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应用马尔可夫链对水中多介质环境中芘的分布和归宿的季节性进行数值模拟。

Numerical simulation of seasonality in the distribution and fate of pyrene in multimedia aquatic environments with Markov chains.

机构信息

School of Resources and Environmental Engineering, Jilin Institute of Chemical Technology, NO. 45 Chengde Street, Jilin, 132022, People's Republic of China.

Institute of Grassland Science, Northeast Normal University, and Key Laboratory of Vegetation Ecology, Ministry of Education, Changchun, Jilin, 130024, China.

出版信息

Sci Rep. 2017 Aug 29;7(1):9796. doi: 10.1038/s41598-017-10569-7.

Abstract

This case study investigated the distribution and fate of organic pollutants in aquatic environments based on laboratory experiments and modeling. Pyrene (Pyr) is a hydrocarbon pollutant with adverse effects on aquatic ecosystems and human health, and was thus selected for this case study. The movement of Pyr was primarily influenced by its sorption from water onto sediment, and its desorption from sediment into water. Its elimination was mainly via biodegradation by microorganisms in sediment and by volatilization from water into air. The transport and elimination rates for Pyr were considerably influenced by temperature and moisture. Results of modeling with Markov chains revealed that the elimination of Pyr from water/sediment systems was the most rapid under wet conditions. Under average conditions, a Pyr concentration of 100 μg/L of in water in such a system declined to a negligible level over 250 h. Under wet conditions, this decrease occurred over 120 h. Finally, under dry conditions, it took 550 h to achieve the same degree of elimination.

摘要

本案例研究基于实验室实验和建模,调查了有机污染物在水生环境中的分布和归宿。芘(Pyr)是一种对水生生态系统和人类健康有不利影响的碳氢化合物污染物,因此被选为案例研究的对象。Pyr 的迁移主要受其从水中向沉积物的吸附以及从沉积物向水中的解吸影响。其消除主要通过沉积物中的微生物的生物降解以及从水中挥发进入空气来实现。Pyr 的迁移和消除速率受温度和湿度的显著影响。马尔可夫链建模的结果表明,在潮湿条件下,从水/沉积物系统中消除 Pyr 的速度最快。在平均条件下,系统中 100μg/L 的 Pyr 在水中的浓度在 250h 内降至可忽略的水平。在潮湿条件下,这一减少发生在 120h 内。最后,在干燥条件下,需要 550h 才能达到相同的消除程度。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/037c/5575142/ac563d4ed10a/41598_2017_10569_Fig1_HTML.jpg

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