• 한국화재소방학회논문지
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• 제27권6호
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• pp.57-63
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• 2013

이 연구에서는 피페라지노메틸-비스-포스폰산(PIPEABP), 메틸피페라지노메틸-비스-포스폰산(MPIPEABP), N,N-디메틸렌디아미노메틸-비스-포스폰산(MDEDAP)으로 처리된 리기다 소나무의 연소성을 시험하였다. 15 wt%의 알킬렌디아미노알킬-비스-포스폰산 수용액으로 리기다 소나무에 3회 붓칠하여 실온에서 건조시킨 후, 콘칼로리미터(ISO 5660-1)를 이용하여 그의 연소성을 시험하였다. 그 결과, 알킬렌디아미노알킬-비스-포스폰산으로 처리한 시험편은 비스-디메틸아미노메틸 포스피닉산(DMDAP) (280 s)을 제외하고, 연소속도 감소에 의하여 무처리한 시험편에 비해 최대질량감소율 도달시간 ($TMLR_{peak}$) = (315~420) s을 지연시켰다. 그리고 그의 화학 합성물로 처리한 시험편은 무처리한 시험편보다 높은 연기발생률(TSRR) = (407.3~902.0) $m^2/m^2$과 높은 $CO_{mean}$ (0.0765~0.0832) kg/kg 값을 보였다. 특별히 피페라지노메틸-비스-포스폰산으로 처리한 시험편에 대하여 1차 연기발생속도(1st-SPR) = 0.0124 g/s 피이크는 무처리한 시험편에 비하여 낮았다. 이에 반하여 2차 연기발생속도(2nd-SPR) = 0.183 g/s 피이크는 높았다. 따라서 알킬렌디아미노알킬-비스-포스폰산으로 처리한 시험편은 처리하지 않은 시험편에 비하여 그의 연소 억제성을 부분적으로 향상시켰다.

• 한국화재소방학회논문지
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• 제27권4호
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• pp.21-26
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• 2013

이 연구에서는 비스-디메틸아미노메틸 포스핀산, 비스-디에틸아미노메틸 포스핀산, 비스-디부틸아미노메틸 포스핀산을 처리한 리기다 소나무의 연소성을 시험하였다. 시험편은 15 wt%의 비스-디알킬아미노알킬 포스핀산 수용액으로 리기다 소나무에 3회 붓칠하여 실온에서 건조시킨 후, 콘칼로리미터(ISO 5660-1)를 이용하여 그의 연소성을 시험하였다. 그 결과, 비스-디알킬아미노알킬 포스핀산으로 처리한 시험편은 처리하지 않은 시험편에 비하여 그의 연소 억제성을 부분적으로 향상시켰다. 비스-디알킬아미노알킬 포스핀산으로 처리한 시험편은 무처리한 시험편에 비해 총연기방출률($16.94{\sim}18.92m^2/m^2$)과 $CO_{2mean}$ 발생량(1.98~2.09 kg/kg)을 감소시켰다. 그러나 무처리한 시험편에 비해 최대질량감소율($16.94{\sim}18.92m^2/m^2$)과 1차-연기발생속도(0.0153~0.0167 g/s)를 증가시켰다. 따라서 비스-디알킬아미노알킬 포스핀산으로 처리한 시험편은 순수 리기다 소나무 시험편에 비하여 부분적으로 낮은 연소성질을 나타내었다.

• 환경위생공학
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• 제14권4호
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• pp.85-92
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• 1999

Indoor air quality tends to be the dominant contributor to personal exposure because most people spend over 90% of their time indoors. For some contaminants, exposure to indoor air poses a potentially greater health threat than outdoor air exposures. Indoor nitrogen dioxide ($NO_2$) levels are mainly affected gas range, flue gas spillage, kerosene heaters, wood-burning appliances and cigarette smoke. In addition, indoor $NO_2$ levels are influenced by such house characterization as surface reaction and air exchange rate. In this study, the measurements of indoor and outdoor $NO_2$ concentrations were taken using identical protocols, and information was collected on housing characteristics using identical questionnaires in 14 houses out of 15 houses for daily 30 daily 30 days in Brisbane, Australia.The usage of gas range was the most contributing factor in indoor $NO_2$ concentration in relation to house characteristics. Average indoor and outdoor ratios of NO2 concentration in electronic and gas cooking houses were $0.6{\pm}0.1$ and $0.9{\pm}0.2$, respectively. The frequency distributions of $NO_2$ concentration in each house were approximately log-normal Geometric mean of indoor $NO_2$ concentrations of electronic and gas cooking houses for daily 30 days ranged from 2.5 ppm to 11.5 ppm with a mean 6.8 and from 4.7 ppm to 28.6 ppm with a mean 15.6 ppm, respectively. The $NO_2$ concentrations between electronic and gas cooking houses were significantly different (p<0.05). Since each house has different life-style and house characteristics, sampling interval to measure the $NO_2$ levels was recommended above 7 days.

• Asian Pacific Journal of Cancer Prevention
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• 제15권24호
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• pp.10653-10658
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• 2015

Background: A very high incidence of lung cancer is observed in Mizoram and Manipur, North East India. We conducted a population based case control study to establish associations of p53 codon 72 polymorphisms and interactions with environmental factors for this high incidence. Material and Methods: A total of 272 lung cancer cases and 544 controls matched for age (${\pm}5years$), sex and ethnicity were collected and p53 codon 72 polymorphism genotypes were analyzed using a polymerase chain based restriction fragment length polymorphism assay. We used conditional multiple logistic regression analysis to calculate adjusted odds ratios and 95% confidence intervals after adjusting for confounding factors. Results: p53 Pro/Pro genotype was significantly associated with increased risk of lung cancer in the study population (adjusted OR=2.14, CI=1.35-3.38, p=0.001). Interactions of the p53 Pro/Pro genotype with exposure to wood smoke (adjusted OR=3.60, CI=1.85-6.98, p<0.001) and cooking oil fumes (adjusted OR=3.27, CI=1.55-6.87, p=0.002), betel quid chewing (adjusted OR=3.85, CI=1.96-7.55, p<0.001), tobacco smoking (adjusted OR=4.42, CI=2.27-8.63, p<0.001) and alcohol consumption (adjusted OR=3.31, CI=1.10-10.03, p=0.034) were significant regarding the increased risk of lung cancer in the study population. Conclusions: The present study provided preliminary evidence that a p53 codon 72 polymorphism may effect lung cancer risk in the study population, interacting synergistically with environmental factors.