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- れれ くまじ
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5 NOEC 0.01mg/L 10µg/L Oryzias latipes LC mg/L 870µg/L OECD TG 203(1992) Oryzias latipes GLP (48 ) mg/l ph HPLC Probit ( :EcoTox-Statics) (LC50)1.36 mg/l LC mg/L 871µg/L PNEC mg/l mg/l mg/L mg/l mg/l ACR Acute chronic ratio mg/L mg/L 10 PNECwater mg/L µg/L PNECwater (0.0026mg/L) mg/L Federal Water Quality Guideline (2002) mg/L PNEC mg/L 72 EC 50GRO 0.006mg/L 2, mg/L (0.003µg/L) PNEC PNECwater PNECwater 3
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7 ECHA:Exp Key Toxicity to aquatic algae and cyanobacteria d7-492d-9117-a9a9746cf ECHA: Long-term toxicity to aquatic invertebrates Velte,J.S.(1984):Acute Toxicity of Hydrazine Hydrate to the Fathead Minnow (Pimephales promelas) and Daphnid (Daphnia pulex).bull. Environ. Contam. Toxicol.33(5): ECOTOX no Brooke,L.(1987):Report of the Flow-Through and Static Acute Test Comparisons with Fathead Minnows and Acute Tests with an Amphipod and a Cladoceran.Memo to L.Larson, Center for Lake Superior Environmental Studies dated August 31:24 p. ECOTOX no Hunt,T.P., J.W. Fisher, J.M. Livingston, and M.E. Putnam(1981):Temperature Effects on Hydrazine Toxicity to Bluegills.Bull. Environ. Contam. Toxicol.27(5): ECOTOX no
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10 [1] (2002) ( h14-05/chap01/03/26.pdf) [2], (2005) No. 73 ( dt/pdf/ci_02_001/risk/pdf_hyoukasyo/253riskdoc.pdf) [3] [4] OECD SIDS Initial Assessment Report. [5] European Union European Union Risk Assessment Report. [6] International Programme on Chemical Safety Environmental Health Criteria [7] WHO / IPCS CICAD Concise International Chemical Assessment Document [8] Government of Canada, Environmental Canada, Health Canada Canadian Environmental Protection Act Priority Substances List Assessment Report [9] Australia NICNAS: Priority Existing Chemical Assessment Reports [10] Hirzel, S BUA-Report. [11] Japan < challenge/list0708.pdf> [12] United States Environmental Protection Agency Office of Water Office of Science and Technology (2009): National Recommended Water Quality Criteria < [13] Environment Agency: Chemical Standards < [14] Environment Canada (2015): Canadian Environmental Quality Guidelines < tml> [15] Environment Canada (2013): Canadian Environmental Protection Act, 1999 Federal Environmental Quality Guidelines< fact-fait/feqg-recommand-eng.php > [16] Federal Ministry for the Environment, Nature Conservation and Nuclear Safety (2014): Water Resources Management in Germany Part 2 Water quality < eil_02_englisch_barrierefrei.pdf > [17] Crommentuijn, T., D.F. Kalf, M.D. Polder, R. Posthumus, and E.J. van de Plassche Maximum Permissible Concentrations and Negligible Concentrations for Pesticides.Report No National Institute of Public Health and Environmental Protection, Bilthoven, The Netherlands. [18] National Institute of Public Health and the Environment (1999): Environmental Risk Limits in Netherlands, Setting Integrated Environmental Quality Standards for Substances in the Netherlands, Environmental quality standards for soil, water & air. 8
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19 EC50 Median Effective Concentration LC50 Median Lethal Concentration NR-LETH LOEC(Lowest Observed Effect Concentration NOEC No Observed Effect Concentration ABN(Abnormal DVP(Developmental changes GRO Growth HEMT Hematological Parameters IMM Immobilization LOCO(locomotion MOR Mortality MUL PGRT Population Growth Rate PHY(Physiology) REP Reproduction STRC Structural Changes RATE 17
20 ECHA:Exp Key Toxicity to aquatic algae and cyanobacteria entuuid=0f d7-492d-9117-a9a9746cf ECHA: Long-term toxicity to aquatic invertebrates Velte,J.S.(1984):Acute Toxicity of Hydrazine Hydrate to the Fathead Minnow (Pimephales promelas) and Daphnid (Daphnia pulex).bull. Environ. Contam. Toxicol.33(5): ECOTOX no Brooke,L.(1987):Report of the Flow-Through and Static Acute Test Comparisons with Fathead Minnows and Acute Tests with an Amphipod and a Cladoceran.Memo to L.Larson, Center for Lake Superior Environmental Studies dated August 31:24 p. ECOTOX no Hunt,T.P., J.W. Fisher, J.M. Livingston, and M.E. Putnam(1981):Temperature Effects on Hydrazine Toxicity to Bluegills.Bull. Environ. Contam. Toxicol.27(5): ECOTOX no Bringmann,G., and R. Kuhn(1978):Limiting Values for the Noxious Effects of Water Pollutant Material to Blue Algae (Microcystis aeruginosa) and Green Algae (Scenedesmus quadricauda) in Cell Propagation Inhibition Tests (Grenzwerte der Schadwirkung Wasse.Vom Wasser50:45-60 ECOTOX no Civil and Environmental Engineering Development Office(1978):Proceedings of the Conference on Environmental Chemistry of Hydrazine Fuels.CEEDO-TR-78-14, Proc. Conf. Environ. Chem. Hydrazine Fuels, Sept.13, 1977, Tyndall AFB, FL:176 p. ECOTOX no Bringmann,G., R. Kuhn, and A. Winter(1980):Determination of the Biological Effect From Water Pollutants to Protozoa. III. Saprozoic Flagellates (Bestimmung der Biologischen Schadwirkung Wassergefahrdender Stoffe Gegen Protozoen III. Saprozoische Flagellaten).Z. Wasser-Abwasser-Forsch.13(5): ECOTOX no Bringmann,G., and R. Kuhn(1977):Limiting Values for the Damaging Action of Water Pollutants to Bacteria (Pseudomonas putida) and Green Algae (Scenedesmus quadricauda) in the Cell Multiplication Inhibition Test.Z. Wasser-Abwasser-Forsch.10(3-4): ECOTOX no Fisher,J.W., D.S. Myers, and M.L. Meyers(1980):The Effects of Selected Hydrazines upon Fish and Invertebrates.AMRL-TR-79-93, Tech.Rep.Aerosp.Med.Res.Lab., Wright-Patterson Air Force Base, OH:25 p. ECOTOX no Bringmann,G., and R. Kuhn(1977):Results of the Damaging Effect of Water Pollutants on Daphnia magna (Befunde der Schadwirkung Wassergefahrdender Stoffe Gegen Daphnia magna).z. Wasser-Abwasser-Forsch.10(5): ECOTOX no Bringmann,G., and R. Kuehn(1982):Results of Toxic Action of Water Pollutants on Daphnia magna Straus Tested by an Improved Standardized Procedure.Z. Wasser-Abwasser-Forsch.15(1): 1-6 ECOTOX no Slonim,A.R.(1986):Acute Toxicity of Some Hydrazine Compounds to Salamander Larvae, Ambystoma spp..bull. Environ. Contam. Toxicol.37(5): ECOTOX no Evans,D.W., and L.M. Coughlin(1992):Effect of Lithium/Hydrazine Water Chemistry on Short-Term Survival of Zebra Mussel.J. Shellfish Res.11(1): ECOTOX no
21 Proteau,J.P., P. Lim, and R. Labat(1979):Toxicity of a Nitrogenous Derivative, Hydrazine Hydrate, for Carassius carassius L., Rutilus rutilus L. and Different Development Stages of Brachydanio rerio.ann. Limnol.15(3): ECOTOX no Henderson,V., J.W. Fisher, and R. D'Allessandris(1981):Toxic and Teratogenic Effects of Hydrazine on Fathead Minnow (Pimephales promelas) Embryos.Bull. Environ. Contam. Toxicol.26(6): ECOTOX no Fisher,J.W., C.B. Harrah, L.K. Weaver, and W.I. Wingo(1978):Acute and Behavioral Effects of Hydrazine on Lepomis macrochirus.aerospace Med.Res.Lab., Wright-Patterson Air Force Base, OH:10 p. ECOTOX no Henderson,V., J.W. Fisher, R. D'Allessandris, and J.M. Livingston(1983):Effects of Hydrazine on Functional Morphology of Rainbow Trout Embryos and Larvae.Trans. Am. Fish. Soc.112: ECOTOX no Fisher,J.W., C.B. Harrah, and W.O. Berry(1980):Hydrazine: Acute Toxicity to Bluegills and Sublethal Effects on Dorsal Light Response and Agression.Trans. Am. Fish. Soc.109(3): ECOTOX no Slonim,A.R.(1977):Acute Toxicity of Selected Hydrazines to the Common Guppy.Water Res.11(10): ECOTOX no Applegate,V.C., J.H. Howell, A.E.,Jr. Hall, and M.A. Smith(1957):Toxicity of 4,346 Chemicals to Larval Lampreys and Fishes.Spec.Sci.Rep.Fish.No.207, Fish Wildl.Serv., U.S.D.I., Washington, DC:157 p. ECOTOX no Loeb,H.A., and W.H. Kelly(1963):Acute Oral Toxicity of 1,496 Chemicals Force-Fed to Carp.U.S.Fish.Wildl.Serv., Sp.Sci.Rep.-Fish.No.471, Washington, D.C.:124 p. ECOTOX no Greenhouse,G.(1976):Evaluation of the Teratogenic Effects of Hydrazine, Methylhydrazine, and Dimethylhydrazine on Embryos of Xenopus laevis, the South African Clawed Toad.Teratology13: ECOTOX no
0 0 0 0............ PNEC.............................. PNECsed.................. 0 0 0 0 PNEC logpow. * Oncorhynchus mykisslc0. mg/l UFs0,000 0.000 mg/l0. µg/lpnec PNECwater PNECwater * Sangster, J. ()
化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]
![化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]](/thumbs/104/163316306.jpg "化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]")
(1) CAS 302-01-2 N 2 H 4 32.0 CAS 7803-57-8 2 1) 2.0 2,3) 113.5 2,4) 1.011 (15 ) 2,3) 1.0036 (25 ) 2,4) 2.1 kpa (16 mmhg) (20 ) 3) 1ppm=1.31 mg/m 3 at 25, n- / -1.37 ( ) 3) 5) K b1 8.510-7 K b2 8.910-16
,161 t 9,753 t 2,408 t LC 50 mg/ L EC 50 mg/l * 5 : Selenastrum 6772-h, Sb 2 O 3, : capricornutum 6 3 Selenastrum h, Sb
1 20017 1543 CAS 1309644 125 Sb 2 O 3 291.52 1 99 1. 2 655 1,425 2 2 2 3 5.2 5.67 2 2 2. 10 12,161 t 9,753 t 2,408 t 4 3. 1 2 3 4. LC 50 mg/ L EC 50 mg/l * 5 : Selenastrum 6772-h, Sb 2 O 3, : capricornutum
CAS NC(CH 2 ) 4 CN 1,4- C 6 H 8 N c.c d = Pa
1 200117 21512 CAS 111693 110 NC(CH 2 ) 4 CN 1,4- C 6 H 8 N 2 108.14 1 99 2-1. 2 1 295 159 c.c. 550 3 1.7-4.9 20 d 0.965 4 3.73 = 1 0.3 Pa 0.002 mmhg20 2 log Pow-0.32 m/z 41, 1.0 68 0.54 54 0.43 4 Koc9-16
CAS H 3 C C CH 2 C 9 H tert d = hpa
1 200140 35 CAS 98839 1335-2- H 3 C C CH 2 C 9 H 10 118.18 1 99 4-tert- 1. 2-23.2 2 163164 2 54 574 3 0.96.6 20 d 4 0.9082 2 4.07 = 1 2.5 hpa 1.9 mmhg20 2 4 log Pow3.48 3.44 m/z 118, 1.0 103 0.58 91 0.21
3, ,104 t mg/l 30 mg/l BOD mg 14 C 8, /kg 11 8, 1 11 OH = cm 3 / sec 11 OH /cm ppm
3, 3-1 200019 4800 CAS 91941 1138 3, 3-4, 4 - -3, 3 - H 2 N Cl Cl NH 2 C 12 H 10 C l2 N 2 253.13 1 95 1. 2 3, 4 132-133 402 5 >200 5 700kg/m 3 5 8.73 = 1 5.610-8 kpa 4.210-7 mmhg20 4 6 log Pow3.51 3.57
橡三酸化二アンチモン.PDF
1 2001 7 1 543( ) CAS 1309 64 4 1 25 ( ) Sb 2 O 3 291.52 1) 99 1. 2) 655 3) 1,425 3) ( ) 2) ( ) 2) ( ) 2) 5.2 ( ) 5.67 ( ) 3) 2) 2. 10 12,161 t ( 9,753 t 2,408 t) 4 2 1) 3. 1) 2) 3) 4. Selenastrum capricornutum
化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]
![化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]](/thumbs/39/20150687.jpg "化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]")
(1) 1,2- DMP CAS 131-11-3 C 10 H 10 O 4 194.2 2 1) 5.5 2,3) 283.7 2,3) 1.192 (20 ) 4) 133 Pa (1 mmhg) (20 ) 5) 1ppm=7.94 mg/m 3 at 25, n- / 1.56 ( ) 6) 4) ( )3.2 (30 ph 7)11.6 (30 ph 9)25 (18 ph 9) 5)
CAS O C O * DOP* DEHP 2- C O O * n- C 24 H 38 O CH 2 CH 2 CH 2 CH 3 CH (CH 2 ) % 2- A BHT , 4
2-1 9628 31307 CAS 117817 2- O C O * DOP* DEHP 2- C O O * n- C 24 H 38 O 4 390.56 CH 2 CH 2 CH 2 CH 3 CH (CH 2 ) 3 1 99 % 2- ABHT 1. 2-55 3 3, 4 386 171 350 6 0.1 % d 20 4 0.9861 4 13.48 0.30410-4 Pa 2.2810-7
化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]
![化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]](/thumbs/39/20157433.jpg "化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]")
1,3-1,3- (1) 1,3-1,3- - CAS 542-75-6 C 3 H 4 Cl 2 110.97 2 1) -84 2) 108 2,3) 112 (trans-) 4) 104 (cis-) 4) 1.225 (20 ) 2) 5.2 kpa (39 mmhg) (25 ) 2) 4.5 kpa (34 mmhg) (25 ) 4) 5.7 kpa (43 mmhg) (25 )
,309 t 22,069 t 7,240 t µg/l µg/l < ,431-70, , , mg/l m
1 20019 1527 CAS 1317368 1230 PbO 223.20 1 99 1. 2 888 2 9.53 0.017 g/l 20 3 3 2 2. 10 29,309 t 22,069 t 7,240 t 4 1 3. 1 2 3.5 6 1 µg/l 9.1-24 2 µg/l < 43 6 27,431-70,000 4.5-1,300 13.4-17 31.7 0.48-3,459
http://www.who.int/ipcs/publications/ehc/en/index.html EHC 1 2 3 4 / EHC http://www.nihs.go.jp/dcbi/publist/ehchsg/ 1-8) WHO/IPCS CICAD (Concise Inter
3 [ ] Priority IARC JMPR 2004 10 Priority 1 Priority 1 Priority 2 Priority 3 Priority 1 1-1) CERI) http://www.cerij.or.jp/ceri_jp/koukai/sheet/sheet_indx4.htm http://www.safe.nite.go.jp/data/sougou/pk_list.html?table_name=hyoka&rank=sh
98-02.PDF
1 982 2207 CAS 67630 2- H 3 C H 3 C CH OH C 3 H 8 O 60.10 1 99.9 % n- 1. 2-88.5 3 82.5 3 11.7c.c. 455 4 212 d 20 4 0.78505 3 2.1 = 1 4 4.4 kpa 33 mmhg20 4 log Pow0.05 0.07 5 m/z45, 1.0 43 0.19 27 0.17
橡アジポニトリル.PDF
1 200117 21512( ) CAS 111693 110( ) 1,4- NC(CH 2 ) 4 CN C 6 H 8 N 2 108.14 1) 99 2-1. 2) 1 2) 295 2) 159(c.c.) 3) 550 3) 1.7-4.9 vol % ( ) 3) d 20 0.965 2) 3.73 ( = 1) 4 0.3 Pa (0.002 mmhg) (20) 2) log
初期リスク評価報告書作成指針（案）
BCF: Bioconcentration Factor EC 50 : Median Effect Concentration 1 50 EEC: Estimated Environmental Concentration EHI: Estimated Human Intake EUSES: Europian Union System for the Evaluation of Substances
［２０］3,5,5-トリメチル-1-ヘキサノール
[20]3,5,5-トリメチル-1-ヘキサノール 20 3,5,5-トリメチル-1-ヘキサノール 1. 物 質 に 関 する 基 本 的 事 項 (1) 分 子 式 分 子 量 構 造 式 物 質 名 : 3,5,5-トリメチル-1-ヘキサノール ( 別 の 呼 称 :3,5,5-トリメチルヘキサン-1-オール) CAS 番 号 :3452-97-9 化 審 法 官 報 告 示 整 理 番 号 :2-217
橡99-24_00 アリルアルコール.PDF
1 9924 2260 CAS 107186 H 2 C CH CH 2 OH 2- -1- C 3 H 6 O 58.08 1 99 1. 2, 3 3, 4, 5-129 96-97 2 21c.c. 24o.c. 2 6, 7 378 6, 7 2.5-18 d 20 4 0.8540 2, 5 2.00 = 1 2.7 kpa 20 mmhg204.3 kpa 32 mmhg30 4 log
橡96-07.PDF
1 967 2482 CAS 50000 CH 2 O 30.03 2952% 12.5 % 1. 2) -92 2) -19.5 2) 5085 3) 424 3) 7.073.0% 4) 20 d 4 0.815 5) 1.03 ( = 1) 5) 1.33 kpa (10 mmhg) (-88.0) 2) log Pow0.35 ( ) 6) 0.35 ( ) 7) 1) m/z 29 ( 1.0
OECD OECD NOEC 14 7296 LC 50 EC 50 7296 4896 OECD TG210Fish, Early-life Stage toxicity Test ISO 12890Water quality - Determination of toxicity to embryos and larvae of freshwater fish Semi-static method
1 I ( )
1 I. 3 1. 4 2. 6 3. 7 4. 8 4.1 8 4.2 ( ) 9 4.3 13 4.4 16 4.5 17 5. 19 5.1 20 5.2 25 5.3 33 6. 37 6.1 37 6.2 41 6.3 44 7. 46 7.1 46 7.2 47 II. 48 A 50 1 50 2 51 3 56 4 59 60 B 61 1 61 2 62 3 65 4 67 68
NPE EO NPE NPE 1 NPE NPE1 EO n NPE NPEn NP 1
10 11 1 1 1 1 1 1 1 1 0 1 10 11 1 1 1 NPE EO NPE NPE 1 NPE NPE1 EO n NPE NPEn NP 1 10 CAS C H 0O 10 C H O 11 1-11- (n = ) 1-0- (n = 10) C 1H O CAS 0-- C 1H O CAS 10-- CAS C 1H O 1-- 10 11 1 1 1 1 1 1 1
t 492 t mg/l 30 mg/l BOD 95 OH = cm 3 / sec 25 8 OH /cm 3 12 = ph ph
2-1 200169 2740 CAS 110-49-6 1103 2- O H 3 C C O CH 2 CH 2 O CH 3 C 5 H 10 O 3 118.13 200168 2-1 99 2-1. 2 2, 3-65 2, 3 144145 45 o.c. 3 392 3 1.512.3 d19 1.009 2 4.07 = 1 30 Pa 0.23 mmhg20 2 4 log Pow0.10
橡96-01.PDF
1 961 31 CAS 71432 C 6 H 6 78.11 1) 99 % 1. 5.5 2) 80.1 2) -11 3) 293563 3) 1.48.0% 3) d 20 0.8786 4) 2.77 ( = 1) 4) 4 13.33 kpa (100 mmhg) (26.9) 2) log Pow2.13 ( ) 5) 2.14 ( ) 6) m/z78 ( 1.0 )77 ( 0.20
橡フタル酸ブチルベンジル.PDF
1 97 7 3 1312 CAS 85 68 7 O BBP 1, 2- C 19 H 20 O 4 312.4 C C O O O (CH 2 ) 3 1 99.9 % 1. 2-35 3 2, 3 370 3, 4 199 d 25 4 1.117 2 10.8 = 1 5 1.15 10-3 Pa 8.6 10-6 mmhg 20 5 253 Pa 1.9 mmhg 200 5 log Pow
,977 t 157,977 t mg l mg l BOD 9398 % OH = cm 3 / sec 11 = cm 3 / sec OH = /
1 9625 2219 CAS 75569 1, 2-1, 2- H 2 C CH CH 3 C 3 H 6 O 58.08 1 99 % 1. 2 2, 3-112.13 2, 3 34.23-37 449 2.8-37 % 2 d 0 4 0.859 4 d 20 0.8304 2 2, 4 2.00 = 1 53.33 kpa 400 mmhg18 59.33 kpa 445 mmhg20 5
資料２
OECD GLP OECD OECD 1960 30 OECD TG 2001 10 17 8 TG 202 208 TG 201 1984 6 TG 202 1984 4 TG 202 2000 10 TG 203 1992 7 TG 204 14 1984 4 TG 205 1984 4 TG 206 1984 4 TG 207 1984 4 TG 208 1984 4 2000 TG 209
資料３ 諸外国における位置づけ
1 1. ( 1) ) 2) 3) 4) 5) 6) 7) 8) 9) 10) 11) 12) 13) 14) 15) 16) ( 1) ) 2) 3) 4) 5) 6) 7)28 8)Ames 9) 10) 11) ( 1) ) 2) 3) 4) ( 1) ) 2) 3) 4) 2 TSCA (a) FIFRA (b) (c) FFDCA (d) FFDCA (e) FFDCA (f) (g) PMN
化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]
![化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]](/thumbs/95/123764426.jpg "化学物質の環境リスク初期評価（平成９～１２年度）結果[39物質]")
(1) CAS 108-88-3 C 7 H 8 92.13 2 3.14 1) -95 2) 110.6 2) 0.866 (20 ) 2) 2.93 kpa (22 mmhg) (20 ) 3) 5.33 kpa (40 mmhg) (31.8 ) 3) 1ppm=3.77 mg/m 3 at 25, n- / 2.69 ( ) 3) 4) 4) 0.067 % (w/w) (23.5 ) 2,5)
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1 2 21-3 CS VOC- CS syasuma@tc4.so-net.ne.jp 4 [] MCS, 200501212B () SHSMCS CS 66 14 16 5 () MCS 16 (GSTs) 14 (8ppb40ppb) 2002192155-161) 6769 68 68 EPA Terr, 1989 69 QEESI 3 70 6 EPA MCS 10 9 8 MCS 6
（Ⅱ）化学物質の環境リスク初期評価（13物質）の結果
1,4-1 1,4- p- 1, 4-1, 4- CAS 123-91-1 C 4 H 8 O 2 88.11 2 1) 2) 11.80 3) 1- / (logp ow ) 101.1 760 mmhg 3) 1.033720 4) 37 mmhg25 5) 1 ppm = 3.60 mg/m 3 at 25, 6) -0.27 7) 8) 9) 3 7) 7) 10) 11) OH NO NO
ナノ材料の有害性評価
CRM CRM 181 TG424 TG42419971995TG407 PBPK PBPK DNA DNA PBPK C C art vein Ramsey & Andersen (1984) ( Qalv Cinh Qt Cvein ) ( Qt Qalv PN ) = + + { ( )} Qi Ci = i Pi ( C ) art Ci dai dt = Qi Qt Pi ( C ) art
橡H8フィリピン報告書_日本語） PDF
1 2 7,000 7,000 3 1986 Execut ive Order 192 Depart ment of Environment and Natural Resources Department of Natural Resources Ministry of House Settlements 8 4 8 6 4 35,000 5,000 30,000 7,000 192 Environmental
加 水 分 解 性 環 境 中 で 加 水 分 解 性 の 基 をもたない 10) 生 物 濃 縮 性 ( 濃 縮 性 が 無 いまたは 低 いと 判 断 される 物 質 生 物 濃 縮 係 数 (BCF): 11) ) 7.9~27.0 ( 試 験 生 物 :コイ 試 験 期 間 :6 週 間 試
[4]2,5-ジクロロアニリン 4 2,5-ジクロロアニリン 1. 物 質 に 関 する 基 本 的 事 項 (1) 分 子 式 分 子 量 構 造 式 物 質 名 :2,5-ジクロロアニリン CAS 番 号 :95-82-9 化 審 法 官 報 公 示 整 理 番 号 :3-261(ジクロルアニリン) 化 管 法 政 令 番 号 :1-156(ジクロロアニリン) RTECS 番 号 :BX2610000
<4D F736F F D C6E30385F A B B83932E444F43>
1,2,4-1,2,4-Trimethylbenzene Pseudocumene 1,3,5-1,3,5-Trimethylbenzene Mesitylene CH 3 CH 3 CH 3 CH 3 CH 3 CH 3 1,2,4-trimethylbenzene 1,3,5-trimethylbenzene CAS 95-63-6 CAS 108-67-8 C 9 H 12 C 9 H 12
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EU 1970 EU 1975 Waste Framework Directive, WFD EU 1970 1970 EU PCB Hazardous Waste Directive, HWD 1991 EU waste hierarchy 1975 1989 Community Strategy for Waste Management 1 No. 1 No. 5 1 Questions and
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73 88 Takeshi MIZUGUCHI This article investigates several studies, proposals and practices regarding environmental accounting and environmental information disclosure. Objects of the investigation include
（Ⅱ）化学物質の環境リスク初期評価（13物質）の結果
1 ( ) DBDPO CAS 1163-19-5 C 12 Br 10 O 959.2 2 1) 305 2) 3.0 1) 1- / (logp ow ) 1) 5.03 mmhg306 1) 1) 3) 4) 5) 1.010-4 6) mg/l25 3 7) OH 8) 4 9) 6 BOD 0% 14 100 mg/l 30 7) 10) BCF 5 < 42 60 mg/l 7) 50
［１７］N,N-ジメチルドデシルアミン=N=オキシド
[17]N,N- ジメチルドデシルアミン =N= オキシド 1. 物質に関する基本的事項 (1) 分子式 分子量 構造式 物質名 : N,N- ジメチルドデシルアミン =N= オキシド ( 別の呼称 : アルキルアミンオキサイド ドデシルジメチルアミンオキシド ) CAS 番号 :1643-20-5 化審法官報告示整理番号 :2-198 化管法政令番号 :1-166 RTECS 番号 :JR6650000
0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 ND(<0.03) g/ 0/12 N
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