Method of control and monitoring of the reduction of the organic micropollutants in the water holding

• 1. 一种用于同时去除水中微量重金属离子和有机污染物的纳米纤维膜的制备方法 [P] . 中国专利： CN109351210A . 2019-02-19
• 2. 一种再生水中微量有毒有害有机污染物的深度处理方法 [P] . 中国专利： CN104355393B . 2017.04.12
• 3. METHOD OF MONITORING AND MONITORING THE ABATEMENT OF ORGANIC MICROPOLLUTANTS IN WASTEWATER [P] . 法国专利： FR3009789A1 . 2015-02-27

  机译： 废水中有机微污染物的监测和监测方法

• 4. METHOD AND SYSTEM FOR WATER TREATMENT, PARTICULARLY FOR REMOVING ANTHROPOGENIC IMPURITIES IN THE FORM OF MICROPLASTIC AND/OR DISSOLVED ORGANIC-CHEMICAL MICROPOLLUTANTS [P] . 世界知识产权组织专利： WO2019219106A1 . 2019-11-21

  机译： 用于水处理的方法和系统，特别是用于去除微塑性和/或溶解的有机化学微形式的人为杂质

• 5. METHOD AND SYSTEM FOR ELIMINATING ORGANIC MICROPOLLUTANTS IN WASTEWATER BY MEANS OF A CERAMIC MEMBRANE ENZYME REACTOR [P] . 世界知识产权组织专利： WO2015177395A1 . 2015-11-26

  机译： 陶瓷膜酶反应器消除废水中有机微污染物的方法和系统

• 1. A one-pot method for controlled synthesis and selective etching of organic-inorganic hybrid perovskite crystals [J] . Yu Hou, Mengjiong Chen, Hongwei Qiao, 能源化学：英文版 . 2019,第006期
• 2. A one-pot method for controlled synthesis and selective etching of organic-inorganic hybrid perovskite crystals [J] . Yu Hou, Mengjiong Chen, Hongwei Qiao, 天然气化学（英文版） . 2019,第006期
• 3. Biochar Water Treatment for Control of Organic Micropollutants with UVA Surrogate Monitoring [J] . Kearns Joshua, Dickenson Eric, Aung Myat Thandar, Environmental Engineering Science . 2021,第5期
• 4. Polar organic chemical integrative sampler (POCIS): Application for monitoring organic micropollutants in wastewater effluent and surface water [J] . Miège C., Budzinski H., Jacquet R., Journal of environmental monitoring: JEM . 2012,第2期
• 5. MONITORING METHYL TERTIARY BUTYL ETHER (MTBE) AND OTHER ORGANIC MICROPOLLUTANTS IN GROUNDWATER: RESULTS FROM THE DANISH NATIONAL MONITORING PROGRAM [J] . RENE K. JUHLER, GITTE FELDING Water, Air, and Soil Pollution . 2003,第1a4期
• 6. Evaluation of different methods supporting swimming pool water disinfection in the aspect of removing organic micropollutants [C] . Anna Lempart, Edyta Kudlek, Mariusz Dudziak Conference on Interdisciplinary Problems in Environmental Protection and Engineering . 2019
• 7. Development of gas chromatography/mass spectrometric methods for monitoring of micro-organic pollutants in natural waters [D] . 門上 希和夫 1991
• 8. Recent trends in water analysis triggering future monitoring of organic micropollutants [O] . Torsten C. Schmidt -1
• 9. Polar organic chemical integrative sampler (POCIS): application for monitoring organic micropollutants in wastewater effluent and surface water [O] . Cécile Miège, Hélène Budzinski, Romain Jacquet, 2012
• 10. Nitroguanidine Wastewater Pollution Control Technology: Phase II Wastewater Characterization and Analytical Methods Development for Organics [R] . Burrows, E. P., Brueggemann, E. E., Hoke, S. H., 1984

• 1. Comparison of Using an Electronic System and Conventional Monitoring Method for Monitoring the Quality of Drinking Water and Defects Discovery in Rural Area Water Distribution Network of Abarkouh, Iran [J] . Reza Ali Fallahzadeh ,Maryam Gholami ,Elham Madreseh . 健康（英文） . 2015,第1期
• 2. Methods for Controlling and Reduction of Pollutions by Using Electromagnetic Field [J] . Munendra Jain ,Neeraj Jain . 地学前缘 . 2009,第S1期
• 3. BACKGROUND： Vibrio vulnifi cus inside the body could activate the NF-!B signaling pathwayand initiate the inflammatory cascade. The lung is one of the earliest organs affected by sepsisassociated with acute lung injury. High mobility group protein B1 （HMGB1） is an important late-actingpro-infl ammatory cytokine involving in the pathophysiology of sepsis. It is also involved in the injuryprocess in the lung, liver and intestine. There has been no report on the involvement of HMGB1 inVibrio vulnifi cus sepsis-induced lung injury.METHODS： Sixty rats were randomly divided into a normal control group （group A, n=10） anda Vibrio vulnificus sepsis group （group B, n=50）. Sepsis was induced in the rats by subcutaneousinjection of Vibrio vulnificus （concentration 6×108 cfu/mL, volume 0.1 mL/100g）） into the left lowerlimbs. The rats in group B were sacrifi ced separately 1, 6, 12, 24, and 48 hours after the infection.Their lungs were stored as specimens, lung water content was measured, and lung pathology wasobserved under a light microscope. The expressions of the HMGB1 gene and protein in the lungswere detected by RT-PCR and Western blot. Data were analyzed with one-way analysis of variance（ANOVA） and the LSD method for pair-wise comparison between the two groups. P〈0.05 wasconsidered statistically signifi cant.RESULTS： Compared to group A （0.652±0.177）, HMGB1 mRNA expression in the lungs ofgroup B was signifi cantly higher at 0 hour （1.161±0.358, P=0.013）, 24 hours （1.679±0.235, P=0.000）,and 48 hours （1.258±0.274, P=0.004） （P〈0.05）, and peaked at 24 hours. Compared to group A（0.594±0.190）, HMGB1 protein expression at 6 hours （1.408±0.567, P=0.026） after infection wassignificantly increased （P〈0. 05）, and peaked at 24 hours （2.415±1.064, P=0.000） after infection.Compared to group A （0.699±0.054）, lung water content was significantly increased at 6 hours（0.759±0.030, P=0.001）,12 hours （0.767±0.023, P=0.000）, 24 hours （0.771±0.043, P=0.000） and 48hours （0.789±0.137, P=0.000） after infection （P〈0.05）. Compared to group A, pathological changesat 12 hours in group B indicate marked pulmonary vascular congestion, interstitial edema andinfl ammatory infi ltration. Alveolar cavity collapse and boundaries of the alveolar septum could not beclearly identifi ed.CONCLUSION： Vibrio vulnifi cus sepsis can lead to injury in rat lungs, and increased HMGB1expression in lung tissue may be one of the mechanisms for injury from Vibrio vulnifi cus sepsis. [J] . Qiao-meng Qiu ,Zhong-wang Li ,Lu-ming Tang . 世界急诊医学杂志(英文) . 2011,第4期
• 4. 水中优先控制有毒有机污染物监测技术及在城市供水中的应用 [C] . 贾瑞宝 ,赵玉德 . 中国科协首届学术年会 . 1999
• 5. NaHSO3活化KMnO4快速氧化水中微量有机污染物的效能与机理 [A] . 孙波 . 2017