• 제목/요약/키워드: unvegetated habitat

검색결과 3건 처리시간 0.016초

진동만 잘피발과 인근 잘피가 없는 해역의 어류군집 비교 (Comparisons of Fish Assemblages Associated with Eelgrass Bed and Adjacent Unvegetad Habitat in Jindong Bay)

  • 곽석남;허성회;최창근
    • 한국어류학회지
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    • 제18권2호
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    • pp.119-128
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    • 2006
  • 진동만 다구리 잘피밭과 인근 잘피가 없는 해역의 어류군집을 비교하기 위해서 2002년 1월부터 12월까지 소형 빔 트롤을 이용하여 어류를 매월 채집하였다. 조사기간 동안 우점하였던 쥐노래미, 감성돔, 농어, 베도라치, 흰베도라치, 주둥치, 문절망둑, 그리고 실양태가 우점하였다. 특히 감성돔과 농어는 잘피밭에서 문절망둑과 실양태는 잘피가 없는 해역에서 많이 출현하였다. 청보리멸, 산호해마, 복섬 및 돌팍망둑, 실고기, 흰꼬리볼락 및 볼락 등은 잘피밭에서만, 양태 및 날개망둑 등은 잘피가 없는 해역에서만 출현하였다. 본 조사해역에서 출현한 어류는 대부분이 소형 어종이거나 대형 어종의 유어들로 구성되어 있어서, 잘피밭이 작은 크기의 어종들에게 좋은 성육장의 역할을 하고 있었다. 어류군집은 뚜렷한 계절변동을 보였는데, 출현 종수는 2002년 5월에, 출현 개체수는 2002년 4월에서 7월 사이에 아주 높았다. 한편 생체량은 2002년 4월과 7월에 가장 높은 수치를 나타내었다. 대체적으로 겨울철에는 출현 종수, 개체수 및 생체량이 모두 낮았다. 잘피밭과 잘피가 없는 인근해역의 어류 군집을 비교해보면, 출현 종수, 개체수 및 생체량이 모두 잘피밭에서 높게 나타났다. 이와 같은 결과는 잘피밭은 잘피가 밀생되어 있어서 먹이 이용 가능성 및 포식자로부터 보호받을 수 있는 서식처의 특성에 의한 것으로 주요 우점종의 체장분포에서도 두 서식처간의 차이가 뚜렷하게 나타났다.

Evaluation of carbon flux in vegetative bay based on ecosystem production and CO2 exchange driven by coastal autotrophs

  • Kim, Ju-Hyoung;Kang, Eun Ju;Kim, Keunyong;Jeong, Hae Jin;Lee, Kitack;Edwards, Matthew S.;Park, Myung Gil;Lee, Byeong-Gweon;Kim, Kwang Young
    • ALGAE
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    • 제30권2호
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    • pp.121-137
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    • 2015
  • Studies on carbon flux in the oceans have been highlighted in recent years due to increasing awareness about climate change, but the coastal ecosystem remains one of the unexplored fields in this regard. In this study, the dynamics of carbon flux in a vegetative coastal ecosystem were examined by an evaluation of net and gross ecosystem production (NEP and GEP) and $CO_2$ exchange rates (net ecosystem exchange, NEE). To estimate NEP and GEP, community production and respiration were measured along different habitat types (eelgrass and macroalgal beds, shallow and deep sedimentary, and deep rocky shore) at Gwangyang Bay, Korea from 20 June to 20 July 2007. Vegetative areas showed significantly higher ecosystem production than the other habitat types. Specifically, eelgrass beds had the highest daily GEP ($6.97{\pm}0.02g\;C\;m^{-2}\;d^{-1}$), with a large amount of biomass and high productivity of eelgrass, whereas the outer macroalgal vegetation had the lowest GEP ($0.97{\pm}0.04g\;C\;m^{-2}\;d^{-1}$). In addition, macroalgal vegetation showed the highest daily NEP ($3.31{\pm}0.45g\;C\;m^{-2}\;d^{-1}$) due to its highest P : R ratio (2.33). Furthermore, the eelgrass beds acted as a $CO_2$ sink through the air-seawater interface according to NEE data, with a carbon sink rate of $0.63mg\;C\;m^{-2}\;d^{-1}$. Overall, ecosystem production was found to be extremely high in the vegetated systems (eelgrass and macroalgal beds), which occupy a relatively small area compared to the unvegetated systems according to our conceptual diagram of a carbon-flux box model. These results indicate that the vegetative ecosystems showed significantly high capturing efficiency of inorganic carbon through coastal primary production.

Ecological Functions and Losses of Traditional Korean Village Groves

  • Lee, D.-W.;Park, C.-R.
    • 한국제4기학회지
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    • 제18권2호통권23호
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    • pp.65-66
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    • 2004
  • There have been groves, in many cases, along with hedgerows and remnant forests around a traditional Korean village. A village grove is very closely connected to the life of residents. Sometimes it was a holy place where important village festivals were held, and became a resting place for farmers, especially in sunny summer. As a matter of fact, it is noted that traditional Korean village groves had been fostered for many purpose as religion, Confucianism, scenery, sanitation, traffic guard, public security, agriculture, hunting, and military and public uses were included in Chosun Govemor General(1938). Village groves were usually located at the outlet of watershed inside which a village was built. In addition, village groves used to be established along part of mountain ranges, streams and streets. A unique type of village grove, called bibosoop was fostered especially where the outlet of watershed was largely opened. In other cases, it was placed where a part of mountain range was relatively low, or where village residents were likely to see ugly objects such as a huge cliff, stony upland with an unvegetated area and the like(Kim and Jang 1994). In a sense, a sheltebelt is a sort of bibosoop as it is a landscape element to complement places that are exposed to strong winds. However, it is comparable to other typical bibosoop that is situated at a topographically very specific zone of watershed. In this paper, we will address potential functions of Korean village groves from a perspective of modern landscape ecology and show current status of some remnants, based on preliminary surveys. A village grove functions as barrier or filter of objects such as water, nutrients, and other elements and habitat of wildlife (park et al. 2003, Lee 2004). The village grove slows down the flow of water and air, maintains soil moisture an hinders soil erosion, enabling cultivation of crops and bringing up creatures nearby. It contributes to enhancing biodiversity. Birds rest on shrubby and woody trees of the element. Presumably, other organisms may also inhabit the village groves and take advantage of it when those move from a forest patch to others. Emerging insects acclimate themselves in the shade of the green space before they fly to sunny air. Besides the village grove acts as a component of agroforestry system as leaf litter is shed from a grove to an asjacent agricultural area, and transformed into green manure(Lee 2004). By the way, many of the landscape elements were destroyed or declined in Koea during the past several decades. The losses have been parallel or linked to environmental degradation. Unfortunately, we have a little reliable data as for how many groves have disappeared in Korea until now. There has been no complete census on the village groves in Korea, and the viewpoints of survey were to a degree different depending on surveyors. So, it is difficult to analyze the temporal and spatial change of village groves. Currently, national inventory data of Korean village groves are available in three reports. We reviewed the locations of village groves and arranged those according to the present administrative units, DONG. With the limited data, we found that at least 484 of village groves were recorded in South Korea. Among all provinces, village groves were most in Gyeongsanbuk-Do Province and least in Chungcheongbuk-Do Province(Table 1). This is a preliminary report prepared while some quantitative data regarding functions and lossers of the village groves are being collected. More detailed data will be introduced in the near future.

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