Biodiv Sci ›› 2014, Vol. 22 ›› Issue (2): 117-128. DOI: 10.3724/SP.J.1003.2014.13130
• Orginal Article • Previous Articles Next Articles
Sarula Kang1, Qing Zhang1, Jianming Niu1,2,*(), Jianjun Dong1, Wenjing Ma1, Xin Li2,3, Changming Chang1, Chenwei Shang1
Received:
2013-05-28
Accepted:
2013-12-20
Online:
2014-03-20
Published:
2014-04-03
Contact:
Niu Jianming
Sarula Kang,Qing Zhang,Jianming Niu,Jianjun Dong,Wenjing Ma,Xin Li,Changming Chang,Chenwei Shang. Effect of mining landscape history on local species diversity: a case study of the Yimin open-pit coal mine in Inner Mongolia[J]. Biodiv Sci, 2014, 22(2): 117-128.
Fig. 2 Distribution of natural vegetation area (marked in gray), reclamation vegetation area (marked in black) and non-vegetation area (marked in dark gray) in one of the study sites (marked in black triangle) on the Yimin open-pit coal mine in Inner Mongolia.
差异显著性检验 Notable difference test | 差异显著性 Significance | |
---|---|---|
物种丰富度(单因素ANOVA) Species richness (One-Way ANOVA ) | 0.000** | |
功能群内丰富度(单样本t检验) Richness of functional groups (One-Sample t test) | 灌木与半灌木 Shrubs and semi-shrubs (SS) | 0.083 |
多年生丛生禾草 Perennial bunchgrasses (PB) | 0.035* | |
多年生根茎禾草 Perennial rhizome grasses (PR) | 0.003** | |
多年生杂类草 Perennial forbs (PF) | 0.000** | |
一二年生草本 Annuals and biennials (AB) | 0.046* |
Table 1 Difference of species diversity among different sites at the Yimin open-pit coal mine in Inner Mongolia
差异显著性检验 Notable difference test | 差异显著性 Significance | |
---|---|---|
物种丰富度(单因素ANOVA) Species richness (One-Way ANOVA ) | 0.000** | |
功能群内丰富度(单样本t检验) Richness of functional groups (One-Sample t test) | 灌木与半灌木 Shrubs and semi-shrubs (SS) | 0.083 |
多年生丛生禾草 Perennial bunchgrasses (PB) | 0.035* | |
多年生根茎禾草 Perennial rhizome grasses (PR) | 0.003** | |
多年生杂类草 Perennial forbs (PF) | 0.000** | |
一二年生草本 Annuals and biennials (AB) | 0.046* |
Fig. 4 Changes of integral index of connectivity (IIC) and probability of connectivity (PC) of all plots and different buffer regions at the Yimin mine in Inner Mongolia during different stages after being exploited.
Fig. 5 Correlation between diversity indices (IIC) and landscape (PC) indices at different time: SR, Species richness; SS, Shrub and semi-shrub; PB, Perennial bunchgrasses; PR, Perennial rhizome grass; PF, Perennial forbs; AB, Annuals and biennials.
Fig. 6 Coefficient of determination between diversity indices and landscape indices change with different buffers (Unit: km): dotted line with circle indicate R2 between diversity and PC; dotted line with prismatic indicate R2 between diversity and IIC; solid line with triangle indicate R2 between diversity and landscape percentage. SR, Species richness; SS, Shrub and semi-shrub; PB, Perennial bunchgrasses; PR, Perennial rhizome grass; PF, Perennial forbs; AB, Annuals and biennials.
景观百分率 vs. 所有物种 LP vs. all species | 景观百分率 vs. 多年生根茎禾草 LP vs. PR | 景观百分率 vs. 多年生杂草 LP vs. PF | 生境连接度 vs. 所有物种 HC vs. all species | 生境连接度 vs. 多年生根茎禾草 HC vs. PR | 生境连接度 vs. 多年生杂草 HC vs. PF | |||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
a | b | c | a | b | c | a | b | c | IIC | PC | IIC | PC | IIC | PC | ||||||
1975_1km | 0.470* | – | –0.470* | NS | – | NS | NS | – | NS | 0.472* | 0.473* | NS | NS | NS | NS | |||||
1975_2km | 0.512** | – | –0.512** | NS | – | NS | 0.510** | – | –0.510** | 0.481* | 0.493* | NS | NS | 0.516** | 0.518** | |||||
1975_3km | 0.580** | – | –0.580** | NS | – | NS | 0.519** | – | –0.519** | 0.530** | 0.555** | NS | NS | 0.520** | NS | |||||
1975_4km | 0.736** | – | –0.736** | NS | – | NS | NS | – | NS | 0.649* | 0.706* | NS | NS | NS | NS | |||||
1975_6km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1975_8km | NS | – | NS | NS | – | NS | NS | – | NS | 0.867** | 0.841** | NS | NS | NS | NS | |||||
1975_10km | NS | – | NS | NS | – | NS | NS | – | NS | 0.660* | 0.687* | NS | NS | NS | NS | |||||
1990_1km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1990_2km | NS | – | NS | NS | – | NS | 0.430* | – | –0.430* | NS | NS | NS | NS | NS | NS | |||||
1990_3km | 0.508** | – | –0.508** | NS | – | NS | 0.466* | – | –0.466* | 0.447* | NS | NS | NS | NS | 0.462* | |||||
1990_4km | 0.690** | – | –0.690** | NS | – | NS | NS | – | NS | NS | 0.638* | NS | NS | NS | NS | |||||
1990_6km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1990_8km | NS | – | NS | NS | – | NS | NS | – | NS | 0.854** | 0.835** | NS | NS | NS | NS | |||||
1990_10km | NS | – | NS | NS | – | NS | NS | – | NS | 0.651* | 0.677* | NS | NS | NS | NS | |||||
2000_1km | NS | NS | NS | 0.481* | NS | –0.440* | NS | NS | NS | NS | NS | 0.530** | 0.535** | NS | NS | |||||
2000_2km | NS | NS | NS | 0.500* | –0.450* | –0.490* | NS | NS | NS | NS | NS | 0.448* | 0.494* | NS | NS | |||||
2000_3km | NS | NS | NS | 0.459* | –0.503* | –.419* | NS | NS | NS | 0.445* | 0.425* | NS | 0.421* | NS | NS | |||||
2000_4km | NS | NS | NS | 0.524** | NS | –0.524** | NS | NS | NS | NS | NS | NS | NS | NS | NS | |||||
2000_6km | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | |||||
2000_8km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.846** | 0.824** | NS | NS | NS | NS | |||||
2000_10km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.647* | 0.674* | NS | NS | NS | NS | |||||
2010_1km | NS | NS | NS | 0.557** | –0.477* | –0.513** | NS | NS | NS | 0.460* | 0.441* | 0.507** | 0.544** | NS | NS | |||||
2010_2km | NS | NS | NS | 0.560** | –0.500* | –0.490* | NS | NS | NS | 0.398* | NS | 0.426* | 0.473* | NS | NS | |||||
2010_3km | NS | NS | NS | 0.474* | –0.498* | –0.415* | NS | NS | NS | 0.464* | NS | NS | 0.402* | NS | NS | |||||
2010_4km | NS | NS | NS | 0.490* | NS | NS | NS | NS | NS | 0.644* | NS | NS | NS | NS | NS | |||||
2010_6km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.699* | 0.633* | NS | NS | NS | NS | |||||
2010_8km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.798** | 0.843** | NS | NS | NS | NS | |||||
2010_10km | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS |
Table 2 Correlation between landscape percentage/habitat connectivity and species richness/species richness of each functional group. The functional groups of without significant correlation with landscape indices were absent in this table (e.g. SS, PB, and AB).
景观百分率 vs. 所有物种 LP vs. all species | 景观百分率 vs. 多年生根茎禾草 LP vs. PR | 景观百分率 vs. 多年生杂草 LP vs. PF | 生境连接度 vs. 所有物种 HC vs. all species | 生境连接度 vs. 多年生根茎禾草 HC vs. PR | 生境连接度 vs. 多年生杂草 HC vs. PF | |||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
a | b | c | a | b | c | a | b | c | IIC | PC | IIC | PC | IIC | PC | ||||||
1975_1km | 0.470* | – | –0.470* | NS | – | NS | NS | – | NS | 0.472* | 0.473* | NS | NS | NS | NS | |||||
1975_2km | 0.512** | – | –0.512** | NS | – | NS | 0.510** | – | –0.510** | 0.481* | 0.493* | NS | NS | 0.516** | 0.518** | |||||
1975_3km | 0.580** | – | –0.580** | NS | – | NS | 0.519** | – | –0.519** | 0.530** | 0.555** | NS | NS | 0.520** | NS | |||||
1975_4km | 0.736** | – | –0.736** | NS | – | NS | NS | – | NS | 0.649* | 0.706* | NS | NS | NS | NS | |||||
1975_6km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1975_8km | NS | – | NS | NS | – | NS | NS | – | NS | 0.867** | 0.841** | NS | NS | NS | NS | |||||
1975_10km | NS | – | NS | NS | – | NS | NS | – | NS | 0.660* | 0.687* | NS | NS | NS | NS | |||||
1990_1km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1990_2km | NS | – | NS | NS | – | NS | 0.430* | – | –0.430* | NS | NS | NS | NS | NS | NS | |||||
1990_3km | 0.508** | – | –0.508** | NS | – | NS | 0.466* | – | –0.466* | 0.447* | NS | NS | NS | NS | 0.462* | |||||
1990_4km | 0.690** | – | –0.690** | NS | – | NS | NS | – | NS | NS | 0.638* | NS | NS | NS | NS | |||||
1990_6km | NS | – | NS | NS | – | NS | NS | – | NS | NS | NS | NS | NS | NS | NS | |||||
1990_8km | NS | – | NS | NS | – | NS | NS | – | NS | 0.854** | 0.835** | NS | NS | NS | NS | |||||
1990_10km | NS | – | NS | NS | – | NS | NS | – | NS | 0.651* | 0.677* | NS | NS | NS | NS | |||||
2000_1km | NS | NS | NS | 0.481* | NS | –0.440* | NS | NS | NS | NS | NS | 0.530** | 0.535** | NS | NS | |||||
2000_2km | NS | NS | NS | 0.500* | –0.450* | –0.490* | NS | NS | NS | NS | NS | 0.448* | 0.494* | NS | NS | |||||
2000_3km | NS | NS | NS | 0.459* | –0.503* | –.419* | NS | NS | NS | 0.445* | 0.425* | NS | 0.421* | NS | NS | |||||
2000_4km | NS | NS | NS | 0.524** | NS | –0.524** | NS | NS | NS | NS | NS | NS | NS | NS | NS | |||||
2000_6km | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | |||||
2000_8km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.846** | 0.824** | NS | NS | NS | NS | |||||
2000_10km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.647* | 0.674* | NS | NS | NS | NS | |||||
2010_1km | NS | NS | NS | 0.557** | –0.477* | –0.513** | NS | NS | NS | 0.460* | 0.441* | 0.507** | 0.544** | NS | NS | |||||
2010_2km | NS | NS | NS | 0.560** | –0.500* | –0.490* | NS | NS | NS | 0.398* | NS | 0.426* | 0.473* | NS | NS | |||||
2010_3km | NS | NS | NS | 0.474* | –0.498* | –0.415* | NS | NS | NS | 0.464* | NS | NS | 0.402* | NS | NS | |||||
2010_4km | NS | NS | NS | 0.490* | NS | NS | NS | NS | NS | 0.644* | NS | NS | NS | NS | NS | |||||
2010_6km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.699* | 0.633* | NS | NS | NS | NS | |||||
2010_8km | NS | NS | NS | NS | NS | NS | NS | NS | NS | 0.798** | 0.843** | NS | NS | NS | NS | |||||
2010_10km | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS | NS |
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