• 한국환경보건학회지
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• 제32권2호
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• pp.171-178
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• 2006

The objectives of this study were to investigate the formation of trihalomethanes(THMs) and to compare the concentration level of THMs of swimming pools water by different disinfection methods such as chlorine, ozone-chlorine, and salt brine electrolysis generator (SBEG). The concentration of chloroform was the highest in the chlorine system, and the SBEG was the highest in the production of bromodichloromethane (BDCM), dibromochloromethane (DBCM) and bromoform. The average concentration of total trihalomethanes (TTHMs) in three disinfection systems were $64.5{\pm}27.4mg/l(SBEG),\;43.8{\pm}22.3mg/l(chlorine)$, and $30.6{\pm}16.1mg/l(ozone-chlorine)$, respectively. In chlorine and ozone-chlorine disinfection system, chloroform concentration was highest, followed by BDCN, then DBCM. In the SBEG, TTHMs was composed of 42% of chloroform, 28.9% of bromoform, 15.1% of BDCM and 14% of DBCM, respectively. The strongest correlation was obtained in the levels of chloroform and TTHMs in chlorine, and ozone-chlorine disinfection systems from both indoor and outdoor swimming pools ($r=0.989{\sim}0.999$, p<0.01). In the SBEG, the levels of BDCM and TTHMs showed a good correlation (r=0.913, p<0.01). In chlorine and ozone-chlorine disinfection systems at indoor swimming pools, pH, TOC and $KMnO_4$ consumption showed strong correlation with chloroform and TTHMs concentrations (p<0.01). In the SBEG, pH and TOC were also strongly correlated with chloroform (p<0.01). pH and TTHMs were correlated as well (p<0.05).

• 한국환경과학회지
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• 제13권1호
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• pp.55-59
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• 2004

The effect of ozone on the formation and the removal of disinfection byproducts(DBPs) of chlorination process was studied to elucidate the performance of water treatment process. The samples of raw water, prechlorination process, and preozonation process were analyzed quantitatively according to the Standard Methods for the Examination of drinking water. As a result, most of total trihalomethanes(THMs) which were formed in prechlorine treatment process was not removed in the preozonation process. Most of haloacetic acids(HAAs), haloacetonitriles(HANs), and chloral hydrate(CH) was removed in sedimentation and biological activated carbon(BAC) filtration processes. However, DBPs were increased more or less by postchlorine step. In particular, the formation of THMs and HAAs depends on ozone more than chlorine, but, the formation of HANs and CH depends on chlorine more than ozone. The seasonal variation of DBPs concentration for the year needs to be investigated to study the temperature effect because DBPs strongly depend on temperature among various efficient factors.

• 한국물환경학회지
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• 제21권6호
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• pp.676-681
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• 2005

This study was researched for disinfection by-products (DBPs) by preozonation, prechlorination and/or postchlorination. DBPs including trihalomethanes (THMs), haloacetic acids (HAAs), halonitriles, and aldehydes were analyzed by the treatment steps of prechlorination, preozonation, sedimentation, filtration, and postchlorination comparatively. THMs were detected as $52.20{\mu}g/L$ after prechlorination and decreased during sedimentation and filtration process. The HAAs and aldehydes increased more during preozonaiton than prechlorination. However, chlorinated DBPs and aldehydes increased more by postchlorination. Chlorinated DBPs formed by preozonation increased 26% more than the chlorination process. If aldehydes were included in the total DBPs, DBPs increased up to 39% by preozonation. Preozonation could increase the removal efficiency of organic carbon during the coagulation and sedimentation processes. Ozonation might produce aldehydes that are not permitted for drinking water regulations. Also, DBPs were produced by preozonation than by chlorination. These results would bring a need for alternative disinfection studies to decrease DBPs.

• Journal of Preventive Medicine and Public Health
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• 제16권1호
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• pp.79-88
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• 1983

There has been some evidence concerning the fact that trihalomethanes(THMs), toxic chlorinated compounds, may be present in drinking water. One of the important methodologies to evaluate the toxicity of THMs is to determine enzyme alteration in experimental animal tissues after treatment. This study was intended to investigate how lactic dehydrogenase(LDH) of rat tissues is affected by administration of chloroform($CHCl_3$) and dichloromonobromomethane($CHCl_2\;Br$). THMs, high dose(1/10 LD50) or low dose(1/50 LD50) of $CHCl_3$ or $CHCl_{2}Br$ were administered orally to experimental rats for 4 or 8 weeks. The treated groups of rats were sacrificed to determine LDH specific activity and isozyme pattern in various organs which were liver, thigh muscle, kidney and brain. The conclusions were obtained as follows: 1. Alteration of LDH activities and isozyme patterns were revealed before morphologic changes in tissues. 2. The LDH specific activities were increased significantly in liver and brain after administration of high concentrations of $CHCl_3$ and $CHCl_{2}Br$ for 4 weeks respectively. Otherwise, they were decreased significantly in liver, muscle and kidney after administration for 8 weeks. 3. The isozyme activities of LDH-4 and LDH-5 were increased in muscle, brain, and especially the liver. 4. It was more distinct for the decrement of LDH H-type isozyme than the increment of M-type isozyme in muscle.

• Korean Chemical Engineering Research
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• 제44권2호
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• pp.216-226
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• 2006

클로로포름(chloroform), 디클로로아세틱에시드(dichloroacetic acid; DCAA), 트리클로로아세틱에시드(trichloroacetic acid; TCAA) 등은 먹는 물의 염소소독 시 발생되는 주요한 소독부산물이다. 이 중 클로로포름과 DCAA는 발암물질로 분류되어 있어 이에 대한 분포특성연구는 서울시의 먹는 물의 안전성을 판단하기 위해 중요하다. 2002~2004년의 3년 동안 배급 수 계통별로 소독부산물을 분석하였다. 이 중 총트리할로메탄(total trihalomethanes; THMs)의 평균 농도가 정수장에서 생산된 물에서는 0.015 mg/L, 직접 각 가정으로 공급되는 직수에서는 0.019 mg/L, 물탱크를 경유해 각 가정으로 공급되는 물탱크 수에서는 0.023 mg/L로 체류시간이 증가함에 따라 그의 농도는 증가하는 것으로 나타났다. 또한, 수온의 영향으로 인해 여름철에 비교적 높은 농도로 검출되었다. THMs 이외의 다른 소독부산물들도 역시 유사한 경향을 나타내었다. 검출된 소독부산물의 양은 환경부 먹는물 수질기준의 1/4~1/6 정도의 낮은 수준이기 때문에 서울시 수돗물은 소독부산물에 있어 항상 안전한 것으로 나타났다.

• 수도
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• 통권44호
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• pp.6-12
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• 1988

This study was performed to measure the elimination effects of chlorine dioxide on phenol compounds, trihalomethanes (THMs) and algae in drinking water supply. The raw and chlorinated water were treated with 0.5ppm of chlorine dioxide. The phenols contained 0.052mg/1, 0.019mg/1 of raw and treatedwater was absolutely destroyed. The THMs was reduced to 50-60% of the concentration and the algae was inhibited to about 50% of the growth.

• Biotechnology and Bioprocess Engineering:BBE
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• 제7권1호
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• pp.31-37
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• 2002

This paper was investigated to clarify the possibility of a biodegradation of materials adsorbed on different porous granular-activated carbons (GACs) such as coal-& coconut-based GAC. Total organic carbon, humic substance and ammonia were used to compare their removal efficiencies. The objective of this study is to determine the adsorption capacity of bioregenerated GAC. When raw water reacted with chloride, the yield of THMs increased as a function of the input amount of chloride. The formation of trihalomethanes (THMs) was investigated in water treated with chlorine when humic acid was used as THM precursor. As the input amount of chloride in raw water increased by two or five-fold to remove the $NH_3$, the chloroform of the THMs significantly increased also five or ten-fold. It was found that the chloroform was significantly removed by the treatment of biological activated carbon (BAG) in comparison with the ozone treatment, and the removal efficiency of THMs in coal-typed GAC was $10-30\%$ better than coconut-typed GAC due to the biological degradation on the surface of the activated carbons.

• 한국응용과학기술학회지
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• 제21권4호
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• pp.364-369
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• 2004

It has been confirmed that some Trihalomethanes (THMs) suspected as carcinogens, can be formed during chlorination for water supply through the reaction of chlorine and humic substances in water. The electrochemical characteristics on activated carbon fiber filter (ACF) electrode were investigated to remove the THMs in the chlorination process of drinking water. The electrochemical removal efficiency depended on the applied voltage and flow rate. In this study, the best result showed that the removal efficiency of THMs was higher than 99%.

• Environmental Analysis Health and Toxicology
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• 제12권3_4호
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• pp.23-29
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• 1997

The main reason of applying chlorination is to sterilize microbes existing in the drinking water treatment. But chlorination could lead to the formation of disinfection by-products (DBPs) by the reaction of free chlorine with humic substance in the water. Especially the DBPs including trihalomethanes (THMs), haloacetic acids (HAAs), haloacetonitriles (HANs), and haloketones (HKs) exist in the tap water. The US environmental protection agency (US EPA) defines that trihalomethanes, dichloroacetic acid, trichloroacetic acid, and dichloroacetonitrile among DBPs are probable/possible human carcinogens. US EPA suggests maximum contaminant levels (MCLs) for THMs (80$\mu$g/L) and HAAs (60$\mu$g/L) in drinking water. In Korea, THMs in drinking water has been surveyed but DBPs in general has not been studied in drinking water practically. Therefore only THMs have been regulating as criteria compounds since 1990 but neither HAAs nor HANs. Researches on HAAs are yet to be found. HAA formation potentials(HAAFPs) have not been practiced. HAAs depends on the characteristics of water sources by chlorination. In this study, HAAFPs from three distinct sources were investigated by laboratory chlorination experiments. This study was performed to measure the level of HAAs in drinking water in Seoul area. At April 1996, after collecting the raw waters from the three sites with the different properties, the water samples were chlorinated at various conditions(pH 5.5, pH 7.0 and without pH adjustment) in the state of raw water to have 0. 5mg/L of residual chlorine concentration. And the raw water, treated water, and tap water of water treatment were collected to measure the HAAs concentration. The quantitative analysis of HAAs was conducted by US EPA methods.

• 한국환경과학회지
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• 제13권7호
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• pp.627-635
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• 2004

Evaluated were household THMs exposure associated with the use of municipal tap water treated with chlorine and with ozone-chlorine. The current study measured the THMs concentrations in the tap water and indoor and outdoor air in the two types of household, along with an estimation of THMs exposure from water ingestion, showering, and the inhalation of indoor air. Chloroform was the most abundant THMs in all three media, yet no bromoform was detected in any sample. Contrary to previous findings, the fall water THMs concentrations exhibited no significant difference between the chlorine and ozone-chlorine treated water. However, the spring median chloroform concentration in the tap water treated with chlorine (17.6 ppb) was 1.3 times higher than that in the tap water treated with ozone-chlorine (13.4 ppb). It is suggested that the effects of the water parameters should be considered when evaluating the advantage of ozone-chlorine disinfection for THMs formation over chlorine disinfection. The indoor air THMs concentration trend was also consistent with the water concentration trend, yet the outdoor air THMs concentrations did not differ significantly between the two types of household. The indoor to outdoor air concentration ratios were comparable with previous studies. The THMs exposure estimates from water ingestion, showering, and the inhalation of indoor air suggested that, for the residents living in the surveyed households, their exposure to THMs in the home was mostly associated with their household water use, rather than the indoor air. The THMs exposure estimates from tap water ingestion were similar to those from showering.