• 한국환경과학회지
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• 제12권6호
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• pp.665-676
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• 2003

본 연구는 서울지역의 PM$_{2.5}$의 화학적 조성을 조사하기 위하여 2000년 10월 1일부터 200l년 9월 26일까지 계절별(봄, 여름, 가을 겨울)로 PM$_{2.5}$ dichotomous air sampler를 이용하여 포집한 후, ICP-MS를 이용하여 검출한계 이상인 13가지의 중금속 성분(Al, As, Ba, Ca, Cd, Cr, Cu, Fe, Mn, Pb, Si, V, Zn)과 IC를 이용하여 5가지의 수용성 이온성분($Na^{+}$, NH$_4$$^{+}$, Cl￣, NO$_3$$^{-}$ , SO$_4$$^2$￣)을 측정/분석하였다. 분석결과에 얻어진 PM$_{2.5}$의 농도와 화학적 성분의 농도를 계절별로 비교하였으며, 중금속 성분의 정성적인 발생원의 기여도를 파악하기 위하여 주성분 분석을 실시하였다.1) 조사기간 중 PM$_{2.5}$의 계절별 농도는 겨울(33.91 $\mu\textrm{g}$/㎥) > 봄(28.79 $\mu\textrm{g}$/㎥) > 가을(18.62 $\mu\textrm{g}$/㎥) >여름(14.92 $\mu\textrm{g}$/㎥) 순으로 조사되어 주로 겨울철에 대기중 PM$_{2.5}$의 농도가 높은 것을 확인할 수 있었다. PM$_{10}$에 대한 PM$_{2.5}$의 기여도는 33.7~83.5 %로 나타났으며, PM$_{2.5}$PM$_{10}$의 평균비는 0.54로 조사되었고, 회귀분석에서 PM$_{10}$=4.20PM$_{2.5}$+.9.91, $R^2$=0.73 (p < 0.05)의 회귀관계식을 나타나 PM$_{2.5}$로 PM$_{10}$을 73% 수준에서 설명할 수 있었으며 통계적으로 유의한 값을 보였다. 2) PM$_{2.5}$의 중금속 성분은 Si > Fe > Al> Zn >Ca>Ba>V>Pb>As>Cu>Cr>Cd 순으로 높은 농도를 보였다. 중금속 성분의PM$_{2.5}$PM$_{10}$의 비는 인위적인 발생원에서 기인하는 Cd, Cr, Pb, V, Zn과 같은 중금속 성분의 비율이 높은 조사되었고, 자연적인 발생원에서 기인하는 Al, Ca, Fe, Mn, Si와 같은 중금속 성분의 비율이 낮게 조사되었다 특히 Al, Ca, Fe의 비율이 봄철에 높아 중국에서 발생한 황사의 영향을 받은 것으로 사료된다. 3) PM$_{2.5}$ 중 이온 성분의 농도는 NO$_3$￣ > SO$_4$$^2$￣ > Cl￣ > NH$_4$$^{+}$ 순으로 조사되었으며, PM$_{2.5}$PM$_{10}$의 비를 조사한 결과, NO$_3$￣,SO$_4$$^2$￣, Cl￣의 비율이 높아 PM$_{10}$에 포함되어 있는 PM$_{2.5}$가 산성오염물질에 많은 영향을 받는 것으로 조사되었다 4) PM$_{2.5}$의 정성적인 발생원을 추정하기 위해 중금속 성분에 대한 주성분 분석의 결과 3개의 주성분으로 나누어 졌으며, 주요 발생원은 자연발생원인 토양성분과 석유연료 연소에서 배출되는 성분으로 추정되어 이 발생원이 중금속 성분 농도에 영향을 미치는 것으로 사료되며, PM$_{2.5}$의 화학적 성분은 지역여건과 기상조건, 계절변동에 많은 영향을 받는 것으로 사료된다. 이상의 연구결과에서 PM$_{10}$에 비해 인체에 유해한 화학적 성분(중금속, 이온 성분)이 포함되어 있는 PM$_{2.5}$에 대한 철저한 관리 및 규제 설정이 요구되며, 측정지점의 특성상 자동차 배기가스와 금속제련 및 가공에 의한 영향을 주로 받는 것으로 추정되었다 또한 지역여건과 기상조건에 영향을 많이 받는 PM$_{2.5}$에 대한 지속적인 연구와 자료축적이 요구되고 발생원에 대한 정량적인 기여도를 평가하기 위한 연구가 필요하다고 생각된다. 연구가 필요하다고 생각된다.기 위한 연구가 필요하다고 생각된다. 연구가 필요하다고 생각된다.

• 한국환경과학회지
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• 제26권1호
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• pp.29-36
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• 2017

Aerosol mass size distributions were investigated at 865 m high the of Jirisan national park. A nanosampler cascade impactor was used to collect aerosols. The atmospheric aerosol particles had a unimodal mass size distribution, which peaked at $0.5-1.0{\mu}m$, and a mass aerodynamic diameter of $1.13{\mu}m$. The annual average concentrations of TSP, $PM_{10}$, $PM_{2.5}$, $PM_1$, $PM_{0.5}$ and $PM_{0.1}$ were $20.9{\mu}g/m^3$, $19.3{\mu}g/m^3$, $14.9{\mu}g/m^3$, $10.7{\mu}g/m^3$, $5.3{\mu}g/m^3$, $1.2{\mu}g/m^3$, respectively. TSP concentrations were below $30{\mu}g/m^3$ during the sampling period. On average $PM_{10}$, $PM_{2.5}$, $PM_1$, $PM_{0.5}$ and $PM_{0.1}$ made up 0.91, 0.70, 0.41, 0.19 and 0.07 of TSP, respectively. The annual average of PM2.5/PM10 ratio was 0.77.

• 한국환경과학회지
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• 제27권7호
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• pp.577-586
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• 2018

This research investigated the characteristics of $PM_{10}$ and $PM_{2.5}$ concentration at roadside (Choryangdong) and residential (Sujeongdong) locations in Busan. The $PM_{10}$ concentration at roadside and residential locations were 50.5 and $42.9{\mu}g/m^3$, respectively, and $PM_{2.5}$ at roadside and residential were 28.1 and $23.9{\mu}g/m^3$, respectively. The roadside/residential ratio of $PM_{10}$ and $PM_{2.5}$ concentration were 1.18, and the $PM_{2.5}/PM_{10}$ ratio at roadside and residential were 0.55 and 0.56, respectively. The $PM_{10}$ concentration in spring at roadside were $64.6{\mu}g/m^3$, and were the highest, followed by $48.0{\mu}g/m^3$ and $45.2{\mu}g/m^3$ in winter and summer. Number of exceedances per year of the daily limit value for $PM_{10}$ at roadside and residential were 66 and 39 days, respectively. The $PM_{10}$ and $PM_{2.5}$ concentration, and $PM_{2.5}/PM_{10}$ ratio at roadside were $53.0{\mu}g/m^3$, $29.0{\mu}g/m^3$ and 0.55 for day, and $45.5{\mu}g/m^3$, $26.7{\mu}g/m^3$ and 0.59 for night, respectively. These results indicate that understanding the relationship between roadside and residential could provide insight into establishing a strategy to control urban air quality.

• 대한핵의학회지
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• 제14권1호
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• pp.1-8
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• 1980

Serum TSH levels were measured by radioimmunoassay before and after intravenous administration of synthetic thyrotropin-releasing hormone (TRH) to 15 normal subjects and 55 patients with primary thyroid disease (14 patients with euthyroidism, 24 patients with thyrotoxicosis and 17 patients with hypothyroidism) to evaluate pituitary TSH reserve and its diagnostic availability. The observed results were as follows. 1. In normal subjects, serum TSH responses to synthetic TRH were $3.2{\pm}1.0$ at 0min (baseline TSH level), $8.0{\pm}4.0$ at 10min, $11.7{\pm}5.0$ at 20min, $13.7{\pm}7.1$ at 30min, $9.7{\pm}5.0$ at 60min., $5.2{\pm}2.0$ at 120min. and $3.6{\pm}0.4{\mu}U/ml$ at 180 min. Serum TSH peaked at $20{\sim}30$ minutes and returned nearly to baseline at 180minutes. 2. In euthyroid group, serum TSH responses to synthetic TRH were $3.3{\pm}1.6$ at 0min, $8.6{\pm}8.0$ at 10min, $10.9{\pm}8.5$ at 20min, $12.5{\pm}8.4$ at 30min, $9.0{\pm}5.9$ at 60min, $5.6{\pm}2.6$ at 120min and $3.5{\pm}1.3{\mu}U/ml$ at 180min. No significant difference revealed between euthyroid group and normal subjects (p>0.05). 3. In hyperthyroid group, serum TSH responses to synthetic TRH were $1.5{\pm}0.6$ at 0min, $2.2{\pm}0.8$ at 10min., $2.3{\pm}1.0$ at 20min., $2.4{\pm}1.5$ at 30min., $2.1{\pm}1.1$ at 60min., $1.9{\pm}0.2$ at 120min. and $1.5{\pm}0.8{\mu}U/ml$ at 180min., No response to TRH showed. 4. In hypothyroid group, mean values of serum TSH response to synthetic TRH were 42.0 at 0min., 60.6 at 10min., 124.8 at 20min., 123.0 at 30min., 101.6 at 60min., 64.3 at 120min. and $15.5{\mu}U/ml$ at 180 min., Patients with primary hypothyroidism showed an exaggerated TSH response to synthetic TRH despite their high basal TSH. 5. Side effects attending synthetic TRH administration were transient nausea (59.0%), desire to micturate (59.0%), feeling of flushing(19.7%), dizziness (45.9%), metallic taste (9.8%) and headache (19.7%). Any side effect didn't show in 16.4%. These symptoms began almost immediately after TRH intravenous injection and lasted several minutes, and not related to dose or response in the person experiencing it.

• 한국산업보건학회지
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• 제17권1호
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• pp.13-20
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• 2007

This study was performed to investigate the concentrations of PM($PM_{10}$, $PM_{2.5}$, $PM_{1}$) and it's affecting factors in the subway from line 1 to line 8 in Seoul metropolitan area, from Sep. 1 to 30, 2005. PM concentrations were measured at the entrances and centers in subway passenger cabins by a light scattering equipment. And the affecting factors to PM were estimated based on the number of passenger, door open and close and running area etc. The geometric means of $PM_{10}$, $PM_{2.5}$ and $PM_{1}$ concentration in Seoul subway passenger cabins were $214{\mu}g/m^3$, $86.6{\mu}g/m^3$ and $27.0{\mu}g/m^3$, respectively. These mean concentrations in subway carriage were higher when it ran on an underground track than on a ground track. And running time(7AM-9AM, 11AM-13PM, 6PM-8PM) significantly influenced to the concentrations of $PM_{10}$, $PM_{2.5}$ and $PM_{1}$. Daily profile of $PM_{10}$ and $PM_{2.5}$, $PM_{1}$ expressed as an 10 minutes average, showed similar variation pattern over day period. In correlation analysis, significant relations among $PM_{10}$, $PM_{2.5}$ and $PM_{1}$ were detected(p〈0.01). In particular, correlation coefficient between $PM_{10}$and $PM_{1}$ was highly significant(r=0.94). Further study is needed to identity the sources of PM in subway cabins and to compare pollutants concentration among subway lines.

• 시큐리티연구
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• 제36호
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• pp.93-109
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• 2013

본 연구에서는 경호, 경비현장에서 이루어지는 대치상황에서 경호, 경비원의 장비 중 삼단봉을 선택하여 머리치기 동작의 운동학적 분석을 실시하였다. H대학교 경호학과 학생 출신10명을 대상으로 연구를 실시하였다. 숙련자 그룹에서 삼단봉 교육 프로그램 실시하였고, 숙련자그룹과 비숙련자 그룹으로 연구 하였다. 구간별 소요시간은 숙련자 (e2) 0.428sec 비숙련자 0.435 sec, (e3) 에서는 숙련지 0.230 sec 비숙련자 0.232 sec 소요되었으며, 비숙련자 그룹에서 소요시간이 많이 소요된 것으로 나타났다. 신체중심 이동 변위는 좌, 우 숙련자$2.16{\pm}0.95cm$, $3.78{\pm}1.42cm$, 전체적으로 $5.94{\pm}2.03cm$ 변화를 보였다. 비숙련자 $2.97{\pm}1.01cm$, $4.56{\pm}1.57cm$, 전체적으로 $7.53{\pm}2.13cm$ 변화를 보였고, 전, 후 이동에서는 숙련자$32.48{\pm}3.86cm$, $35.21{\pm}4.64cm$, 전체적으로 $69.36{\pm}5.72cm$ 변화를 보였다. 비숙련자 $34.50{\pm}6.12cm$, $37.04{\pm}3.70cm$, 전체적으로 $71.46{\pm}7.17cm$ 변화를 보였다. 그리고 상, 하 이동변위에서는 숙련자 $5.62{\pm}2.49cm$, $4.54{\pm}1.87cm$, 전체적으로 $10.11{\pm}1.57cm$ 변화를 보였다. 비숙련자 $6.33{\pm}1.78cm$, $4.86{\pm}1.85cm$, 전체적으로 $10.68{\pm}1.81cm$ 변화를 보였다. 손목관절의 각도 변화에서 손목각도이며, 숙련자e1, $114.62{\pm}7.13$, e2 $68.27{\pm}6.37$, e3 $131.64{\pm}6.27$, 비숙련자 e1, $112.62{\pm}6.13$, e2 $66.28{\pm}7.38$, e3 $137.42{\pm}4.28$ 팔꿉치 관절의 각도 변화이며, 숙련자 e1, $132.31{\pm}6.55$, e2 $117.92{\pm}8.42$, e3 $144.41{\pm}6.32$, 비숙련자 e1, $133.58{\pm}8.56$, e2 $114.45{\pm}8.21$, e3 $139.89{\pm}4.38$ 어깨관절의 각도 변화이며, 숙련자 e1, $13.55{\pm}3.85$, e2 $131.42{\pm}11.24$, e3 $78.32{\pm}6.28$, 비숙련자 e1, $9.45{\pm}1.23$, e2 $136.74{\pm}13.21$, e3 $79.75{\pm}4.24$, 각 변화를 보였다.

• 한국환경과학회지
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• 제26권9호
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• pp.1045-1055
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• 2017

Characterization of spatio-temporal variations in $PM_{2.5}$ in Gyeongnam (GN) province during 2015-2016 was investigated to assess the air quality in this area in terms of fine particles. Yearly mean concentrations of $PM_{2.5}$ ranged from 19.1 to $29.5{\mu}gm^{-3}$. High concentrations of $PM_{2.5}$ were observed in spring ($21.2-30.3{\mu}gm^{-3}$) and winter ($20.2-30.3{\mu}gm^{-3}$). Low concentrations of $PM_{2.5}$ were generally observed in fall ($16.2-23.2{\mu}gm^{-3}$). $PM_{2.5}$ concentration was highest in the morning (10 AM). The fractions of $PM_{2.5}$ in $PM_{10}$ were 0.51-0.62 and two were significantly correlated (r=0.779-0.830), suggesting common sources (fossil fuel combustion, mobile sources, etc). CO was significantly correlated with $PM_{2.5}$ in highly urbanized areas such as the city of Changwon (CW, r=0.711), compared to other air pollutants ($SO_2$, $NO_2$, and $O_3$), suggesting dominance of industrial combustion sources.

• The Korean Journal of Physiology
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• 제15권1호
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• pp.45-51
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• 1981

The aim of this study was to investigate the pulmonary function tests of athletes related to Running, Swimming, Cycle, Taekwando, Wrestling, Boxing, Yudo, Badminton, Base-ball, Soccer, Hand-ball, Basket-ball and Volley-ball. Subjects were 269 athletes from 18 to 22 years of age. They were college students and citizens. The results are as follows: 1) Frequency of breath: (cycles/min., $M{\pm}S.D$) Running shows $13{\pm}3.6$, Swimming $12{\pm}3.2$, Cycle $13{\pm}3.4$, Taekwondo $12{\pm}4.0$, Wrestling $14{\pm}2.5$, Boxing $15{\pm}4.5$, Yudo $13{\pm}3.2$, Badminton $14{\pm}5.7$, Base-ball $15{\pm}6.2$, Soccer $13{\pm}2.5$, Hand-ball $14{\pm}2.5$, Basket-ball $12{\pm}5.6$, Volley-ball $12{\pm}4.2$(Table 2, Fig. 1). 2) Vital capacity: (1, $M{\pm}S.D$) Running shows $4.29{\pm}0.634$, Swimming $4.30{\pm}0.608$, Cycle $4.08{\pm}0.718$, Taekwondo $4.32{\pm}0.595$, Wrestling $4.40{\pm}0.663$, Boxing $4.45{\pm}0.779$, Yudo $4.58{\pm}0.389$, Badminton $3.98{\pm}0.556$, Base-ball $3.99{\pm}0.617$, Soccer $4.42{\pm}0.728$, Hand-ball $4.23{\pm}0.397$, Basket-ball $4.28{\pm}0.426$, Volley-ball $4.60{\pm}0.620$(Table 2, Table 3, Fig. 2). 3) Tidal volume: (ml, $M{\pm}S.D$) Running shows $615{\pm}180$, Swimming $603{\pm}121$, Cycle $529{\pm}189$, Taekwondo $726{\pm}112$, Wrestling $512{\pm}90$, Boxing$622{\pm}134$, Yudo $583{\pm}89$, Badminton $672{\pm}121$, Base-ball $714{\pm}97$, Soccer $579{\pm}89$, Hand-ball $507{\pm}69$, Basket-ball $628{\pm}133$, Volley-ball $597{\pm}144$(Table 2, Fig.3). 4) Breath holding time : (sec., $M{\pm}S.D$) Running shows $64{\pm}18.8$, Swimming $81{\pm}23.0$, Cycle $54{\pm}13.6$, Taekwondo $55{\pm}11.8$, Wrestling $78{\pm}12.5$, Boxing $63{\pm}9.6$, Yudo $71{\pm}14.4$, Badminton $62{\pm}9.8$, Base-ball $58{\pm}8.9$, Soccer $65{\pm}10.9$, Hand-ball $66{\pm}7.6$, Basket-ball $62{\pm}8.8$, Volley-ball $57{\pm}13.4$(Table 2, Fig.4).

• 한국환경보건학회지
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• 제20권1호
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• pp.75-82
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• 1994

Bioconcentration Factor (BCF) is known as important criteria for ecotoxicology on hazardous chemicals. But there is no standard method for determining BCF and reported BCFs were slightly different in accordance with authors. This study was performed with aims to determine BCFs on BPMC and Carbaryl. Carassius auratus(goldfish) be chosen as test organism and test period were 3-day, 5-day and 10-day. Extract solvents were n-hexane and acetonitrile. GC-ECD was used to detecting carbamates. The obtained results were as follows: 1. It was possible to determine short term BCF$_s$ of Carbaryl or BPMC through relatively simple procedure. 2. BCF$_3$ of Carbaryl in concentration of 1, 2, 5, 10 ppm were 0.34 $\pm$ 0.06, 0.18 $\pm$ 0.02, 0.10 $\pm$ 0.01, 0.06 $\pm$ 0.01 respectively. BCF$_5$ of Carbaryl were 0.34 $\pm$ 0.05, 0.18 $\pm$ 0.02, 0.13 $\pm$ 0.01 and 0.07 $\pm$ 0.01, BCF$_{10}3$ of Carbaryl were 0.45 $\pm$ 0.05, 0.27 $\pm$ 0.02, 0.16 $\pm$ 0.02 and 0.09 $\pm$ 0.01. BCF$_3$ of BPMC in concentration of 1, 2, 5 ppm were 4.66 $\pm$ 0.17, 2.64 $\pm$ 0.49, 1.88 $\pm$ 0.24 respectively. BCF$_5$ of BPMC were 4.09 $\pm$ 0.50, 2.42 $\pm$ 0.37 and 1.83 $\pm$ 0.15. 3. BCF$_s$ of BPMC were decreased as increasing concentration. However, BPMC concentration in fish were increased in contrast to BCF. But more concentrated BPMC was found in fish 3-day test than found concentration in fish 5-day test. 4. Same trend appeared in Carbaryl. BCF$_s$ of Carbaryl were decreased as increasing concentration and prolonging test period. But found Carbaryl concentration in fish were increased. 5. BCF$_s$ of BPMC were higher than that of Carbaryl by 10 times, in spite of the physicochemical properties of the two carbamates were similar to each other. Further study is recommended to find out the reason of the difference.

• 한국축산시설환경학회지
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• 제12권3호
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• pp.115-122
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• 2006

본 연구는 터널환기 무창육계사의 계사내부의 위치별 먼지 농도 분포와 배기홴에서 배출된 먼지의 확산범위를 알아보고자 수행하였으며 결과는 다음과 같다. 1. 입기구 방향의 계사 1/4 지점의 먼지농도는 TSP의 경우 $301.0{\sim}1,366.0\;{\mu}g/m^3$으로 입기구의 위치에 따라 차이가 있었다. 2. 터널홴 앞 3m 지점에서는 TSP $2065.8{\sim}3,092.2\;{\mu}g/m^3$, PM 2.5 $27.6{\sim}36.3\;{\mu}g/m^3$, PM 1.0 $8.3{\sim}11.3\;{\mu}g/m^3$으로 입기구에 비하여 증가하였다. 3. 배기홴으로부터 3m의 지점의 먼지 배출량은 TSP $354.8{\sim}574.8\;{\mu}g/m^3$으로 매우 높았으며 PM10 $94.4{\sim}156.2\;{\mu}g/m^3$, PM2.5 $14.6{\sim}18.0\;{\mu}g/m^3$, PM1.0 $6.0{\sim}6.4\;{\mu}g/m^3$ 이었다. 4. 배기홴으로부터 50m 떨어진 지점에서의 분진농도는 TSP $25.1\;{\mu}g/m^3$, PM10 $8.8\;{\mu}g/m^3$, PM2.5 $5.6\;{\mu}g/m^3$, PM1.0 $4.9\;{\mu}g/m^3$으로 매우 낮은 분진농도를 보였다. 5. 입기구와 배기구 간 분진농도의 차이는 TSP의 경우 입기구에서 $317.9\;{\mu}g/m^3$인데 비하여 배기구는 $2,678.5\;{\mu}g/m^3$로 8.42배 높았으며 PM10 7.4배, PM2.5 3.4배, PM1.0 1.6배 높았다. 6. 배기홴으로부터 거리별 분진의 배출농도는 3m 지점에서 $446.6\;{\mu}g/m^3$ 이었으나 20 m 지점에서는 $156.3\;{\mu}g/m^3$로 34.9% 수준이었고 PM10 34.9%, PM2.5 48.7%, PM1.0 86.8% 수준이었다.