• 제목/요약/키워드: Land Use Planning System

검색결과 322건 처리시간 0.019초

GIS 기반의 모형을 이용한 도암댐 유역의 산림 파편화에 따른 수(水)환경 영향 평가 (Evaluation of Water Quality Impacts of Forest Fragmentation at Doam-Dam Watershed using GIS-based Modeling System)

  • 허성구;김기성;안재훈;윤정숙;임경재;최중대;신용철;유창원
    • 한국지리정보학회지
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    • 제9권4호
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    • pp.81-94
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    • 2006
  • 본 연구에서는 도암댐 유역에서의 산림파편화에 따른 수(水)환경 영향을 평가하였다. 이를 위해서 Soil and Water Assessment Tool (SWAT) 모형을 이용하였다. 도암댐 유역에서 산림파편화에 따른 수환경 영향만을 평가하기 위해서는 먼저 기상변화에 따른 영향을 배제시켜야 한다. 1985년과 2000년 강수량 분석결과 계절별 강수량에 상당히 많은 차이가 나타나, 본 연구에서는 1985년 기상자료를 이용하여 산림파편화에 따른 수환경 영향을 평가하였다. 산림 파편화에 따른 영향은 시간적 공간적으로 변화하기 때문에 본 연구에서는 수환경의 시 공간적 영향을 분석하였다. 도암댐 수계중 산림파편화가 가장 많이 발생한 소유역에서는 산림파편화로 인하여 유출량이 겨울철, 봄철, 여름철, 가을철 각각 $8,366m^3/month$, $72,763m^3/month$, $149,901m^3/month$, 그리고 $107,109m^3/month$ 증가하였다. 이렇게 증가된 유출량으로 인하여 상당한 양의 토양유실이 발생하여 하천의 부영양화 등을 초래한 것으로 판단된다. 이러한 토양유실로 인하여 가장 많은 산림파편화가 일어난 소유역에서 겨울철, 봄철, 여름철, 그리고 가을철, 유사농도가 각각 5.448mg/L, 13.354mg/L, 20.680mg/L, 그리고 24.680mg/L 증가하였다. 봄철 유사농도가 많이 증가한 이유는 산림지역과는 달리 농경지에서의 봄철 융설로 인한 토양유실이 많이 발생하였기 때문이다. 여름철과 가을철 유사농도가 증가한 이유 또한 과거 산림지역이었던 곳이 산림파편화로 인하여 상당부분 농경지로 전환되었으며, 이 지역에서의 영농에 따른 토양유실 증가로 유사농도가 증가한 것으로 판단된다. 본 연구의 결과를 종합해 보면 홍수조절, 토양유실 저감, 수질 개선과 같은 산림 고유의 기능은 유역내 산림파편화로 인하여 매우 빨리 손실될 수 있다. 따라서 도암댐 유역 내에서 산림 파편화에 따른 부정적 영향을 최소화시키기 위해서는 복합적인 토지이용계획을 수립하여 이행되어야 한다.

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Microbe Hunting: A Curious Case of Cryptococcus

  • Bartlett, Karen H.;Kidd, Sarah;Duncan, Colleen;Chow, Yat;Bach, Paxton;Mak, Sunny;MacDougall, Laura;Fyfe, Murray
    • 한국환경보건학회:학술대회논문집
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    • 한국환경보건학회 2005년도 국제학술대회
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    • pp.45-72
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    • 2005
  • C. neoformans-associated cryptococcosis is primarily a disease of immunocompromised persons, has a world-wide distribution, and is often spread by pigeons in the urban environment. In contrast, C. gattii causes infection in normal hosts, has only been described in tropical and semi-tropical areas of the world, and has a unique niche in river gum Eucalyptus trees. Cryptococcosis is acquired through inhalation of the yeast propagules from the environment. C. gattii has been identified as the cause of an emerging infectious disease centered on Vancouver Island, British Columbia, Canada. No cases of C. gattii-disease were diagnosed prior to 1999; the current incidence rate is 36 cases per million population. A search was initiated in 2001 to find the ecological niche of this basidiomycetous yeast. C. gaftii was found in the environment in treed areas of Vancouver Island. The highest percentage of colonized-tree clusters were found around central Vancouver Island, with decreasing rates of colonization to the north and south. Climate, soil and vegetation cover of this area, called the Coastal Douglas fir biogeoclimatic zone, is unique to British Columbia and Canada. The concentration of airborne C. gattii was highest in the dry summer months, and lowest during late fall, winter, and early spring, months which have heavy rainfall. The study of the emerging colonization of this organism and subsequent cases of environmentally acquired disease will be informative in planning public health management of new routes of exposure to exotic agents in areas impacted by changing climate and land use patterns. Cryptococcosis is an infection associated with an encapsulated, basidiomycetous yeast Cryptococcus neoformans. The route of entry for this organism is through the lungs, with possible systemic spread via the circulatory system to the brain and meninges. There are four cryptococcal serogroups associated with disease in humans and animals, distinguished by capsular polysaccharide antigens. Cryptococcus neoformans: variety grubii (serotype A), variety neoformans (serotype D), and variety gattii (serotypes B and C) (Franzot et at. 1999). C. neoformans variety gattii has recently been elevated to species status, C. gattii. C. neoformans val. grubii and var. neoformans have a world-wide distribution, and are particularly associated with soil and weathered bird droppings. In contrast, C. gattii (CG) is not associated with bird excrement, is primarily found in tropical and subtropical climates, and has a restricted environmental niche associated with specific tree species. (Ellis & Pfiffer 1990) Ellis and Pfeiffer theorize that, as a basidiomycete, CG requires an association with a tree in order to become pathogenic to mammals. In Australia, CG has been found to be associated with five species of Eucalypts, Eucalyptus camaldulensis, E. tereticornis, E. blakelyi, E. gomphocephala, and E. rudis. Eucalypts, although originally native to Australia, now have a world-wide distribution. CG has been found associated with imported eucalypts in India, California, Brazil, and Egypt. In addition, in Brazil and Columbia, where eucalypts have been naturalized, native trees have been shown to harbour CG (Callejas et al. 1998; Montenegro et al. 2000). In British Columbia, Canada, since the beginning of 1999, there have been 120 confirmed cases of cryptococcal mycoses associated with CG in humans, including 4 fatalities (data from British Columbia Centre for Disease Control), and over 200 cases in animal pets in BC (data from Central Laboratory for Veterinarians). What is remarkable about the BC outbreak of C. gattii-cryptococcosis is that all of the cases have been residents of, or visitors to, a narrow area along the eastern coast of Vancouver Island, BC, from the tip of the island in the south (Victoria) to Courtenay on the north-central island as illustrated in Figure 1. Of the first 38 human cases, 58% were male with a mean age of 59.7 years (range 20 - 82): 36 cases (95%) were Caucasian. Ten cases (26%) presented with meningitis, the remainder presented with respiratory symptoms. Cultures recovered from cases of cryptococcosis associated with the outbreak were typed as serogroup B, which is specific to CG (Bartlett et al. 2003). This was the first reported outbreak of CVG in Canada, or indeed, the world. Where infection with CG is endemic, for example, Australia, the incidence of cryptococcosis ranges from 1.8 - 4.7 per million between the southern and northern states (Sorrell 2001). However, the overall incidence of cryptococcosis in immunocompenent individuals has been estimated at 0.2 per million population per year (Kwon-Chung et al. 1984). The population of Vancouver Island is approximately 720,000,consequently, even if the organism were endemic, one would expect a maximum of 0.15 cases of cryptococcal disease annually.

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