生态环境学报 ›› 2022, Vol. 31 ›› Issue (9): 1876-1884.DOI: 10.16258/j.cnki.1674-5906.2022.09.018
王钊1,2,3(), 张曼胤1,2,3,*(
), 胡宇坤1,2,3, 刘魏魏1,2,3, 张苗苗1,2,3
收稿日期:
2022-04-06
出版日期:
2022-09-18
发布日期:
2022-11-07
通讯作者:
*张曼胤(1979年生),男,研究员,博士,硕士研究生导师,研究方向为湿地生态功能作用机理、湿地监测与评价、湿地保护规划、湿地恢复设计等。E-mail: cneco@126.com作者简介:
王钊(1996年生),男,硕士研究生,主要研究方向为湿地生态学。E-mail: wangz435@nenu.edu.cn
基金资助:
WANG Zhao1,2,3(), ZHANG Manyin1,2,3,*(
), HU Yukun1,2,3, LIU Weiwei1,2,3, ZHANG Miaomiao1,2,3
Received:
2022-04-06
Online:
2022-09-18
Published:
2022-11-07
摘要:
盐度是滨海湿地最重要的环境特征之一,然而滨海湿地盐度的变化如何影响汞甲基化过程目前仍缺乏相关研究。基于室内培养的方法,研究了厌氧条件下江苏盐城滨海湿地沉积物甲基汞质量分数和硫酸盐还原菌绝对含量随盐度梯度(0、0.6%、1.2%、1.8%、2.4%和3.0%)的变化特征。结果表明,海盐处理下,随着盐度的升高,甲基汞质量分数总体呈现先增加后减少的趋势,1.2%盐度下,沉积物汞甲基化程度最高;随着培养时间(1-29 d)的增长,甲基汞质量分数总体也呈现出先增加后减少的趋势,培养8 d时,沉积物汞甲基化程度最高。海盐处理下,随着盐度的升高,硫酸盐还原菌的绝对含量总体增加,表明海水盐度未对硫酸盐还原菌生长产生盐胁迫;随着培养时间(1-29 d)的增加,硫酸盐还原菌的绝对含量表现为先增加后减少的趋势,当培养时间超过15 d时,硫酸盐还原菌的生长会受到抑制。该实验条件下,硫酸盐还原菌绝对含量与甲基汞质量分数间无显著线性相关,可溶性有机碳对甲基汞质量分数随时间的变化具有较高的解释度。该研究表明滨海湿地盐度的时空变化对汞甲基化过程有较重要的影响。研究结果可为预测盐度变化所带来的甲基汞生态风险提供了依据。
中图分类号:
王钊, 张曼胤, 胡宇坤, 刘魏魏, 张苗苗. 盐度对典型滨海湿地沉积物汞甲基化的影响[J]. 生态环境学报, 2022, 31(9): 1876-1884.
WANG Zhao, ZHANG Manyin, HU Yukun, LIU Weiwei, ZHANG Miaomiao. Effect of Salinity on Mercury Methylation in Sediments of A Typical Coastal Wetland[J]. Ecology and Environment, 2022, 31(9): 1876-1884.
样地 Sample plots | 样本量 Sample size | 经纬度 Longitude and latitude | 主要植被类型 Main vegetation type |
---|---|---|---|
新洋港北 North of Xinyang Port | 5 | 120.5660°-120.5666°E, 33.6356°-33.6362°N | 芦苇 Phragmites australis、盐度碱蓬 Suaeda salsa |
核心保护区 Core Reserve | 10 | 120.5537°-120.6141°E, 33.5778°-33.6090°N | 芦苇 Phragmites australis、互花米草 Spartina alterniflora、盐地碱蓬 Suaeda salsa |
大丰麋鹿区 Dafeng Elk Natural Reserve | 5 | 120.8491°-120.8622°E, 33.0529°-33.0550°N | 互花米草 Spartina alterniflora、白茅 Imperata cylindrica |
表1 野外样品采集情况
Table 1 Description of sample collection in the field
样地 Sample plots | 样本量 Sample size | 经纬度 Longitude and latitude | 主要植被类型 Main vegetation type |
---|---|---|---|
新洋港北 North of Xinyang Port | 5 | 120.5660°-120.5666°E, 33.6356°-33.6362°N | 芦苇 Phragmites australis、盐度碱蓬 Suaeda salsa |
核心保护区 Core Reserve | 10 | 120.5537°-120.6141°E, 33.5778°-33.6090°N | 芦苇 Phragmites australis、互花米草 Spartina alterniflora、盐地碱蓬 Suaeda salsa |
大丰麋鹿区 Dafeng Elk Natural Reserve | 5 | 120.8491°-120.8622°E, 33.0529°-33.0550°N | 互花米草 Spartina alterniflora、白茅 Imperata cylindrica |
图2 不同盐度和时间下pH和DOC的差异 平均值±标准误,n=5。不同小写字母表示同时间不同盐度处理之间差异显著;不同大写字母表示同盐度不同时间处理之间差异显著。下同
Figure 2 Differences in pH and DOC among different salinity levels and incubation time Mean±SE, n=5. Different lowercase letters indicate that the same incubation time has significant differences among different salinity levels at 0.05 level; different capital letters indicate that the same salinity has significant differences among different incubation time at 0.05 level. The same below
时间 Time/d | 盐度 Salinity/% | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | 0.6 | 1.2 | 1.8 | 2.4 | 3.0 | |||||||
t | P | t | P | t | P | t | P | t | P | t | P | |
1 | 4.016 | 0.057ns | 21.496 | 0.002** | 18.796 | 0.003** | 2.219 | 0.157ns | 9.591 | 0.011* | 9.148 | 0.012* |
8 | 8.331 | 0.014* | 9.705 | 0.010* | 11.241 | 0.008** | 13.096 | 0.006** | 21.224 | 0.002** | 8.727 | 0.013* |
15 | 10.371 | 0.009** | 20.370 | 0.002** | 34.204 | <0.001*** | 5.398 | 0.033* | 29.100 | 0.001** | 5.408 | 0.033* |
22 | 5.620 | 0.030* | 3.402 | 0.080ns | 11.017 | 0.008** | 11.568 | 0.007** | 4.376 | 0.048* | 5.456 | 0.032* |
29 | 7.526 | 0.017* | 3.243ns | 0.083ns | -2.752 | 0.111ns | 2.349 | 0.143ns | 6.092 | 0.03* | 4.673 | 0.043* |
表2 模拟盐度下沉积物甲基汞质量分数与混合均质样本底值的差异
Table 2 Differences in methylmercury contents between the sediments under simulated salinity and the background level
时间 Time/d | 盐度 Salinity/% | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | 0.6 | 1.2 | 1.8 | 2.4 | 3.0 | |||||||
t | P | t | P | t | P | t | P | t | P | t | P | |
1 | 4.016 | 0.057ns | 21.496 | 0.002** | 18.796 | 0.003** | 2.219 | 0.157ns | 9.591 | 0.011* | 9.148 | 0.012* |
8 | 8.331 | 0.014* | 9.705 | 0.010* | 11.241 | 0.008** | 13.096 | 0.006** | 21.224 | 0.002** | 8.727 | 0.013* |
15 | 10.371 | 0.009** | 20.370 | 0.002** | 34.204 | <0.001*** | 5.398 | 0.033* | 29.100 | 0.001** | 5.408 | 0.033* |
22 | 5.620 | 0.030* | 3.402 | 0.080ns | 11.017 | 0.008** | 11.568 | 0.007** | 4.376 | 0.048* | 5.456 | 0.032* |
29 | 7.526 | 0.017* | 3.243ns | 0.083ns | -2.752 | 0.111ns | 2.349 | 0.143ns | 6.092 | 0.03* | 4.673 | 0.043* |
图3 不同盐度和时间下甲基汞质量分数与SRB绝对含量的差异
Figure 3 Differences in methylmercury content and absolute abundance of sulfate-reducing bacteria among different salinity levels and incubation time
图4 pH和DOC与甲基汞质量分数之间的关系 n=3。r表示相关系数,P表示显著性检验大小
Figure 4 Relationships between pH, DOC and methylmercury content n=3. r represents the correlation coefficient; P represents the value of significant test
图5 SRB绝对含量与甲基汞质量分数之间的关系 n=3。r表示相关系数,P表示显著性检验大小,对数转换指取以10为底的对数
Figure 5 Relationship between absolute abundance of SRB and methylmercury content n=3. r represents the correlation coefficient; P represents the value of significant test. Logarithmic transform points to the base 10 logarithm
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