生态环境学报 ›› 2026, Vol. 35 ›› Issue (7): 1114-1124.DOI: 10.16258/j.cnki.1674-5906.2026.07.011
收稿日期:2025-05-06
修回日期:2025-11-17
接受日期:2025-12-10
出版日期:2026-07-18
发布日期:2026-07-17
通讯作者:
*杨玉庆,275303560@qq.com
作者简介:张军梅(1972年生),女,正高级工程师,研究方向为水利工程建设与管理。E-mail: 82318012@qq.com
基金资助:
Zhang Junmei(
), Fang Yanli, Yang Yuqing*(
)
Received:2025-05-06
Revised:2025-11-17
Accepted:2025-12-10
Online:2026-07-18
Published:2026-07-17
摘要:
黄河作为中国第二长河,其生态环境健康持续受到广泛关注。随着《中华人民共和国黄河保护法》的实施,评估黄河重点河段的重金属含量特征及其生态风险具有重要意义。选取三门峡段为研究对象,采用ICP-MS技术分析水体中13种重金属的含量。结果表明,Pb在部分采样点超出地表水Ⅱ类水质标准限值,而Cd、Cr、Cu、Zn和As均低于Ⅱ类限值。基于6种典型重金属(Cd、Cr、Cu、Zn、Pb、Ni)的实测含量,设置3个复合暴露梯度,评估其对斑马鱼(Danio rerio)胚胎发育、仔鱼神经递质和前体物质含量及运动行为的影响。实验结果表明,环境剂量和高浓度重金属复合暴露组孵化率分别显著降低15.8%和31.3%,畸形率分别显著增加140%和256%。此外,各复合暴露组84 h心率分别显著增加16.3%、15.9%和21.7%。高浓度复合暴露显著增加了斑马鱼体内GABA、谷氨酸、苯丙氨酸、酪氨酸和色氨酸含量,分别显著增加8.40%、23.3%、77.1%、111%和104%,且加快了斑马鱼在持续光照和光暗刺激下的运动速率,提示其可诱发神经系统过度兴奋。该研究揭示了黄河三门峡段水体中重金属含量特征,阐明了环境剂量重金属复合暴露对水生生物产生的潜在负面影响,为黄河水生态保护与环境风险管理提供了科学依据。
中图分类号:
张军梅, 方艳丽, 杨玉庆. 黄河流域三门峡段水体重金属含量特征及对斑马鱼胚胎和仔鱼的生物毒性研究[J]. 生态环境学报, 2026, 35(7): 1114-1124.
Zhang Junmei, Fang Yanli, Yang Yuqing. Heavy Metal Content in the Sanmenxia Section of the Yellow River Basin and Its Developmental Toxicity to Zebrafish Embryos and Larvae[J]. Ecology and Environmental Sciences, 2026, 35(7): 1114-1124.
| 重金属 | 质量浓度/ (μg∙L−1) | 质量浓度中位数/ (μg∙L−1) | 平均值/ (μg∙L−1) | 标准差 | 变异 系数 | 地表水质II类标准限值/ (μg∙L−1) |
|---|---|---|---|---|---|---|
| Cr | 0.315-25.4 | 0.814 | 5.21 | 8.53 | 164 | 50 |
| Mn | 0.413-2730 | 1.26 | 84.8 | 405 | 478 | - |
| Fe | 87.8-1670 | 138 | 348 | 423 | 121 | - |
| Pb | 0.0643-29.1 | 0.129 | 2.24 | 5.60 | 249 | 10 |
| Al | 2.12-1280 | 4.61 | 182 | 349 | 191 | - |
| As | 2.13-25.4 | 6.00 | 7.21 | 4.63 | 64.3 | 50 |
| Cd | 0.0362-2.74 | 0.116 | 0.305 | 0.556 | 182 | 5 |
| Cu | 0.324-33.5 | 1.77 | 4.29 | 6.59 | 154 | 1000 |
| Zn | 2.18-120 | 4.65 | 22.2 | 34.1 | 154 | 1000 |
| V | 2.07-13.1 | 5.58 | 6.13 | 2.10 | 34.2 | - |
| Co | 0.122-15.0 | 0.350 | 1.75 | 3.40 | 194 | - |
| Ni | 3.38-29.3 | 10.9 | 10.5 | 3.96 | 37.6 | - |
| Ag | 0.0166-0.175 | 0.0360 | 0.0500 | 0.0390 | 79.0 | - |
表1 黄河流域三门峡地区地表水中13种重金属质量浓度(2016年)
Table 1 Concentrations of 13 heavy metals in surface water of Yellow River Basin Sanmenxia
| 重金属 | 质量浓度/ (μg∙L−1) | 质量浓度中位数/ (μg∙L−1) | 平均值/ (μg∙L−1) | 标准差 | 变异 系数 | 地表水质II类标准限值/ (μg∙L−1) |
|---|---|---|---|---|---|---|
| Cr | 0.315-25.4 | 0.814 | 5.21 | 8.53 | 164 | 50 |
| Mn | 0.413-2730 | 1.26 | 84.8 | 405 | 478 | - |
| Fe | 87.8-1670 | 138 | 348 | 423 | 121 | - |
| Pb | 0.0643-29.1 | 0.129 | 2.24 | 5.60 | 249 | 10 |
| Al | 2.12-1280 | 4.61 | 182 | 349 | 191 | - |
| As | 2.13-25.4 | 6.00 | 7.21 | 4.63 | 64.3 | 50 |
| Cd | 0.0362-2.74 | 0.116 | 0.305 | 0.556 | 182 | 5 |
| Cu | 0.324-33.5 | 1.77 | 4.29 | 6.59 | 154 | 1000 |
| Zn | 2.18-120 | 4.65 | 22.2 | 34.1 | 154 | 1000 |
| V | 2.07-13.1 | 5.58 | 6.13 | 2.10 | 34.2 | - |
| Co | 0.122-15.0 | 0.350 | 1.75 | 3.40 | 194 | - |
| Ni | 3.38-29.3 | 10.9 | 10.5 | 3.96 | 37.6 | - |
| Ag | 0.0166-0.175 | 0.0360 | 0.0500 | 0.0390 | 79.0 | - |
| 重金属 | 质量浓度/ (μg∙L−1) | 质量浓度中位数/ (μg∙L−1) | 平均值/ (μg∙L−1) | 标准差 | 变异 系数 | 地表水质II类标准限值/ (μg∙L−1) |
|---|---|---|---|---|---|---|
| Cr | 0.382-32.1 | 0.970 | 9.19 | 11.2 | 121 | 50 |
| Mn | 0.600-138 | 1.81 | 35.5 | 48.7 | 137 | - |
| Fe | 55.2-1990 | 126 | 479 | 609 | 127 | - |
| Pb | 0.0757-29.4 | 0.686 | 3.77 | 7.92 | 210 | 10 |
| Al | 3.68-1460 | 7.53 | 336 | 469 | 139 | - |
| As | 2.11-26.0 | 6.03 | 7.64 | 7.23 | 94.6 | 50 |
| Cd | 0.0429-3.72 | 0.116 | 0.649 | 1.16 | 179 | 5 |
| Cu | 0.701-28.5 | 2.94 | 4.73 | 6.90 | 146 | 1000 |
| Zn | 2.52-172 | 10.0 | 38.5 | 49.6 | 129 | 1000 |
| V | 4.57-10.5 | 5.43 | 6.05 | 1.54 | 25.5 | - |
| Co | 0.108-9.64 | 0.617 | 1.50 | 2.71 | 181 | - |
| Ni | 3.29-30.2 | 10.8 | 11.7 | 6.96 | 59.5 | - |
| Ag | 0.0186-0.914 | 0.0360 | 0.174 | 0.293 | 169 | - |
表2 黄河流域三门峡地区地表水中13种重金属质量浓度(2024年)
Table 2 Concentrations of 13 heavy metals in surface water of Yellow River Basin Sanmenxia
| 重金属 | 质量浓度/ (μg∙L−1) | 质量浓度中位数/ (μg∙L−1) | 平均值/ (μg∙L−1) | 标准差 | 变异 系数 | 地表水质II类标准限值/ (μg∙L−1) |
|---|---|---|---|---|---|---|
| Cr | 0.382-32.1 | 0.970 | 9.19 | 11.2 | 121 | 50 |
| Mn | 0.600-138 | 1.81 | 35.5 | 48.7 | 137 | - |
| Fe | 55.2-1990 | 126 | 479 | 609 | 127 | - |
| Pb | 0.0757-29.4 | 0.686 | 3.77 | 7.92 | 210 | 10 |
| Al | 3.68-1460 | 7.53 | 336 | 469 | 139 | - |
| As | 2.11-26.0 | 6.03 | 7.64 | 7.23 | 94.6 | 50 |
| Cd | 0.0429-3.72 | 0.116 | 0.649 | 1.16 | 179 | 5 |
| Cu | 0.701-28.5 | 2.94 | 4.73 | 6.90 | 146 | 1000 |
| Zn | 2.52-172 | 10.0 | 38.5 | 49.6 | 129 | 1000 |
| V | 4.57-10.5 | 5.43 | 6.05 | 1.54 | 25.5 | - |
| Co | 0.108-9.64 | 0.617 | 1.50 | 2.71 | 181 | - |
| Ni | 3.29-30.2 | 10.8 | 11.7 | 6.96 | 59.5 | - |
| Ag | 0.0186-0.914 | 0.0360 | 0.174 | 0.293 | 169 | - |
图2 重金属复合暴露对斑马鱼仔鱼孵化率和畸形率的影响 *p<0.05,**p<0.01,***p<0.001表示与对照组相比具有显著性差异。下同
Figure 2 Effects of heavy metal combined exposure on hatching rate (a) and malformation rate (b) of zebrafish embryos/larvae
图3 重金属复合暴露对斑马鱼仔鱼48 h和84 h心率以及144 h体长的影响
Figure 3 Effects of heavy metal combined exposure on the heart rate of zebrafish at 48 h and 84 h, as well as the length at 144 h
图5 重金属复合暴露144 h对斑马鱼仔鱼神经递质前体物质质量分数的影响
Figure 5 Effects of heavy metal combined exposure of 144 h on the neurotransmitter precursors levels of zebrafish larvae
图6 重金属复合暴露144 h对斑马鱼仔鱼在光照下运动行为的影响 **p<0.01表示与对照组相比具有显著性差异
Figure 6 Effects of heavy metal combined exposure of 144 h on the locomotor behavior under light of zebrafish larvae
图7 重金属复合暴露144 h对斑马鱼仔鱼在光暗刺激下运动行为的影响
Figure 7 Effects of heavy metal combined exposure of 144 h on the locomotor behavior under light-dark-light-dark photoperiod stimulation of zebrafish larvae
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