704.15 | 912.09 | 798.39 | 948.98 | 927.08 | ||
草本 Herb | 866.67 | 789.47 | 692.55 | 806.12 | 736.84 |
群落类型 Community type | 更新潜力 Regeneration potential | 物种多样性 Species diversity | Godron指数 Godron index | 立地质量 Site quality | 保护强度 Protection intensity | 平均值 Mean |
---|---|---|---|---|---|---|
1 青杨林 PCS | 0.22 | 0.00 | 0.00 | 0.54 | 0.00 | 0.15 |
2 青杨辽东栎混交林 PQM | 0.93 | 0.71 | 0.78 | 0.00 | 0.13 | 0.51 |
3 青杨白桦混交林 PBM | 0.47 | 0.64 | 0.70 | 0.24 | 0.00 | 0.41 |
4 杨桦落叶松混交林 PBL | 0.00 | 0.50 | 0.78 | 0.50 | 0.20 | 0.40 |
5 青杨白杄混交林 PPM | 0.23 | 0.92 | 0.52 | 0.46 | 0.13 | 0.45 |
6 杨桦青杄混交林 PBP | 0.24 | 0.63 | 0.68 | 0.44 | 0.53 | 0.50 |
7 油松白桦混交林 TBM | 0.93 | 1.00 | 0.72 | 0.40 | 0.00 | 0.61 |
8 落叶松辽东栎混交林 LQM | 0.05 | 0.90 | 0.41 | 0.88 | 0.28 | 0.50 |
9 落叶松青杨混交林 LPM | 0.01 | 0.68 | 0.79 | 0.93 | 0.10 | 0.50 |
10 白杄杨桦混交林 PPB | 0.51 | 0.86 | 0.98 | 0.89 | 0.39 | 0.73 |
11 落叶松白杄混交林 LMM | 1.00 | 0.63 | 0.88 | 0.61 | 0.39 | 0.70 |
12 落叶松青杄混交林 LWM | 0.69 | 0.76 | 0.65 | 0.86 | 0.70 | 0.73 |
13 青杄林 PWS | 0.41 | 0.59 | 1.00 | 1.00 | 1.00 | 0.80 |
表8 群落5项稳定性指标的隶属度及其平均值
Table 8 Subordinate function values of five stability indexes and their means of community
群落类型 Community type | 更新潜力 Regeneration potential | 物种多样性 Species diversity | Godron指数 Godron index | 立地质量 Site quality | 保护强度 Protection intensity | 平均值 Mean |
---|---|---|---|---|---|---|
1 青杨林 PCS | 0.22 | 0.00 | 0.00 | 0.54 | 0.00 | 0.15 |
2 青杨辽东栎混交林 PQM | 0.93 | 0.71 | 0.78 | 0.00 | 0.13 | 0.51 |
3 青杨白桦混交林 PBM | 0.47 | 0.64 | 0.70 | 0.24 | 0.00 | 0.41 |
4 杨桦落叶松混交林 PBL | 0.00 | 0.50 | 0.78 | 0.50 | 0.20 | 0.40 |
5 青杨白杄混交林 PPM | 0.23 | 0.92 | 0.52 | 0.46 | 0.13 | 0.45 |
6 杨桦青杄混交林 PBP | 0.24 | 0.63 | 0.68 | 0.44 | 0.53 | 0.50 |
7 油松白桦混交林 TBM | 0.93 | 1.00 | 0.72 | 0.40 | 0.00 | 0.61 |
8 落叶松辽东栎混交林 LQM | 0.05 | 0.90 | 0.41 | 0.88 | 0.28 | 0.50 |
9 落叶松青杨混交林 LPM | 0.01 | 0.68 | 0.79 | 0.93 | 0.10 | 0.50 |
10 白杄杨桦混交林 PPB | 0.51 | 0.86 | 0.98 | 0.89 | 0.39 | 0.73 |
11 落叶松白杄混交林 LMM | 1.00 | 0.63 | 0.88 | 0.61 | 0.39 | 0.70 |
12 落叶松青杄混交林 LWM | 0.69 | 0.76 | 0.65 | 0.86 | 0.70 | 0.73 |
13 青杄林 PWS | 0.41 | 0.59 | 1.00 | 1.00 | 1.00 | 0.80 |
图1 13个群落的Godron散点图。 LMM, 落叶松白杄混交林; LPM, 落叶松青杨混交林; LQM, 落叶松辽东栎混交林; LWM, 落叶松青杄混交林; PBL, 杨桦落叶松混交林; PBM, 青杨白桦混交林; PBP, 杨桦青杄混交林; PCS, 青杨林; PPB, 白杄杨桦混交林; PPM, 青杨白杄混交林; PQM, 青杨辽东栎混交林; PWS, 青杄林; TBM, 油松白桦混交林。
Fig. 1 Godron scatter graphs of 13 communities. LMM, Larix principis-rupprechtii + Picea meyeri mixed forest; LPM, Larix principis-rupprechtii + Populus cathayana mixed forest; LQM, Larix principis-rupprechtii + Quercus wutaishanica mixed forest; LWM, Larix principis-rupprechtii + Picea wilsonii mixed forest; PBL, Populus cathayana + Betula platyphylla + Larix principis-rupprechtii mixed forest; PBM, Populus cathayana + Betula platyphylla mixed forest; PBP, Populus cathayana + Betula platyphylla + Picea wilsonii mixed forest; PCS, Populus cathayana single forest; PPB, Picea meyeri + Populus cathayana + Betula platyphylla mixed forest; PPM, Populus cathayana + Picea meyeri mixed forest; PQM, Populus cathayana + Quercus wutaishanica mixed forest; PWS, Picea wilsonii single forest; TBM, Pinus tabulaeformis + Betula platyphylla mixed forest.
群落类型 Community type | 曲线类型 Type of curve | 相关系数 Correlation coefficient | 交点坐标 Coordinates | 标准值 Standard value |
---|---|---|---|---|
1 青杨林 PCS | y = -0.01x2 + 1.87x + 10.75 | 0.98 | 35.75/64.25 | 890.01 |
2 青杨辽东栎混交林 PQM | y = -0.02x2 + 2.36x + 15.23 | 0.96 | 29.53/70.47 | 976.17 |
3 青杨白桦混交林 PBM | y = -0.02x2 + 2.25x + 16.13 | 0.95 | 30.16/69.84 | 967.45 |
4 杨桦落叶松混交林 PBL | y = -0.02x2 + 2.35x + 15.59 | 0.96 | 29.56/70.44 | 975.76 |
5 青杨白杄混交林 PPM | y = -0.01x2 + 2.21x + 13.10 | 0.97 | 31.64/68.36 | 946.95 |
6 杨桦青杄混交林 PBP | y = -0.02x2 + 2.23x + 16.13 | 0.96 | 30.38/69.62 | 964.40 |
7 油松白桦混交林 TBM | y = -0.02x2 + 2.22x + 16.85 | 0.95 | 30.05/69.95 | 968.97 |
8 落叶松辽东栎混交林 LQM | y = -0.01x2 + 2.06x + 14.28 | 0.97 | 32.53/67.47 | 934.62 |
9 落叶松青杨混交林 LPM | y = -0.02x2 + 2.36x + 15.56 | 0.96 | 29.46/70.54 | 977.14 |
10 白杄杨桦混交林 PPB | y = -0.02x2 + 2.49x + 16.61 | 0.93 | 27.99/72.01 | 997.51 |
11 落叶松白杄混交林 LMM | y = -0.02x2 + 2.46x + 15.19 | 0.94 | 28.75/71.25 | 986.98 |
12 落叶松青杄混交林 LWM | y = -0.01x2 + 2.16x + 17.04 | 0.95 | 30.61/69.39 | 961.21 |
13 青杄林 PWS | y = -0.02x2 + 2.55x + 16.01 | 0.94 | 27.81/72.19 | 1 000.00 |
表5 13个群落的Godron指数与标准值
Table 5 Godron index and standard index of 13 communities
群落类型 Community type | 曲线类型 Type of curve | 相关系数 Correlation coefficient | 交点坐标 Coordinates | 标准值 Standard value |
---|---|---|---|---|
1 青杨林 PCS | y = -0.01x2 + 1.87x + 10.75 | 0.98 | 35.75/64.25 | 890.01 |
2 青杨辽东栎混交林 PQM | y = -0.02x2 + 2.36x + 15.23 | 0.96 | 29.53/70.47 | 976.17 |
3 青杨白桦混交林 PBM | y = -0.02x2 + 2.25x + 16.13 | 0.95 | 30.16/69.84 | 967.45 |
4 杨桦落叶松混交林 PBL | y = -0.02x2 + 2.35x + 15.59 | 0.96 | 29.56/70.44 | 975.76 |
5 青杨白杄混交林 PPM | y = -0.01x2 + 2.21x + 13.10 | 0.97 | 31.64/68.36 | 946.95 |
6 杨桦青杄混交林 PBP | y = -0.02x2 + 2.23x + 16.13 | 0.96 | 30.38/69.62 | 964.40 |
7 油松白桦混交林 TBM | y = -0.02x2 + 2.22x + 16.85 | 0.95 | 30.05/69.95 | 968.97 |
8 落叶松辽东栎混交林 LQM | y = -0.01x2 + 2.06x + 14.28 | 0.97 | 32.53/67.47 | 934.62 |
9 落叶松青杨混交林 LPM | y = -0.02x2 + 2.36x + 15.56 | 0.96 | 29.46/70.54 | 977.14 |
10 白杄杨桦混交林 PPB | y = -0.02x2 + 2.49x + 16.61 | 0.93 | 27.99/72.01 | 997.51 |
11 落叶松白杄混交林 LMM | y = -0.02x2 + 2.46x + 15.19 | 0.94 | 28.75/71.25 | 986.98 |
12 落叶松青杄混交林 LWM | y = -0.01x2 + 2.16x + 17.04 | 0.95 | 30.61/69.39 | 961.21 |
13 青杄林 PWS | y = -0.02x2 + 2.55x + 16.01 | 0.94 | 27.81/72.19 | 1 000.00 |
群落类型 Community type | 立木蓄积量 Growing stock volume (m3·hm-2) | 标准值 Standard value | 平均树高 Mean of tree height (m) | 标准值 Standard value | 枯落物厚度 Litter thickness (cm) | 标准值 Standard value | 平均值 Mean |
---|---|---|---|---|---|---|---|
1 青杨林 PCS | 316.27 | 966.86 | 15.06 | 741.81 | 2.20 | 362.44 | 690.37 |
2 青杨辽东栎混交林 PQM | 102.13 | 312.23 | 10.02 | 493.60 | 3.93 | 647.45 | 484.42 |
3 青杨白桦混交林 PBM | 103.87 | 317.53 | 14.31 | 705.10 | 3.57 | 588.14 | 536.92 |
4 杨桦落叶松混交林 PBL | 177.58 | 542.86 | 15.70 | 773.17 | 4.27 | 703.46 | 673.16 |
5 青杨白杄混交林 PPM | 129.97 | 397.33 | 16.14 | 795.00 | 4.63 | 762.77 | 651.70 |
6 杨桦青杄混交林 PBP | 139.37 | 426.07 | 13.78 | 678.89 | 4.92 | 810.54 | 638.50 |
7 油松白桦混交林 TBM | 224.34 | 685.82 | 11.38 | 560.68 | 3.70 | 609.56 | 618.69 |
8 落叶松辽东栎混交林 LQM | 273.25 | 835.34 | 20.30 | 1 000.00 | 4.70 | 774.30 | 869.88 |
9 落叶松青杨混交林 LPM | 327.11 | 1 000.00 | 16.24 | 800.05 | 5.38 | 886.33 | 895.46 |
10 白杄杨桦混交林 PPB | 323.94 | 990.29 | 14.41 | 710.09 | 5.60 | 922.57 | 874.32 |
11 落叶松白杄混交林 LMM | 160.75 | 491.41 | 15.08 | 742.77 | 5.80 | 955.52 | 729.90 |
12 落叶松青杄混交林 LWM | 262.14 | 801.37 | 18.81 | 926.64 | 5.10 | 840.20 | 856.07 |
13 青杄林 PWS | 300.92 | 919.93 | 17.73 | 873.60 | 6.07 | 1 000.00 | 931.18 |
表6 群落立地质量特征
Table 6 Site quality characteristics of community
群落类型 Community type | 立木蓄积量 Growing stock volume (m3·hm-2) | 标准值 Standard value | 平均树高 Mean of tree height (m) | 标准值 Standard value | 枯落物厚度 Litter thickness (cm) | 标准值 Standard value | 平均值 Mean |
---|---|---|---|---|---|---|---|
1 青杨林 PCS | 316.27 | 966.86 | 15.06 | 741.81 | 2.20 | 362.44 | 690.37 |
2 青杨辽东栎混交林 PQM | 102.13 | 312.23 | 10.02 | 493.60 | 3.93 | 647.45 | 484.42 |
3 青杨白桦混交林 PBM | 103.87 | 317.53 | 14.31 | 705.10 | 3.57 | 588.14 | 536.92 |
4 杨桦落叶松混交林 PBL | 177.58 | 542.86 | 15.70 | 773.17 | 4.27 | 703.46 | 673.16 |
5 青杨白杄混交林 PPM | 129.97 | 397.33 | 16.14 | 795.00 | 4.63 | 762.77 | 651.70 |
6 杨桦青杄混交林 PBP | 139.37 | 426.07 | 13.78 | 678.89 | 4.92 | 810.54 | 638.50 |
7 油松白桦混交林 TBM | 224.34 | 685.82 | 11.38 | 560.68 | 3.70 | 609.56 | 618.69 |
8 落叶松辽东栎混交林 LQM | 273.25 | 835.34 | 20.30 | 1 000.00 | 4.70 | 774.30 | 869.88 |
9 落叶松青杨混交林 LPM | 327.11 | 1 000.00 | 16.24 | 800.05 | 5.38 | 886.33 | 895.46 |
10 白杄杨桦混交林 PPB | 323.94 | 990.29 | 14.41 | 710.09 | 5.60 | 922.57 | 874.32 |
11 落叶松白杄混交林 LMM | 160.75 | 491.41 | 15.08 | 742.77 | 5.80 | 955.52 | 729.90 |
12 落叶松青杄混交林 LWM | 262.14 | 801.37 | 18.81 | 926.64 | 5.10 | 840.20 | 856.07 |
13 青杄林 PWS | 300.92 | 919.93 | 17.73 | 873.60 | 6.07 | 1 000.00 | 931.18 |
群落类型 Community type | 实验区 Test area (0.18) | 缓冲区 Buffer area (0.31) | 核心区 Core area (0.52) | 总和 Total | 保护程度 Protection degree |
---|---|---|---|---|---|
1 青杨林 PCS | 3 | 0 | 0 | 3 | 0.18 |
2 青杨辽东栎混交林 PQM | 2 | 1 | 0 | 3 | 0.22 |
3 青杨白桦混交林 PBM | 6 | 0 | 0 | 6 | 0.18 |
4 杨桦落叶松混交林 PBL | 3 | 3 | 0 | 6 | 0.25 |
5 青杨白杄混交林 PPM | 2 | 1 | 0 | 3 | 0.22 |
6 杨桦青杄混交林 PBP | 1 | 3 | 2 | 6 | 0.36 |
7 油松白桦混交林 TBM | 5 | 0 | 0 | 5 | 0.18 |
8 落叶松辽东栎混交林 LQM | 3 | 1 | 1 | 5 | 0.27 |
9 落叶松青杨混交林 LPM | 3 | 1 | 0 | 4 | 0.21 |
10 白杄杨桦混交林 PPB | 0 | 3 | 0 | 3 | 0.31 |
11 落叶松白杄混交林 LMM | 0 | 3 | 0 | 3 | 0.31 |
12 落叶松青杄混交林 LWM | 0 | 3 | 3 | 6 | 0.41 |
13 青杄林 PWS | 0 | 0 | 3 | 3 | 0.51 |
表7 群落保护程度
Table 7 Protection degree of community
群落类型 Community type | 实验区 Test area (0.18) | 缓冲区 Buffer area (0.31) | 核心区 Core area (0.52) | 总和 Total | 保护程度 Protection degree |
---|---|---|---|---|---|
1 青杨林 PCS | 3 | 0 | 0 | 3 | 0.18 |
2 青杨辽东栎混交林 PQM | 2 | 1 | 0 | 3 | 0.22 |
3 青杨白桦混交林 PBM | 6 | 0 | 0 | 6 | 0.18 |
4 杨桦落叶松混交林 PBL | 3 | 3 | 0 | 6 | 0.25 |
5 青杨白杄混交林 PPM | 2 | 1 | 0 | 3 | 0.22 |
6 杨桦青杄混交林 PBP | 1 | 3 | 2 | 6 | 0.36 |
7 油松白桦混交林 TBM | 5 | 0 | 0 | 5 | 0.18 |
8 落叶松辽东栎混交林 LQM | 3 | 1 | 1 | 5 | 0.27 |
9 落叶松青杨混交林 LPM | 3 | 1 | 0 | 4 | 0.21 |
10 白杄杨桦混交林 PPB | 0 | 3 | 0 | 3 | 0.31 |
11 落叶松白杄混交林 LMM | 0 | 3 | 0 | 3 | 0.31 |
12 落叶松青杄混交林 LWM | 0 | 3 | 3 | 6 | 0.41 |
13 青杄林 PWS | 0 | 0 | 3 | 3 | 0.51 |
[1] | An LJ ( 安丽娟), Zhu ZH ( 朱志红), Wang XA ( 王孝安), Guo H ( 郭华) (2007). Stability analysis of major communities in Malan forest region of Ziwuling Mountain. Acta Botanica Boreali-Occidentalia Sinica (西北植物学报), 27, 1000-1007. (in Chinese with English abstract) |
[2] |
Cardinale BJ, Srivastava DS, Duffy JE, Wright JP, Downing AL, Sankaran M, Jouseau C (2006). Effects of biodiversity on the functioning of trophic groups and ecosystems. Nature, 443, 989-992.
URL PMID |
[3] | Cheng XQ ( 程小琴), Han HR ( 韩海荣), Wei AS ( 魏阿沙), Zhang YH ( 张延华), Yi LT ( 伊力塔), Chen Y ( 陈圆) (2007). Niche characteristics of dominant species in forest community in Pangquangou Nature Reserve, Shanxi Province. Journal of Beijing Forestry University (北京林业大学学报), 29(Suppl. 2), 283-287. (in Chinese with English abstract) |
[4] | Dang CL ( 党承林) (1998). Redundancy structure in phytocoenosiums as an explanation of ecosystem stability. Acta Ecologica Sinica (生态学报), 18, 665-672. (in Chinese with English abstract) |
[5] | Dang CL ( 党承林), Wang CY ( 王崇云), Wang BR ( 王宝荣), Li YL ( 李彦玲), Huang QM ( 黄其明) (2002). Succession and stability in plant community. Chinese Journal of Ecology (生态学杂志), 21, 30-35. (in Chinese with English abstract) |
[6] |
Doak DF, Bigger D, Harding EK, Marvier MA, O’Malley RE, Thomson D (1998). The statistical inevitability of sta- bility-diversity relationships in community ecology. The American Naturalist, 151, 264-276.
URL PMID |
[7] | Elton CS (1958). The Ecology of Invasion by Animals and Plants. Chapmanand Hall, London. 143-153. |
[8] | Gao JF ( 高俊峰), Zhang YX ( 张芸香) (2005). Species diversity in overlapped zones of typical secondary forests in Guandishan Mountains. Acta Botanica Boreali- Occidentalia Sinica (西北植物学报), 25, 2017-2023. (in Chinese with English abstract) |
[9] | Gao RM ( 高润梅), Guo JP ( 郭晋平) (2010). Succession and prediction of the riparian forest in upper-reach of Wenyuhe watershed. Acta Ecologica Sinica (生态学报), 30, 1564-1572. (in Chinese with English abstract) |
[10] | Gao RM ( 高润梅), Guo JP ( 郭晋平), Guo YD ( 郭跃东) (2011a). Characteristics of soil seed bank and tree regenerations of riparian forests in the upper reach of Wenyuhe watershed in Shanxi Province. Plant Science Journal (植物科学学报), 29, 580-588. (in Chinese with English abstract) |
[11] | Gao RM ( 高润梅), Guo JP ( 郭晋平), Guo YD ( 郭跃东), Zhang DX ( 张东旭) (2011b). Community structure and plant diversity characteristics of riparian forests on upper reaches of Wenyuhe River. Forest Research (林业科学研究), 24(1), 74-81. (in Chinese with English abstract) |
[12] | Grime JP (1998). Benefits of plant diversity to ecosystems: immediate, filter and founder effects. Journal of Ecology, 86, 902-910. |
[13] |
Guo JP ( 郭晋平), Li HB ( 李海波), Liu N ( 刘宁), Zhang YX ( 张芸香) (2009). Comparison of responses of Larix principis-rupprechtii and Picea meyeri seedling growth to light availability and planting density under controlled environment. Scientia Silvae Sinicae (林业科学), 45, 53-59. (in Chinese with English abstract)
DOI URL |
[14] | Guo QQ ( 郭其强), Zhang WH ( 张文辉), Cao XP ( 曹旭平) (2009). Establishment of an evaluation model of the forest community stability based on fuzzy synthetic evaluation: a case study of main forest communities in Huanglong Mountains. Scientia Silvae Sinicae (林业科学), 45, 19-24. (in Chinese with English abstract) |
[15] | Guo YD ( 郭跃东), Guo JP ( 郭晋平), Zhang YX ( 张芸香), Ji JC ( 吉久昌) (2010). Environmental gradient analysis and succession process of riparian forest communities in upper reach of Wenyuhe watershed. Acta Ecologica Sinica (生态学报), 30, 4046-4055. (in Chinese with English abstract) |
[16] |
Ives AR, Carpenter SR (2007). Stability and diversity of ecosystems. Science, 317, 58-62.
URL PMID |
[17] | Liu XW ( 柳新伟), Zhou HC ( 周厚诚), Li P ( 李萍), Peng SL ( 彭少麟) (2004). A conceptual analysis of ecosystem stability. Acta Ecologica Sinica (生态学报), 24, 2635-2640. (in Chinese with English abstract) |
[18] |
Lu QB ( 鲁庆彬), You WY ( 游卫云), Zhao CJ ( 赵昌杰), Wang XW ( 王向伟), Meng XX ( 孟秀祥) (2011). Effects of tourism disturbance on plant diversity in Qingshan Lake scenic area of Zhejiang Province. Chinese Journal of Applied Ecology (应用生态学报), 22, 295-302. (in Chinese with English abstract)
URL PMID |
[19] | MacArthur RH (1955). Fluctuations of animal populations, and a measure of community stability. Ecology, 36, 533-536. |
[20] | Ma FY ( 马风云) (2002). Research advances on ecosystem stability. Journal of Desert Research (中国沙漠), 22, 401-407. (in Chinese with English abstract) |
[21] | Ma JM ( 马姜明), Li K ( 李昆) (2004). Current situation of research and prospects on forest ecosystem stability. World Forestry Research (世界林业研究), 17, 15-19. (in Chinese with English abstract) |
[22] | McCann K, Hastings A, Huxel GR (1998). Weak trophic interactions and the balance of nature. Nature, 395, 794-798. |
[23] |
McCann KS (2000). The diversity-stability debate. Nature, 405, 228-233.
URL PMID |
[24] | Meng XY ( 孟宪宇) (2006). Forest Measuration (测树学) 3rd edn. China Forestry Publishing House, Beijing. 139-141. (in Chinese) |
[25] | Moore JC, Hunt HW (1988). Resource compartmentation and the stability of real ecosystems. Nature, 333, 261-263. |
[26] | Naiman RJ, Décamps H (1997). The ecology of interfaces: riparian zones. Annual Review of Ecology and Systematics, 28, 621-658. |
[27] | Naiman RJ, Décamps H, McClain ME, (2005). Riparian- Ecology, Conservation and Management of Streamside Communities. Academic Press, London. 91-120. |
[28] | Naiman RJ, Robern EB, Bisson PA (2000). Riparian ecology and management in the Pacific coastal rain forest. BioScience, 50, 996-1011. |
[29] | Polis GA (1998). Stability is woven by complex webs. Nature, 395, 744-745. |
[30] |
Richardson DM, Holmes PM, Esler KJ, Galatowitsch SM, Stromberg JC, Kirkman SP, Pyšek P, Hobbs RJ (2007). Riparian vegetation: degradation, alien plant invasions, and restoration prospects. Diversity and Distributions, 13, 126-139.
DOI URL |
[31] |
Tilman D, Downing JA (1994). Biodiversity and stability in grasslands. Nature, 367, 363-365.
DOI URL |
[32] |
Walker BH (1992). Biodiversity and ecological redundancy. Conservation Biology, 6, 18-23.
DOI URL |
[33] | Wan HL ( 万慧霖), Feng ZW ( 冯宗炜) (2008). Species composition and succession trend of evergreen broad-leaved forest in Lushan Mountain, Jiangxi Province, China. Acta Ecologica Sinica (生态学报), 28, 1147-1156. (in Chinese with English abstract) |
[34] | Wang GH ( 王国宏) (2002). Further thoughts on diversity and stability in ecosystem. Biodiversity Science (生物多样性), 10, 126-134. (in Chinese with English abstract) |
[35] |
Wang LH ( 王立海), Meng C ( 孟春) (2005). Landscape diversity and stability of Korean pine broad-leaved forest in Xiaoxing’anling forest region. Chinese Journal of Applied Ecology (应用生态学报), 16, 2267-2270. (in Chinese with English abstract)
URL PMID |
[36] |
Wang QH ( 王庆海), Yuan XH ( 袁小环), Wu JY ( 武菊英), Teng WJ ( 滕文军) (2008). Index system and fuzzy synthetic assessment in landscape evaluation of ornamental grasses. Chinese Journal of Applied Ecology (应用生态学报), 19, 381-386. (in Chinese with English abstract)
URL PMID |
[37] | Xu H ( 许涵), Li YD ( 李意德), Luo TS ( 骆土寿), Lin MX ( 林明献), Chen DX ( 陈德祥), Mo JH ( 莫锦华), Luo W ( 罗文), Hong XJ ( 洪小江), Jiang ZL ( 蒋忠亮) (2009). Community structure characteristics of tropical montane rain forests with different regeneration types in Jianfengling. Scientia Silvae Sinicae (林业科学), 45, 14-20. (in Chinese with English abstract) |
[38] | Yan DF ( 闫东锋), Wang XY ( 王向阳), Yang XT ( 杨喜田) (2011). Comparison of the analysis methods for forest community stability using principal component analysis and stability degree index methods. Journal of Henan Agricultural University (河南农业大学学报), 45, 166-171, 182. (in Chinese with English abstract) |
[39] | Yang HX ( 阳含熙), Pan YD ( 潘愉德), Wu YG ( 伍业钢) (1988). Markov chain model of succession of the mixed broadleaf Korean pine forest at Changbaishan biosphere reserves in China. Acta Ecologica Sinica (生态学报), 8, 211-219. (in Chinese with English abstract) |
[40] | Zhang JC ( 张建春), Peng BZ ( 彭补拙) (2002). A study on riparian area and its ecological rehabilitation. Geographical Research (地理研究), 21, 373-383. (in Chinese with English abstract) |
[41] | Zhang JT ( 张金屯) (2004). Quantitative Ecology (数量生态学) 2nd edn. Chinese Science and Technology Press, Beijing. 94-98. (in Chinese) |
[42] | Zhang JY ( 张继义), Zhao HL ( 赵哈林) (2003). Review on the study of vegetation stability. Chinese Journal of Ecology (生态学杂志), 22, 42-48. (in Chinese with English abstract) |
[43] | Zhang LM ( 张立敏), Chen B ( 陈斌), Li ZY ( 李正跃) (2010). Analysis of the species diversity and community stability in local-community using the neutral theory. Acta Ecologica Sinica (生态学报), 30, 1556-1563. (in Chinese with English abstract) |
[44] | Zhang M ( 张谧), Xiong GM ( 熊高明), Zhao CM ( 赵常明), Chen ZG ( 陈志刚), Xie ZQ ( 谢宗强) (2003). The structures and patterns of a Fagus engleriana-Cyclobalanopsis oxyodon community in Shennongjia Area, Hubei Province. Acta Phytoecologica Sinica (植物生态学报), 27, 603-609. (in Chinese with English abstract) |
[45] | Zheng YR ( 郑元润) (2000). Comparison of methods for studying stability of forest community. Scientia Silvae Sinicae (林业科学), 36, 28-32. (in Chinese with English abstract) |
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