Correlation between the composition and diversity of community species and soil factors under two geological conditions
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摘要:
为对比岩溶和非岩溶条件下物种组成及多样性的差异，明晰不同地质背景造就的不同土壤因子对物种多样性的影响，在兼有岩溶区与非岩溶区的桂林毛村采用野外样地调查法对研究区进行物种组成及多样性的对比研究。结果表明：(1)研究区内共记录了123种植物，其中岩溶区占35科46属87种，非岩溶区占48科61属95种，非岩溶区植物科属种数量明显大于岩溶区；（2）岩溶区物种多样性为：草本样方>灌木样方>乔木样方；在非岩溶区为：灌木样方>乔木样方>草本样方；（3）不同地质背景造就了不同的土壤因子，其中土壤全氮含量对物种多样性影响最为显著。综上，岩溶区物种组成明显低于非岩溶区，物种多样性也不及非岩溶区，土壤因子与物种多样性之间存在相关性，土壤全氮对物种多样性影响最为显著，土层深度减弱了土壤因子与物种多样性之间的相关性。对比岩溶区与非岩溶区土壤因子与物种之间的关系差异，为区域生态系统恢复重建提供了理论基础。
Abstract:In order to compare the differences of species composition and diversity between karst and non-karst areas, and to explore the influence of different soil factors under these two geological conditions on species diversity, we conducted a field investigation in Maocun of Guilin that is composed of both karst and non-karst areas. Results show that a total of 123 species is recorded in the study area, including 87 species, 46 genera and 35 families in karst area and 95 species, 61 genera and 48 families in the non-karst area. The number of species composition in non-karst area is significantly higher than that in the karst area. In addition, the quadrat of species diversity in karst area is listed as: herb quadrat>shrub quadrat>tree quadrat. In the non-karst area, it is listed as, shrub quadrat>tree quadrat>herb quadrat. Finally, different types of geological background contribute to different soil factors, among which the total nitrogen content of soil has the most significant effect on species diversity. In conclusion, the species composition and diversity in the karst area is significantly lower than that in the non-karst area, and there is a correlation between soil factors and species diversity. Total nitrogen of soil has the most significant effect on species diversity, and the soil depth weakens the correlation between soil factors and species diversity. Comparing the relationship between soil factors and species in karst and non-karst areas provides a theoretical basis for the restoration and reconstruction of regional ecosystem.
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Key words:
- karst area /
- species composition /
- diversity /
- redundancy analysis
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表 1 岩溶与非岩溶区基本概况
Table 1. Basic survey of karst and non-karst areas
区域 样方 土壤类型 土层厚度/cm 经纬度 海拔/m 坡度 群落优势种 非岩溶区 乔木 红壤 100 25°11′03.89″N 110°32′32.09″E 277 34° 木荷Schima superba Gardn. et Champ.、甜槠Castanopsis eyrei (Champ. ex Benth.) Tutch. 灌木 红壤 80 25°11′02.44″N 110°32′31.28″E 235 34° 杜鹃Rhododendron simsii Planch.、木荷Schima superba Gardn. et Champ.、山鸡椒
Litsea cubeba (Lour) Pers.、甜槠Castanopsis eyrei (Champ. ex Benth.) Tutch.、盐肤木Rhus chinensis Mill.草本 红壤 85.33 25°11′03.09″N 110°32′32.56″E 288 34° 狗脊蕨Woodwardia unigemmata (Makino) Nakai、扭黄茅Heteropogon contortus L． Beauv.、五节芒Miscanthus floridulus (Lab.) Warb. ex Schum et Laut.、铁萁芒Dicranopteris linearis (Burm.) Underw. 岩溶区 乔木 黄色石灰土 56.33 25°11′17.18″N 110°32′23.09″E 217 40° 檵木Loropetalum chinense (R. Br.) Oliver、青冈Cyclobalanopsis glauca (Thunberg) Oersted 灌木 棕色石灰土 46 25°11′24.13″N 110°32′48.21″E 183 35° 檵木Loropetalum chinense (R. Br.) Oliver、龙须藤Bauhinia championii (Benth.) Benth 草本 黄色石灰土 46 25°11′16.33″N 110°32′22.89″E 225 40° 络石Trachelospermum jasminoides (Lindl.) Lem.、类芦Neyraudia reynaudiana (kunth.) Keng、葛藤Pueraria lobate (Willd.) Ohwi、五节芒Miscanthus floridulus (Lab.) Warb. ex Schum et Laut.Miscanthus floridulus (Lab.) Warb. ex Schum et Laut. 
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表 2 岩溶区各样方中代表物种重要值
Table 2. Important values of representative species in different quadrats of the karst area
样方 物种名称 盖度 相对盖度 密度 相对密度 频度 相对频度 重要值 % % 株·m−2 % % % 草本 类芦
Neyraudia reynaudiana (kunth.) Keng62.50 19.00 1.00 2.91 0.80 16.67 38.58 葛藤
Pueraria lobate (Willd.) Ohwi62.50 26.60 1.00 2.91 0.20 4.17 33.68 五节芒
Miscanthus floridulus (Lab.) Warb. ex Schum et Laut.62.50 19.00 0.67 1.94 0.60 12.50 33.44 络石
Trachelospermum jasminoides (Lindl.) Lem.1.50 0.46 8.00 23.30 0.20 4.17 27.92 井栏凤尾蕨
Pteris multifida Poir.37.50 11.40 1.00 2.91 0.60 12.50 26.81 苔草
Carex tristachya2.50 0.76 6.67 19.42 0.20 4.17 24.34 弓果黍
Cyrtococcum patens (Linn.) A. Camus2.50 0.76 4.67 13.59 0.40 8.33 22.69 山蒜
Allium nipponicum Fr. et Sav2.50 0.76 3.67 10.68 0.20 4.17 15.61 海金沙
Lygodium japonicum (Thunb.) Sw.15.00 4.56 1.67 4.85 0.20 4.17 13.58 蛇莓
Duchesnea indica (Andr.) Focke2.50 0.76 2.00 5.83 0.20 4.17 10.75 灌木 檵木
Loropetalum chinense (R. Br.) Oliver62.50 19.21 1.50 66.90 31.33 66.90 153.02 龙须藤
Bauhinia championii (Benth.) Benth.37.50 19.21 0.08 3.56 1.67 3.56 26.33 齿叶黄皮
Clausena dunniana Levl.15.00 7.68 0.09 3.91 1.83 3.91 15.51 海金子
Pittosporum illicioides Mak.15.00 7.68 0.05 2.14 1.00 2.14 11.95 火棘
Pyracantha fortuneana (Maxim.) Li15.00 7.68 0.02 0.71 0.33 0.71 9.11 九里香
Murraya exotica L. Mant.15.00 7.68 0.02 0.71 0.33 0.71 9.11 野独活
Miliusa chunii W. T. Wang2.50 1.28 0.09 3.91 1.83 3.91 9.11 灌木 棕榈
Trachycarpus fortunei (Hook.) H. Wendl.15.00 7.68 0.01 0.36 0.17 0.36 8.40 红背山麻杆
Alchornea trewioides (Benth.) Muell. Arg.0.10 0.05 0.09 3.91 1.83 3.91 7.88 鸡爪簕
Oxyceros sinensis Lour.5.00 2.56 0.05 2.14 1.00 2.14 6.83 乔木 檵木
Loropetalum chinense (R. Br.) Oliver0.02 44.70 0.03 31.20 13.00 31.20 107.10 青冈
Cyclobalanopsis glauca (Thunberg) Oersted0.002 1 4.74 0.03 27.20 11.33 27.20 59.14 密花树
Rapanea neriifolia (Sieb. et Zucc.) Mez0.002 3.51 0.02 23.20 9.67 23.20 49.91 盐肤木
Rhus chinensis Mill.0.01 31.94 0.001 5 2.40 1.00 2.40 36.74 海金子
Pittosporum illicioides Mak.0.001 5 3.43 0.01 9.60 4.00 9.60 22.63 老虎刺
Pterolobium punctatum Hemsl.0.001 5 4.80 0.001 0.80 0.33 0.80 6.40 野独活
Miliusa chunii W. T. Wang0.000 7 1.53 0.000 8 0.80 0.33 0.80 3.13 木犀
Osmanthus fragrans (Thunb.) Loureiro0.000 5 1.20 0.000 8 0.80 0.33 0.80 2.80 枇杷
Eriobotrya japonica (Thunb.) Lindl.0.000 5 1.05 0.000 8 0.80 0.33 0.80 2.65 粗叶榕
Ficus hirta Vahl0.000 1 0.03 0.0002 0.03 1.33 0.03 0.09
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表 3 非岩溶区各样方中代表物种重要值
Table 3. Important values of representative species in different quadrat of the non-karst areas
样方 物种名称 盖度 相对盖度 密度 相对密度 频度 相对频度 重要值 % % 株·m−2 % % % 草本 五节芒
Miscanthus floridulus (Lab.) Warb. ex Schum et Laut.45.00 43.80 16.60 53.9 0.17 5.00 60.65 铁芒箕
Dicranopteris linearis (Burm.) Underw.37.50 10.51 1.40 4.55 0.33 10.00 58.34 扭黄茅
Heteropogon contortus L． Beauv．62.5 26.28 0.20 0.65 1.00 30.00 56.93 狗脊蕨
Woodwardia unigemmata (Makino) Nakai15.00 10.51 6.40 20.78 0.17 5.00 36.29 玉叶金花
Mussaenda pubescens Ait. F. Hort. Kew. Ed.2.50 1.75 0.20 0.65 0.67 20.00 22.4 卵叶菝葜
Smilax arisanensis15 1.75 0.2 0.65 0.17 5 16.16 弓果黍
Cyrtococcum patens (Linn.) A. Camus0.1 0.07 3.4 11.04 0.17 5 16.11 山姜
Alpinia japonica (Thunb.) Miq.2.5 1.75 0.8 2.6 0.17 5 9.35 菝葜
Smilax china Linn.2.5 1.75 0.4 1.3 0.17 5 8.05 小白酒草
Conyza. Canadensis (L.) Crong.2.5 1.75 0.4 1.3 0.17 5 8.05 灌木 木荷
Schima superba Gardn. et Champ.15 0.05 0.28 18.13 0.67 10.26 39.65 杜鹃
Rhododendron simsii Planch.15 7.4 0.17 10.88 0.83 12.82 31.1 甜槠
Castanopsis eyrei (Champ. ex Benth.) Tutch.37.5 18.49 0.1 6.74 0.33 5.13 30.36 山鸡椒
Litsea cubeba (Lour.) Pers.2.5 1.23 0.32 20.73 0.5 7.69 29.65 盐肤木
Rhus chinensis Mill.37.5 18.49 0.21 13.47 0.5 7.69 28.44 野独活
Miliusa chunii W. T. Wang37.5 18.49 0.02 1.04 0.33 5.13 24.66 菝葜
Smilax china Linn.15 7.4 0.08 5.18 0.5 7.69 20.27 荚蒾
Viburnum dilatatum Thunb.15 7.4 0.13 8.29 0.17 2.56 18.25 紫金牛
Ardisia japonica (Thunberg) Blume15 7.4 0.1 6.22 0.17 2.56 16.18 赤楠
Syzygium buxifolium Hook. et Arn.2.5 1.23 0.03 2.07 0.67 10.26 13.56 乔木 甜槠
Castanopsis eyrei Tutch.1.272 66.6 0.085 54.26 1 18.75 139.61 木荷
Schima superba Gardn. et Champ.0.473 3 24.78 0.038 3 24.47 1 18.75 68 白栎
Quercus fabri Hance0.012 0.63 0.02 12.77 0.33 6.25 19.65 腺叶杜茎山
Maesa membranacea A. DC.0.000 6 0.03 0.001 7 1.06 0.67 12.5 13.6 黄樟
Cinnamomum porrectum (Roxb.) Kosterm.0.097 6 5.11 0.002 5 1.6 0.33 6.25 12.96 枫香
Liquidambar formosana Hance0.051 2 2.68 0.002 5 1.6 0.33 6.25 10.53 薄叶润楠
Machilus leptophylla Hand.-Mazz.0.000 7 0.04 0.003 3 2.13 0.33 6.25 8.42 九里香
Murraya exotica L. Mant.0.000 6 0.03 0.000 8 0.53 0.33 6.25 6.81 杉木
Cunninghamia lanceolata (Lamb.) Hook.0.000 6 0.03 0.000 8 0.53 0.33 6.25 6.81 罗伞
Brassaiopsis glomerulata (Bl.) Regel0.000 1 0.01 0.000 8 0.53 0.33 6.25 6.79
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表 4 岩溶区与非岩溶区不同样方物种多样性
Table 4. Species diversity in different quadrats of karst and non-karst areas
多样性指数 岩溶区 非岩溶区 草本样方 灌木样方 乔木样方 草本样方 灌木样方 乔木样方 S 30.00 36.00 32.00 33.00 43.00 39.00 D 0.87 0.60 0.76 0.63 0.87 0.63 H 3.32 2.68 2.36 3.19 3.67 2.01 P 0.96 0.98 0.96 0.98 0.93 0.65 Jsw 0.72 0.47 0.49 0.61 0.70 0.38 注：S为丰富度指数；D为Simpson指数；H为Shanonon-Wiene指数；P为PIE指数；Jsw为Pielou指数。
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表 5 岩溶区与非岩溶区土壤理化性质对比
Table 5. Comparison of physical and chemical properties of soil in karst and non-karst areas
土壤层次 样方 研究区 pH SOM/g·kg−1 TN/g·kg−1 AN/mg·kg−1 TP/g·kg−1 AP/mg·kg−1 TK/g·kg−1 AK/mg·kg−1 0~20 cm 草本 岩溶区 6.51±0.18 33.42±1.21 1.83±0.84 86.99±20.22 1.25±0.04 14.13±3.56 50.32±4.25 38.61±25.8 非岩溶区 4.7±0.30 42.46±1.85 0.73±0.23 101.14±30.68 1.09±0.1 58.18±2.91 48.37±25.6 30.81±3.38 灌木 岩溶区 6.73±0.30 51.75±4.42 1.83±0.22 191.11±78.57 1.22±0.05 23.84±3.56 120.25±51.50 41.22±16.1 非岩溶区 4.53±0.09 56.13±5.9 0.83±0.41 73.50±34.36 0.99±0.04 66.06±19.31 34.99±28.89 25.28±12.88 乔木 岩溶区 6.54±0.27 50.39±3.95 1.33±0.15 186.23±70.03 1.14±0.1 16.85±2.93 100.73±45.84 37.2±7.35 非岩溶区 4.5±0.13 38.06±4 0.63±0.06 78.04±17.7 1.02±0.05 6.39±8.33 39.48±16.91 34.39±2.03 20~40 cm 草本 岩溶区 6.85±0.08 23.47±1.71 0.68±0.12 49.54±11.22 1.33±0.06 19.57±8.40 63.33±18.88 20.4±3.43 非岩溶区 4.76±0.11 19.94±0.86 0.67±0.23 37.01±10.15 1.1±0.06 62.06±0.7 55.85±36.11 21.37±2.25 灌木 岩溶区 6.77±0.35 50.75±2.84 0.88±0.74 99.58±59.26 1.28±0.03 20.86±8.30 132.61±57.44 26.58±10.31 非岩溶区 4.78±0.09 4.772.23 0.40±0.05 37.11±18.52 1.08±0.04 74.90±8.08 40.37±32.27 26.58±10.31 乔木 岩溶区 6.82±0.12 50.39±3.61 0.96±0.4 125.24±69.01 1.17±0.12 19.05±0.9 99.33±27.23 24.52±11.89 非岩溶区 4.71±0.20 25.61±1.64 0.36±0.08 26.48±9.65 1.08±0.04 79.74±6.42 41.98±18.63 21.59±8.64 注：表中数值为平均值±标准误。
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表 6 土壤因子在RDA中蒙特卡洛置换检验结果
Table 6. Monte Carlo substitution test results of soil factors in RDA
0~20 cm 土壤因子 R2 P 20~40 cm土壤因子 R2 P TN 0.546 3 0.002 TK 0.267 5 0.102 pH 0.288 3 0.084 SOM 0.244 8 0.111 TK 0.242 5 0.124 AP 0.236 7 0.138 TP 0.212 0.145 TP 0.230 5 0.121 AN 0.192 0.199 pH 0.22 0.163 SOM 0.162 9 0.259 AK 0.104 8 0.419 AP 0.137 3 0.354 AN 0.103 7 0.399 AK 0.111 8 0.426 TN 0.066 3 0.611
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[1] 温亚利. 中国生物多样性保护政策的经济分析[D]. 北京: 北京林业大学, 2003: 20
Wen Yali. Economic analysis of China bidiversity protection policy[D]. Beijing: Beijing Forestry University, 2003: 20.
[2] Ruiz-Jaen M C, Aide T M. Restoration Success: How Is It Being Measured?[J]. Restoration Ecology, 2005, 13(3):569-577.
[3] Chu C, Lutz J A, Král K, et al. Direct and indirect effects of climate on richness drive the latitudinal diversity gradient in forest trees[J]. Ecology Letters, 2019, 22(2):245-255.
[4] Jonathan A Bennett, John Klironomos. Mechanisms of plant-soil feedback: interactions among biotic and abiotic drivers[J]. The New Phytologist, 2019, 222(1):91-96.
[5] 常跃畅. 福建省代表性土壤的氧化铁组成与磁化率及其发生学意义[D]. 杭州: 浙江大学, 2014
CHANG Yuechang. Forms of Iron Oxides and magnetic susceptibility of representative soils in Fujian Province and theirs genetic significance[D]. Hangzhou: Zhejiang University, 2014
[6] 刘俊廷. 晋西黄土区恢复年限对林下植被多样性及土壤理化性质的影响[D]. 北京: 北京林业大学, 2020.
LIU Junyan. The effect of vegetation recovery on the diversity of undergrowth vegetation and the physical and chemical properties of soil in the loess plateau of western Shanxi Province[D]. Beijing: Beijing Forestry University, 2020
[7] 付义勋. 三江并流区草地分布地质条件影响分析[D]. 昆明: 云南大学, 2019
FU Yixun. Impact analysis on geological condition of grassland distribution in the Three Parallel Rivers Region[D]. Kunming: Yunnan University, 2019
[8] 曾勇, 姜立君, 柯妍, 吕倩, 赵莉, 梁家栋, 胡涵, 令狐博. 重庆合川地区中二叠世晚期腕足动物群落物种多样性与生态系统功能(生产力)的关系[J]. 中国科学: 地球科学, 2012, 42(11): 1627-1633.
ZENG Yong, JIANG Lijun, KE Yan, LV Qian, ZHAO Li, LIANG Jiadong, HU Han, LING Hubo. The relationship between species diversity and ecosystem function (productivity) of the late Middle Permian brachiopodscommunity at the region of Hechuan, Chongqing, China[J]. Science China: Earth Sciences, 2012, 42(11): 1627-1633.
[9] 路洪海, 周蓓, 章程. 不同地质背景下发育的土壤及其对物种多样性的影响[J]. 地理与地理信息科学, 2007,23(1):83-86. doi: 10.3969/j.issn.1672-0504.2007.01.020
LU Honghai, ZHOU Bei, ZHANG Cheng. Species diversity and its correlation with soil factors under different geological background conditions[J]. Geography and Geo-Information Science, 2007,23(1):83-86. doi: 10.3969/j.issn.1672-0504.2007.01.020
[10] I Tomášková. Evaluation of changes in the tree species composition of Czech forests[J]. Journal of Forest Science, 2018, 50(1):31-37.
[11] 常继方. 氮磷添加对呼伦贝尔草地植物群落物种多样性与稳定性的影响[D]. 哈尔滨: 黑龙江八一农垦大学, 2020
CHANG Jifang. The addition of nitrogen and phosphorus to Hulunbuir grassland plants the influence of diversity and stability of falling species is often followed[D]. Harbin, Heilongjiang Bayi Agricultural University, 2020
[12] 覃建勋, 付伟, 郑国东, 邓宾, 吴天生, 赵辛金, 卢炳科, 覃勇新. 广西岩溶区表层土壤硒元素分布特征与影响因素探究:以武鸣县为例[J]. 土壤学报, 2020, 57(5):1299-1310.
QIN Jianxun, FU Wei, ZHENG Guodong, DENG Bin, WU Tiansheng, ZHAO Xinjin, LU Bingke, QIN Yongxin. Selenium distribution in surface soil layer of karst area of Guangxi and its affecting factors: A case study of Wuming county[J]. Acta Pedologica Sinica, 2020, 57(5):1299-1310.
[13] 周蓓, 李艳娜, 陈忠. 生物多样性对岩溶地区生态保护、恢复及重建的意义[J]. 山地农业生物学报, 2003, 22(3):248-252. doi: 10.3969/j.issn.1008-0457.2003.03.014
ZHOU Bei, LI Yanna, CHEN Zhong. The significance of biodiversity in protection, restoration and reconstruction of karst ecosystem[J]. Journal of Mountain Agriculture and Biology, 2003, 22(3):248-252. doi: 10.3969/j.issn.1008-0457.2003.03.014
[14] 袁道先. 全球岩溶生态系统对比: 科学目标和执行计划[J]. 地球科学进展, 2001, 16(4):461-466.
YUAN Daoxian. World correlation of karst ecosystem: Objectives and implementation plan[J]. Advance in Earth Sciences, 2001, 16(4):461-466.
[15] 王江南, 冯火炬, 李百球, 方楷, 施建敏. 石灰岩山地淡竹林“岩石—土壤—植物”的元素分布与迁移积聚特征[J]. 中国岩溶, 2018, 37(5):770-776.
WANG Jiangnan, FENG Huoju, LI Baiqiu, FANG Kai, SHI Jianmin. Distribution, transportation and accumulation of mineral elements in a rock-soil-plant system of Phyllostachys glauca in limestone mountains[J]. Carsologica Sinica, 2018, 37(5):770-776.
[16] 侯满福. 不同碳酸盐岩地球化学背景下的植物物种多样性和物种组成研究[D]. 桂林: 广西师范大学, 2005
HOU Manfu. Plant species diversity and component in different Geo-chemical surroundings in karst area [D]. Guilin: Guangxi Normal University, 2005
[17] 侯满福, 蒋忠诚. 茂兰喀斯特原生林不同地球化学环境的植物物种多样性[J]. 生态环境, 2006, 15(3):572-576.
HOU Manfu, JIANG Zhongcheng. Species diversity of karst original forest in different geochemical environments in Maolan[J]. Ecology and Enviroment, 2006, 15(3):572-576.
[18] 周运超, 潘根兴. 茂兰森林生态系统对岩溶环境的适应与调节[J]. 中国岩溶, 2001, 18(1):47-52. doi: 10.3969/j.issn.1001-4810.2001.01.009
ZHOU Yunchao, PAN Genxing. Adaptation and adjustment of Maolan forest ecosystem to karst environment[J]. Carsologica Sinica, 2001, 18(1):47-52. doi: 10.3969/j.issn.1001-4810.2001.01.009
[19] 莫春梦. 桂林市毛村流域碳酸盐岩混合溶蚀实验研究[D]. 北京: 中国地质大学, 2019
MO Chunmeng. Experimental study on mixed dissolution of carbonate rock in Maocun watershed of Guilin[D]. Beijing: China University of Geosciences, 2019
[20] 陈志辉, 王克林, 陈洪松, 何寻阳. 喀斯特环境移民迁出区植物多样性研究[J]. 中国生态农业学报, 2008, 16(3):723-727.
CHEN Zhihui, WANG Kelin, CHEN Hongsong, HE Xunyang. Plant diversity during natural recovery process of vegetation in karst environment emigrantareas[J]. Chinese Journal of Eco-Agriculture, 2008, 16(3):723-727.
[21] 隋玉龙, 马小欣, 马莉, 陆贵巧, 周国娜. 雾灵山几种常见植物群落表现面积的研究[J]. 绿色科技, 2014(1):86-88.
SUI Yulong, MA Xiaoxin, MA Li, LU Guiqiao, ZHOU Guona. Study on the area of some common plant communities in Mount Wuling[J]. Journal of Green Science and Technology, 2014(1):86-88.
[22] 黎燕琼, 郑绍伟, 龚固堂, 陈俊华, 朱志芳, 吴雪仙, 慕长龙. 生物多样性研究进展[J]. 四川林业科技, 2011, 32(4):12-19. doi: 10.3969/j.issn.1003-5508.2011.04.003
LI Yanqiong, ZHENG Shaowei, GONG Gutang, CHEN Junhua, ZHU Zhifang, WU Xuexian, MU Changlong. Advances in biodiversity research[J]. Journal of Sichuan Forestry Science and Technology, 2011, 32(4):12-19. doi: 10.3969/j.issn.1003-5508.2011.04.003
[23] 袁秀, 马克明, 王德. 草地植物群落最优分类数的确定:以黄河三角洲为例[J]. 生态学报, 2013, 33(8):2514-2520.
YUAN Xiu, MA Keming, WANG De. Optimal number of herb vegetation clusters: a case study on Yellow River Delta[J]. Acta Ecocogica Sinica, 2013, 33(8):2514-2520.
[24] 陈晓熹, 杨新东, 曾献兴, 陈流保, 谢冲林, 黄久香, 吴建辉, 李意德, 许涵. 环境因子对青云山自然保护区森林群落物种分布的影响[J]. 生态学杂志, 2019, 38(12):3642-3650. doi: 10.13292/j.1000-4890.201912.015
CHEN Xiaoxi, YANG Xindong, ZENG Xianxin, CHEN Liubao, XIE Chonglin, HUANG Jiuxiang, WU Jianhui, LI Yide, XU Han. Influences of environmental factors on species distribution in forest community in Wengyuan Qingyunshang Nature Reserve, Guangdong[J]. Chinese Journal of Ecology, 2019, 38(12):3642-3650. doi: 10.13292/j.1000-4890.201912.015
[25] 董世魁, 汤琳, 张相锋, 刘世梁, 刘全儒, 苏旭坤, 张勇, 武晓宇, 赵珍珍, 李钰, 沙威. 高寒草地植物物种多样性与功能多样性的关系[J]. 生态学报, 2017, 37(5):1472-1483.
DONG Shikui, TANG Lin, ZHANG Xiangfeng, LIU Shiliang, LIU Quanru, SU Xunkun, ZHANG Yong, WU Xiaoyu, ZHAO Zhenzhen, LI Yu, SHA Wei. Relationship between plant species diversity and functional diversity in alpine grasslands[J]. Acta Ecocogica Sinica, 2017, 37(5):1472-1483.
[26] 李杰, 乌仁其其格, 黄振艳. 呼伦贝尔草甸草原不同退化程度草地群落物种组成特征分析[J]. 广东农业科学, 2013, 40(18):139-143,180. doi: 10.3969/j.issn.1004-874X.2013.18.047
LI Jie, WUREN Qiqige, HUANG Zhenyan. Analysis on characteristic of plant community species composition under different degenerayion degree grassland in the meadow steppe of Hulunbuir[J]. Guangdong Agricultural Sciences, 2013, 40(18):139-143,180. doi: 10.3969/j.issn.1004-874X.2013.18.047
[27] 唐志尧, 方精云. 植物物种多样性的垂直分布格局[J]. 生物多样性, 2004, 12(1):20-28.
TANG Zhiyao, FANG Jingyun. A review on the elevational patterns plant species diversity[J]. Biodiversity Science, 2004, 12(1):20-28.
[28] 周运超, 王世杰, 卢红梅. 喀斯特石漠化过程中土壤的空间分布[J]. 地球与环境, 2010, 38(1):1-7. doi: 10.14050/j.cnki.1672-9250.2010.01.006
ZHOU Yunchao, WANG Shijie, LU Hongmei. Spatial distribution of soils during the process of karst rocky desertification[J]. Earth and Environment, 2010, 38(1):1-7. doi: 10.14050/j.cnki.1672-9250.2010.01.006
[29] 农友, 卢立华, 贾宏炎, 雷丽群, 明安刚, 李华, 王亚南, 韦菊玲. 桂西南岩溶区不同恢复模式群落生物量及林下植物多样性[J]. 林业科学研究, 2017, 30(2):200-205. doi: 10.13275/j.cnki.lykxyj.2017.02.003
NONG You, LU Lihua, JIA Hongyan, LEI Liqun, MING Angang, LI Hua, WANG Yanan, WEI Juling. Community biomass and understory plant diversity under different vegetation restoration models of karst region in Southwest Guangxi[J]. Forest Research, 2017, 30(2):200-205. doi: 10.13275/j.cnki.lykxyj.2017.02.003
[30] 司彬, 姚小华, 任华东, 李生, 何丙辉. 滇东喀斯特植被恢复演替过程中物种多样性研究[J]. 西南大学学报(自然科学版), 2009, 31(1):132-139. doi: 10.13718/j.cnki.xdzk.2009.01.001
SI Bin, YAO Xiaohua, REN Huadong, LI Sheng, HE Binghui. Species diversity in the process of vegetation succession in the karst area in eastern Yunnan[J]. Journal of Southwest University (Natural science edition), 2009, 31(1):132-139. doi: 10.13718/j.cnki.xdzk.2009.01.001
[31] 齐代华. 九寨沟水生植物物种多样性及其环境关系研究[D]. 重庆: 西南大学, 2007
QI Daihua. Species diversity of aquatic plant and its correlation with environment in Jiuzhaigou[D]. Chongqing: Southwest University, 2007.
[32] 隋媛媛, 杜峰, 张兴昌. 黄土丘陵区撂荒群落土壤速效养分空间变异性研究[J]. 草业学报, 2011, 20(2):76-84. doi: 10.11686/cyxb20110209
SUI Yuanyuan, DU Feng, ZHANG Xingchang. Spatial heterogeneity of available soil nutrients in abandoned olefield communities in the loess Hilly Region[J]. Acta Pran Aculturae Sinica, 2011, 20(2):76-84. doi: 10.11686/cyxb20110209
[33] Hinsinger P. Bioavailability of soil inorganic P in the rhizosphere as affected by root-induced chemical changes: A review[J]. Plant & Soil, 2001, 237(2):179.
[34] 潘攀, 王长庭, 胡雷, 刘斯莉, 李洁. 植物群落和土壤对人工草地恢复演替的协同响应[J]. 生态环境学报, 2020, 29(12):2355-2364. doi: 10.16258/j.cnki.1674-5906.2020.12.006
PAN Pan, WANG Changting, HU Lei, LIU Sili, LI Jie. The synergetic responses of plant community and soil to the restorative succession of cultivated grassland[J]. Ecology and Environmental Sciences, 2020, 29(12):2355-2364. doi: 10.16258/j.cnki.1674-5906.2020.12.006
[35] 高英志, 韩兴国, 汪诗平. 放牧对草原土壤的影响[J]. 生态学报, 2004, 24(4):791-797. doi: 10.3321/j.issn:1000-0933.2004.04.021
GAO Yingzhi, HAN Xingguo, WANG Shiping. The effects grazing on grassland soils[J]. Acta Ecocogica Sinica, 2004, 24(4):791-797. doi: 10.3321/j.issn:1000-0933.2004.04.021
[36] 嘎玛达尔基, 杨泽, 谭星儒, 王珊珊, 李伟晶, 游翠海, 王彦兵, 张兵伟, 任婷婷, 陈世苹. 凋落物输入变化和氮添加对半干旱草原群落生产力及功能群组成的影响[J]. 植物生态学报, 2020, 44(8):791-806. doi: 10.17521/cjpe.2020.0126
GAMADAERJI, YANG Ze, TANG Xingru, WANG Shanshan, LI Weijing, YOU Cuihai, WANG Yanbing, ZHANG Bingwei, REN Tingting, CHEN Shiping. Effect of altered litter input and nitrogen addition on ecosystem aboveground primary productivity and plant functional group composition in a semiarid grassland[J]. Chinese Journal of Plant Ecology, 2020, 44(8):791-806. doi: 10.17521/cjpe.2020.0126
[37] 徐洪雨, 王英宇, 宋桂龙, 韩烈保. 华北土石山区公路边坡常见植物根系地下分布特征[J]. 中国水土保持科学, 2013, 11(2):51-58. doi: 10.3969/j.issn.1672-3007.2013.02.009
XU Hongyu, WANG Yingyu, SONG Guilong, HAN Liebao. Characteristics of root system distribution of common plants on freeway slopes in earthy-rocky mountain area of North China[J]. Science of Soil and Water Conservation, 2013, 11(2):51-58. doi: 10.3969/j.issn.1672-3007.2013.02.009
[38] 徐远杰, 陈亚宁, 李卫红, 付爱红, 马晓东, 桂东伟, 陈亚鹏. 伊犁河谷山地植物群落物种多样性分布格局及环境解释[J]. 植物生态学报, 2010, 34(10):1142-1154. doi: 10.3773/j.issn.1005-264x.2010.10.003
XU Yuanjie, CHEN Yaning, LI Weihong, FU Aihong, MA Xiaodong, GUI Dongwei, CHEN Yapeng. Distribution pattern and environmental interpretation of plant species diversity in the mountainous region of Ili River Valley, Xinjiang, China[J]. Chinese Journal of Plant Ecocogy, 2010, 34(10):1142-1154. doi: 10.3773/j.issn.1005-264x.2010.10.003
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