生态环境学报 ›› 2026, Vol. 35 ›› Issue (6): 948-962.DOI: 10.16258/j.cnki.1674-5906.2026.06.012
田昀鑫1,2(
), 王娇1,2,*(
), 贾小旭1,2, 马昌坤3, 邵明安1,2
收稿日期:2025-11-26
修回日期:2026-03-30
接受日期:2026-04-27
出版日期:2026-06-18
发布日期:2026-06-08
通讯作者:
* 王娇,E-mail: 作者简介:田昀鑫(2002年生),女,硕士研究生,主要研究方向为旱区生态水文。E-mail: tianyunxin24@mails.ucas.ac.cn
基金资助:
TIAN Yunxin1,2(
), WANG Jiao1,2,*(
), JIA Xiaoxu1,2, MA Changkun3, SHAO Ming’an1,2
Received:2025-11-26
Revised:2026-03-30
Accepted:2026-04-27
Online:2026-06-18
Published:2026-06-08
摘要:
天山北坡经济带土地开发利用对地表水环境形成显著压力,部分水体富营养化,威胁区域社会经济稳定发展与生态安全。明确地表水体营养盐现状及对土地利用格局的响应特征对支撑区域可持续发展具有重要意义。基于实地调查采样,获取了2023-2024年典型地表水氮磷营养盐含量、CODCr、BOD5等指标实测数据,结合单因子评价法分析水质状况,通过相关性分析、冗余分析等揭示营养盐指标对土地利用的响应特征,同时基于同位素示踪方法解析硝酸盐的可能来源。结果表明,1)天山北坡经济带地表水营养盐指标总体处于较低水平,42.16%采样点符合III类水质标准,但硝态氮和总氮仍存在超标风险。2)空间差异上,西区、西北区和东区主要面临氮污染风险,中区则主要为总磷与有机污染风险。3)西区地表水硝酸盐主要受耕地的调控,来源为农业化肥与土壤氮矿化;中区受耕地与建设用地共同作用,地表水硝酸盐来源为土壤氮矿化、生活污水与粪肥;西北区与东区则主要受建设用地影响,以生活污水和粪肥为主要来源。4)土地利用尤其是建设用地显著影响河流水营养盐含量,湖泊与水库营养盐指标不受土地利用影响。研究结果可为天山北坡经济带地表水环境保护、差异化污染防控提供科学依据。
中图分类号:
田昀鑫, 王娇, 贾小旭, 马昌坤, 邵明安. 天山北坡经济带地表水营养盐特征及其对土地利用的响应[J]. 生态环境学报, 2026, 35(6): 948-962.
TIAN Yunxin, WANG Jiao, JIA Xiaoxu, MA Changkun, SHAO Ming’an. Characteristics of Surface Water Nutrients and Their Response to Land Use in the Economic Belt on the Northern Slope of the Tianshan Mountains[J]. Ecology and Environmental Sciences, 2026, 35(6): 948-962.
| 营养盐指标 | Ⅰ类 | Ⅱ类 | Ⅲ类 | Ⅳ类 | Ⅴ类 |
|---|---|---|---|---|---|
| NH3-N | 0.15 | 0.5 | 1.0 | 1.5 | 2.0 |
| TN | 0.2 | 0.5 | 1.0 | 1.5 | 2.0 |
| TP | 0.02(湖、库0.01) | 0.1(湖、库0.025) | 0.2(湖、库0.05) | 0.3(湖、库0.1) | 0.4(湖、库0.2) |
| CODCr | 15 | 15 | 20 | 30 | 40 |
| BOD5 | 3 | 3 | 4 | 6 | 10 |
表1 地表水环境质量标准基本项目标准限值
Table 1 Standard limits for basic surface water quality parameters mg·L?1
| 营养盐指标 | Ⅰ类 | Ⅱ类 | Ⅲ类 | Ⅳ类 | Ⅴ类 |
|---|---|---|---|---|---|
| NH3-N | 0.15 | 0.5 | 1.0 | 1.5 | 2.0 |
| TN | 0.2 | 0.5 | 1.0 | 1.5 | 2.0 |
| TP | 0.02(湖、库0.01) | 0.1(湖、库0.025) | 0.2(湖、库0.05) | 0.3(湖、库0.1) | 0.4(湖、库0.2) |
| CODCr | 15 | 15 | 20 | 30 | 40 |
| BOD5 | 3 | 3 | 4 | 6 | 10 |
| 营养盐指标 | 水体类型 | 样本数 | 最大质量浓度/ (mg·L−1) | 最小质量浓度/ (mg·L−1) | 5%剪除后均值/ (mg·L−1) | 标准差 | 变异系数 | 超过Ⅲ类比例/ % | 单因子污染指数(Pi) | |
|---|---|---|---|---|---|---|---|---|---|---|
| 变化范围 | 平均值 | |||||||||
| NO3−-N | 河流 | 109 | 7.46 | 0.14 | 1.14 | 1.32 | 0.86 | 39.45 | 0.01-7.46 | 1.26 |
| 湖泊 | 16 | 2.55 | 0.08 | 0.66 | 0.67 | 0.99 | 18.75 | 0.08-2.55 | 0.73 | |
| 水库 | 60 | 4.46 | 0.06 | 0.95 | 0.73 | 1.29 | 25.00 | 0.01-2.76 | 0.82 | |
| NH3-N | 河流 | 109 | 0.77 | 0.01 | 0.17 | 0.12 | 1.45 | 0.00 | 0.04-2.28 | 0.27 |
| 湖泊 | 16 | 0.64 | 0.08 | 0.33 | 0.21 | 1.60 | 0.00 | 0.05-0.62 | 0.28 | |
| 水库 | 60 | 1.33 | 0.01 | 0.30 | 0.31 | 0.95 | 3.33 | 0.04-4.46 | 0.47 | |
| NO2−-N | 河流 | 109 | 1.88 | <ρ(LOD) | <ρ(LOD) | 0.62 | 0.00 | - | - | - |
| 湖泊 | 16 | 0.47 | <ρ(LOD) | 0.01 | 0.39 | 0.07 | - | - | - | |
| 水库 | 60 | 0.38 | <ρ(LOD) | 0.01 | 0.32 | 0.12 | - | - | - | |
| TN | 河流 | 109 | 8.16 | <ρ(LOD) | 0.94 | 1.52 | 0.62 | 35.78 | 0.02-8.16 | 1.18 |
| 湖泊 | 16 | 1.75 | 0.11 | 0.90 | 0.52 | 1.73 | 56.25 | 0.11-1.75 | 0.90 | |
| 水库 | 60 | 3.75 | <ρ(LOD) | 0.72 | 0.74 | 0.98 | 30.00 | 0.00-3.75 | 0.80 | |
| TP | 河流 | 109 | 3.79 | <ρ(LOD) | 0.02 | 0.40 | 0.04 | 6.42 | 0.00-18.93 | 0.42 |
| 湖泊 | 16 | 0.09 | <ρ(LOD) | 0.02 | 0.03 | 0.68 | 12.50 | 0.00-1.80 | 0.50 | |
| 水库 | 60 | 0.71 | <ρ(LOD) | 0.02 | 0.12 | 0.15 | 11.67 | 0.00-14.20 | 0.78 | |
| CODCr | 河流 | 109 | 57.38 | <ρ(LOD) | 5.87 | 11.32 | 0.52 | 9.17 | 0.00-2.87 | 0.40 |
| 湖泊 | 16 | 144.86 | <ρ(LOD) | 30.47 | 37.60 | 0.81 | 43.75 | 0.00-7.24 | 1.73 | |
| 水库 | 60 | 64.95 | <ρ(LOD) | 13.71 | 18.72 | 0.73 | 18.33 | 0.00-3.25 | 0.77 | |
| BOD5 | 河流 | 68 | 15.00 | <ρ(LOD) | 1.48 | 2.65 | 0.56 | 8.82 | 0.00-1.68 | 0.34 |
| 湖泊 | 15 | 18.20 | <ρ(LOD) | 2.21 | 4.56 | 0.48 | 46.67 | 0.00-4.55 | 1.64 | |
| 水库 | 28 | 15.83 | <ρ(LOD) | 1.96 | 3.98 | 0.49 | 17.86 | 0.00-1.60 | 0.44 | |
表2 天山北坡经济带典型地表水体营养盐指标统计结果
Table 2 Statistical results of nutrients in typical surface water in the economic belt on the northern slope of the Tianshan Mountains
| 营养盐指标 | 水体类型 | 样本数 | 最大质量浓度/ (mg·L−1) | 最小质量浓度/ (mg·L−1) | 5%剪除后均值/ (mg·L−1) | 标准差 | 变异系数 | 超过Ⅲ类比例/ % | 单因子污染指数(Pi) | |
|---|---|---|---|---|---|---|---|---|---|---|
| 变化范围 | 平均值 | |||||||||
| NO3−-N | 河流 | 109 | 7.46 | 0.14 | 1.14 | 1.32 | 0.86 | 39.45 | 0.01-7.46 | 1.26 |
| 湖泊 | 16 | 2.55 | 0.08 | 0.66 | 0.67 | 0.99 | 18.75 | 0.08-2.55 | 0.73 | |
| 水库 | 60 | 4.46 | 0.06 | 0.95 | 0.73 | 1.29 | 25.00 | 0.01-2.76 | 0.82 | |
| NH3-N | 河流 | 109 | 0.77 | 0.01 | 0.17 | 0.12 | 1.45 | 0.00 | 0.04-2.28 | 0.27 |
| 湖泊 | 16 | 0.64 | 0.08 | 0.33 | 0.21 | 1.60 | 0.00 | 0.05-0.62 | 0.28 | |
| 水库 | 60 | 1.33 | 0.01 | 0.30 | 0.31 | 0.95 | 3.33 | 0.04-4.46 | 0.47 | |
| NO2−-N | 河流 | 109 | 1.88 | <ρ(LOD) | <ρ(LOD) | 0.62 | 0.00 | - | - | - |
| 湖泊 | 16 | 0.47 | <ρ(LOD) | 0.01 | 0.39 | 0.07 | - | - | - | |
| 水库 | 60 | 0.38 | <ρ(LOD) | 0.01 | 0.32 | 0.12 | - | - | - | |
| TN | 河流 | 109 | 8.16 | <ρ(LOD) | 0.94 | 1.52 | 0.62 | 35.78 | 0.02-8.16 | 1.18 |
| 湖泊 | 16 | 1.75 | 0.11 | 0.90 | 0.52 | 1.73 | 56.25 | 0.11-1.75 | 0.90 | |
| 水库 | 60 | 3.75 | <ρ(LOD) | 0.72 | 0.74 | 0.98 | 30.00 | 0.00-3.75 | 0.80 | |
| TP | 河流 | 109 | 3.79 | <ρ(LOD) | 0.02 | 0.40 | 0.04 | 6.42 | 0.00-18.93 | 0.42 |
| 湖泊 | 16 | 0.09 | <ρ(LOD) | 0.02 | 0.03 | 0.68 | 12.50 | 0.00-1.80 | 0.50 | |
| 水库 | 60 | 0.71 | <ρ(LOD) | 0.02 | 0.12 | 0.15 | 11.67 | 0.00-14.20 | 0.78 | |
| CODCr | 河流 | 109 | 57.38 | <ρ(LOD) | 5.87 | 11.32 | 0.52 | 9.17 | 0.00-2.87 | 0.40 |
| 湖泊 | 16 | 144.86 | <ρ(LOD) | 30.47 | 37.60 | 0.81 | 43.75 | 0.00-7.24 | 1.73 | |
| 水库 | 60 | 64.95 | <ρ(LOD) | 13.71 | 18.72 | 0.73 | 18.33 | 0.00-3.25 | 0.77 | |
| BOD5 | 河流 | 68 | 15.00 | <ρ(LOD) | 1.48 | 2.65 | 0.56 | 8.82 | 0.00-1.68 | 0.34 |
| 湖泊 | 15 | 18.20 | <ρ(LOD) | 2.21 | 4.56 | 0.48 | 46.67 | 0.00-4.55 | 1.64 | |
| 水库 | 28 | 15.83 | <ρ(LOD) | 1.96 | 3.98 | 0.49 | 17.86 | 0.00-1.60 | 0.44 | |
| 营养盐指标 | 不同分区地表水营养盐均值 | |||
|---|---|---|---|---|
| 西北区 | 西区 | 中区 | 东区 | |
| NO3⁻-N | 1.34 | 0.84 | 0.90 | 1.97 |
| NH3-N | 0.14 | 0.23 | 0.24 | 0.11 |
| NO2⁻-N | <ρ(LOD) | 0.025 | <ρ(LOD) | 0.003 |
| TN | 1.62 | 0.62 | 0.52 | 1.61 |
| TP | 0.03 | 0.01 | 0.01 | <ρ(LOD) |
| CODCr | 10.09 | 10.01 | 11.83 | 2.08 |
| BOD5 | 2.31 | 0.80 | 4.29 | - |
表3 天山北坡经济带不同分区地表水营养盐指标平均值
Table 3 Mean values of nutrients in surface water from different subregions in the economic belt on the northern slope of the Tianshan Mountains mg·L?1
| 营养盐指标 | 不同分区地表水营养盐均值 | |||
|---|---|---|---|---|
| 西北区 | 西区 | 中区 | 东区 | |
| NO3⁻-N | 1.34 | 0.84 | 0.90 | 1.97 |
| NH3-N | 0.14 | 0.23 | 0.24 | 0.11 |
| NO2⁻-N | <ρ(LOD) | 0.025 | <ρ(LOD) | 0.003 |
| TN | 1.62 | 0.62 | 0.52 | 1.61 |
| TP | 0.03 | 0.01 | 0.01 | <ρ(LOD) |
| CODCr | 10.09 | 10.01 | 11.83 | 2.08 |
| BOD5 | 2.31 | 0.80 | 4.29 | - |
图3 天山北坡经济带地表水营养盐指标相关性分析 *表示相关性在p<0.05水平下显著;**表示相关性在p<0.01水平下显著
Figure 3 Correlation analysis of nutrients in surface water in the economic belt on the northern slope of the Tianshan Mountains
图4 不同缓冲区尺度下水体营养盐指标与土地利用的相关性 *表示相关性在p<0.05水平下显著;**表示相关性在p<0.01水平下显著
Figure 4 Correlation analysis between water nutrients and land use type at different buffer zone scales
图5 河流水营养盐指标与土地利用类型冗余分析排序 黑色箭头表示土地利用类型的面积占比(解释变量);红色箭头表示水质指标的质量浓度(响应变量)
Figure 5 Ranking of nutrient indicators in river water and land use type for redundancy analysis
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