• 제목/요약/키워드: Secondary Pollution

검색결과 248건 처리시간 0.031초

인접구조물 하부통과에 따른 굴착공법에 대한 고찰 (A Study on Excavation Method According to Passage under Adjacent Structure)

  • 김태현;고진석;조영동
    • 화약ㆍ발파
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    • 제23권1호
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    • pp.31-39
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    • 2005
  • 본 연구는 중앙선(덕소-원주간) 복선전철 터널공사론 기초로 한 것으로 주변 보안물건에 대한 피해가 발생되지 않도록 시험발파를 통한 발파 환경 영향권 분석을 실시하고, 그 결과를 상호 비교, 분석하여 안전하고 효율적인 공사가 수행될 수 있도록 적합한 대체 굴착공법의 적용에 대하여 연구하였다. 시험발파를 통해 제시된 대체굴착공법을 이용하여 더 안전하고 효과적인 작업을 수행한 수 있었으며, 무진동 구간은 일반적으로 2차 작업이 병행되므로 breaker 작업에 의한 진동이 지속적으로 발생되어 연구지역의 경우 적용이 사실상 어렵다고 판단됨에 따라 선대구경 수평보링 공법+라인드릴링 공법+다분할 미진동 소발파 공법을 적용함으로써 발파진동 기준치 이내의 수준으로 굴착작업이 가능하였다.

PMF 모델을 이용한 경산지역 PM2.5의 오염원 기여도 추정 (Source Apportionment of PM2.5 in Gyeongsan Using the PMF Model)

  • 정영진;황인조
    • 한국대기환경학회지
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    • 제31권6호
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    • pp.508-519
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    • 2015
  • The objective of this study was to quantitatively estimate $PM_{2.5}$ source contribution in Gyeongsan. Ambient $PM_{2.5}$ samples have been collected on zefluor, quartz and nylasorb filter by $PM_{2.5}$ samplers of cyclone method from September 2010 to December 2012. Collected samples were analyzed for determining 17 inorganic elements, 8 ions, and 8 carbon components after pretreatment. Based on these chemical information, the PMF model was applied to estimate the quantitative contribution of air pollution sources. The results of the PMF modeling showed that the sources were apportioned by biomass burning source (15.5%), secondary sulfate source (16.0%), industry source (10.4%), soil source (7.0%), gasoline source (9.1%), incinerator source (10.4%), diesel emission source (11.0%), and secondary nitrate source (20.6%), respectively. To analyze local source impacts from various wind directions, the CPF analysis were performed using source contribution results with the wind direction values measured at the site.

흐름 메카니즘에 의한 깔따구들의 분포(I) - 인공수로 실험 - (The Distribution of Chironomids by Flow Mechanisms - Artificial Channel Measurement -)

  • 이상호;이정민;박재현;송미영
    • 한국물환경학회지
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    • 제22권1호
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    • pp.150-158
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    • 2006
  • Over the past few years, many studies have been conducted on the flow, sediment movement, pollution transportation and scour etc. However, very few attempts have been made at the hydraulic studies reflecting upon the ecological function. The objective of this study is to examine the structures of the flow and turbulence in an open circular channel and their relationship to distribution of the organisms and chironomids. Under different flow conditions, the organic matter and some chironomids were injected into the channel. Using the obtained velocity data, the flow mechanisms and the turbulent shear stresses were analyzed. Organic matters and chironomids were distributed on the region that the velocity was slower and the turbulent shear stresses were smaller. Some habitat moved even though chironomids were inhabited. This phenomenon has relationship with the flow mechanism. Some chironomids have distributed around the habitat structure of a hemisphere. The secondary flow has affected the deposition of the organic matters and the distribution of chironomids.

낙동강 하구생태계의 세균 생물량과 이차생산성 (Bacterial Biomass and Secondary Productivity in Naktong River Estuary)

  • 송성주;권오섭;이혜주;이진애;김영의
    • 미생물학회지
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    • 제32권3호
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    • pp.238-244
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    • 1994
  • 부영양화된 낙동강 하구역에서 세균에 의한 용존 유기물의 이용능을 조사하고 이에 미치는 환경요인의 영향을 파악하기 위하여 미생물학적 요인과 물리화학적 환경요인의 연중 변화를 분석하였다. 총세균수는 0.33 ~ $2.09{\times}10^7$ cells/ml의 변화폭을 나타냈으며, 오염부하량이 큰 정점에서 종속영양세균의 개체수와 비례하였다. 세균이 체적과 생물량은 각각 0.064~0.156 ${\mu}m^3$/cell, 0.163~1.036 ${\mu}g$-C/ml을 나타냈다. 세균의 이차생산성은 0.24~60.86 ${\mu}g$-C/l/h의 범위로 측정되었으며, 부영양화 지표로 사용되는 환경인자와 밀접한 관계를 보였다. 담수역에 속하는 정점에서의 세균생산성의 계절별 변화는 동계에 최고치를, 하계에 최저치를 나타내어 갈수기의 오염부하량 증가와 밀접한 상관성을 보였다. 해수역에 속하는 다대의 경우 동계에 낮은 값을, 하계에 높은 값을 나타내고, 환경요인 중 엽록소 a, 수은 등과 밀접한 상관성을 보였다 (r>0.5, p<0.05). 이로 미루어 낙동강 하구의 하구언 상류역에서는 주위에서 유입되는 유기물이, 하구언 하류역에서는 식물성 플랑크톤의 광합성 산무링 세균의 이차생산성에 미치는 주 영양물질임을 암시하고 있다.

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2015년 봄철에 선박으로 관측한 서해상 이차에어로졸 성분의 농도 및 오염 특성 (Concentration and Pollution Characteristics of Secondary Aerosol Components Over the Yellow Sea by Ship-Borne Observation in Spring, 2015)

  • 고희정;강창희;차주완;류상범
    • 대기
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    • 제27권1호
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    • pp.29-40
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    • 2017
  • The $PM_{10}$ and $PM_{2.5}$ particles over the Yellow Sea of Korea were collected by ship-borne observation during two cruises in spring, 2015. Their water-soluble ionic components such as $NH_4^+$, $Na^+$, $K^+$, $Mg^{2+}$, $Ca^{2+}$, $SO_4^{2-}$, $NO_3^-$, $Cl^-$, $F^-$, $CH_3COO^-$, $HCOO^-$, and $CH_3SO_3^-$ were analyzed, in order to examine the pollution characteristics of the secondary aerosol components. The comparative study of particle size distribution has resulted that $NH_4^+$, $nss-SO_4^{2-}$, $nss-Mg2+$, $nss-K^+$, $HCOO^-$, and $CH_3SO_3^-$ species mostly existed in fine particle mode. Meanwhile, nss-F-and sea-salt species were distributed in both fine and coarse particle mode, $NO_3^-$, $nss-Ca^{2+}$, $CH_3COO^-$ species were rich in coarse particle mode. The concentrations of secondary pollutants($nss-SO_4^{2-}$, $NO_3^-$, $NH_4^+$) increased in fine particles, and those of natural components ($nss-Ca^{2+}$, Sea-salt) increased in coarse particles. $NH_4^+$ exists as the form of $(NH_4)_2SO_4$ and $NH_4NO_3$, and mostly as $(NH_4)_2SO_4$ in fine particles. $NH_4NO_3$ has lower content compared to $(NH_4)_2SO_4$, and it mostly existed in fine particles at Yellow Sea I and in coarse particles at Yellow Sea II. The concentration ratios of $NO_3^-/nss-SO_4^{2-}$ for Yellow Sea I and Yellow Sea II were 0.52 and 0.16 in coarse particles, and they were 0.64 and 0.38 in fine particles, respectively, showing that the stationary source emissions were more important than mobile source emissions in Yellow Sea II (except Passage II-4).

남산의 생태학적 진단 (Ecological Diagnosis on Mt. nam in Seoul, Korea)

  • 이창석;문정숙;김재은;조현제;이남주
    • The Korean Journal of Ecology
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    • 제21권5_3호
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    • pp.713-721
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    • 1998
  • The effects of artificial interference on the vegetation landscape in Mt. Nam of Seoul, Korea were clarified by analysing the distribution of vegetation landscape element and the number and size of patch depicted as a vegetation map in terms of landscape ecological principles. The effects of artificial interference on vegetation were also confirmed from the environmental gradient analysis on plant community extended from the lowland to the peak of that mountain. Vegetation landscape elements were divided into plantation and secondary forest in actual vegtation map. The ratio of plantation to secondary forest was higher in the lowland below mid-slope and the southern slope. Most afforested land were occupied by Robinia pseudoacacia and Populus tomentoglandulosa, Pinus rigida, P. koraiensis, Metasequoia glyptostroboides, Alnus hirsuta and so on are localy planted. In addition, projects to replace those afforested trees by P. densiflora as a kind of campaign for "Restoration of the one original feature of Mt. Nam" or to replace those tree species by planting young Abies holophylla or P. koraiensis under the mature afforested trees are also carried out in recent years. In cases of secondary forest, the southern slope was dominated by P. densiflora and the northern one by Q. mongolica. But the lowland of the northern slope is dominated by P. densiflora as the same as that in the southern slope. Vegetation landscape elements in Mt. Nam were much simplified comparing with that of suburban area around Seoul. The number of patches, which reflects the degree of diverse artificial interference was more in the lower area than in the upper area and more in the southern slope than in the northern one. On the other hand, the size of patch showed the antagonistic tendency to that of the number of patch. As a result of environmental gradient analysis, vegetation distribution in Mt. Nam was different from that in suburban area around Seoul. For example, Alnus japonica community, Zelkova serrata community, and Carpinus laxiflora community, which is established in mountain comparatively rare in artificial interference disappeared in Mt. Nam. As a result of analysis on vegetational succession in P. densiflora community and Q. mongolica community, both communities showed a tendency of retrogressive succession differently from that in control site located in suburban area around Seoul. In addition, species composition of P. densiflora and Q. mongolica communities in Mt. Nam were also different from those in Mt. Surak located around Seoul. It was interpreted that those results were originated from the environmental pollution and excessive arti ficial interferences.rferences.

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도로변에서 발생되는 미세먼지로써 타이어와 도로 마모입자 채집과 분석 연구 (A Study on the Collection and Analysis of Tire and Road Wear Particles(TRWPs) as Fine Dust Generated on the Roadside)

  • 강태우;김혁중
    • 한국건설순환자원학회논문집
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    • 제10권3호
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    • pp.293-299
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    • 2022
  • 본 연구에서는 도로변 미세먼지 내 타이어와 도로 마모입자의 정량화 분석과 타이어와 도로 마모입자 내 타이어 및 도로 성분 비율을 확인하기 위한 연구를 수행하였다. 이에 시간당 1,300여대 교통량을 갖는 충청남도 지자체중에서 C도시의 종합버스터미널 부근 정류장의 경계석 6곳에서 먼지 샘플을 채집하였다. 채집된 먼지 샘플 1,000 g에 대해 크기와 밀도 분리 수행한 결과 미세먼지 샘플 24 g과 타이어와 도로 마모입자 약 0.05 g이 분리되었다. 즉, 도로변 미세먼지에는 타이어와 도로 마모입자가 약 0.21 % 존재하는 것으로 분석되었다. 분리된 타이어와 도로 마모입자에 대해 주사전자현미경(SEM)을 이용하여 형상을 분석한 결과 지우개가루 형상이 관찰되었다. 또한, 도로변 미세먼지 내 존재하는 타이어와 도로 마모입자는 자동차 주행 중 타이어와 도로간 마찰에 의해 생성되어 도로변으로 분산되었기 때문에 열중량분석기(TGA)와 가스크로마토 질량분석기(GC/MS)를 이용하여 성분 분석을 수행하였다. 정량화 계산식을 통해 성분에 대한 타이어 및 도로 성분 비율을 도출한 결과 약 3:7로 분석되었다. 본 연구는 도로변 미세먼지 발생원의 구성원과 함량 분석을 위해 객관적이고 신뢰도 높은 분석 기법을 제시하였다. 추후, 도로건설과 타이어 소재의 미세먼지 저감 기술 확보와 개선 방안 확보를 위한 선행적 기초 연구로써 활용되기를 기대하고 지속적으로 더 많은 지역과 샘플 분석에 대한 통계 데이터를 확보하여 신뢰도 높은 연구를 수행하고자 한다.

PMF모델을 이용한 대기 중 PM-10 오염원의 정량적 기여도 추정 (Estimation of Quantitative Source Contribution of Ambient PM-10 Using the PMF Model)

  • 황인조;김동술
    • 한국대기환경학회지
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    • 제19권6호
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    • pp.719-731
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    • 2003
  • In order to maintain and manage ambient air quality, it is necessary to identify sources and to apportion its sources for ambient particulate matters. The receptor methods were one of the statistical methods to achieve reasonable air pollution strategies. Also, receptor methods, a field of chemometrics, is based on manifold applied statistics and is a statistical methodology that analyzes the physicochemical properties of gaseous and particulate pollutant on various atmospheric receptors, identifies the sources of air pollutants, and quantifies the apportionment of the sources to the receptors. The objective of this study was 1) after obtaining results from the PMF modeling, the existing sources of air at the study area were qualitatively identified and the contributions of each source were quantitatively estimated as well. 2) finally efficient air pollution management and control strategies of each source were suggested. The PMF model was intensively applied to estimate the quantitative contribution of air pollution sources based on the chemical information (128 samples and 25 chemical species). Through a case study of the PMF modeling for the PM-10 aerosols, the total of 11 factors were determined. The multiple linear regression analysis between the observed PM-10 mass concentration and the estimated G matrix had been performed following the FPEAK test. Finally the regression analysis provided quantitative source contributions (scaled G matrix) and source profiles (scaled F matrix). The results of the PMF modeling showed that the sources were apportioned by secondary aerosol related source 28.8 %, soil related source 16.8%, waste incineration source 11.5%, field burning source 11.0%, fossil fuel combustion source 10%, industry related source 8.3%, motor vehicle source 7.9%, oil/coal combustion source 4.4%, non-ferrous metal source 0.3%. and aged sea- salt source 0.2%, respectively.

Considerations in Establishing a Decision-Making process for Korea's Places of Refuge

  • Lee, Chang-Hyun
    • 한국항해항만학회지
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    • 제38권6호
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    • pp.629-636
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    • 2014
  • To minimize secondary damages from marine environment pollution resulting from marine accidents, International Maritime Organization(IMO) adopted "Guidelines on Places of Refuge(POR) for ships in need of assistance" as Resolution A.949(23) in it is 23rd General Assembly in 2003 and recommends Parties to the Organization designate PoR. This resolution suggests that they establish a "Decision-Making process" so as to provide reasonable PoR when disabled ships request use of PoR. Korea has not been performed introduce a PoR system in the country. Therefore, there is no decision-making process to deal with ships which need PoR. When Korea implements the PoR system in the future, the nation should establish a Decision-Making process to provide reasonable PoR in case ships in need of assistance request for PoR. In order to present what should be considered in the process of establishing a Decision-Making process for PoR in Korea in the future, in this study presents matters which should be considered in the process of founding PoR Decision-Making processes. When Korea tries to conduct POR system so that other countries' PoR Decision-Making process and the relating process of IMO and REMPEC (Regional Marine Pollution Emergency Response Centre for the Mediterranean Sea) were investigated and analyzed. In addition, in times of marine accident in Korea's sea areas, Korea's action manuals for marine accident which regulates management for an accident is analyzed and articles will be presented to be taken into account during establishing final PoR Decision-Making process.

통합환경관리제도 운영을 위한 최적가용기법 평가·선정기법 연구 (Evaluation and Selection Method of Best Available Techniques for Integrated Environmental Management System)

  • 박재홍
    • 한국물환경학회지
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    • 제33권3호
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    • pp.348-358
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    • 2017
  • The process of evaluating and selecting the best available techniques presents various characteristics for each country. In the case of EU, BAT is selected through TWG meeting after first screening, mass and energy balance, impact assessment and decision support process. Korea has proposed four principles to select BAT that can be carbon neutral for each environmental infrastructure in order to reduce greenhouse gas emissions. In order to evaluate and select the best available technique, it is necessary to differentiate the method according to whether it is a technique generally applied at the current workplace, whether it is a single technique or a combination technique, and whether it is a technology technique or management technique. In the case of a single technique, it should be evaluated whether it is a technique applied in the workplace, excessive cost, superior environmental technique over BAT, and secondary environmental pollution. In the case of multiple techniques, it is necessary to examine whether the emission standards are met and whether the pollutants can be treated at the same level as BAT. In the case of BAT candidates for management techniques, whether or not they contribute directly or indirectly to lowering the emission level of pollutants can be an important evaluation item. In the case of environmental techniques that are not generally applied in the workplace, it is recommended that the following 8 steps be carried out, including those prescribed by law. In the first stage, the list of performance evaluation factors is listed. In the second stage, the level of disposal of pollutants and the level of satisfaction with standards are listed. In the third stage, the environmental evaluation elements are listed. In the fourth stage, Is to list the economic evaluation elements, step 6 is to list the pollution and accident prevention evaluation factors, step 7 is the quantitative evaluation of the technical working group, and step 8 is BAT confirmation through deliberation of the central environmental policy committee.