Benzenamine,diazotized,coupledwithDyer'smulberryextract

Benzenamine,diazotized,coupledwithaniline,condensationproducts

DIANILINIUM HYDROGEN PHOSPHONATE

Phenyleneamine

Aminobenzene

benzenaminium

Benzeneamine

Benzenamine

Krystallin

Phenylamine

Aminophen

Anilinum

Arylamine

Benzamine

Benzidam

D'aniline

PAYRUJLWNCNPSJ-UHFFFAOYSA-N

Anilin

Anilina

ANILINE

Aniline reagent

Anyvim

Cyanol

Huile D'aniline

Kyanol

Aniline and homologues

Aniline and homologs

Aniline oil

ANL

phenyl amine

phenyl-amine

Aniline, analytical standard

AC1Q1HGK

Blue Oil

Aniline oil, phenylamine

Benzene, amino

ANILINE, ACS

CHEMBL538

SIR7XX2F1K

AC1L1LU6

ACMC-1AZO2

UNII-SIR7XX2F1K

AC1Q528I

Benzene, amino-

CCRIS 44

HSDB 43

Huile d'aniline [French]

KSC178M0R

S667

Anilin [Czech]

Benzene,amino (aniline)

CI Oxidation Base 1

UN1547

A0463

BDBM92572

DSSTox_CID_90

HMDB03012

Aniline (and salts)

BIDD:ER0581

DB06728

LS-270

RP18568

STR00216

Anilina [Italian, Polish]

C00292

nchembio.257-comp9

Rcra waste number U012

AK110130

Aniline, PESTANAL(R), analytical standard

Aniline, United States Pharmacopeia (USP) Reference Standard

BENZENE,AMINO (ANILINE)

DTXSID8020090

OR033948

OR108779

OR232570

OR250454

OR280906

OR306800

OR306801

STK301792

UN 1547

A833829

Aniline(S#299)-Liq

CHEBI:17296

NCI-C03736

AJ-70174

AN-23725

BP-12047

Caswell No. 051C

CI 76000

CJ-15802

DSSTox_GSID_20090

MO 08492

ANILINE (13C6)

Aniline, AR, >=99%

Aniline, LR, >=99%

DSSTox_RID_75359

MFCD00007629

ZINC17886255

AI3-03053

C.I. Oxidation Base 1

DB-013441

KB-250667

RTR-002007

AKOS000268796

EPA Pesticide Chemical Code 251400

Epitope ID:117704

J-519591

RCRA waste no. U012

FT-0622394

62-53-3

Aniline, ReagentPlus(R), 99%

I01-10413

Tox21_200345

Aniline, ACS reagent, >=99.5%

BENZENAMINE, MAGNESIUM SALT (2:1)

F2190-0417

C.I. 76000

CAS-62-53-3

Aniline, 99% 100g

Aniline, JIS special grade, >=99.0%

MCULE-9347486445

NCGC00091297-01

NCGC00091297-02

NCGC00091297-03

NCGC00257899-01

Aniline, SAJ first grade, >=99.0%

EINECS 200-539-3

37342-16-8

91782-30-8

97862-10-7

Aniline [UN1547] [Poison]

EC 200-539-3

SR-01000944923

142-04-1 (hydrochloride)

146997-94-6

542-11-0 (hydrobromide)

9622-EP2269990A1

9622-EP2270011A1

9622-EP2272817A1

9622-EP2272822A1

9622-EP2272849A1

9622-EP2275102A1

9622-EP2275403A1

9622-EP2275413A1

9622-EP2276085A1

9622-EP2277865A1

9622-EP2277880A1

9622-EP2277881A1

9622-EP2279750A1

9622-EP2280001A1

9622-EP2280004A1

9622-EP2280005A1

9622-EP2280012A2

9622-EP2280020A1

9622-EP2280021A1

9622-EP2281817A1

9622-EP2281818A1

9622-EP2284157A1

9622-EP2284161A1

9622-EP2284174A1

9622-EP2284920A1

9622-EP2287152A2

9622-EP2287156A1

9622-EP2289884A1

9622-EP2289893A1

9622-EP2289894A2

9622-EP2292593A2

9622-EP2292597A1

9622-EP2292610A1

9622-EP2295053A1

9622-EP2295402A2

9622-EP2295409A1

9622-EP2295411A1

9622-EP2295418A1

9622-EP2295421A1

9622-EP2295429A1

9622-EP2295439A1

9622-EP2295503A1

9622-EP2298312A1

9622-EP2298743A1

9622-EP2298749A1

9622-EP2298768A1

9622-EP2298770A1

9622-EP2298776A1

9622-EP2298828A1

9622-EP2301920A1

9622-EP2301923A1

9622-EP2301928A1

9622-EP2301930A1

9622-EP2301939A1

9622-EP2301983A1

9622-EP2302132A1

9622-EP2305652A2

9622-EP2305687A1

9622-EP2305769A2

9622-EP2305808A1

9622-EP2308833A2

9622-EP2308839A1

9622-EP2308840A1

9622-EP2308848A1

9622-EP2308851A1

9622-EP2308858A1

9622-EP2308861A1

9622-EP2308872A1

9622-EP2308873A1

9622-EP2308877A1

9622-EP2308880A1

9622-EP2311802A1

9622-EP2311803A1

9622-EP2311804A2

9622-EP2311806A2

9622-EP2311807A1

9622-EP2311808A1

9622-EP2311816A1

9622-EP2311817A1

9622-EP2311818A1

9622-EP2311825A1

9622-EP2311829A1

9622-EP2311830A1

9622-EP2314558A1

9622-EP2314576A1

9622-EP2314590A1

9622-EP2314593A1

9622-EP2315502A1

9622-EP2316452A1

9622-EP2316829A1

9622-EP2316831A1

9622-EP2371810A1

9622-EP2371812A1

9622-EP2372804A1

9622-EP2378585A1

Aniline, ASTM, ACS reagent, 99.5%

MolPort-000-871-542

12588-EP2272517A1

12588-EP2272813A2

12588-EP2275395A2

12588-EP2275409A1

12588-EP2275469A1

12588-EP2276085A1

12588-EP2284920A1

12588-EP2287940A1

12588-EP2289965A1

12588-EP2292586A2

12588-EP2292601A1

12588-EP2292602A1

12588-EP2292603A1

12588-EP2292618A1

12588-EP2293650A1

12588-EP2295402A2

12588-EP2295421A1

12588-EP2298729A1

12588-EP2298737A1

12588-EP2298739A1

12588-EP2298740A1

12588-EP2298741A1

12588-EP2298771A2

12588-EP2298828A1

12588-EP2299509A1

12588-EP2299510A1

12588-EP2301920A1

12588-EP2301936A1

12588-EP2301983A1

12588-EP2305769A2

12588-EP2308926A1

12588-EP2309564A1

12588-EP2311825A1

12588-EP2311826A2

12588-EP2314558A1

12588-EP2315502A1

12588-EP2316831A1

12588-EP2371810A1

12588-EP2371812A1

12588-EP2371813A1

12588-EP2372804A1

12588-EP2378585A1

2424-53-5 (monosulfate)

542-15-4 (nitrate)

85560-EP2281861A2

85560-EP2298749A1

85560-EP2305657A2

Aniline [UN1547] [Poison]

147630-EP2289877A1

45497-73-2 (hydriodide)

ANILINE (SEE ALSO ANILINE HYDROCHOLORIDE 142-04-1)

SR-01000944923-1

20305-50-4 (sulfate)

ANILINE- 2,3,4,5,6-D5

Aniline, p.a., ACS reagent, 99.0%

542-16-5 (sulfate [2:1])

53894-37-4 (magnesium[1:1] salt)

33921-12-9 (phosphonate [1:1])

17843-02-6 (phosphate [2:1])

37832-42-1 (phosphate [1:1])

InChI=1/C6H7N/c7-6-4-2-1-3-5-6/h1-5H,7H

The measured Henry's Law constant for aniline is 2.02X10-6 atm-cu m/mole(1). This Henry's Law constant indicates that aniline is expected to volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 12 days(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 131 days(SRC). Aniline's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). Aniline is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 0.67 mm Hg(3).
Literature: (1) Jayasinghe DS et al; Environ Sci Technol 26: 2275-81 (1992) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Data Compilation Washington, DC: Taylor and Francis, (2002)

Primary anilines may bind to soils due to the ability of the aromatic amino group to form covalent bonds with humic and fulvic material in soils(1). The Koc of aniline in 5 European soils was reported in the range of 43.8-497.7(2). The Koc values in 2 silt loams were 130 and 410 with the higher value occurring in the more acidic soil(3). The Koc of aniline in colloidal organic carbon from groundwater (pH 6.5) was reported as 3,870(4). The adsorption constant for adsorption to H-montmorillonite (pH 8.35) and Na-montmorillonite (pH 6.8) is 1,300 and 130(5). The Koc of aniline in 3 silt-clay loams were 269 (pH 4.4), 48 (pH 6.5) and 16 (pH 7.2)(6). A mean Koc value of 55 was determined for aniline in 4 sewage sludges(7). The Koc in five second-generation reference EUROSOILS was 8, 32, 19, 27 and 137(8). According to a classification scheme(9), this Koc data suggests that aniline may have very high to medium mobility in soil. The pKa of aniline is 4.60(10, indicating that this compound will partially exist in the protonated (cation) form; however, in the pH range between pH5 and pH9, aniline will exist primarily in the non-protonated form; in the protonated form in the environment, cations generally adsorb more strongly to soils containing organic carbon and clay than their neutral counterparts(11). In a sorption study using pond sediment from Cherokee Park pond in Athens GA, the sorption kinetics of aniline were characterized by a rapid initial loss of aniline from the aqueous phase followed by a much slower rate of disappearance. The initial sorption was a reversible cation-exchange followed by a slower covalent-binding. It was shown that at pH values greater than the pKa, sorption kinetics were slower than at pH3.75 (rate constants of 4.53-7.95/hr above versus 13.3 below)(12).
Literature: (1) Adrian P et al; Chemosphere 18: 1599-1609 (1989) (2) Gawlik BM et al; Chemosphere 36: 2903-19 (1998) (3) Pillai P et al; Chemosphere 11: 299-317 (1982) (4) Means JC; Amer Chem Soc 186th Natl Mtg 23: 250-1 (1982) (5) Bailey GW et al; Soil Sci Soc Amer Proc 32: 222-34 (1968) (6) Lee LS et al; Environ Toxicol Chem 16: 1575-82 (1997) (7) Kordel W et al; Chemosphere 35: 107-19 (1997) (8) Gawlik BM et al; Chemosphere 41: 1337-47 (2000) (9) Swann RL et al; Res Rev 85: 17-28 (1983) (10) Perrin DD; Dissociation Constants of Organic Bases in Aqueous Solution. IUPAC Chem Data Series. Suppl. London Buttersworth (1972) (11) Doucette WJ; pp. 141-188 in Handbook of Property Estimation Methods for Chemicals. Boethling RS, Mackay D, eds. Boca Raton, FL: Lewis Publ (2000) (12) Weber EJ et al; Environ Sci Technol 35: 2470-75 (2001)
Literature: #Under short-term conditions (24-hr), the sorption of aniline in a silty clay soil was not solely dependent on cation exchange and that solubility was a consideration(1); passing rainwater through a soil column had no effect on the sorption to the silty clay soil(1). Using four Indiana soils and one Iowa soil, abiotic loss of aniline from the aqueous phase to the soil phase occurred with an initial rapid loss due to reversible mass transfer processes followed by a slow loss due to irreversible reactions(2).
Literature: (1) Donaldson FP, Nyman MC; Chemosphere 65: 854-62 (2006) (2) Fabrega-Duque JR et al; Environ Sci Technol 34: 1687-93 (2000)