生态环境学报 ›› 2024, Vol. 33 ›› Issue (8): 1279-1288.DOI: 10.16258/j.cnki.1674-5906.2024.08.012
收稿日期:
2024-05-09
出版日期:
2024-08-18
发布日期:
2024-09-25
作者简介:
卢聪(1988年生),男,高级工程师,博士,主要从事污染控制技术研究。E-mail: lucong_1988@163.com
基金资助:
Received:
2024-05-09
Online:
2024-08-18
Published:
2024-09-25
摘要:
新型溴代阻燃剂十溴二苯乙烷(DBDPE)已经成为目前最常用的溴代阻燃剂。随着DBDPE在各种环境介质中被普遍检测到,其环境污染和治理正引起广泛的关注。迄今为止,生物炭负载零价铁材料(nZVI/BC)去除沉积物中DBDPE的应用尚未见报道。利用甘蔗渣通过液相还原法制备nZVI/BC,研究nZVI/BC去除沉积物体系里DBDPE的动力学过程,并探究其作用机制,为利用碳基零价铁去除沉积物中DBDPE提供了科学依据和技术支持。研究发现增加材料投加量、含水量、反应温度和降低底物初始质量分数,均能提高DBDPE的去除效率。高剂量的nZVI/BC能提供更多的吸附位点,并增大与DBDPE的接触面积,从而吸附更多的DBDPE分子。DBDPE质量分数的增加,将进一步增加DBDPE分子间的竞争反应,导致DBDPE分子与nZVI/BC颗粒的接触率降低。大量的水可以提供更多的活性H,从而提高与DBDPE反应的机会。温度升高,分子运动增强,提高了nZVI/BC与DBDPE的接触频率,也提高了nZVI的反应活性。SEM表征结果显示,生物炭(BC)的加入使纳米零价铁(nZVI)均匀分散在生物炭的表面,改善了nZVI的分散程度,提高了nZVI的反应活性。红外吸收光谱FTIR检测结果表明反应后nZVI/BC表面的−OH的伸缩振动和−CH2−的弯曲强度均减弱,Fe−CO特征峰消失,并且出现了C=C的伸缩振动峰。nZVI/BC的微孔及介孔结构和表面的Fe−O、−OH、−CH2−、C−O、C−H、C=O和−COOH等基团均能为DBDPE提供吸附位点,且DBDPE苯环结构上的π电子可能与nZVI/BC表面上的阳离子形成π−电荷相互作用。GC-ECNI-MS检测结果表明DBDPE被nZVI/BC降解过程中可能脱溴生成八溴二苯乙烷,ECOSAR (Ecological Structure Activity Relationships)软件预测nZVI/BC对DBDPE的降解降低了母体的生物毒性。
中图分类号:
卢聪. 生物炭负载纳米零价铁对沉积物中十溴二苯乙烷去除效果及机制[J]. 生态环境学报, 2024, 33(8): 1279-1288.
LU Cong. Removal Effect and Mechanism of DBDPE in Sediments by Biochar-loaded Nano-zero-valent Iron[J]. Ecology and Environment, 2024, 33(8): 1279-1288.
投加量/ (g∙g−1) | 初始质量分数/ (mg∙kg−1) | 温度/ ℃ | 沉积物与水 质量比 | k1/ h−1 | r2 |
---|---|---|---|---|---|
0.02 | 10 | 25 | 1∶2 | 0.0064 | 0.659 |
0.04 | 10 | 25 | 1∶2 | 0.0089 | 0.633 |
0.08 | 10 | 25 | 1∶2 | 0.0117 | 0.652 |
0.10 | 10 | 20 | 1∶2 | 0.0159 | 0.830 |
0.10 | 10 | 25 | 1∶2 | 0.0190 | 0.793 |
0.10 | 10 | 30 | 1∶2 | 0.0260 | 0.821 |
0.10 | 15 | 25 | 1∶2 | 0.0138 | 0.724 |
0.10 | 20 | 25 | 1∶2 | 0.0118 | 0.787 |
0.10 | 10 | 25 | 2∶1 | ‒ | ‒ |
0.10 | 10 | 25 | 1∶1 | 0.0108 | 0.749 |
0.10 | 10 | 25 | 1∶3 | 0.0224 | 0.848 |
表1 不同影响因素条件下nZVI/BC对沉积物中DBDPE去除的动力学参数
Table 1 Kinetics parameters of DBDPE removal by nZVI/BC under different influencing factors in sediment
投加量/ (g∙g−1) | 初始质量分数/ (mg∙kg−1) | 温度/ ℃ | 沉积物与水 质量比 | k1/ h−1 | r2 |
---|---|---|---|---|---|
0.02 | 10 | 25 | 1∶2 | 0.0064 | 0.659 |
0.04 | 10 | 25 | 1∶2 | 0.0089 | 0.633 |
0.08 | 10 | 25 | 1∶2 | 0.0117 | 0.652 |
0.10 | 10 | 20 | 1∶2 | 0.0159 | 0.830 |
0.10 | 10 | 25 | 1∶2 | 0.0190 | 0.793 |
0.10 | 10 | 30 | 1∶2 | 0.0260 | 0.821 |
0.10 | 15 | 25 | 1∶2 | 0.0138 | 0.724 |
0.10 | 20 | 25 | 1∶2 | 0.0118 | 0.787 |
0.10 | 10 | 25 | 2∶1 | ‒ | ‒ |
0.10 | 10 | 25 | 1∶1 | 0.0108 | 0.749 |
0.10 | 10 | 25 | 1∶3 | 0.0224 | 0.848 |
图6 不同影响因素下nZVI/BC对沉积物中DBDPE去除的准一级动力学模拟
Figure 6 The pseudo-first-order kinetics model of DBDPE removal by nZVI/BCunder different influencing factors in sediment
化合物 | 急性毒性/(mg∙L−1) | 慢性毒性/(mg∙L−1) | |||||
---|---|---|---|---|---|---|---|
鱼 (LC50) | 绿藻 (EC50) | 水蚤 (LC50) | 鱼 (ChV) | 绿藻 (ChV) | 水蚤 (ChV) | ||
DBDPE | 2.8×10−8 | 3.0×10−6 | 4.7×10−8 | 9.8×10−9 | 8.5×10−6 | 9.1×10−8 | |
Octa-BDPE | 6.9×10−6 | 2.0×10−4 | 8.9×10−6 | 1.8×10−6 | 3.2×10−4 | 8.5×10−6 |
表2 ECOSAR模型预测DBDPE及其降解产物的急性和慢性毒性
Table 2 Acute and chronic toxicity of DBDPE and its degradation products using ECOSAR software
化合物 | 急性毒性/(mg∙L−1) | 慢性毒性/(mg∙L−1) | |||||
---|---|---|---|---|---|---|---|
鱼 (LC50) | 绿藻 (EC50) | 水蚤 (LC50) | 鱼 (ChV) | 绿藻 (ChV) | 水蚤 (ChV) | ||
DBDPE | 2.8×10−8 | 3.0×10−6 | 4.7×10−8 | 9.8×10−9 | 8.5×10−6 | 9.1×10−8 | |
Octa-BDPE | 6.9×10−6 | 2.0×10−4 | 8.9×10−6 | 1.8×10−6 | 3.2×10−4 | 8.5×10−6 |
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