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硝化颗粒对四环素的吸附和生物降解及四环素对颗粒的毒性。

Sorption and biodegradation of tetracycline by nitrifying granules and the toxicity of tetracycline on granules.

机构信息

Shandong Provincial Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Jinan, China.

出版信息

J Hazard Mater. 2011 Jul 15;191(1-3):103-9. doi: 10.1016/j.jhazmat.2011.04.048. Epub 2011 Apr 19.

Abstract

This paper examines the simultaneous sorption and biodegradation performance of tetracycline (TC) by the nitrifying granular sludge as well as the short-term exposure toxicity of TC. The removal of TC was characterized by a quick sorption and a slow process of biodegradation. The adsorption process fits pseudo-second-order kinetic model, with a complex mechanism of surface adsorption and intra-particle diffusion. Both temperature and mixed liquor suspended solid (MLSS) influenced TC sorption to the granules. TC biodegradation was enhanced with the increase of COD and NH(4)(+)-N concentrations, with except of the NH(4)(+)-N concentrations higher than 150 mg/L. With the ATU addition, TC degradation was weakened remarkably, indicating a synergistic effect of multiple microbes. Results of the short-term exposure (12h) effects showed that the respirometric activities of the microbes decreased greatly. The addition of TC also decreased the rate of NH(4)(+)-N utilization considerably, with the half saturation constant (K(s)) increasing from 297.7 to 347.2 mg/L.

摘要

本文研究了硝化颗粒污泥对四环素(TC)的同步吸附和生物降解性能以及 TC 的短期暴露毒性。TC 的去除过程表现为快速吸附和缓慢的生物降解过程。吸附过程符合准二级动力学模型,具有表面吸附和颗粒内扩散的复杂机制。温度和混合液悬浮固体(MLSS)均影响 TC 对颗粒的吸附。随着 COD 和 NH(4)(+)-N 浓度的增加,TC 生物降解得到增强,除了 NH(4)(+)-N 浓度高于 150mg/L 以外。随着 ATU 的添加,TC 的降解明显减弱,表明多种微生物存在协同作用。短期暴露(12h)效应的结果表明,微生物的呼吸活性大大降低。TC 的添加也大大降低了 NH(4)(+)-N 的利用速率,半饱和常数(K(s))从 297.7mg/L 增加到 347.2mg/L。

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