生态环境学报 ›› 2023, Vol. 32 ›› Issue (8): 1525-1536.DOI: 10.16258/j.cnki.1674-5906.2023.08.018
• 研究论文【环境科学】 •
上一篇
姚林杰1,2(), 张佳宁1,2, 张恒瑞1,2, 赵艳云1,2, 张庆1,2,3, 李元恒4,5,*(
)
收稿日期:
2022-07-28
出版日期:
2023-08-18
发布日期:
2023-11-08
通讯作者:
*李元恒。E-mail: nmglyh@hotmail.com作者简介:
姚林杰(1996生),女,硕士研究生,研究方向为景观生态学。E-mail: 245969390@qq.com
基金资助:
YAO Linjie1,2(), ZHANG Jianing1,2, ZHANG Hengrui1,2, ZHAO Yanyun1,2, ZHANG Qing1,2,3, LI Yuanheng4,5,*(
)
Received:
2022-07-28
Online:
2023-08-18
Published:
2023-11-08
摘要:
内蒙古自治区作为中国北方重要的生态安全屏障,其重要性不言而喻。精准掌握内蒙古自治区自然资本利用状况是其可持续发展的基础,有利于提升绿色发展水平,构建绿色特色优势现代产业体系,促进生态保护与经济建设协调发展。生态足迹模型是一种广泛应用于判别可持续发展程度的重要方法。该文在行政单元内部开展生态足迹研究,进一步明确生态足迹空间异质性,为开展更为精准细致的工作提供有力支持。基于净初级生产力构建了内蒙古12个盟市均衡因子和产量因子,采用生态足迹模型对内蒙古1990-2020年每隔5年共7个时期的自然资本进行核算;并结合相应年份人口空间分布公里网格数据集对其生态足迹、生态承载力、生态赤字/盈余进行空间化显示;最后采用区域土地可持续利用指数分析内蒙古土地可持续利用程度。结果表明:内蒙古6种地类中,林地均衡因子最高,呼伦贝尔市各地类的产量因子均高于内蒙古其他区域。内蒙古生态承载力呈现先下降后小幅上升趋势,生态足迹呈现上升趋势,并在1995-2000年由生态盈余转为生态赤字。内蒙古生态赤字面积由9.1%上升至51%,并具有明显的空间异质性。生态赤字主要集中在呼和浩特市、包头市、鄂尔多斯市、通辽市的市区。内蒙古区域土地可持续利用指数由0.67降至0.15,由轻度可持续状态转变为强不可续状态,可持续利用程度较低的区域集中于工业化、城市化等发展较快的地区。该研究可以为实现高质量可持续发展提供依据,为推动生态文明建设提供科学指导。
中图分类号:
姚林杰, 张佳宁, 张恒瑞, 赵艳云, 张庆, 李元恒. 基于生态足迹的内蒙古自然资源可持续利用分析[J]. 生态环境学报, 2023, 32(8): 1525-1536.
YAO Linjie, ZHANG Jianing, ZHANG Hengrui, ZHAO Yanyun, ZHANG Qing, LI Yuanheng. Sustainable Utilization of Natural Resources in Inner Mongolia Based on Ecological Footprint[J]. Ecology and Environment, 2023, 32(8): 1525-1536.
可持续性大类 | 可持续性亚类 | 取值区间 |
---|---|---|
可持续性 | 极强可续性 | 0.9<LUSC<1 |
强可续性 | 0.8<LUSC≤0.9 | |
中度可持续性 | 0.7<LUSC≤0.8 | |
轻度可持续性 | 0.6<LUSC≤0.7 | |
临界状态 | 可持续→不可持续性临界状态 | 0.5<LUSC≤0.6 |
不可持续→可持续性临界状态 | 0.4<LUSC≤0.5 | |
不可持续性 | 轻度不可续性 | 0.3<LUSC≤0.4 |
中度不可续性 | 0.2<LUSC≤0.3 | |
强不可续性 | 0.1<LUSC≤0.2 | |
极强不可续性 | 0<LUSC≤0.1 |
表1 区域土地利用可持续性的评价标准
Table 1 Evaluation standard of land use sustainability
可持续性大类 | 可持续性亚类 | 取值区间 |
---|---|---|
可持续性 | 极强可续性 | 0.9<LUSC<1 |
强可续性 | 0.8<LUSC≤0.9 | |
中度可持续性 | 0.7<LUSC≤0.8 | |
轻度可持续性 | 0.6<LUSC≤0.7 | |
临界状态 | 可持续→不可持续性临界状态 | 0.5<LUSC≤0.6 |
不可持续→可持续性临界状态 | 0.4<LUSC≤0.5 | |
不可持续性 | 轻度不可续性 | 0.3<LUSC≤0.4 |
中度不可续性 | 0.2<LUSC≤0.3 | |
强不可续性 | 0.1<LUSC≤0.2 | |
极强不可续性 | 0<LUSC≤0.1 |
盟市/土地利用类型 | 耕地 | 林地 | 草地 | 水体 | 建设用地 | 化石能源用地 | 平均值 | 变异系数 |
---|---|---|---|---|---|---|---|---|
呼和浩特市 | 0.996 | 1.143 | 0947 | 0.95 | 0.996 | 1.143 | 1.029 | 0.080 |
包头市 | 1.375 | 1.393 | 0.875 | 1.023 | 1.375 | 1.393 | 1.239 | 0.169 |
呼伦贝尔市 | 0.903 | 1.166 | 0.817 | 0.695 | 0.903 | 1.166 | 0.942 | 0.184 |
兴安盟 | 0.798 | 1.229 | 0.965 | 0.73 | 0.798 | 1.229 | 0.958 | 0.213 |
通辽市 | 1.024 | 1.153 | 0.957 | 0.953 | 1.024 | 1.153 | 1.044 | 0.079 |
赤峰市 | 0.951 | 1.261 | 0.953 | 0.887 | 0.951 | 1.261 | 1.044 | 0.149 |
锡林郭勒盟 | 1.486 | 1.862 | 0.97 | 0.815 | 1.486 | 1.862 | 1.414 | 0.284 |
乌兰察布市 | 1.201 | 1.619 | 0.859 | 1.019 | 1.201 | 1.619 | 1.253 | 0.227 |
鄂尔多斯市 | 1.223 | 1.212 | 0.972 | 0.985 | 1.223 | 1.212 | 1.138 | 0.099 |
巴彦淖尔市 | 1.374 | 1.159 | 0.858 | 0.938 | 1.374 | 1.159 | 1.143 | 0.172 |
乌海市 | 1.236 | 1.409 | 0.936 | 1.124 | 1.236 | 1.409 | 1.225 | 0.134 |
阿拉善盟 | 1.094 | 1.189 | 0.97 | 0.632 | 1.094 | 1.189 | 1.028 | 0.187 |
表2 内蒙古各盟市不同土地类型均衡因子
Table 2 Equilibrium factors of different land types in all leagues and cities in Inner Mongolia
盟市/土地利用类型 | 耕地 | 林地 | 草地 | 水体 | 建设用地 | 化石能源用地 | 平均值 | 变异系数 |
---|---|---|---|---|---|---|---|---|
呼和浩特市 | 0.996 | 1.143 | 0947 | 0.95 | 0.996 | 1.143 | 1.029 | 0.080 |
包头市 | 1.375 | 1.393 | 0.875 | 1.023 | 1.375 | 1.393 | 1.239 | 0.169 |
呼伦贝尔市 | 0.903 | 1.166 | 0.817 | 0.695 | 0.903 | 1.166 | 0.942 | 0.184 |
兴安盟 | 0.798 | 1.229 | 0.965 | 0.73 | 0.798 | 1.229 | 0.958 | 0.213 |
通辽市 | 1.024 | 1.153 | 0.957 | 0.953 | 1.024 | 1.153 | 1.044 | 0.079 |
赤峰市 | 0.951 | 1.261 | 0.953 | 0.887 | 0.951 | 1.261 | 1.044 | 0.149 |
锡林郭勒盟 | 1.486 | 1.862 | 0.97 | 0.815 | 1.486 | 1.862 | 1.414 | 0.284 |
乌兰察布市 | 1.201 | 1.619 | 0.859 | 1.019 | 1.201 | 1.619 | 1.253 | 0.227 |
鄂尔多斯市 | 1.223 | 1.212 | 0.972 | 0.985 | 1.223 | 1.212 | 1.138 | 0.099 |
巴彦淖尔市 | 1.374 | 1.159 | 0.858 | 0.938 | 1.374 | 1.159 | 1.143 | 0.172 |
乌海市 | 1.236 | 1.409 | 0.936 | 1.124 | 1.236 | 1.409 | 1.225 | 0.134 |
阿拉善盟 | 1.094 | 1.189 | 0.97 | 0.632 | 1.094 | 1.189 | 1.028 | 0.187 |
盟市/土地利用类型 | 耕地 | 林地 | 草地 | 水体 | 建设 用地 | 化石能源用地 |
---|---|---|---|---|---|---|
呼和浩特市 | 0.865 | 0.686 | 0.952 | 1.079 | 0.865 | 0 |
包头市 | 0.668 | 0.396 | 0.509 | 0.692 | 0.668 | 0 |
呼伦贝尔市 | 1.423 | 1.084 | 1.55 | 1.534 | 1.423 | 0 |
兴安盟 | 1.042 | 0.948 | 1.516 | 1.333 | 1.042 | 0 |
通辽市 | 0.999 | 0.665 | 1.125 | 1.302 | 0.999 | 0 |
赤峰市 | 0.977 | 0.766 | 1.177 | 1.273 | 0.977 | 0 |
锡林郭勒盟 | 1.048 | 0.776 | 0.823 | 0.803 | 1.048 | 0 |
乌兰察布市 | 0.854 | 0.677 | 0.735 | 1.011 | 0.854 | 0 |
鄂尔多斯市 | 0.604 | 0.355 | 0.578 | 0.678 | 0.604 | 0 |
巴彦淖尔市 | 0.636 | 0.316 | 0.476 | 0.605 | 0.636 | 0 |
乌海市 | 0.368 | 0.245 | 0.336 | 0.467 | 0.368 | 0 |
阿拉善盟 | 0.484 | 0.311 | 0.488 | 0.445 | 0.484 | 0 |
平均值 | 0.831 | 0.602 | 0.856 | 0.935 | 0.831 | 0 |
变异系数 | 0.338 | 0.435 | 0.461 | 0.379 | 0.338 | 0 |
表3 内蒙古各盟市6种土地类型产量因子
Table 3 Yield factors of different land types in all leagues and cities in Inner Mongolia
盟市/土地利用类型 | 耕地 | 林地 | 草地 | 水体 | 建设 用地 | 化石能源用地 |
---|---|---|---|---|---|---|
呼和浩特市 | 0.865 | 0.686 | 0.952 | 1.079 | 0.865 | 0 |
包头市 | 0.668 | 0.396 | 0.509 | 0.692 | 0.668 | 0 |
呼伦贝尔市 | 1.423 | 1.084 | 1.55 | 1.534 | 1.423 | 0 |
兴安盟 | 1.042 | 0.948 | 1.516 | 1.333 | 1.042 | 0 |
通辽市 | 0.999 | 0.665 | 1.125 | 1.302 | 0.999 | 0 |
赤峰市 | 0.977 | 0.766 | 1.177 | 1.273 | 0.977 | 0 |
锡林郭勒盟 | 1.048 | 0.776 | 0.823 | 0.803 | 1.048 | 0 |
乌兰察布市 | 0.854 | 0.677 | 0.735 | 1.011 | 0.854 | 0 |
鄂尔多斯市 | 0.604 | 0.355 | 0.578 | 0.678 | 0.604 | 0 |
巴彦淖尔市 | 0.636 | 0.316 | 0.476 | 0.605 | 0.636 | 0 |
乌海市 | 0.368 | 0.245 | 0.336 | 0.467 | 0.368 | 0 |
阿拉善盟 | 0.484 | 0.311 | 0.488 | 0.445 | 0.484 | 0 |
平均值 | 0.831 | 0.602 | 0.856 | 0.935 | 0.831 | 0 |
变异系数 | 0.338 | 0.435 | 0.461 | 0.379 | 0.338 | 0 |
图2 内蒙古1990-2020年人均生态承载力、人均生态足迹、人均生态赤字/盈余变化趋势
Figure 2 Trends of per capita ecological carrying capacity, per capita ecological footprint, and per capita ecological deficit/surplus in Inner Mongolia from 1990 to 2020
图3 内蒙古1990-2020年生态承载力、生态足迹、生态赤字(盈余)空间分布图
Figure 3 Spatial distribution of ecological carrying capacity, ecological footprint and ecological deficit in Inner Mongolia from 1990 to 2020
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