生态环境学报 ›› 2026, Vol. 35 ›› Issue (5): 819-830.DOI: 10.16258/j.cnki.1674-5906.2026.05.014
• 研究论文【环境科学】 •
上一篇
魏龙毅1(
), 林亲铁1,*(
), 刘煜欣1, 万家豪1, 姚丽敏2, 钟松雄3
收稿日期:2025-10-08
修回日期:2025-12-21
接受日期:2026-01-21
出版日期:2026-05-18
发布日期:2026-05-08
通讯作者:
*E-mail: 作者简介:魏龙毅(2000年生),男,硕士研究生,从事土壤修复研究。E-mail: 2607818377@qq.com
基金资助:
WEI Longyi1(
), LIN Qintie1,*(
), LIU Yuxin1, WAN Jiahao1, YAO Limin2, ZHONG Songxiong3
Received:2025-10-08
Revised:2025-12-21
Accepted:2026-01-21
Online:2026-05-18
Published:2026-05-08
摘要:
砷(As)作为广泛分布于地质高背景区土壤中的潜在有毒元素,其高含量与特定赋存形态可能引发显著的生态与健康风险。为揭示典型地质高背景区土壤中砷的空间分布规律及其富集机制,以广州某高背景地块为研究对象,系统采集0-12 m深度范围内2336组土壤样品,利用分层统计方法分析砷含量的垂向变化特征,并结合区域地质调查资料将研究区划分为三类岩性单元;从高、中、低砷含量岩性中各选取3组代表性样品,开展连续提取实验以解析砷的赋存形态;进一步运用Spearman相关分析探讨砷与铁(Fe)之间的关系,并借助XRD、XPS和SEM-EDS等表征手段,揭示砷的矿物结合机制与赋存状态。结果表明,研究区土壤砷含量整体随深度增加而升高,深层土壤富集特征明显;砷形态以残渣态和铁氧化物结合态为主,活性形态占比较低,呈现出“总量高-活性低”的污染特征。砷与铁含量之间呈显著正相关(r=0.733,p<0.001)。微观表征结果进一步证实砷主要赋存于以铁、铝氧化物为主的矿物团聚体中。该研究阐明了地质高背景区土壤砷的分布规律与地球化学过程,为地质高背景土壤砷的环境风险评估与污染防控提供科学依据。
中图分类号:
魏龙毅, 林亲铁, 刘煜欣, 万家豪, 姚丽敏, 钟松雄. 广州某地质高背景地块土壤砷污染特征及成因分析[J]. 生态环境学报, 2026, 35(5): 819-830.
WEI Longyi, LIN Qintie, LIU Yuxin, WAN Jiahao, YAO Limin, ZHONG Songxiong. Arsenic Contamination Characteristics and Source Analysis in Soils of a Geogenic High-background Area in Guangzhou, China[J]. Ecology and Environmental Sciences, 2026, 35(5): 819-830.
| 步骤 | 分级形态 | 提取剂 | 提取步骤 |
|---|---|---|---|
| 1 | 非特异性吸附态 | (NH4)2SO4 (0.05 M) | 室温振荡2 h, 提取两次 |
| 2 | 特异性吸附态 | (NH4)2H2PO4 (0.05 M) | 室温振荡12 h |
| 3 | 无定形铁氧 结合态 | (NH4)2C2O4 (0.2 M) pH=3.2 | 在室温避光下 摇晃4 h |
| 4 | 结晶型铁氧 结合态 | (NH4)2C2O4(0.2 M)+抗坏血酸 (0.1 M) pH=3.2 | 在 (96±3) ℃光照下水浴间断振荡30 min |
| 5 | 残渣态 | HNO3/HCl | 消解,参考土壤 重金属总量分析 |
表1 形态提取步骤
Table 1 Steps of speciation extraction
| 步骤 | 分级形态 | 提取剂 | 提取步骤 |
|---|---|---|---|
| 1 | 非特异性吸附态 | (NH4)2SO4 (0.05 M) | 室温振荡2 h, 提取两次 |
| 2 | 特异性吸附态 | (NH4)2H2PO4 (0.05 M) | 室温振荡12 h |
| 3 | 无定形铁氧 结合态 | (NH4)2C2O4 (0.2 M) pH=3.2 | 在室温避光下 摇晃4 h |
| 4 | 结晶型铁氧 结合态 | (NH4)2C2O4(0.2 M)+抗坏血酸 (0.1 M) pH=3.2 | 在 (96±3) ℃光照下水浴间断振荡30 min |
| 5 | 残渣态 | HNO3/HCl | 消解,参考土壤 重金属总量分析 |
| 土壤样品编号 | pH | w(SOM)/ % | CEC/ (cmol∙kg−1) | w(As)/ (mg∙kg−1) | ρ(As)/(μg∙L−1) | |
|---|---|---|---|---|---|---|
| 水平振荡法 | 硫酸硝酸法 | |||||
| PL | 7.61 | 4.97 | 5.61 | 52.87 | 1.01 | 1.48 |
| PM | 7.06 | 6.30 | 5.92 | 103.48 | 1.05 | 0.88 |
| PH | 7.98 | 4.22 | 3.68 | 389.92 | 6.75 | 11.47 |
| FL | 4.76 | 6.17 | 2.44 | 54.26 | 0.98 | 1.04 |
| FM | 5.16 | 6.71 | 2.83 | 150.34 | 0.90 | 0.84 |
| FH | 4.86 | 5.12 | 2.21 | 1193.77 | 0.94 | 0.92 |
| SL | 4.71 | 5.26 | 3.19 | 40.98 | 0.94 | 0.83 |
| SM | 4.67 | 6.01 | 2.58 | 71.81 | 0.96 | 1.03 |
| SH | 5.22 | 5.28 | 5.17 | 857.33 | 1.05 | 1.34 |
表2 土壤基本理化性质及砷含量
Table 2 Basic physicochemical properties and heavy metal contents of soil
| 土壤样品编号 | pH | w(SOM)/ % | CEC/ (cmol∙kg−1) | w(As)/ (mg∙kg−1) | ρ(As)/(μg∙L−1) | |
|---|---|---|---|---|---|---|
| 水平振荡法 | 硫酸硝酸法 | |||||
| PL | 7.61 | 4.97 | 5.61 | 52.87 | 1.01 | 1.48 |
| PM | 7.06 | 6.30 | 5.92 | 103.48 | 1.05 | 0.88 |
| PH | 7.98 | 4.22 | 3.68 | 389.92 | 6.75 | 11.47 |
| FL | 4.76 | 6.17 | 2.44 | 54.26 | 0.98 | 1.04 |
| FM | 5.16 | 6.71 | 2.83 | 150.34 | 0.90 | 0.84 |
| FH | 4.86 | 5.12 | 2.21 | 1193.77 | 0.94 | 0.92 |
| SL | 4.71 | 5.26 | 3.19 | 40.98 | 0.94 | 0.83 |
| SM | 4.67 | 6.01 | 2.58 | 71.81 | 0.96 | 1.03 |
| SH | 5.22 | 5.28 | 5.17 | 857.33 | 1.05 | 1.34 |
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