Scientia Agricultura Sinica ›› 2020, Vol. 53 ›› Issue (13): 2573-2583.doi: 10.3864/j.issn.0578-1752.2020.13.006

• PROCESS AND MECHANISM OF TEMPERATE MEADOW STEPPE DEGRADATION • Previous Articles     Next Articles

Effects of Mowing Disturbance on Grassland Plant Functional Groups and Diversity in Leymus chinensis Meadow Steppe

YAN RuiRui1,ZHANG Yu1,XIN XiaoPing1(),WEI ZhiJun2,Wuren qiqige3,GUO MeiLan4   

  1. 1Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences/Hulunber Grassland Ecosystem Research Station, Beijing 100081
    2 College of Grassland and Resources Environmental, Inner Mongolia Agricultural University, Hohhot 010019
    3Hulunber College/Inner Mongolia Autonomous Region Key Laboratory of Meadow Grassland Ecosystem and Global Change, Hailar 021008, Inner Mongolia
    4School of Life Sciences, Jining Teachers College, Wulanchabu 012000, Inner Mongolia
  • Received:2019-09-07 Accepted:2019-12-20 Online:2020-07-01 Published:2020-07-16
  • Contact: XiaoPing XIN E-mail:xinxiaoping@caas.cn

Abstract:

【Objective】 Mowing is one of the main utilization methods of grassland, and plant functional groups and community species diversity are important ecological indicators for evaluating the degradation of grassland ecosystem under interference conditions. The plant functional groups and diversity in Leymus chinensis meadow grassland under different mowing were studied to understand the change process and mechanism of grassland functional groups and diversity, so as to provide a theoretical basis for ecological restoration of degraded mowing grassland. 【Method】 Taking the Hulunber Leymus chinensis meadow steppe as the experimental platform, the community vegetation was investigated by the sample method in the season with the most vigorous plant growth from 2014 to 2018 (early August of every year). The changes of community function groups and species diversity, as well as the interaction between different cutting time and cutting treatments, were analyzed under the conditions of annual cutting (G1), biennial cutting (G2), missed cutting 10 m (G3), missed cutting 10 m (G4) and control (CK), and the correlation between plant function groups and community species diversity was discussed. 【Result】 It was found that Leymus chinensis was the dominant species under different cutting systems, but with the increase of cutting frequency, the important value of Leymus chinensis decreased gradually, and the important value of the degraded indicator species such as Potentilla acaulis and Thermopsis lanceolate increased. The important values of leymus chinensis, Cleistogenes squarrosa, Adenophora stenanthina, Bupleurum scorzonerifolium and Poa ratensis were higher than those of other treatments. The proportion of important values of gramineae and leguminous plants decreased under annual and perennial mowing treatment, and the proportion of compositae and sedge plants increased, which were mostly degraded plants. After mowing treatment for 5 years, the species diversity index of plant communities under different mowing systems increased, among which shannon-wiener diversity index and Simpson dominance index increased significantly under the treatment of 10 m of mowed zone. The change trend of evenness index of 5 mowed treatments was different, among which, the evenness of community of G3 and G4 treated grassland showed an increasing trend, increasing by 16% and 5.8%, respectively. The evenness index under G1, G2 and CK grassland decreased, among which G1 decreased the most (by 1.8%), followed by CK (by 1.6%), and G2 grassland decreased the least. According to the change analysis of plant community species diversity index, it was found that the plant community species diversity was improved after 5 years of different mowing treatments and 10 m of missed mowing treatments. There was a significant negative correlation between community species diversity index and important values of plant functional group of Gramineae, and a significant positive correlation between community species diversity index and important values of Ranunculaceae and Compositae. 【Conclusion】 Long-term and high-frequency mowing would lead to grassland degradation, and long-term non-utilization of grassland would also lead to retrograde succession of grassland. Mowing every two years and a missed cut zone of 10 m could alleviate the decrease of the proportion of dominant plants such as Gramineae in the community and promote the increase of the proportion of Ranunculaceae. After five years of different mowing treatment, the community diversity of mowing treatment with 10 m mowing zone was improved, that is, moderate mowing disturbance to the grassland (two-year mowing and missed cut 10m) was conducive to the sustainable development of the grassland.

Key words: mowing, mowing system, Leymus chinensis meadow steppe, plant functional groups, community species biodiversity

Fig. 1

Monthly precipitation and temperature in 2014-2018 for the experiment plot"

Fig. 2

Test processing specific arrangement"

Table 1

Change of important value of plants in Leymus chinensis meadow steppe under different mowing disturbance"

种名 Species G1 G2 G3 G4 CK
羊草 Leymus chinensis 30.71 36.43 30.98 31.63 30.56
裂叶蒿 Artemisia laciniata 18.14 0.00 7.98 2.90 1.77
蓬子菜 Galium verum 4.86 1.09 5.69 6.22 3.62
长柱沙参 Adenophora stenanthina 4.03 4.76 4.20 5.91 3.13
寸草苔Carex duriuscula 3.70 6.37 3.14 6.33 3.13
披针叶黄华Thermopsis lanceolata 3.40 1.85 6.68 4.37 2.13
展枝唐松草Thalictrum squarrosum 3.16 1.36 6.95 6.81 6.02
羽茅Achnatherum sibiricum 3.12 0.00 2.05 1.33 3.75
洽草Koeleria cristata 2.80 1.16 5.59 0.68 0.45
柴胡Bupleurum scorzonerifolium 2.60 7.59 4.13 6.26 4.83
山葱Veratrum nigrum 2.42 0.00 0.00 0.00 4.37
山韭Allium thunbergii 2.37 0.00 0.00 0.00 0.65
广布野豌豆Vicia cracca 2.37 1.17 0.48 0.79 1.00
无芒雀麦Bromus inermis 1.79 0.81 1.47 0.00 0.00
贝加尔针茅Stipa baicalensis 1.63 1.37 1.53 0.00 2.19
线叶菊Filifolium sibiricum 1.56 0.00 0.00 0.00 0.00
山野豌豆Vicia amoena 1.32 0.92 3.49 1.32 0.58
扁蓿豆Medicago falcata 1.13 0.00 0.87 3.02 0.77
狗舌草Tephroseris kirilowii 1.10 0.39 0.00 1.15 0.00
石竹Dianthus chinensis 1.09 0.00 1.24 0.00 7.55
细叶白头翁Pulsatilla turczaninovii 1.03 8.70 0.00 0.00 0.79
二裂委陵菜Potentilla bifurca 1.01 6.28 1.32 3.47 3.59
苦荬菜Ixeris polycephala 0.92 0.62 0.00 0.00 1.14
防风Saposhnikovia divaricata 0.86 0.00 0.33 0.40 1.11
地榆Sanguisorba officinalis 0.75 0.00 1.82 0.37 4.54
早熟禾Poa sphondylodes 0.70 2.51 2.70 2.92 1.54
双齿葱Allium bidentatum 0.55 2.05 0.47 0.73 0.21
野韭Allium ramosum 0.43 0.00 0.00 0.42 0.66
飞蓬Erigeron acer 0.42 1.25 0.00 1.99 0.60
糙隐子草Cleistogenes squarrosa 0.00 2.82 0.88 1.56 0.52
细叶韭Allium tenuissimum 0.00 2.23 0.40 1.11 0.63
鸦葱Scorzonera austriaca 0.00 1.99 0.00 0.88 0.78
多裂叶荆芥Schizonepeta multifida 0.00 1.31 0.00 0.00 0.26
细叶百合Lilium pumilum 0.00 1.13 0.00 0.00 0.00
黄蒿Artemisia scoparia 0.00 1.00 3.18 0.00 1.17
柳穿榆Linaria vulgaris 0.00 0.79 0.39 0.00 1.14
驴蹄草Caltha palustris 0.00 0.24 0.00 0.98 0.00
狭叶青蒿Artemisia dracunculus 0.00 0.00 1.68 3.01 0.98
星毛委陵菜Potentilla acaulis 0.00 0.00 0.36 1.65 0.00
红茎委陵菜Potentilla nudicaulis 0.00 0.00 0.00 1.42 0.00
囊花鸢尾Iris ventricosa 0.00 0.00 0.00 0.00 1.03
东北大戟Euphorbia manschurica 0.00 0.00 0.00 0.00 0.52
山柳菊Hieracium krameri 0.00 0.00 0.00 0.00 0.00

Table 2

Interactive analysis of important values of plant functional groups in Leymus chinensis meadow steppe under mowing disturbance"

功能群Function 影响因素 Factor F 显著性Sig.
禾本科Gramineae 年际Interannual 9.309 <0.001***
处理Treatment 3.681 0.011*
年际×处理Interannual×Treatment 1.504 0.136
豆科Leguminosae 年际Interannual 7.342 <0.001***
处理Treatment 1.01 0.412
年际×处理Interannual×Treatment 1.758 0.066
毛茛科Ranunculaceae 年际Interannual 2.258 0.076
处理Treatment 1.857 0.133
年际×处理Interannual×Treatment 1.254 0.263
菊科Asteraeeae 年际Interannual 1.093 0.370
处理Treatment 0.821 0.518
年际×处理Interannual×Treatment 0.991 0.481
莎草科Cyperaceae 年际Interannual 5.933 <0.001***
处理Treatment 1.098 0.368
年际×处理Interannual×Treatment 2.242 0.015*
其他科Other family 年际Interannual 5.134 0.002**
处理Treatment 0.819 0.519
年际×处理Interannual×Treatment 0.735 0.745

Fig. 3

Interannual variation of vegetation functional group structure under different castration treatments"

Fig. 4

Interannual variation of community species diversity under different castration treatments Different capital letters indicate significant difference of diversity index under different treatments (P<0.05), while lowercase letters indicate significant difference of diversity index between different years (P<0.05)"

Table 3

Correlation between plant functional groups and community species biodiversity"

因子
Factor
丰富度指数
Margarlef index
多样性指数
Shannon-
Wiener index
优势度指数
Simpson index
均匀度指数
Pielou index
禾本科
Poaceae
豆科
Leguminosae
毛茛科
Ranunculaceae
菊科
Asteraceae
莎草科
Cyperaceae
杂草类
Broadleaved herb
丰富度指数
Margarlef index
1 0.853** 0.659** 0.27 -0.661** -0.131 0.540** 0.298 0.115 0.689**
多样性指数
Shannon-Wiener
index
1 0.925** 0.714** -0.841** -0.036 0.668** 0.466* 0.138 0.679**
优势度指数
Simpson index
1 0.849** -0.875** 0.113 0.670** 0.504* 0.093 0.603**
均匀度指数
pielou index
1 -0.657** 0.256 0.572** 0.393 -0.029 0.322
禾本科Poaceae 1 -0.027 -0.562** -0.668** -0.272 -0.672**
豆科Leguminosae 1 -0.062 -0.133 -0.628** -0.148
毛茛科
Ranunculaceae
1 0.18 0.04 0.322
菊科Asteraceae 1 0.152 0.166
莎草科
Cyperaceae
1 0.091
杂草类
Broadleaved herb
1
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