• 제목/요약/키워드: Number of Trees

검색결과 912건 처리시간 0.031초

광주광역시 노거수의 분포 및 생육현황 (Distribution and Growth Status of Legally Protected Old and Big Trees in Gwangju, Korea)

  • 임동옥;제갈은기
    • 한국환경생태학회지
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    • 제25권5호
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    • pp.736-746
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    • 2011
  • 본 연구는 광주광역시에 분포하는 보호수 및 노거수의 분포 및 생육현황을 조사하여 보호수와 노거수 관리방안을 제시하고자 시도하였다. 광주광역시에 분포하는 보호수는 9종 68개체로 이 중 광산구가 18개체로 가장 많았으며, 노거수는 10종 155개체로 확인되었다. 기존문헌에 잘못 기록된 종명은 정확한 식물명으로 수정되어야 한다. 보호수의 활력도 평균은 1.2였으며 지면상태 평균은 1.7이었고 노거수의 활력도 평균은 1.3, 지면상태 평균은 2.0으로 활력도는 큰 차이가 없었고 지면 상태는 노거수가 조금 더 좋지 못한 것으로 나타났다. 활력도가 3.2~4.0범위를 보여 절대관리가 필요한 보호수는 광산구 송대동 대촌마을 은행나무 1개체 이었고, 노거수는 광산구 산수동 감동마을의 왕버들 1개체로 나타났다. 보호수 및 노거수의 관리방안에서 제일 중요한 것은 기본적으로 노거수가 자랄 수 있는 최소한의 생육공간을 확보하는 것으로 보호수와 노거수 근계 위의 아스팔트나 시멘트 포장을 제거해 주어야 한다고 판단된다.

철도 위험도 통합 평가 방법 및 도구 개발 (Development of Integrated Method and Tool for Railway Risk Assessment)

  • 한상훈;안광일;왕종배;이호중
    • 한국철도학회:학술대회논문집
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    • 한국철도학회 2006년도 추계학술대회 논문집
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    • pp.1132-1139
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    • 2006
  • Railway risk is evaluated by a method of linking event trees and fault trees as the general PSA(Probabilistic Safety Assessment) model for the risk assessment of complex systems. Accident scenarios causing undesirable events are modeled by event trees comprised of several accident sequences. Each branch located in the accident progression of the event tree is modeled by an fault tree or can be represented by some value too simply. We usually evaluate the frequency of the whole sequence by adding them after calculating the frequency of each sequence at a time. However, since there are quite a number of event trees and fault trees in the railway risk assessment model, the number of sequence to evaluate increases and preparation for the risk assessment costs much time all the more. Also, it may induce errors when analysts perform the work of quantification. Therefore, the systematic maintenance and control of event trees and fault trees will be essential for the railway risk assessment. In this paper we introduce an integrated assessment method using one-top model and develop a risk assessment tool for the maintenance and control of the railway risk model.

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Dieback Reality of Apple Trees Resulting from Soil-Borne Fungal Pathogens in South Korea from 2016 to 2019

  • Lee, Sung-Hee;Shin, Hyunman;Chang, Who-Bong;Ryu, Kyoung-Yul;Kim, Heung Tae;Cha, Byeongjin;Cha, Jae-Soon
    • 식물병연구
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    • 제26권2호
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    • pp.88-94
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    • 2020
  • Recently, the severe dieback of apple trees resulting from soil-borne diseases has occurred in South Korea. The casual agents of dieback were surveyed on 74 apple orchards that had been damaged nationwide in 2016-2019. The number of apple orchards affected alone by Phytophthora rot, violet root rot, and white root rot was 31, 34, and 3, respectively. Also, the total number of mixed infection orchards was 6. Out of 9,112 apple trees affected by dieback, the trees damaged by Phytophthora rot, violet root rot, and white root rot were 3,332, 3,831, and 44, respectively. Moreover, the total number of mixed infection apple trees was 1,905. The provinces mainly affected were Gyeongnam, Gyeongbuk, Chungbuk, and Jeonbuk. The survey on these infected apple orchards will be available to form management strategy for the dieback that had been increased by soil-borne fungal pathogens.

마을 내 잔존 노거수의 생육현황 및 실태진단 - 경주시 현곡면을 중심으로 - (Diagnosis of the growth status and actual condition of the remaining old trees in the village - Focused on Hyeongok-myeon in Gyeongju-si -)

  • 김영훈;덩베이지아;천겅;유주한
    • 한국환경복원기술학회지
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    • 제23권6호
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    • pp.109-123
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    • 2020
  • The purpose of this study is to provide basic data for the establishment of future countermeasures by diagnosing the growth status and actual condition of undesignated old trees distributed in Hyeongok-myeon, Gyeongju, Gyeongsangbuk-do. The number of old trees surveyed was 2 weeks in Gajeong-ri, 2 weeks in Haguri, 3 weeks in Nae-Tae-ri, 1 week in Nawon-ri, 6 weeks in Oryu-ri, 3 weeks in Sangguri, and 2 weeks in Sohyeon-ri, The trees species composition was 6 trees Celtis sinensis Pers., 1 Diospyros lotus L. trees, 4 trees Salix chaenomeloides Kimura trees, 2 Styphnolobium japonicum L. trees, and 7 Zelkova serrata (Thunb.) Makino trees. Growth status is 7.1~22.0m in height, 14.6~25.1m in long axis, 10.2~19.2m in short axis, root diameter is 76.0~236.4cm, diamter at breast height is 67.0~220.0cm, soil acidity is pH4.9~7.0, soil The hardness was measured to be 4.0-27.0mm. The result grade of the scoring data of health information is represented by monitoring generally, monitoring critically, and absolute monitoring, and it was confirmed that out of the 20 trees population in Hyeongok-myeon, the general monitoring grade was 7 weeks, the major monitoring grade was 13 weeks, and there was no absolute monitoring grade. Accordingly, the number of old trees of the general surveillance level was maintained at the current level, and ecological surgical operations were introduced for the major surveillance level, but the case of village forests should be different, and sequential treatments were the old tree urgently needed. The level and bark of the target tree, the state of the crown, the root exposure, the presence of pests and pests, the vitality and the ground condition, the degree of pollution are normal, poor, or very poor, operation and protection management, soil improvement, removal of cover, and disinfection were urgently needed for the old trees with the surveyed data. In order to compensate for these matters, continuous monitoring and management measures for the old number should be sought.

설악산국립공원 상록침엽수 고사목 공간분포 특성 - 서북능선 일원을 대상으로 - (Spatial Distribution of Evergreen Coniferous Dead Trees in Seoraksan National Park - In the Case of Northwestern Ridge -)

  • 김진원;박홍철;박은하;이나연;오충현
    • 한국환경복원기술학회지
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    • 제23권5호
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    • pp.59-71
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    • 2020
  • Using high-resolution stereoscopic aerial images (in 2008, 2012 and 2016), we conducted to analyze the spatial characteristics affecting evergreen coniferous die-off in the northwestern ridge (major distribution area such as Abies nephrolepis), Seoraksan National Park. The detected number of dead trees at evergreen coniferous forest (5.24㎢) was 1,223 in 2008, was 2,585 in 2012 and was 3,239 in 2016. The number of cumulated dead trees was 7,047 in 2016. In recent years, the number of dead trees increased relatively in the northwest ridge, Seoraksan National Park. Among the analysed spatial factor (altitude, aspect, slope, solar radiation and topographic wetness index), the number of dead trees was increased in the conditions with high altitude, steep slope and dry soil moisture. A spatial distribution of dead tree was divided into 2 groups largely (high altitude with high solar radiation, low altitude with steep slope). In conclusion, the dead trees of evergreen coniferous were concentrated at spatial distribution characteristics causing dryness in the northwestern ridge, Seoraksan National Park.

TREES WITH EQUAL STRONG ROMAN DOMINATION NUMBER AND ROMAN DOMINATION NUMBER

  • Chen, Xue-Gang;Sohn, Moo Young
    • 대한수학회보
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    • 제56권1호
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    • pp.31-44
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    • 2019
  • A graph theoretical model called Roman domination in graphs originates from the historical background that any undefended place (with no legions) of the Roman Empire must be protected by a stronger neighbor place (having two legions). It is applicable to military and commercial decision-making problems. A Roman dominating function for a graph G = (V, E) is a function $f:V{\rightarrow}\{0,1,2\}$ such that every vertex v with f(v)=0 has at least a neighbor w in G for which f(w)=2. The Roman domination number of a graph is the minimum weight ${\sum}_{v{\in}V}\;f(v)$ of a Roman dominating function. In order to deal a problem of a Roman domination-type defensive strategy under multiple simultaneous attacks, ${\acute{A}}lvarez$-Ruiz et al. [1] initiated the study of a new parameter related to Roman dominating function, which is called strong Roman domination. ${\acute{A}}lvarez$-Ruiz et al. posed the following problem: Characterize the graphs G with equal strong Roman domination number and Roman domination number. In this paper, we construct a family of trees. We prove that for a tree, its strong Roman dominance number and Roman dominance number are equal if and only if the tree belongs to this family of trees.

ON [1, 2]-DOMINATION IN TREES

  • Chen, Xue-Gang;Sohn, Moo Young
    • 대한수학회논문집
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    • 제33권2호
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    • pp.631-638
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    • 2018
  • Chellai et al. [3] gave an upper bound on the [1, 2]-domination number of tree and posed an open question "how to classify trees satisfying the sharp bound?". Yang and Wu [5] gave a partial solution for tree of order n with ${\ell}$-leaves such that every non-leaf vertex has degree at least 4. In this paper, we give a new upper bound on the [1, 2]-domination number of tree which extends the result of Yang and Wu. In addition, we design a polynomial time algorithm for solving the open question. By using this algorithm, we give a characterization on the [1, 2]-domination number for trees of order n with ${\ell}$ leaves satisfying $n-{\ell}$. Thereby, the open question posed by Chellai et al. is solved.

확률적 이진 검색 트리 성능 추정 (Estimation of performance for random binary search trees)

  • 김숙영
    • 한국컴퓨터산업학회논문지
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    • 제2권2호
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    • pp.203-210
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    • 2001
  • 이진 트리 검색에 관한 관계 모형들을 추정하고 이론 가설들을 검정하기 위하여 중복되지 않는 자연수들을 자료로 하는 3개 이상 7개 이하의 노드를 가진 모든 가능한 이진 검색 트리 들을 생성하였다. 노드 개수 별로 높이 및 균형도 에 따른 이진 검색 트리 생성 확률들을 추정하였으며 노드 개수와 트리의 높이, 검색에 필요한 비교 횟수의 관계를 나타내는 회귀 모형이 구축되었고 이진 검색 트리의 O(1g(n)) 이론이 적합도 검정 절차에 의하여 실험적으로 채택되었다. 이진 검색 트리의 균형에 따른 검색 성능의 유의적 차이들을 통계적으로 증명하기 위하여 균형도에 따라 확률적으로 생성된 이진 검색 트리들을 세 그룹으로 그룹화하고 그룹간의 검색 비교 횟수를 분산 분석 모형에 의하여 비교 분석하였다.

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Carbon Storage and Uptake by Street Trees in Seoul

  • Jo, Hyun-Kil;Kim, Jin-Young;Park, Hye-Mi
    • Journal of Forest and Environmental Science
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    • 제34권2호
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    • pp.162-164
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    • 2018
  • This study quantified the carbon storage and uptake by street trees in Seoul and explored suitable planting and management strategies. A systematic sampling model was used to select 50 plots to survey the structures of street trees. The average density and cover of street trees were approximately 5.8 trees/$100m^2$ and 12.1%, respectively. Trees with a dbh of less than 30 cm accounted for about 66.3% of the total number of trees surveyed. The total carbon storage and uptake by the street trees were approximately 103,641 t and 10,992 t/yr, respectively. The total carbon uptake equaled the amount of annual carbon emissions from driving of about 11,000 cars. Street tree planting and management strategies were proposed to enhance carbon uptake. They included multi-layered and multi-aged planting, securing ground and space for plant growth, and avoiding excessive tree pruning.

충주시 초등학교 학교숲 식재현황과 개선방안 (Planting Status and Improvement Plan of School Forest in the Elementary Schools at Chung-ju City)

  • 주진희;김원태;국지하;윤용한
    • 한국환경과학회지
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    • 제19권9호
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    • pp.1129-1136
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    • 2010
  • This study investigated the status of planting status of school's flower of 11 elementary schools located in Chung-ju and its results were as follows. Totally 3,502 trees were planted in the 11 schools and the number of species of the trees was 103. For tall tree Thuja orientalis was planted most frequently and for shrub Buxus microphylla was done in the largest number of the schools. In addition, the number of trees planted in a school was averagely two times more in the model schools than in the other ones, and the average number of species of trees was also over three times more in the model schools. When the number of species of trees was examined according to their types, decidous broad leaved tree was found most frequently overall and the model schools had more various species of decidous tree compared to the other ones. Investigation on designation of school's flower and tree with the 11 elementary school, revealed similar results with those of previous studies performed with the schools in other areas and the tendency meant that the designation was uniform to some degree. Moreover, as only a few school's flower and tree were planted or no one was done in some schools, the species of school's flower and tree needed to be determined by considering characteristics and school percepts of a school as well as local features and circumstances of a region. In addition, more efforts should be made to infuse love for school and to improve quality of education by increasing the planting rate of school's flower and tree and by focusing them.