• Title/Summary/Keyword: UV photolysis

검색결과 80건 처리시간 0.018초

발암성 분자와 식품보존제의 광화학 및 열적 반응메카니즘 (Photochemical and Thermal Reaction Mechanism for the Reaction of Carcinogenic Molecules and Food Reservatives)

  • 김민식;채기수;김갑순;성대동
    • 한국식품영양학회지
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    • 제11권3호
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    • pp.267-271
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    • 1998
  • Seyferth 시약인 phenyl(tribromomethyl) mercury 및 diazomethane의 식품보존제인 dehydroacetic acid 및 coumarin과의 발암성과 그 반응기작을 분자 구조적 관점에서 알아보기 위하여 UV/vis 조건과 laser flash photolysis 시켰을 때의 결과는 다음과 같다. 1. Diazomethane과 Phenyl(tribromomethyl) mercury와 dehydroacetic acid와 diazomethane과의 반응은 광화학적 분해 반응에서 생성된 : CBr2와 : CH2 카르벤 중간체의 이탈기 효과에 따라 발암성이 크게 나타났다. 2. laser flash photolysis 상에서 반응시켰을 때 식품보존제의 발암성이 UV/vis 상에서의 photolysis 때보다 크게 나타났다.

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Phosphamidon과 Profenofos의 광분해성 (Photodegradation of Phosphamidon and Profenofos)

  • 민경진;차춘근
    • 한국환경보건학회지
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    • 제26권2호
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    • pp.49-58
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    • 2000
  • The present study was performed to investigate photodegradation rate constants and degradation products of phosphamidon and profenofos by the USEPA method. The two pesticides were very stable in 16 days exposure of sunlight from September 3 to 22, 1999 and humic acid had no sensitizing effect on the photolysis of each pesticide in sunlight. In the UV irradiation test, phosphamidon was rapidly degraded as increasing UV intensity. In case of UV irradiation with TiO2 and with TiO2 powder amount, degradation of profenofos showed no significant difference with UV irradiation. Photodegradation rate of profenofos was slower than that of phosphamidon. In order to identify photolysis products, the extracts of degradation products were analyzed by GC/MS. The mass spectra of photolysis products of phosphamidon were at m/z 153 and 149, those of the profenofos were at m/z 208 and 240, respectively. It was suggested that the photolysis products of phosphamidon were 0, 0-dimethyl phosphate(DMP) and N, N-diethylchloroacetamide, those of profenofos were 4-bromo-2-chlorophenol and 0-ethyl-S-propyl phosphate.

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Piperophos의 광분해 및 분해생성물에 대한 연구 (Photodegradation and Degradation Product of Piperophos)

  • 민경진
    • 한국식품위생안전성학회지
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    • 제19권2호
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    • pp.97-103
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    • 2004
  • Piperophos에 대한 광분해 실험을 수행하여 속도상수와 분해생성물을 측정하였다. 햇빛을 이용한 광분해 실험은 2003년 10월 3일부터 10월 22일 까지 하였으며 상당기간 동안 농약이 햇빛에 안정함을 확인할 수 있었고, humic acid의 광관여 효과가 없음을 알 수 있었다. 자외선을 이용한 광분해 실험에서 piperophos는 자외선을 단독 조사하였을 때 자외선의 세기가 클수록 상대적으로 빠르게 분해되었으며, 광분해 촉매제인 TiO$_2$를 첨가하였을 경우에는 첨가하지 않고 자외선만 조사한 경우보다 상대적으로 느리게 분해되었다. 또, TiO$_2$의 양을 증가시켜도 별 차이가 없었다. 광분해에 의한 분해산물을 확인하고자 UMS분석을 한 결과 piperophos의 분해생성물은 m/z=166의 O,O-dipropyl phosphorodithioate로 추정된다.

휘발성유기화합물의 광분해 제거 특성에 관한 연구 (The Study of VOCs Decomposition Characteristics Using UV Photolysis Process)

  • 서정민;정창훈
    • 한국환경과학회지
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    • 제11권7호
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    • pp.743-748
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    • 2002
  • UV photolysis process is little known in parts of air pollution treatment, so there are not many applications in field. Therefore we have to do more experiment and study application possibility for treatment of VOCs(Volatile organic compounds). To solve these problems, we have been studying for simultaneous application of this technology. It has shown that concentration of TCE and B.T.X., diameter of reactor and wavelength of lamp have effected on decomposition efficiency. Analysis of TCE and B.T.X. concentration was carried out by GC-FID. A cylinderical reactor consisting of a quartz tube and a centrally located lamp(${\psi}25mm$) was used. The length and diameter of reactor were 1800mm, 75mm. It has shown that the generated ozone concentration goes up 250ppm when using 64watt ozone lamp. When using Photolysis process only, the rates of fractional conversion of each material are TCE 79%, Benzene 65%, Toluene 68%, Xylene 76%. This phenomenon can be rationalized in terms of the different bond energy that indicates how easily VOCs species can be decomposed.

광산화 및 광촉매 공정에서 VOCs의 산화반응 속도 산출에 관한 연구 (A Study on the reaction rate constant by UV Photooxidation and Photo-catalytic oxidation process)

  • 정창훈;이경호
    • 한국환경과학회지
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    • 제13권1호
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    • pp.37-40
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    • 2004
  • In this study, the decomposition of gas-phase TCE, Benzene and Toluene, in air streams by direct UV Photolysis and UV/TiO$_2$ process was studied. For direct UV Photolysis, by regressing with computer calculation to the experimental results the value of reaction rate constant k of TCE, Toluene and Benzene in this work were determined to be 0.00392s$\^$-l/, 0.00230s$\^$-1/ and 0.00126s$\^$-1/, respectively. And the adsorption constant K of TCE, Toluene and Benzene in this work were determined to be 0.0519 mol$\^$-l/ ,0.0313mo1$\^$-1/ and 0.0084mo1$\^$-1/, respectively. For UV/TiO$_2$ system by regressing with computer calculation to the experimental results the value of reaction rate constant k of TCE, Toluene, and Benzene in this work were determined to be 5.74g/$\ell$$.$min, 3.85g/$\ell$$.$min, and 1.18g/$\ell$$.$min, respectively. And the catalyst adsorption constant K of TCE, Toluene, and Benzene in this work were determined to be 0.0005㎥/mg, 0.0043㎥/mg and 0.0048㎥/mg, respectively.

KINETICS OF ATRAZINE OXIDATION BY UV RADIATION AND OXALATE ASSISTED H2O2/UV PROCESSES

  • Choi, Hyun-Jin;Choi, Jong-Duck;Kim, Hyun-Kab;Lee, Tae-Jin
    • Environmental Engineering Research
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    • 제11권1호
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    • pp.28-32
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    • 2006
  • The degradation of atrazine was explored using UV alone, $H_2O_2/UV$, oxalate/UV and oxalate-assisted $H_2O_2/UV$. The addition of oxalate to the $H_2O_2/UV$ (oxalate-assisted $H_2O_2/UV$) process was the most effective method for the degradation of atrazine. The overall kinetic rate constant was split into the direct oxidation due to photolysis and that by the radicals from hydrogen peroxide or oxalate. In semi-empirical terms, the initial concentration of hydrogen peroxide had a greater contribution than that of oxalate for atrazine oxidation.

일부 유기인계 농약의 광분해성 (Photodegradation of some Organophosphorous Pesticides)

  • 민경진;차춘근
    • 한국식품위생안전성학회지
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    • 제14권4호
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    • pp.339-345
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    • 1999
  • Dichlorvos 및 methidathion에 대한 광분해 실험을 수행하여 속도상수와 분해생성물을 측정하였다. 햇빛을 이용한 광분해 실험은 1998년 9월 2일부터 9월 18일 까지 수행하였으며 두가지 농약이 상당기간 동안 안정함을 확인할 수 있었다. 또한 햇빛 아래서는 humic acid의 광관여 효과가 없음을 알 수 있었다. 자외선을 이용한 광분해 실험에서 dichlorvos의 광분해속도상수와 반감기는 각각 0.0208 및 33.3분으로 조사되었고, methidathion의 경우는 각각 0.6189 및 1.0분으로 조사되어 methidathion의 광분해는 4분 이내에 99% 이상의 매우 빠른 분해양상을 보였다. 두가지 농약 모두 3시간 이내에 분해되었고, 따라서 먹는물 정수처리시 농약의 분해가 필요할 때는 자외선을 이용하는 것이 좋을 것으로 생각된다. 또한, dichlorvos 및 methidathion은 자외선을 단독조사 하였을 때 보다 TiO$_2$를 첨가하였을 경우 분해는 다소 빠르게 진행되었다. 광분해에 의한 분해생성물을 확인하고자 GC/MS분석을 한 결과 dichlorvos에서는 분해생성물로 m/z=153의 Ο, Ο-dimethyl phosphate(DMP)를 확인하였다. Methidathion의 경우 분해생성물로 m/z=198 과 m/z=214로 각각 Ο, Ο-dimethyl phosphorothioate(DMTP)와 Ο, Ο-dimethyl phosphorodithioate(DMDTP)를 확인하였다.

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광반응을 이용한 Triclosan 분해에서의 UV 광세기와 파장의 효과 (The Effect of UV Intensity and Wavelength on the Photolysis of Triclosan (TCS))

  • 손현석;최석봉;;조경덕
    • 대한환경공학회지
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    • 제27권9호
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    • pp.1006-1015
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    • 2005
  • 본 연구에서는 항균제로 광범위하게 사용되는 triclosan (TCS)의 광분해시, 광분해 효율을 결정하는 OH 라디칼의 기여도를 조사하였다. TCS의 광분해 반응은 365 nm에서 모든 광세기 조건과 254 nm에서 낮은 광세기 조건들에서, 반응 초기 약 5분에서의 분해양상은 유사일차 속도반응 모델을 따르고 있었다. 또한 TCS의 광분해시 메탄올을 $H_2O$ 대신에 용매로 사용하였을 경우 OH 라디칼의 저해작용에 의하여 TCS 분해속도가 감소되었다. TCS의 광분해 속도는 파장이 감소하고, 광세기가 증가함에 따라 유의한 증가를 보였다. TCS의 광분해시 254 nm에서는 $5.77{\times}10^{-5}$ einstein $L^{-1}min^{-1}$이상의 광세기와, 365 nm에서는 $1.56{\times}10^{-4}$ einstein $L^{-1}min^{-1}$ 보다 낮은 광세기 조건에서 photon의 기여도가 증가함을 보였다. 또한 photon의 기여도가 큰 광세기 조건들에서의 TCS에 의해 이용된 quantum yield는 254 nm보다 365 nm에서 높은 효율을 보였다. TCS의 중간부산물로서는 dibenzodichloro-p-dioxin (DCDD)와 dibenzo-p-dioxin가 365 nm하의 $1.37{\times}10^{-4}$$1.56{\times}10^{-4}$ einstein $L^{-1}min^{-1}$의 광세기 조건에서 모두 검출되었다. Dichloro-phenol과 phenol 역시 광반응의 부산물로서 모든 실험에서 발견되었다. 실험 결과를 토대로 TCS의 광분해 메커니즘을 제안하였다.

PCBs의 광화학적 연구: NaOH 및 휴믹산 (humic acid, HA)에 의한 분해특성 (Effects of NaOH and Humic Acid on the UV Photolysis of PCBs)

  • 신혜승;김재현
    • 한국환경보건학회지
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    • 제40권2호
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    • pp.147-156
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    • 2014
  • Objectives: This study was carried out to examine whether the apparent photolysis with or without sensitizers [NaOH and humic acid (HA)] was prompted photodegradation of polychlorinated biphenyl (PCB) in aqueous solution. Methods: PCBs photodegradation occurred using fluorescence black lamps at ${\lambda}_{max}=300nm$. PCB congeners were exposed in 10 ppm HA or 0.05N NaOH solutions, to investigate the decreasing profile of PCB concentration with time. The PCBs were then analyzed by gas chromatography/mass spectrometry (GC-MS). Reductive degradation profile of PCB congeners in the presence of both sensitizers under oxygen-saturated protic conditions was described using the wind-rose diagrams. Results: Use of HA or NaOH decreased PCB concentration with time in the dark and on irradiation, indicating that photolysis underwent through reductive dechlorination through energy transfer and possibly with reactive oxygens. The dechlorination was marked by a chromatographic shift, observed in the GC-MS plots. Therefore it is logical to assume that increasing the dose of sensitizers would increase the photodegradation rates of PCBs. The half-lives of pentachloro-PCB (penta-3) in 0.05N NaOH and 10 ppm HA were estimated at about 47 hours and 39 hours, respectively, under the same experimental conditions of photolysis. It was found that the rate of photolysis of pentachloro-PCB in aqueous solution followed apparent first-order kinetics compared to other congeners. Conclusion: Photochemical degradation (using 328 nm UV light) of penta- and hexa-PCBs in HA or alkaline solution is a viable method for pretreatment method. The results are helpful for the further comprehension of the reaction mechanism for photolytic dechlorination of PCBs in aquatic system.

디아오화합물의 광분해반응과 카르벤 중간체의 확인 (Photolysis of Diazotetracyanocyclopentadiene and Identification of Carbene Intermediate)

  • 김민식;엄태섭;성대동
    • 한국식품영양학회지
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    • 제7권1호
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    • pp.29-35
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    • 1994
  • Photolysis of diazotetracyanocyclopentadiene has been investigated by means of IR and UV-vis spec troscopy in Ar matrix. Parent carbene is produced in low yield and could be detected by UV-vis spectroscopy and IR spectroscopy. The carbene produced from the diazo compound is very photolabile and also decay thermally at temperature as low as 10K. When the diazo compound is photolyzed the Arrhenius plots show a tunneling effect that is not shown as non linearity.

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