Ecology and Environmental Sciences ›› 2026, Vol. 35 ›› Issue (8): 1221-1233.DOI: 10.16258/j.cnki.1674-5906.2026.08.006
• Research Article [Ecology] • Previous Articles Next Articles
Wang Daoyuan1,2,3(
), Zhao Ning1,2,3,*(
), Liu Pingxin1,2,3, Jiao Guiquan1,2,3, Huang Yuming4, Li Xiaohui1,2,3
Received:2026-03-24
Revised:2026-07-19
Accepted:2026-07-28
Online:2026-08-18
Published:2026-08-17
王道远1,2,3(
), 赵宁1,2,3,*(
), 刘平新1,2,3, 焦桂权1,2,3, 黄聿铭4, 李小慧1,2,3
通讯作者:
E-mail: 作者简介:王道远(1998年生),男,助理工程师,硕士,主要研究方向为生态系统服务与土地利用。E-mail: wdy981006@163.com
基金资助:CLC Number:
Wang Daoyuan, Zhao Ning, Liu Pingxin, Jiao Guiquan, Huang Yuming, Li Xiaohui. Research on the Trade-off and Coordination Characteristics of Ecosystem Services and Zoning Management in the Taihang Mountains[J]. Ecology and Environmental Sciences, 2026, 35(8): 1221-1233.
王道远, 赵宁, 刘平新, 焦桂权, 黄聿铭, 李小慧. 太行山区生态系统服务权衡协同特征及分区管控研究[J]. 生态环境学报, 2026, 35(8): 1221-1233.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2026.08.006
| 土地利用类型 | 面积/km2 | 变化率/% | |||||||
|---|---|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2024年 | 2000-2010年 | 2010-2020年 | 2020-2024年 | 2000-2024年 | ||
| 耕地 | 53137.97 | 49931.94 | 50703.45 | 51383.08 | −6.03% | 1.55% | 1.34% | −3.30% | |
| 林地 | 40857.09 | 43869.20 | 46254.90 | 47634.49 | 7.37% | 5.44% | 2.98% | 16.59% | |
| 草地 | 34987.84 | 33121.39 | 27821.56 | 25258.59 | −5.33% | −16.00% | −9.21% | −27.81% | |
| 水域 | 615.06 | 654.48 | 806.47 | 821.89 | 6.41% | 23.22% | 1.91% | 33.63% | |
| 未利用地 | 11.30 | 9.00 | 6.88 | 8.96 | −20.32% | −23.55% | 30.20% | −20.68% | |
| 建设用地 | 7398.59 | 9421.83 | 11414.58 | 11900.83 | 27.35% | 21.15% | 4.26% | 60.85% | |
Table 1 Area and change of land use types in the Taihang Mountains from 2000 to 2024
| 土地利用类型 | 面积/km2 | 变化率/% | |||||||
|---|---|---|---|---|---|---|---|---|---|
| 2000年 | 2010年 | 2020年 | 2024年 | 2000-2010年 | 2010-2020年 | 2020-2024年 | 2000-2024年 | ||
| 耕地 | 53137.97 | 49931.94 | 50703.45 | 51383.08 | −6.03% | 1.55% | 1.34% | −3.30% | |
| 林地 | 40857.09 | 43869.20 | 46254.90 | 47634.49 | 7.37% | 5.44% | 2.98% | 16.59% | |
| 草地 | 34987.84 | 33121.39 | 27821.56 | 25258.59 | −5.33% | −16.00% | −9.21% | −27.81% | |
| 水域 | 615.06 | 654.48 | 806.47 | 821.89 | 6.41% | 23.22% | 1.91% | 33.63% | |
| 未利用地 | 11.30 | 9.00 | 6.88 | 8.96 | −20.32% | −23.55% | 30.20% | −20.68% | |
| 建设用地 | 7398.59 | 9421.83 | 11414.58 | 11900.83 | 27.35% | 21.15% | 4.26% | 60.85% | |
| 年份与面积 | 2024年面积/km2 | |||||||
|---|---|---|---|---|---|---|---|---|
| 2000年面积/km2 | 土地利用类型 | 草地 | 耕地 | 建设用地 | 林地 | 水域 | 未利用地 | 合计 |
| 草地 | 22024.08 | 5620.69 | 389.92 | 6936.12 | 13.32 | 3.71 | 34987.84 | |
| 耕地 | 2531.27 | 44712.36 | 4096.90 | 1581.93 | 213.41 | 2.11 | 53137.97 | |
| 建设用地 | 0.04 | 18.22 | 7287.85 | 0.19 | 92.20 | 0.10 | 7398.59 | |
| 林地 | 696.59 | 961.64 | 86.10 | 39111.34 | 1.26 | 0.15 | 40857.09 | |
| 水域 | 3.78 | 68.16 | 34.64 | 4.91 | 500.90 | 2.66 | 615.06 | |
| 未利用地 | 2.83 | 2.01 | 5.41 | 0.00 | 0.80 | 0.24 | 11.30 | |
| 合计 | 25258.59 | 51383.08 | 11900.83 | 47634.49 | 821.89 | 8.96 | 137007.84 | |
Table 2 Land use transfer matrix in the Taihang Mountains from 2000 to 2024
| 年份与面积 | 2024年面积/km2 | |||||||
|---|---|---|---|---|---|---|---|---|
| 2000年面积/km2 | 土地利用类型 | 草地 | 耕地 | 建设用地 | 林地 | 水域 | 未利用地 | 合计 |
| 草地 | 22024.08 | 5620.69 | 389.92 | 6936.12 | 13.32 | 3.71 | 34987.84 | |
| 耕地 | 2531.27 | 44712.36 | 4096.90 | 1581.93 | 213.41 | 2.11 | 53137.97 | |
| 建设用地 | 0.04 | 18.22 | 7287.85 | 0.19 | 92.20 | 0.10 | 7398.59 | |
| 林地 | 696.59 | 961.64 | 86.10 | 39111.34 | 1.26 | 0.15 | 40857.09 | |
| 水域 | 3.78 | 68.16 | 34.64 | 4.91 | 500.90 | 2.66 | 615.06 | |
| 未利用地 | 2.83 | 2.01 | 5.41 | 0.00 | 0.80 | 0.24 | 11.30 | |
| 合计 | 25258.59 | 51383.08 | 11900.83 | 47634.49 | 821.89 | 8.96 | 137007.84 | |
| 年份 | 土壤保持量/(108 t) | 碳储量/(108 t) | 生境质量 | 产水量/(108 m3) |
|---|---|---|---|---|
| 2000 | 40.84 | 14.9 | 0.435 | 183.01 |
| 2010 | 40.97 | 15.06 | 0.439 | 185.25 |
| 2020 | 48.92 | 15.2 | 0.425 | 236.98 |
| 2024 | 44.71 | 15.29 | 0.42 | 198.82 |
Table 3 Ecosystem services in the Taihang Mountains from 2000 to 2024
| 年份 | 土壤保持量/(108 t) | 碳储量/(108 t) | 生境质量 | 产水量/(108 m3) |
|---|---|---|---|---|
| 2000 | 40.84 | 14.9 | 0.435 | 183.01 |
| 2010 | 40.97 | 15.06 | 0.439 | 185.25 |
| 2020 | 48.92 | 15.2 | 0.425 | 236.98 |
| 2024 | 44.71 | 15.29 | 0.42 | 198.82 |
| 地貌分区 | 功能分区 | 2000-2024年占比变化 | 管控策略 |
|---|---|---|---|
| 山脉主脊区 | B1 | 稳定5%-7% | 鉴于占比长期稳定,以水源涵养和土壤保持为核心,营造针阔混交水源涵养林,建设小型水利水保工程,提升径流调蓄与固土能力,兼顾产水与保土功能协同 |
| B2 | 8%→6% | 针对占比极低且呈零星分布特征,划定生态修复重点区,实施封山育林、人工补植等措施,消除高海拔区域人类干扰点状斑块,推动生态功能向B3、B4转化 | |
| B3 | 34%→29% | 针对占比持续下降趋势,维持现有植被群落结构,开展生境异质性优化,营造多样化植被斑块,提升生物栖息地质量,强化生境维持与生态稳定功能 | |
| B4 | 53%→60% | 鉴于占比持续提升且已占据绝对主导,实施最严格的生态保护管控,禁止一切商业性采伐和开发建设活动,开展天然林抚育、退化林修复,巩固土壤保持、碳汇、生境质量的多功能协同效益 | |
| 山间盆地区 | B1 | 19%→24% | 顺应占比上升趋势,结合盆地汇流特征,建设河滨湿地、库塘水系等水利设施,优化农业种植结构,推广节水农业,提升盆地水源涵养与土壤保持能力,保障农业生产用水与生态用水平衡 |
| B2 | 24%→22% | 针对占比仍较高的现状,严控盆地内建设用地无序扩张,开展工矿废弃地、退化耕地生态修复,增加绿地与生态廊道,降低人类干扰强度,缓解生态脆弱性 | |
| B3 | 28%→19% | 针对占比持续下降的退化趋势,构建“林地—草地—农田”复合生境系统,预留生物迁徙廊道,保护盆地内野生动植物栖息地,遏制生境维持功能下滑,发挥中海拔生境稳定缓冲带作用 | |
| B4 | 29%→35% | 顺应占比稳步上升的良好态势,保护盆地周边山地连片林地斑块,实施封山育林与植被提质工程,扩大高功能生态斑块面积,推动与山脉主脊区B4连片融合,进一步强化碳汇与生境保育功能 | |
| 山前平川区 | B1 | 39%→51% | 针对占比大幅提升的主导地位,构建“农田防护林—河网水系—城市绿地”一体化水土保持与水源涵养体系,推广海绵城市建设,提升降雨拦蓄与土壤保持能力,保障平原区生产生活用水供给 |
| B2 | 31%→22% | 针对占比虽下降但仍占比较高的现状,严守城镇开发边界,开展城镇低效用地再开发,增加城镇生态空间占比,实施耕地质量提升工程,缓解建设用地与耕地的空间竞争,修复人类干扰导致的生态功能退化 | |
| B3 | 14%→9% | 针对占比持续下降的退化趋势,依托城市公园、郊野绿地、农田生态廊道,打造人工与自然结合的生境空间,保护平原区乡土物种,遏制生境质量下滑,强化城市生态缓冲带功能 | |
| B4 | 稳定16%-18% | 鉴于占比长期稳定且为平原区核心高功能生态斑块,严格保护现有近郊山地与交通干线两侧生态公益林,开展植被提质改造,提升碳汇与生境质量,巩固“点带结合”的生态支撑体系 |
Table 4 Gradient zoning and ecological function complex unit management and control strategies in the Taihang Mountains
| 地貌分区 | 功能分区 | 2000-2024年占比变化 | 管控策略 |
|---|---|---|---|
| 山脉主脊区 | B1 | 稳定5%-7% | 鉴于占比长期稳定,以水源涵养和土壤保持为核心,营造针阔混交水源涵养林,建设小型水利水保工程,提升径流调蓄与固土能力,兼顾产水与保土功能协同 |
| B2 | 8%→6% | 针对占比极低且呈零星分布特征,划定生态修复重点区,实施封山育林、人工补植等措施,消除高海拔区域人类干扰点状斑块,推动生态功能向B3、B4转化 | |
| B3 | 34%→29% | 针对占比持续下降趋势,维持现有植被群落结构,开展生境异质性优化,营造多样化植被斑块,提升生物栖息地质量,强化生境维持与生态稳定功能 | |
| B4 | 53%→60% | 鉴于占比持续提升且已占据绝对主导,实施最严格的生态保护管控,禁止一切商业性采伐和开发建设活动,开展天然林抚育、退化林修复,巩固土壤保持、碳汇、生境质量的多功能协同效益 | |
| 山间盆地区 | B1 | 19%→24% | 顺应占比上升趋势,结合盆地汇流特征,建设河滨湿地、库塘水系等水利设施,优化农业种植结构,推广节水农业,提升盆地水源涵养与土壤保持能力,保障农业生产用水与生态用水平衡 |
| B2 | 24%→22% | 针对占比仍较高的现状,严控盆地内建设用地无序扩张,开展工矿废弃地、退化耕地生态修复,增加绿地与生态廊道,降低人类干扰强度,缓解生态脆弱性 | |
| B3 | 28%→19% | 针对占比持续下降的退化趋势,构建“林地—草地—农田”复合生境系统,预留生物迁徙廊道,保护盆地内野生动植物栖息地,遏制生境维持功能下滑,发挥中海拔生境稳定缓冲带作用 | |
| B4 | 29%→35% | 顺应占比稳步上升的良好态势,保护盆地周边山地连片林地斑块,实施封山育林与植被提质工程,扩大高功能生态斑块面积,推动与山脉主脊区B4连片融合,进一步强化碳汇与生境保育功能 | |
| 山前平川区 | B1 | 39%→51% | 针对占比大幅提升的主导地位,构建“农田防护林—河网水系—城市绿地”一体化水土保持与水源涵养体系,推广海绵城市建设,提升降雨拦蓄与土壤保持能力,保障平原区生产生活用水供给 |
| B2 | 31%→22% | 针对占比虽下降但仍占比较高的现状,严守城镇开发边界,开展城镇低效用地再开发,增加城镇生态空间占比,实施耕地质量提升工程,缓解建设用地与耕地的空间竞争,修复人类干扰导致的生态功能退化 | |
| B3 | 14%→9% | 针对占比持续下降的退化趋势,依托城市公园、郊野绿地、农田生态廊道,打造人工与自然结合的生境空间,保护平原区乡土物种,遏制生境质量下滑,强化城市生态缓冲带功能 | |
| B4 | 稳定16%-18% | 鉴于占比长期稳定且为平原区核心高功能生态斑块,严格保护现有近郊山地与交通干线两侧生态公益林,开展植被提质改造,提升碳汇与生境质量,巩固“点带结合”的生态支撑体系 |
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