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      해수활어수조에서 붕장어 (Astroconger myriaster)와 넙치 (Paralichyhus olivaceus)에 의한 오염물 발생량 산정 = Measurement of Waste Generation in Seawater Aquaria by Common Conger (Astroconger myriaster) and Olive Flounder (Paralichyhus olivaceus)

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      https://www.riss.kr/link?id=A104148933

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      다국어 초록 (Multilingual Abstract)

      Waste concentration and waste generation rate in seawater aquaria by common conger (Astroconger myriaster) and olive flounder (Paralichyhus olivaceus) were investigated. The initial fish density of common conger and olive flounder were 3% and 2.8% of total weight of aquarium water, respectively. Wastes in the seawater aquaria, such as protein, total suspended solid (TSS), ammonia, turbidity and chemical oxygen demand (COD) increased with days after stocking. Protein generation rate of common conger increased until 1day after stocking while that of olive flounder increased until 3days. The average protein generation rates of common conger and olive flounder were 0.28g/kg・day and 0.21g/kg・day, respectively. The trends of other waste generation rate were similar to protein generation rate.
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      Waste concentration and waste generation rate in seawater aquaria by common conger (Astroconger myriaster) and olive flounder (Paralichyhus olivaceus) were investigated. The initial fish density of common conger and olive flounder were 3% and 2.8% of ...

      Waste concentration and waste generation rate in seawater aquaria by common conger (Astroconger myriaster) and olive flounder (Paralichyhus olivaceus) were investigated. The initial fish density of common conger and olive flounder were 3% and 2.8% of total weight of aquarium water, respectively. Wastes in the seawater aquaria, such as protein, total suspended solid (TSS), ammonia, turbidity and chemical oxygen demand (COD) increased with days after stocking. Protein generation rate of common conger increased until 1day after stocking while that of olive flounder increased until 3days. The average protein generation rates of common conger and olive flounder were 0.28g/kg・day and 0.21g/kg・day, respectively. The trends of other waste generation rate were similar to protein generation rate.

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      참고문헌 (Reference)

      1 "World J" 31 : 426-428, thermophilicaerobictreatmentofpotatoprocessingwastewater

      2 "Water quality requirement for intensive aquaculture Symposium on New Developments in the Utilization of Heated Effluents and Recirculation Systems or Intensive Aquaculture" 245-252, 1980

      3 "Unit operations and processes in environmental engineering. 2nd ed." PWS Publ. Co 327-, 1996

      4 "The role of circulating catecholamines in the regulation of fish metabolism" 120 : 177-192, 1998

      5 "The adaptations of fish to extremely alkaline environments" 113B (113B): 665-673, 1996

      6 "Suspended solids characteristics from recirculating aquacultural systems and design im- plications" 143-155, 1993

      7 "Standard Method for the Examination of Water and Wastewater" 132-133, 1992

      8 "Protein measurement with the Folin phenol reagent" 265-275, 1951

      9 "Protein Methods. 2nd ed" Wiley-Liss Inc 58-61, 1996

      10 "Performance of a closed recirculating system with foam separation, nitrification and deni- trification units for intensive culture of eel: towards zero emission." 29 : 165-182, 2003

      1 "World J" 31 : 426-428, thermophilicaerobictreatmentofpotatoprocessingwastewater

      2 "Water quality requirement for intensive aquaculture Symposium on New Developments in the Utilization of Heated Effluents and Recirculation Systems or Intensive Aquaculture" 245-252, 1980

      3 "Unit operations and processes in environmental engineering. 2nd ed." PWS Publ. Co 327-, 1996

      4 "The role of circulating catecholamines in the regulation of fish metabolism" 120 : 177-192, 1998

      5 "The adaptations of fish to extremely alkaline environments" 113B (113B): 665-673, 1996

      6 "Suspended solids characteristics from recirculating aquacultural systems and design im- plications" 143-155, 1993

      7 "Standard Method for the Examination of Water and Wastewater" 132-133, 1992

      8 "Protein measurement with the Folin phenol reagent" 265-275, 1951

      9 "Protein Methods. 2nd ed" Wiley-Liss Inc 58-61, 1996

      10 "Performance of a closed recirculating system with foam separation, nitrification and deni- trification units for intensive culture of eel: towards zero emission." 29 : 165-182, 2003

      11 "Nitrogen pollution in mariculture toxicity and excretion of nitrogenous compounds by marine fish" 205-241, 1993

      12 "Lipid and protein changes during the ensilage of blue whiting (Micro- mesistius poutassou Risso) by acid and biological methods" 63 (63): 97-102, 1998

      13 "Biotransformation of fish waste into a stable feed ingredient" 60 (60): 13-18, 1997

      14 "Aquaculture's rapid growth require- ments for alternate protein sources" 50 : 25-28, 1999

      15 "Ammonia toxicity in fish" 45 : 17-23, 2002

      16 "Ammonia removal in selected aquaculture water reuse biofilters" 4 : 135-154, 1985

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      연구자 네트워크맵

      공동연구자 (7)

      유사연구자 (20) 활용도상위20명

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      학술지 이력

      학술지 이력
      연월일 이력구분 이력상세 등재구분
      2026 평가예정 재인증평가 신청대상 (재인증)
      2020-01-01 평가 등재학술지 유지 (재인증) KCI등재
      2017-01-01 평가 등재학술지 유지 (계속평가) KCI등재
      2014-08-06 학술지명변경 외국어명 : Korean Journal of Fisheries and Aquatic Sciences -> Korean Journal of Fisheries and Aquatic Sciences KCI등재
      2013-01-01 평가 등재학술지 유지 (계속평가) KCI등재
      2010-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2009-09-04 학회명변경 한글명 : 한국수산학회 -> 한국수산과학회
      영문명 : The Korean Fisheries Society -> The Korean Society of Fisheries and Aquatic Science
      KCI등재
      2009-07-03 학술지명변경 한글명 : 한국수산학회지 -> 한국수산과학회지
      외국어명 : Journal of The Korean Fisheries Society -> Korean Journal of Fisheries and Aquatic Sciences
      KCI등재
      2008-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2006-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2003-01-01 평가 등재학술지 선정 (등재후보2차) KCI등재
      2002-01-01 평가 등재후보 1차 PASS (등재후보1차) KCI등재후보
      1999-07-01 평가 등재후보학술지 선정 (신규평가) KCI등재후보
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      학술지 인용정보

      학술지 인용정보
      기준연도 WOS-KCI 통합IF(2년) KCIF(2년) KCIF(3년)
      2016 0.47 0.47 0.43
      KCIF(4년) KCIF(5년) 중심성지수(3년) 즉시성지수
      0.43 0.43 0.59 0.17
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