Project/Area Number |
24241014
|
Research Category |
Grant-in-Aid for Scientific Research (A)
|
Allocation Type | Single-year Grants |
Section | 一般 |
Research Field |
Environmental impact assessment/Environmental policy
|
Research Institution | National Institute of Advanced Industrial Science and Technology |
Principal Investigator |
KAMO MASASHI 国立研究開発法人産業技術総合研究所, 安全科学研究部門, 主任研究員 (90415662)
|
Co-Investigator(Kenkyū-buntansha) |
NAITO Wataru 産業技術総合研究所, 安全科学研究部門, 主任研究員 (10357593)
NAGAI Takashi 農業環境技術研究所, 有機化学物質研究領域, 主任研究員 (10391129)
SAKAMOTO Masaki 富山県立大学, 工学部, 講師 (20580070)
NAKAMORI Taizo 横浜国立大学, 環境情報研究科, 講師 (50443081)
YASUTAKA Tetsuo 産業技術総合研究所, 地圏資源環境研究部門, 主任研究員 (60610417)
OAHIMA Yuji 九州大学, 農学研究科, 教授 (70176874)
ONO Kyoko 産業技術総合研究所, 安全科学研究部門, 主任研究員 (90356733)
HAYASHI Takehiko 国立環境研究所, 環境リスク研究センター, 主任研究員 (90534157)
|
Project Period (FY) |
2012-04-01 – 2016-03-31
|
Project Status |
Completed (Fiscal Year 2015)
|
Budget Amount *help |
¥41,210,000 (Direct Cost: ¥31,700,000、Indirect Cost: ¥9,510,000)
Fiscal Year 2015: ¥9,620,000 (Direct Cost: ¥7,400,000、Indirect Cost: ¥2,220,000)
Fiscal Year 2014: ¥10,010,000 (Direct Cost: ¥7,700,000、Indirect Cost: ¥2,310,000)
Fiscal Year 2013: ¥9,620,000 (Direct Cost: ¥7,400,000、Indirect Cost: ¥2,220,000)
Fiscal Year 2012: ¥11,960,000 (Direct Cost: ¥9,200,000、Indirect Cost: ¥2,760,000)
|
Keywords | 生物利用可能量 / DGT / 生態リスク / 生物リガンドモデル / カドミウム / 銅 / 生態リスク評価 / 重金属 / Biotic Ligand Model / 金属 / 水生生物 / 土壌生物 / 利用可能量 / BLM: biotic ligand model / metal / ecological risk / risk assesment / bioavailability / biotic ligand model / risk assessment / soil organisms / aquatic organisms / metals |
Outline of Final Research Achievements |
In this research, we aimed to develop a technique for the risk assessment of metals. Historically, the ecological risk assessment of metals was carried out based on the total concentration of metals in environmental medium. Recent researches revealed that the total metal is less responsible for the risk of metals on living organisms, but some forms of metals which are called bioavailable forms of metals are, and hence the risk assessments are carried out based on the bioavailability in the united states and European countries. Because soil and water quality are different in Japan, the direct application of the methodologies developed in other countries are difficult; hence, we aim to customize the methodologies to be applicable to Japanese cases.
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