1.Reduction of precursors of chlorination by-products in drinking water using fluidized-bed biofilm reactor at low temperature.
Shu-Guang XIE ; Dong-Hui WEN ; Dong-Wen SHI ; Xiao-Yan TANG
Biomedical and Environmental Sciences 2006;19(5):360-366
OBJECTIVETo investigate the reduction of chlorination by-products (CBPs) precursors using the fluidized-bed biofilm reactor (FBBR).
METHODSReduction of total organic carbon (TOC), ultraviolet absorbance (UV254), trihalomethane (THM) formation potential (THMFP), haloacetic acid (HAA) formation potential (HAAFP), and ammonia in FBBR were evaluated in detail. Results The reduction of TOC or UV254 was low, on average 12.6% and 4.7%, respectively, while the reduction of THMFP and HAAFP was significant. The reduction of ammonia was 30%-40% even below 3 degrees C, however, it could quickly rise to over 50% above 3degrees C. Conclusions The FBBR effectively reduces CBPs and ammonia in drinking water even at low temperature and seems to be a very promising and competitive drinking water reactor for polluted surface source waters, especially in China.
Biofilms ; Chlorine ; Water Purification
2.A Case of Squamous Cell Carcinoma Treated with Chlorine Photodynamic Therapy.
Jong Yeob KIM ; Jae Eun CHOI ; Hyo Hyun AHN ; Young Chul KYE ; Soo Hong SEO
Annals of Dermatology 2012;24(4):488-490
No abstract available.
Carcinoma, Squamous Cell
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Chlorine
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Photochemotherapy
4.Inactivation of resistant Mycobacteria mucogenicum in water: chlorine resistance and mechanism analysis.
Yu Qiao CHEN ; Chao CHEN ; Xiao Jian ZHANG ; Qi ZHENG ; Yuan Yuan LIU
Biomedical and Environmental Sciences 2012;25(2):230-237
OBJECTIVETo better understand the mechanism of chlorine resistance of mycobacteria and evaluate the efficiency of various disinfection processes.
METHODSInactivation experiments of one strain Mycobacteria mucogenicum, isolated from a drinking water distribution system in South China were conducted with various chlorine disinfectants. Inactivation efficiency and disinfectant residual, as well as the formation of organic chloramines, were measured during the experiments.
RESULTSThis strain of M. mucogenicum showed high resistance to chlorine. The CT values of 99.9% inactivation by free chlorine, monochloramine and chlorine dioxide were detected as 29.6 +/- 1.46, 170 +/- 6.16, and 10.9 +/-1.55 min. (mg/L) respectively, indicating that chlorine dioxide exhibited significantly higher efficiency than free chlorine and monochloramine. It was also found that M. mucogenicum reacted with chlorine disinfectants more slowly than 5. aureus, but consumed more chlorine disinfectants during longer time of contact. Lipid analysis of the cell construction revealed that 95.7% of cell membrane lipid of M. mucogenicum was composed of saturated long chain fatty acids. Saturated fatty acids were regarded as more stable and more hydrophilic which enabled the cell membrane to prevent the diffusion of chlorine.
CONCLUSIONIt was concluded that different compositions of cell membrane might endow M. mucogenicum with a higher chlorine resistance.
Chlorine ; pharmacology ; Mycobacterium ; drug effects ; Water Microbiology
5.Effect of Sanitization on Raw Vegetables not Heated in Foodservice Operations.
Hye Kyung MOON ; Ji Young JEAN ; Chang Soon KIM
Journal of the Korean Dietetic Association 2004;10(4):381-389
The purpose of this study was to investigate effectiveness of sanitization on raw vegetables not heated in foodservice operations. Microbiological examinations of food materials and cooked food with leek Gukgalli were performed in 2 HACCP-implemented foodservices (A and B) appointed by Food and Drug Administrations, and in 2 other foodservices (C and D) not implemented HACCP. 'Washing and sanitizing raw vegetables' were monitored as CCP at A and B foodservices but only washing has been done in pre-preparation at C and D foodservices. Aerobic plate counts of received leek in A and B foodservices were above 10(7) CFU/g indicating very poor microbiological quality. After sanitization treatment (soaking for 5 minutes in chlorine water: chlorine density 50~100 ppm), its aerobic plate counts decreased to 7.06x10(5) CFU/g (A foodservice) and 4.31x10(5) CFU/g (B foodservice), coliform and faecal coliform were not detected. With this result, the effect of microbial reduction by sanitizer was conformed. But, the conditions of leek were still not acceptable by microbiological standards for ready-to-eat foods. After three more times of rinse has been done, the microbial conditions of leek became acceptable. In C and D foodservices, aerobic plate counts of leek showed decreasing trends by 2x4 times of washings but microbiological quality of leek after pre-preparation were unacceptable by microbiological standards for ready-to-eat foods (C foodservice: 3.58x10(5) CFU/g, D foodservice: 1.29x10(9) CFU/g). For the prevention of foodborne illness, sanitizing raw vegetables should be performed during pre-preparation of non-heated foods.
Chlorine
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Hazard Analysis and Critical Control Points
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Hot Temperature*
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Vegetables*
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Water
6.Two cases of anosmia suspected to be caused by chronic chlorine exposure in cleansing works.
Korean Journal of Occupational and Environmental Medicine 2005;17(2):155-159
OBJECTIVES: We report two cases of anosmia that were suspected to be caused by chronic chlorine exposure in cleansing works METHODS: We examined the cases in order to assess the work-relatedness of their anosmia. We conducted olfactory threshold test and olfactory perception test repeatedly at one-month intervals. Using ion chromatography, we analyzed the detergent that the workers had been using for several years before their olfactory function decreased. RESULTS: A 59-year-old male who had worked in a cleansing process for 10 years (1983-1993) and a 58-year-old female who had worked in the same process for 8 years (1987-1995) were diagnosed with anosmia. The cause of the anosmia was presumed to have been the chlorine gas that was generated from the process of heating the detergent-dissolved water, in which chloride was detected. CONCLUSIONS: This is the first report on anosmia due to chronic chlorine exposure. Greater attention needs to be focused on the prevention of anosmia because there are many workers who have been exposed to chlorine gas in chlorine treating and generating processes.
Chlorine*
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Chromatography
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Detergents
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Female
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Heating
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Hot Temperature
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Humans
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Male
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Middle Aged
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Olfaction Disorders*
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Olfactory Perception
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Water
7.Follow-up for lung function of patients with acute chlorine poisoning after recovery.
Chinese Journal of Industrial Hygiene and Occupational Diseases 2008;26(7):426-427
Adult
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Aged
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Chlorine
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poisoning
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Female
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Follow-Up Studies
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Humans
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Lung
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physiopathology
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Male
;
Middle Aged
;
Young Adult
9.Study on the reactions of azo compounds with acyl halides mediated by Sm/TiCl4.
Journal of Zhejiang University. Science. B 2006;7(3):198-201
Amides can be obtained in good to excellent yield by Sm/TiCl(4) mediated reductive cleavage of N=N bond in azo compounds and successive acylation in one pot. It offers an alternative method for the synthesis of amides from very simple starting materials directly.
Azo Compounds
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chemistry
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Chlorine Compounds
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chemistry
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Combinatorial Chemistry Techniques
;
methods
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Halogens
;
chemistry
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Samarium
;
chemistry
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Titanium
;
chemistry
10.Occurrence of haloacetic acids in drinking water in certain cities of China.
Hong ZHOU ; Xiao-Jian ZHANG ; Zhan-Sheng WANG
Biomedical and Environmental Sciences 2004;17(3):299-308
OBJECTIVESince haloacetic acids (HAAs), which are nonvolatile and of high carcinogenic risk, are common species of chlorinated disinfection by-products(DBPs) in drinking water, and little has been known in China, it is necessary to make a survey about the kinds and levels of HAAs in drinking water of the nation.
METHODHAAs were analyzed using gas chromatography with electron capture detector(GC/ECD) and relatively complex pretreatment process of sample was applied. Five main cities in different areas of China were chosen in the survey.
RESULTSStudies showed that the main species of HAAs in drinking water in China were DCAA and TCAA, ranging from 0.4 microg/L to 12.85 microg/L and from 0.56 microg/L to 10.98 microg/L, respectively. MBAA and DBAA were also detected in one city, ranging from 2.20 microg/L to 4.95 microg/L and 1.10 microg/L to 2.81 microg/L, respectively. Therefore, the contents of HAAs varied, usually no more than 25 microg/L. Based on the acquired data to date, it is known that the concentrations of HAAs in drinking water in China were surely under the limits of Sanitary Standard for Drinking Water Quality (China, 2001).
CONCLUSIONA wider survey of HAAs in drinking water should be conducted throughout the nation to get adequate data and information, the ultimate aim of which is to control HAAs pollution and keep the balance between microbiological safety insurance and chemical risk control, minimize the formation of DBPs and ensure the safety of water supply at the same time.
Acetates ; analysis ; China ; Chlorine ; chemistry ; Cities ; Environmental Monitoring ; Halogens ; chemistry ; Humans ; Seasons ; Water Purification ; Water Supply