Process for the removal of the lead content in the water

• 1. 一种去除地下水中铅铜镉的吸附材料及其制备方法和应用 [P] . 中国专利： CN112755962A . 2021-05-07
• 2. 一种去除水中铅的方法、装置、系统及金属介质的用途 [P] . 中国专利： CN112537855A . 2021-03-23
• 3. AN ECO-FRIENDLY PROCESS FOR THE REMOVAL OF CORROSION PRODUCTS ON LEAD amp; LEAD ALLOYS BY ELECTROLYTIC CLEANING USING NATURAL SEAWATER [P] . IN289341B . 2017-11-10

  机译： 天然海水电解清洗去除铅和铅合金上腐蚀产物的环保工艺

• 4. AN ECO-FRIENDLY PROCESS FOR THE REMOVAL OF CORROSION PRODUCTS ON LEAD amp; LEAD ALLOYS BY ELECTROLYTIC CLEANING USING NATURAL SEAWATER [P] . IN2003DE00637A . 2007-12-07

  机译： 天然海水电解清洗去除铅和铅合金上腐蚀产物的环保工艺

• 5. The planographic printing process by means of a "waterless" planographic printing plate with a residue-free heat-sensitive recording layer, which operates without material removal and fountain solution is coated with a content of water-insoluble components [P] . 德国专利： DE69816012T2 . 2004-02-12

  机译： 通过具有无残留热敏记录层的“无水”平版印刷版进行平版印刷工艺，该记录层无需去除材料即可运行，润版液涂有一定量的水不溶性成分

• 1. The Effect of Hydraulic Retention Times and Loading Rates on the Removal of Pollutants from Fish Processing Wastewater by Anaerobic Process [J] . Dao Khanh Chau, Tran Thanh Dai 食品科学与工程：英文版 . 2018,第006期
• 2. 2-34 Oxygen-content Controllable Graphene Oxide from Electron-beam Irradiated Graphite:Synthesis,Characterization,and Removal of Aqueous Lead(Pb(II)) [J] . Bai Jing, Yin Xiaojie, Qin Zhi 中国科学院近代物理研究所和兰州重离子研究装置年报：英文版 . 2016,第001期
• 3. Determination of 4-nonylphenol and 4-tert-octylphenol compounds in various types of wastewater and their removal rates in different treatment processes in nine wastewater treatment plants of Iran [J] . Bijan Bina, Farzaneh Mohammadi, Mohammad Mehdi Amin, 中国化学工程学报（英文版） . 2018,第001期
• 4. Enhanced Removal of Cadmium and Lead from Water by Ferrate Preoxidation in the Process of Coagulation [C] . Symposium on ferrates : Synthesis, properties, and applications in water and wastewater treatment . 2008
• 5. COPRECIPITATION AND ADSORPTION FOR REMOVAL OF CADMIUM, LEAD, AND ZINC BY THE LIME - SODA ASH WATER SOFTENING PROCESS (CRYSTALLIZATION, HEAVY METAL, CALCIUM-CARBONATE). [D] . CHANG, TSUN-KUO. 1985
• 6. Effects of processing on the proximate and metal contents in three fish species from Nigerian coastal waters [O] . Francisca I Bassey, Fehintola C Oguntunde, Chukwujindu M A Iwegbue, 2014
• 7. Effects of excessive impregnation, magnesium content, and pyrolysis temperature on MgO-coated watermelon rind biochar and its lead removal capacity [O] . Jingzhuo Zhang, Deyi Hou, Zhengtao Shen, 2020
• 8. Investigation of Lead Content in Paints and PCB (Polychlorinated Biphenyls) Content in Water Supply for Eagleton School [R] . Wang, L. K. , Wu, B. C. , Zepka, J. 1984

• 1. 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
• 2. Ammonia Removal from Wastewater through Combination of Absorption Process in the Membrane Contactor and Advance Oxydation Process in Hybride Plasma-Ozone Reactor [J] . Sutrasno Kartohardjono ,Puji Lestari Handayani ,Seswila Deflin . 环境科学与工程：A . 2012,第009期
• 3. 硝酸铅和金属铅作为对照品测定铅含量方法的探讨 [C] . 张宁 ,王俊菊 . 全国饲料及畜产品中重金属检测技术暨农副产品质量安全与仪器分析技术研讨会 . 2009
• 4. 工业污水中硝基苯酚三种异构体含量的测定与去除方法研究 [A] . 张鲜 . 2013