• 환경영향평가
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• 제16권5호
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• pp.327-340
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• 2007

The $PM_{10}$ and $PM_{2.5}$ aerosols were collected at Busan from March to May, 2005, and the concentrations of some metallic elements were analysed to study their characteristics. The mean concentration of $PM_{10}$ was $66.5{\pm}23.0{\mu}g/m^3$ with a range of 22.2 to $118.1{\mu}g/m^3$. The mean concentration of $PM_{2.5}$ was $46.1{\pm}17.2{\mu}g/m^3$ with a range of 9.7 to $83.3{\mu}g/m^3$. The ratio of $PM_{2.5}/PM_{10}$ was 0.69 at Busan. The distribution of metallic elements for $PM_{10}$ and $PM_{2.5}$ were Cd${\ldots}$ ${\ldots}$ $PM_{10}$ were $94.9{\mu}g/m^3$ and $63.7{\mu}g/m^3$, respectively. And The mean mass concentrations of Asian dust and non Asian dust in $PM_{2.5}$ were $56.9{\mu}g/m^3$ and $45.1{\mu}g/m^3$, respectively. The mean values of crustal enrichment factors for five elements (Cd, Cu, Pb, V and Zn) were all higher than 10, possibly suggesting the influence of anthropogenic sources. The soil contribution ratios for $PM_{10}$ and $PM_{2.5}$ were 20.5% and 19.4, respectively.

• 한국농림기상학회지
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• 제5권3호
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• pp.191-199
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• 2003

Optimum transplanting time for extremely early rice cultivation as an after-crop of fruit and vegetables under greenhouse conditions in the southern area was determined. Rice was transplanted on March 10, March 20, March 30, April 10 and April 20 far three years from 1998 to 2000. Meteorological computations for rice production were high for heading between early May and early July, but they were too low for heading between late July and early August. Especially the expected yield predicted with 35,000 spikelets, the average spikelets per $m^2$ for extremely early transplanting. Computation for heading between late July and early August was low by 106 kg/10a compared with that yield at heading during the same period in the field. As the transplanting date in extremely early rice cultivation was earlier) rice growth at early stages was more retarded by low temperature. Rice growth at heading stage recovered with high temperature, showing less difference for the transplanting date. Abnormal tillers occurred by 15.5∼22.2%. The contribution of 1,000 grain weight${\times}$ripened grain ratio to yield of the extremely early rice cultivation in the greenhouse was 50.6%, indicating 16% hi일or than the degree of panicle per $m^2$ on yield. The estimated optimum transplanting time on the basis of yield for the extremely early greenhouse rice cultivation ranged from March 19 to April 28, and the estimated critical transplanting date on the basis of accumulated effective temperature was March 12. Rice reduced the amount of NO$_3$-N by 97.1% and EC by 90.5% in greenhouse soil with continuous fruit/vegetables fer more than a 10-year period, and completely removed the root-knot nematodes.

• 한국조경학회지
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• 제27권4호
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• pp.1-12
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• 1999

This study aims to find basic data for using the quantitative assessment of the sustainability and establishing the systematic index of the planning for local cities to consider the environmentally sound and sustainable development. The research designs to review professional responding to surveys preceded by separate questionnaires and interviews from book reviews, and suggests to make an assessment model of the sustainability for local cities. The research found consequently as follows. Firstly, the research survey items were decides totally 52, grouped 9 assessmental issues and distributed under 4 assessmental domains for the sustainability from the references of book reviews. Secondly, the research result concentrated on the followings from the professional responding to surveys. 1. A most influent factor is the distribution of animals and plants in a nature domain. The next influent factors are the ratio of mass-transportation systems, the numbers of the species of animals and plants, the acreage of conservative forestry, the numbers of reused water resources, and the usage number of water supply, orderly in the nature domain. 2. A most influent factor is the usage number of synthetic detergents in a pollution domain. The next influent factors are the volume of waste water, the number of registered vehicles, the degree of soil pollution, and the charge of development imposition, orderly in the pollution domain. 3. A most influent factor is the acreage of athletic facilities, in an urban domain. the next influent factors are the acreage of recreational facilities, the number and acreage of cultural assets, the number of cultural facilities, the acreage of landscape conservation area, the charge of cultural asset management, orderly in the urban domain. 4. A most influent factor is the number of waste disposal facilities in a participation domain. The next influent factors are the capacity of reused waste, the usage of synthetic detergents, the ratio of waste water disposal, orderly in the participation domain. 5. A most contributed influent domain to the assessment of the sustainability for local cities is the urban domain. The next influent domains are nature domain, participation domain, and pollution domain, orderly in the contribution of the assessment of the sustainability. But, the pollution domain is little relationship with the sustainability. Therefore, it is clear that the abundant greens and the improved level of culture are dominant influences on the sustainabiligy, as like improving the ratio of roadside trees, the acreage of parks, and enlarging the number of cultural facilities.

• Journal of the Korean Wood Science and Technology
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• 제2권4호
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• pp.4-14
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• 1974

The total forest land area in Korea accounts for some 67 percent of the nation's land total. Its productivity, however, is very low. Consequently, forest production accounts for only about 2 percent of the gross national product and a minor proportion of no more than about 5 percent versus primary industry. In this case, however, only the direct income from forestry is taken into account, making no reference to the forestry output induced by other industrial sectors. The value added Or the induced forestry output in manufacturing the primary wood products into higher quality products, makes a larger contribution to the economy than direct contribution. So, this author has tried to analyze the structure of forestry and compute the repercussion effect and the induced output of primary forest products when utilized by other industries for their raw materials, Hsing the input-output table and attached tables for 1963 and 1966 issued by the Bank of Korea. 1. Analysis of forestry structure A. Changes in total output Durng the nine-year period, 1961-1969, the real gross national product in Korea increased 2.1 times, while that of primary industries went up about 1. 4 times. Forestry which was valued at 9,380 million won in 1961, was picked up about 2. 1 times to 20, 120 million won in 1969. The rate of the forestry income in the GNP, accordingly, was no more than 1.5 percent both in 1961 and 1962, whereas its rate in primary industries increased 3.5 to 5.4 percent. Such increase in forestry income is attributable to increased forest production and rise in timber prices. The rate of forestry income, nonetheless, was on the decrease on a gradual basis. B. Changes in input coefficient The input coefficient which indicates the inputs of the forest products into other sectors were up in general in 1966 over 1963. It is noted that the input coefficient indicating the amount of forest products supplied to such industries closely related with forestry as lumber and plywood, and wood products and furniture, showed a downward trend for the period 1963-1966. On the other hand, the forest input into other sectors was generally on the increase. Meanwhile, the input coefficient representing the yolume of the forest products supplied to the forestry sector itself showed an upward tendency, which meant more and more decrease in input from other sectors. Generally speaking, in direct proportion to the higher input coefficient in any industrial sector, the reinput coefficient which denotes the use of its products by the same sector becomes higher and higher. C. Changes in ratio of intermediate input The intermediate input ratio showing the dependency on raw materials went up to 15.43 percent m 1966 from 11. 37 percent in 1963. The dependency of forestry on raw materials was no more than 15.43 percent, accounting for a high 83.57 percent of value added. If the intermediate input ratio increases in any given sector, the input coefficient which represents the fe-use of its products by the same sector becomes large. D. Changes in the ratio of intermediate demand The ratio of the intermediate demand represents the characteristics of the intermediary production in each industry, the intermediate demand ratio in forestry which accunted for 69.7 percent in 1963 went up to 75.2 percent in 1966. In other words, forestry is a remarkable industry in that there is characteristics of the intermediary production. E. Changes in import coefficient The import coefficient which denotes the relation between the production activities and imports, recorded at 4.4 percent in 1963, decreased to 2.4 percent in 1966. The ratio of import to total output is not so high. F. Changes in market composition of imported goods One of the major imported goods in the forestry sector is lumber. The import value increased by 60 percent to 667 million won in 1966 from 407 million won in 1963. The sales of imported forest products to two major outlets-lumber and plywood, and wood products and furniture-increased to 343 million won and 31 million won in 1966 from 240million won and 30 million won in 1963 respectively. On the other hand, imported goods valued at 66 million won were sold to the paper products sector in 1963; however, no supply to this sector was recorded in 1963. Besides these major markets, primary industries such as the fishery, coal and agriculture sectors purchase materials from forestry. 2. Analysis of repercussion effect on production The repercussion effect of final demand in any given sector upon the expansion of the production of other sectors was analyzed, using the inverse matrix coefficient tables attached to the the I.O. Table. A. Changes in intra-sector transaction value of inverse matrix coefficient. The intra-sector transaction value of an inverse matrix coefficient represents the extent of an induced increase in the production of self-support products of the same sector, when it is generated directly and indirectly by one unit of final demand in any given sector. The intra-sector transaction value of the forestry sector rose from 1.04 in 1963 to 1, 11 in 1966. It may well be said, therefore, that forestry induces much more self-supporting products in the production of one unit of final demand for forest products. B. Changes in column total of inverse matrix coefficient It should be noted that the column total indicates the degree of effect of the output of the corresponding and related sectors generated by one unit of final demand in each sector. No changes in the column total of the forestry sector were recorded between the 1963 and 1966 figures, both being the same 1. 19. C. Changes in difference between column total and intra-sector transaction amount. The difference between the column total and intra-sector transaction amount by sector reveals the extent of effect of output of related industrial sector induced indirectly by one unit of final demand in corresponding sector. This change in forestry dropped remarkable to 0.08 in 1966 from 0.15 in 1963. Accordingly, the effect of inducement of indirect output of other forestry-related sectors has decreased; this is a really natural phenomenon, as compared with an increasing input coefficient generated by the re-use of forest products by the forestry sector. 3. Induced output of forestry A. Forest products, wood in particular, are supplied to other industries as their raw materials, increasng their value added. In this connection the primary dependency rate on forestry for 1963 and 1966 was compared, i. e., an increase or decrease in each sector, from 7.71 percent in 1963 to 11.91 percent in 1966 in agriculture, 10.32 to 6.11 in fishery, 16.24 to 19.90 in mining, 0.76 to 0.70 in the manufacturing sector and 2.79 to 4.77 percent in the construction sector. Generally speaking, on the average the dependency on forestry during the period 1963-1966 increased from 5.92 percent to 8.03 percent. Accordingly, it may easily be known that the primary forestry output induced by primary and secondary industries increased from 16, 109 million won in 1963 to 48, 842 million won in 1966. B. The forest products are supplied to other industries as their raw materials. The products are processed further into higher quality products. thus indirectly increasing the value of the forest products. The ratio of the increased value added or the secondary dependency on forestry for 1963 and 1966 showed an increase or decrease, from 5.98 percent to 7.87 percent in agriculture, 9.06 to 5.74 in fishery, 13.56 to 15.81 in mining, 0.68 to 0.61 in the manufacturing sector and 2.71 to 4.54 in the construction sector. The average ratio in this connection increased from 4.69 percent to 5.60 percent. In the meantime, the secondary forestry output induced by primary and secondary industries rose from 12,779 million Wall in 1963 to 34,084 million won in 1966. C. The dependency of tertiary industries on forestry showed very minor ratios of 0.46 percent and 0.04 percent in 1963 and 1966 respectively. The forestry output induced by tertiary industry also decreased from 685 million won to 123 million won during the same period. D. Generally speaking, the ratio of dependency on forestry increased from 17.68 percent in 1963 to 24.28 percent in 1966 in primary industries, from 4.69 percent to 5.70 percent in secondary industries, while, as mentioned above, the ratio in the case of tertiary industry decreased from 0.46 to 0.04 percent during the period 1963-66. The mining industry reveals the heaviest rate of dependency on forestry with 29.80 percent in 1963 and 35.71 percent in 1966. As it result, the direct forestry income, valued at 8,172 million won in 1963, shot up to 22,724 million won in 1966. Its composition ratio lo the national income rose from 1.9 percent in 1963 to 2.3 per cent in 1966. If the induced outcome is taken into account, the total forestry production which was estimated at 37,744 million won in 1963 picked up to 105,773 million won in 1966, about 4.5 times its direct income. It is further noted that the ratio of the gross forestry product to the gross national product. rose significantly from 8.8 percent in 1963 to 10.7 percent in 1966. E. In computing the above mentioned ratio not taken into consideration were such intangible, indirect effects as the drought and flood prevention, check of soil run-off, watershed and land conservation, improvement of the people's recreational and emotional living, and maintenance and increase in the national health and sanitation. F. In conclusion, I would like to emphasize that the forestry sector exercices an important effect upon the national economy and that the effect of induced forestry output is greater than its direct income.

• 한국토양비료학회지
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• 제32권1호
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• pp.47-56
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• 1999

경기도 군포시 및 수원시에서 축산지역과 영농지역 및 주거지역의 토지이용방식을 반영하는 14곳의 지하수 과측정을 대상으로 1997년 1원부터 12월까지 지하수 시료를 채취하여 지하수질의 화학성과 질산태 질소농도를 소사한 결과 지하수의 양이온 조성은 토지이용방식에 따라 큰 차이가 없었지만, 음이온 조성에서는 축산지역 소재 지하수의 $NO{_3}^-$의 비율이 상대적으로 높았다. 영농지역 지하수의 질산태질소 농도는 영농활동의 영향으로 4월과 7월사이에서 증가하는 것으로 나타났으며, 축산지역 지하수는 강우유형에 영향을 받는 것으로 판단할 수 있었고 주거지역의 질산태질소농도는 시기에 상관없이 일정한 수준을 유지했다. 질산태 질소의 오염원을 구명하기 위해 Urea, Ammonium sulfate, 축산 폐수, 청정지역 지하수 중에 포함된 질소의 동위원소비를 측정한 결과 각각 +1.4, -2.7, +27.2, +5.5% 로 나타나 이 ${\delta}^{15}N$ 값을 근거로 지하수중 질산태질소의 ${\delta}^{15}N$ 값이 +5% 이하인 경우 화학비료영향 +5~+10‰은 토양 질소, +10‰ 이상은 축산폐수 또는 생활하수 영향으로 오염원 구분기준을 설정할 수 있었다. 관측정 지하수중 질산태 질소의 ${\delta}^{15}N$ 값은 대부분 토지이용방식에 따른 오염원을 반영했지만, 영농과 축산이 복합적으로 운영되는 농촌지역의 특성상 단일 오염원보다는 두 종류 이상의 오염원이 공동으로 지하수질에 영향을 미치는 것으로 판단할 수 있었다. 또한 각 오염원의 오염 기여도는 관측정 주위의 토지이용방식에 따라 차이가 있었지만, 같은 관측정 내에서도 시기에 따라 그 기여도가 변함을 알 수 있었다.

• 한국토양비료학회지
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• 제6권2호
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• pp.95-105
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• 1973

IR667 계통(系統)(Suwon 213 및 214)과 장려품종(진흥(振興) 및 팔달(八達))의 수용기(受用器)(Sink) 및 급여기(給與器)(Source)의 크기와 그들간(間) 거리(距離), 동화산물의 형태(形態), 기상인자(氣象因子)와 관련(關聯) 수기(受器)(곡실(穀實))충전(充塡) 속도(速度)를 검토(檢討)하여 다음과 같은 결과(結果)를 얻었다. 1. IR667 계통(系統)은 장려 품종보다 최고수기충전속도(最高受器充塡速度)가 크고 빨리온다. 충전속도곡선(充塡速度曲線)의 양상(樣相)은 IR667 계(系)는 준봉형(峻峰型)을 장려품종은 구릉형(丘陵型)을 보인다. 2. 기상인자(氣象因子)는 충전곡선(充塡曲線)의 양상(樣相)에 큰 변화(變化)를 주지 못하는 것 같다. 3. 수기일급기간(受器一給器間) 기능거리(機能距離)(실거리(實距離)${\times}$각엽(各葉)의 생산기여율는 상위엽의존형(上位葉依存型)인 IR667 계(系)에서는 상위엽(上位葉)이 짧고 하위엽의존형(下位葉依存型)인 장려품중에서는 하위엽(下位葉)이 짧다. IR667의 상위엽의존성(上位葉依存性)이 유난히 짧은 제(第)1간장(稈長)(상부(上部)로부터)에 기인(基因)하는것 같다. 4. 간(稈)과 엽초의 유리당(遊離糖)/전분비(澱粉比)에 따라 IR667계(系)는 고당형(高糖型)으로 장려품종은 고전분형(高澱粉型)으로 분류(分類)되었으며 전이성(轉移性)(당(糖))과 비전이성(非轉移性) 동화산물(전분(澱粉))의 비(比)가 수기충전속도(受器充塡速度)와 관련되고 고당형(高糖型)이 생산효율이 높을 것으로 예상된다. 5. 군락구조(群落構造)의 각생산계층내의 균등도(均等度)가 클수록 곡실생산의 효율성이 높다는 가설(假說)을 제시(提示)하고 다수성(多收性) 및 안전성(安全性)과 관련(關聯)하여 검토(檢討)하였다. 6. 엽위별(葉位別) 엽신(葉身)의 N.P.K. 잔존률양상(殘存率樣相)이 진흥(振興)에서는 상부잔존형(上部殘存型)으로, IR667은 중앙부(中央部) 잔존형(殘存型)으로 구분(區分)되어 생산구조 보전형식(保存型式)의 원인(原因)으로 해석되었다. 7. 기관별(器管別) N.P.K 농도(濃度)와 함량분포비율(含量分布比率)에 의(依)하여 IR667은 엽초중심형으로 진흥(振興)은 엽신중심형(葉身中心型)으로 분류(分類)되었다. 8. 동일품종내(同一品種丙)에서 N.P간(間) N.P.K 각양분내(各養分內)에서 품종간(品種間) 수(穗)로의 전이율(轉移率)이 큰 경우 엽신잔존율(葉身殘存率)도 크다.

• Smart Structures and Systems
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• 제4권2호
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• pp.221-232
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• 2008

This paper represents the final results of a research program sponsored by the European Commission through project WIND-CHIME ($\underline{W}$ide Range Non-$\underline{IN}$trusive $\underline{D}$evices toward $\underline{C}$onservation of $\underline{HI}$storical Monuments in the $\underline{ME}$diterranean Area), in which the possibility of using advanced seismic protection technologies to preserve historical monuments in the Mediterranean area is investigated. In the current research, the dynamic characteristics of two outstanding Mamluk-Style minarets, which similar minarets were reported to experience extensive damage during Dahshur 1992 earthquake, are investigated. The first minaret is the Qusun minaret (1337 A.D, 736 Hijri Date (H.D)) located in El-Suyuti cemetery on the southern side of the Salah El-Din citadel. The minaret is currently separated from the surrounding building and is directly resting on the ground (no vaults underneath). The total height of the minaret is 40.28 meters with a base rectangular shaft of about 5.42 ${\times}$ 5.20 m. The second minaret is the southern minaret of Al-Sultaniya (1340 A.D, 739 H.D). It is located about 30.0 meters from Qusun minaret, and it is now standing alone but it seems that it used to be attached to a huge unidentified structure. The style of the minaret and its size attribute it to the first half of the fourteenth century. The minaret total height is 36.69 meters and has a 4.48 ${\times}$ 4.48 m rectangular base. Field investigations were conducted to obtain: (a) geometrical description of the minarets, (b) material properties of the minarets' stones, and (c) soil conditions at the minarets' location. Ambient vibration tests were performed to determine the modal parameters of the minarets such as natural frequencies and mode shapes. A $1/16^{th}$ scale model of Qusun minaret was constructed at Cairo University Concrete Research Laboratory and tested under free vibration with and without SMA wire dampers. The contribution of SMA wire dampers to the structural damping coefficient was evaluated under different vertical loads and vibration amplitudes. Experimental results were used along with the field investigation data to develop a realistic 3-D finite element model that can be used for seismic risk evaluation of the minarets. Examining the updated finite element models under different seismic excitations indicated the vulnerability of such structures to earthquakes with medium to high a/v ratio. The use of SMA wire dampers was found feasible for reducing the seismic risk for this type of structures.

• 한국환경보건학회지
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• 제41권6호
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• pp.369-379
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• 2015

Objectives: The lack of reliable information on environmental pollution and health impacts related to asbestos contamination from abandoned mines has drawn attention to the need for a community health study. This study was performed to evaluate asbestos-related health symptoms among residents near abandoned asbestos mines located in the Chungcheong Provinces. In addition, exposure assessment for asbestos is needed although the exposure to asbestos was in the past. Methods: Past exposure to asbestos among inhabitants near abandoned asbestos mines was estimated by using surface sampling of deposited dust in indoor and outdoor residences. A total of 54 participants were divided into two groups with (34 cases) and without (20 controls) diseases related to asbestos. Surface sampling of deposited dust was carried out in indoor and outdoor residences by collecting 105 samples. Deposited dust for sampling was analyzed by polarization microscope (PLM) and scanning electron microscope?energy dispersive x-ray spectrometer (SEM-EDX) to detect asbestos. Subsequently, the elements of the deposited dust with asbestos were analyzed by SEM-EDX to assess the contribution of sources such as abandoned mines, slate and soil. Results: Among the 105 samples, asbestos was detected by PLM in 29 (27.6%) sampling points, and detected by SEM in 56 (48.6%) sampling points. Asbestos in indoor residences was detected by PLM in four sampling points, and by SEM in 12 sampling points. Asbestos detection in indoor residences may be due to ventilation between indoors and outdoors, and indicates long-term exposure. The asbestos detection rate for outdoor residences in the case group was higher than that in the control group. This can be explained as the case group having had higher exposure to asbestos, and there has been continuous exposure to asbestos in the control group as well as the case group. Conclusion: Past residential asbestos exposure may be associated with asbestosis among local residents near abandoned asbestos mines. Odds ratios were calculated for asbestos detection in outdoor residence by logistic regression analysis. Odds ratio between asbestos detection and asbestosis pulmonum was 3.36 (95% CI 0.90-12.53) (p=0.072), adjusting for age, sex, smoking status and work history with multi-variable logistic regression by PLM analysis method.

• 한국토양비료학회지
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• 제5권2호
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• pp.65-74
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• 1972

IR667의 낮은 등숙률요인(登熟率要因)을 밝히고자 재식밀도(栽植密度)와 질소수준(窒素水準)만을 달리하여 $5m^2$시멘트 pot IR667-수원(水原) 214와 진흥(振興)을 재배(栽培)하여 등숙구조(登熟構造)와 이의 생리적(生理的) 기능(機能)을 비교검토(比較檢討)하여 다음 결과(結果)를 얻었다. 1. IR667의 등숙률(登熟率)은 64로 진흥(振興)의 85보다 훨씬 낮으나 수량(收量)은 IR667이 790kg/10a로 진흥(振興)의 760kg보다 높았다. 2. 출수후(出穗後) 10일(日)의 NAR당(當) 등숙립수(登熟粒數)가 IR667은 6,490으로 진흥(振興)의 6,360보다 약간커서 IR667의 천립중(千粒重)은 29.9로 진흥(振興)의 31.2보다 적으며 NAR당(當) 총립수(總粒數)는 IR667이 10,530으로 진흥(振興)의 7,290보다 훨씬 높아 이것이 IR667의 등숙률(登熟率)이 낮은 요인(要因)이었다. 3. 투광상수(透光常數)는 IR667이 0.115로 진흥(振興)의 0.200보다 적어서 IR667이 보다 큰 등숙구조(登熟構造)를 갖게되는 장점(長點)을 보였다. 4. LAI 증가(增加)에 따른 LAI당(當) 입수(粒數)의 감소율(減少率)은 두 품종(品種)이 같았다. 5. 기초생산속도(基礎生産速度)(CGR)가 최고치(最高値)인 감계엽면적지수(監界葉面積指數)(critical leaf area index)는 IR667은 6.5이고 진흥(振興)은 5.2이며 5.2이하(以下)에서 진흥(振興)의 NAR이 IR667 보다 크다. 6. 최고수량(最高收量)을 얻을수 있는 출수기(出穗期) 최적엽면적지수(最適葉面積指數)(optimum leaf area index)는 IR667이 7.4로 진흥(振興)의 6.2보다 컸다. 출수기(出穗期) 평균엽면적지수(平均葉面積指數)는 IR667이 6.2 진흥(振興)이 4.7로 최적엽면적지수(最適葉面積指數)에 미달(未達)일 뿐 아니라 감계엽면적지수(監界葉面積指數)보다도 적었다. 7. 출당후(出糖後) 20일간(日間) LAI의 감소율(減少率)은 IR667이 크나 광합성량(光合成量)의 감소율(減少率)은 진흥(振興)이 컷다. 8. LAI가 클수록 NAR이 감소(減少)하는데 그 감소율(減少率)은 등숙(登熟)이 진행(進行)됨에 따라 진흥(振興)에서는 감소(減少)하나 IR677에서는 증가(增加) 함은 저온(低溫)에 의(依)한 광합성능(光合成能)의 저하(低下)와 호흡소모(呼吸消耗)에 기인(基因)하며 등숙적온(登熟適溫)이 IR667에서 높다는 것을 의미(意味)한다. 9. 수량(收量)-등숙률곡선(登熟率曲線)은 IR677이 진흥(振興)보다 등숙(登熟)이 수량(收量)에 미치는 영향이 적은 것으로 나타났고 이는 등숙환경(특히 기온)이 IR667에 부적(不適)한 때문으로 등숙환경(登熟環境)개선은 IR667의 최대 증수요인임을 보였다.

• 분석과학
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• 제32권1호
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• pp.17-23
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• 2019

질소산화물(NOx)은 인위적 배출원(화석연료 연소, 이동오염원, 산업배출원 등)과 자연배출원(번개, 생물기원 토양, 산불 등)으로부터 배출된다. 질소안정동위원소를 이용한 분석 기법은 배출원의 기여도 및 추적 인자로 활용되어 왔다. 본 연구는 NOx의 특성을 보기 위하여 ${\delta}^{15}N-NO_2$를 측정하였으며 배출원의 동위원소 특성을 파악하기 위하여 수행되었다. 시료채취가 용이한 Ogawa PAS를 이용하여 대기 중 가스상 질소를 포집하여 안정동위원소를 분석하였다. 도심지역 터널내부의 평균 $NO_2$ 농도는 $3808.8{\pm}2656.5ppbv$이며, ${\delta}^{15}N-NO_2$ 값은 $7.7{\pm}1.8$‰를 나타내며 일반적인 이동오염원의 값을 나타냈다. 고속도로의 이동오염원으로부터 거리에 따른 결과, 고속도로와 인접한 지점의 $NO_2$ 농도는 $965.4{\pm}125.2ppbv$이며 ${\delta}^{15}N-NO_2$는 $5.9{\pm}1.4$‰이었고, 1.1 km 떨어진 지점의 $NO_2$ 농도는 $372.5{\pm}95.9ppbv$이며 ${\delta}^{15}N-NO_2$는 $-11.5{\pm}2.9$‰로 고속도로인근의 값이 높게 나타내었다. 고속도로부터 이동오염원 기여율을 보기 위하여 binary mixing model을 수행하였으며 고속도로와 근접할수록 기여율, 농도 및 동위원소가 높게 나타나는 경향을 나타냈다.