宁夏水土保持生态补偿优先区识别

doi:10.13866/j.azr.2023.09.16

干旱区研究 ›› 2023, Vol. 40 ›› Issue (9): 1527-1536.doi: 10.13866/j.azr.2023.09.16

• 生态与环境 • 上一篇

宁夏水土保持生态补偿优先区识别

申草¹(),任宗萍¹(),李鹏¹,王凯博²,鲁克新¹,任正龑³,魏小燕³

1.西安理工大学省部共建西北旱区生态水利国家重点实验室，陕西西安 710054
2.中国科学院地球环境研究所，陕西西安 710061
3.宁夏回族自治区水土保持检测总站，宁夏银川 750000

收稿日期:2023-04-03 修回日期:2023-06-05 出版日期:2023-09-15 发布日期:2023-09-28
通讯作者: 任宗萍
作者简介:申草（1997-），女，硕士研究生，主要研究方向为水土保持与荒漠化防治. E-mail: 1342152765@qq.com
基金资助:
国家自然科学基金项目(42077074);宁夏流域水土保持生态—经济协同治理技术与发展模式研究(GZ4-21-05-069/-ZC-F)

Identification of priority areas for ecological compensation under soil and water conservation in Ningxia

SHEN Cao¹(),REN Zongping¹(),LI Peng¹,WANG Kaibo²,LU Kexin¹,REN Zhengyan³,WEI Xiaoyan³

1. State Key Laboratory of Eco-hydraulics in Northwest Arid Region of China, Xi’an University of Technology, Xi’an 710054, Shaanxi, China
2. Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, Shaanxi, China
3. Soil and Water Conservation Monitoring Station, Ningxia Hui Autonomous Region, Yinchuan 750000, Ningxia, China

Received:2023-04-03 Revised:2023-06-05 Online:2023-09-15 Published:2023-09-28
Contact: Zongping REN

摘要/Abstract

摘要：

水土保持服务功能下的生态补偿优先区识别的研究，对建立适宜当地生态发展的水土保持生态补偿体系具有重要参考意义。以宁夏为研究区，运用InVEST模型评估水源涵养、土壤保持和碳储存三项主要水土保持服务功能，并进行价值化表达；综合考虑各区县生态补偿优先级和生态脆弱性指数，对全区水土保持生态补偿优先区进行空间识别。研究表明：2000年、2010年、2020年宁夏水土保持价值分别为2478.9×10⁸元、2661.7×10⁸元、2958.5×10⁸元，总体呈现不断增长趋势；在空间上呈现南高北低的空间分布特征，其最高值位于泾源县，最低值位于金凤区；全区20 a来水土保持优先补偿区动态变化差异较小，补偿优先区主要位于生态价值高、经济落后的南部地区，而生态补偿次级优先区则位于中部和北部生态价值较低、经济水平较高区域。对生态补偿优先区进行补偿能够有效提高生态补偿的效率，促进区域生态环境和经济社会可持续发展。

关键词: 生态服务价值, 生态补偿优先区, 水土保持, InVEST模型

Abstract:

Identifying priority areas for ecological compensation under soil and water conservation is an important reference for establishing a suitable compensation system to support local ecological development. In this study, the Ningxia Hui Autonomous Region is taken as the study area, and the InVEST model is employed to evaluate three major soil and water conservation service functions: water connotation, soil conservation, and carbon storage. Their respective value amounts were assessed. Additionally, the ecological compensation priority and ecological vulnerability index of each district and county are considered to conduct a spatial identification of priority areas for ecological compensation for soil and water conservation in Ningxia. Research has shown that the value of soil and water conservation in Ningxia has steadily increased each decade from 2000 to 2020, reaching 247.89 billion yuan, 266.17 billion yuan, and 295.85 billion yuan, respectively. Geographically, the southern regions generally exhibit higher values, whereas the northern regions show lower values, with Jingyuan County, Guyuan City, and Jinfeng District, Yinchuan City, representing the highest, and lowest values, respectively. Over the years, the priority compensation areas for soil and water conservation have experienced relatively minor changes. These areas are mainly located in the southern regions, characterized by high ecological value but economic backwardness. The secondary priority areas for ecological compensation are located in the central and northern regions, characterized by low ecological value but high economic development. Compensating these priority areas can effectively improve the efficiency of ecological compensation, foster the regional ecological environment, and promote sustainable economic, and social development.

Key words: ecological service value, ecological compensation priority zone, soil and water conservation, InVEST model

申草,任宗萍,李鹏,王凯博,鲁克新,任正龑,魏小燕. 宁夏水土保持生态补偿优先区识别[J]. 干旱区研究, 2023, 40(9): 1527-1536.

SHEN Cao,REN Zongping,LI Peng,WANG Kaibo,LU Kexin,REN Zhengyan,WEI Xiaoyan. Identification of priority areas for ecological compensation under soil and water conservation in Ningxia[J]. Arid Zone Research, 2023, 40(9): 1527-1536.

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评价分数	1级区	2级区	3级区
强脆弱性	5	4	3
弱脆弱性	4	3	2

分目标层	本层权重	准则层	本层权重	指标层	指标说明
生态压力度	0.14	人口活动压力	0.4	人口密度	正向指标
生态压力度	0.14	经济活动压力	0.6	地均GDP	负向指标
生态敏感性	0.62	地形因子	0.2	高程	正向指标
				坡度	正向指标
				地形起伏度	正向指标
		气象因子	0.1	降雨侵蚀力	正向指标
				年均气温	负向指标
				年均相对湿度	负向指标
		地表因子	0.1	植被覆盖率	负向指标
		土壤因子	0.5	土壤侵蚀强度	正向指标
生态恢复力	0.24	景观结构	0.2	景观多样性指数	负向指标
		功能	0.5	土壤有机质	正向指标
		生态环境质量	0.3	生物丰度	负向指标

地区	2000年		2010年		2020年
地区	水保价值 /(10⁴元·km^-2)	GDP/(10⁴元·km^-2)	水保价值 /(10⁴元·km^-2)	GDP/(10⁴元·km^-2)	水保价值 /(10⁴元·km^-2)	GDP /(10⁴元·km^-2)
泾源县	2293.5	13.9	2452.9	64.5	2480.6	183.8
海原县	635.6	8.4	665.6	43.8	842.5	152.6
彭阳县	1133.5	10.2	1253.8	73.7	1194.0	253.3
西吉县	1081.4	12.2	1200.9	82.8	963.4	223.3
隆德县	1888.3	36.9	2021.2	110.8	1190.4	315.9
同心县	402.7	7.8	424.1	60.2	573.8	207.7
盐池县	229.2	14.6	265.7	41.8	336.5	161.3
原州区	957.0	17.9	1017.1	161.3	1019.4	495.8
红寺堡区	251.8	16.6	255.3	34.9	325.6	301.6
沙坡头区	211.8	25.6	218.6	159.6	324.7	354.5
中宁县	231.3	27.3	229.8	205.5	301.8	523.2
平罗县	218.6	48.8	245.3	393.4	367.7	812.1
贺兰县	171.7	124.0	172.3	449.9	459.3	1158.7
青铜峡市	243.2	83.0	261.1	486.1	232.9	663.0
永宁县	177.2	149.6	181.7	666.2	255.7	1093.2
惠农区	194.2	111.4	189.5	390.9	343.8	1473.2
利通区	197.6	153.2	245.0	955.0	235.1	1055.7
大武口区	258.2	247.8	287.2	1278.7	406.0	1968.7
西夏区	174.8	34.8	181.9	531.6	550.5	3590.9
灵武市	258.0	449.4	272.9	1638.6	201.1	1748.6
兴庆区	150.1	307.8	154.2	3805.1	199.3	8244.0
金凤区	160.2	484.3	138.7	4759.2	209.3	10489.3

生态补偿区划	补偿面积/（km²）	补偿面积占比/%	水土保持价值/10⁸元	水土保持价值占比/%	GDP占比/%	水土流失面积占比/%
优先补偿区	23726	0.46	1892.2	0.64	0.12	0.71
次级补偿区	8132	0.16	455.5	0.15	0.09	0.15
一般补偿区	10533	0.2	342.2	0.12	0.18	0.08
潜在补偿区	9532	0.18	268.6	0.09	0.61	0.07

宁夏水土保持生态补偿优先区识别

Identification of priority areas for ecological compensation under soil and water conservation in Ningxia

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