Analysis of 1H-benzotriazole removal efficiency from wastewater in individual process phases of a sequencing batch reactor SBR

IF 4.5 3区 工程技术 Q1 WATER RESOURCES
Joanna Struk-Sokołowska , Urszula Kotowska , Janina Piekutin , Piotr Laskowski , Artur Mielcarek
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引用次数: 5

Abstract

The research focused on a very dangerous and commonly used compound which has carcinogenic and mutagenic impact on living organisms. 1H-benzotriazole (1H-BTR) is used as a corrosion inhibitor for installations in industrial plants, in the production of biocides, detergents, drugs, tires, rubber, in refrigeration systems and de-icing substances, while its derivates are UV stabilizers in plastics, paints, films and sunscreens. It is also an additive in petroleum products (lubricants, hydraulic fluids). The paper presents quantitative changes of 1H-BTR after sequencing batch reactor (SBR) process. The studies have been carried out for 411 cycles of SBR during which concentration of 1H-BTR was changed in the range of 50–1000 μg L−1. SBR operating cycle consisted of 6 phases: filling (dilution-40 min), mixing I (dephospatation-20 min), aeration with stirring (nitrification and oxidation of organic compounds-300 min), mixing II (denitrification-30 or 60 min), settling and decantation (separation-40 min), downtime (90 or 60 min). The technological parameters of the activated sludge (sludge volume index, solids and hydraulic retention time) were as similar as possible to those maintained in the real wastewater treatment plant (WWTP). Mixed liquor suspended solids concentration was 3.50 kg m−3. Conducted studies showed that industrial wastewater containing 1H-BTR can be effectively treated in SBR. The conducted studies showed that removal of 1H-BTR with more than 80% efficiency is possible at effluent concentrations not exceeding 200 μg L−1. Higher concentrations of 1H-BTR in wastewater lead to a sharp decrease in removal efficiency. The lowest removal efficiency (56.6%) was recorded at the initial 1H-BTR concentration of 100 μg L−1. On the other hand, the highest efficiency (88.2%) at the initial concentration of 1000 μg L−1. The concentration of 1H-BTR in treated wastewater was 1.1 μg L−1 in the control reactor and from 7.2 to 434.0 μg L−1 for an initial concentration from 50 to 1000 μg L−1, respectively. The aeration phase was superior in terms of 1H-BTR removal, regardless of the benzotriazole doze in the raw wastewater. In the anaerobic mixing phases I and II in the SBR, the decomposition of the 1H-BTR was 5.3 and 4.9 times slower, respectively, compared to aerobic conditions.

Abstract Image

序批式SBR各工艺阶段对废水中h -苯并三唑的去除率分析
研究的重点是一种非常危险和常用的化合物,它对生物体具有致癌和诱变作用。h -苯并三唑(1H-BTR)被用作工业装置的缓蚀剂,用于生产杀菌剂、洗涤剂、药品、轮胎、橡胶、制冷系统和除冰物质,而其衍生物是塑料、油漆、薄膜和防晒霜中的紫外线稳定剂。它也是石油产品(润滑剂、液压油)的添加剂。介绍了序批式反应器(SBR)处理后1H-BTR的定量变化。研究进行了411次SBR循环,期间1H-BTR浓度在50-1000 μg L−1范围内变化。SBR运行周期包括6个阶段:填充(稀释-40分钟),混合I(脱磷-20分钟),曝气搅拌(硝化和氧化有机化合物-300分钟),混合II(反硝化-30或60分钟),沉淀和滗析(分离-40分钟),停机(90或60分钟)。活性污泥的工艺参数(污泥体积指数、固形物和水力停留时间)尽可能与实际污水处理厂保持的相似。混液悬浮物浓度为3.50 kg m−3。有研究表明,含1H-BTR的工业废水在SBR中可以得到有效的处理。所进行的研究表明,在废水浓度不超过200 μg L−1的情况下,h - btr的去除率可能超过80%。废水中h - btr浓度越高,去除率急剧下降。h - btr初始浓度为100 μg L−1时,去除率最低,为56.6%。另一方面,在初始浓度为1000 μg L−1时,效率最高(88.2%)。当初始浓度为50 ~ 1000 μ L−1时,对照反应器中h - btr的浓度分别为1.1 μ L−1和7.2 ~ 434.0 μ L−1。无论原废水中是否含有苯并三唑,曝气相对h - btr的去除率均较好。在SBR的厌氧混合阶段,h - btr的分解速度分别比好氧条件慢5.3倍和4.9倍。
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来源期刊
Water Resources and Industry
Water Resources and Industry Social Sciences-Geography, Planning and Development
CiteScore
8.10
自引率
5.90%
发文量
23
审稿时长
75 days
期刊介绍: Water Resources and Industry moves research to innovation by focusing on the role industry plays in the exploitation, management and treatment of water resources. Different industries use radically different water resources in their production processes, while they produce, treat and dispose a wide variety of wastewater qualities. Depending on the geographical location of the facilities, the impact on the local resources will vary, pre-empting the applicability of one single approach. The aims and scope of the journal include: -Industrial water footprint assessment - an evaluation of tools and methodologies -What constitutes good corporate governance and policy and how to evaluate water-related risk -What constitutes good stakeholder collaboration and engagement -New technologies enabling companies to better manage water resources -Integration of water and energy and of water treatment and production processes in industry
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