ISAVYTVYFVQUDY-UHFFFAOYSA-N

para-tert-Octylphenol

p-tert-Octylphenol

4mga

p-Terc.oktylfenol

P-T-Octylphenol

tert-Octylphenol, flaked

4-tert-Octylphenol

IOY9FVU3J3

27L

4-t-Octylphenol

AC1L1RR4

AC1Q1MH6

p-tert.-octylphenol

ACMC-1C0TS

UNII-IOY9FVU3J3

4-tert-Octylphenol, analytical standard

KSC491S6L

2025AB

4-tert-octyl-phenol

NSC5427

NSC7248

para-tert.-octyl phenol

SCHEMBL10141

CTK3J1965

p-(tert-octyl)phenol

BIDD:ER0044

CHEMBL259327

NE10184

p-Octylphenol (VAN)

RL01724

C14205

CCRIS 8947

HSDB 5411

p-terc.Oktylfenol [Czech]

4-(TERT-OCTYL)PHENOL

BBL027379

DTXSID9022360

FR-0872

Jsp002415

NSC 5427

NSC-5427

NSC-7248

OR034336

OR106635

OR106636

OR106637

SBB008090

STK594853

CHEBI:34445

DSSTox_CID_2360

ZINC1686938

AJ-29864

AK-59170

AN-23179

ANW-20579

CJ-06382

CJ-27869

DSSTox_GSID_22360

p-(tert-octyl)-pheno

4-tert-Octylphenol, 97%

BB_SC-2007

BDBM50423506

DSSTox_RID_76556

MFCD00002368

ZINC01686938

AI3-10011

DB-063344

KB-187721

LS-105148

RTR-005279

ST24042806

ST50828074

TR-005279

AKOS005516422

J-523827

W-108198

4-tert-Octylphenol, certified reference material, TraceCERT(R)

BRN 0513992

p-(1',3',3'-Tetramethylbutyl)phenol

I01-10180

p-(1,3,3-Tetramethylbutyl)phenol

Tox21_112084

Tox21_400011

140-66-9

Phenol, p-(tert-octyl)-

4-(1,3,3-Tetramethylbutyl)phenol

MCULE-1575585247

NCGC00164127-01

NCGC00164127-02

NCGC00164127-03

NCGC00164127-04

NCGC00164127-05

NCGC00164127-06

NCGC00164127-07

NCGC00181157-01

CAS-140-66-9

EINECS 205-426-2

p-(1',1',3',3'-Tetramethylbutyl)fenol

p-(1',1',3',3'-Tetramethylbutyl)phenol

37769-53-2

85771-77-3

4-tert-Octylphenol solution, 1 mug/mL in acetone, analytical standard

p-(1,1,3,3-Tetramethylbutyl)phenol

SR-01000944308

Tox21_112084_1

124765-79-3

4-(1,1,3,3-TETRAMETHYLBUTYL)PHENOL

4-tert-Octylphenol solution, 10 mug/mL in acetone, analytical standard

MolPort-001-791-606

p-(1,1,3,3-tetramethylbutyl)-pheno

4-(1,1,3,3-TetraMethyl-Butyl)Phenol

4-(2,4,4-trimethylpentan-2-yl)phenol

4-tert-Octylphenol solution, 1000 mug/mL in acetone, analytical standard

SR-01000944308-2

4-(1,1,3,3-tetramethylbutyl)-pheno

phenol,-(1,1,3,3-tetramethylbutyl)-

Phenol, p-(1,1,3,3-tetramethylbutyl)-

4-06-00-03484 (Beilstein Handbook Reference)

Phenol, 4-(1,1,3,3-tetramethylbutyl)-

p-(1 inverted exclamation mark ,1 inverted exclamation mark ,3 inverted exclamation mark ,3 inverted exclamation mark -tetramethylbutyl)fenol

WLN: QR DX1 & 1 & 1X1 & 1 & 1

InChI=1/C14H22O/c1-13(2,3)10-14(4,5)11-6-8-12(15)9-7-11/h6-9,15H,10H2,1-5H

The Henry's Law constant for 4-(1,1,3,3-tetramethylbutyl)phenol is estimated as 6.9X10-6 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This value indicates that 4-(1,1,3,3-tetramethylbutyl)phenol will volatilize from water surfaces(2,SRC). 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) is estimated as approximately 8 days(2,SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) is estimated as approximately 61 days(2,SRC). The Henry's Law constant(1,SRC) indicates that volatilization from moist soil may occur(SRC).
Literature: (1) Meylan WM, Howard PH; Environ Toxicol Chem 10: 1283-93 (1991) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 15-1 to 15-29 (1990)

The Koc of 4-(1,1,3,3-tetramethylbutyl)phenol is estimated as approximately 18,000(SRC), using an estimated log Kow of 5.28(1,SRC) and a regression-derived equation(2,SRC). According to a recommended classification scheme(3), this estimated Koc value suggests that 4-(1,1,3,3-tetramethylbutyl)phenol will be immobile in soil(SRC). However, this compound was measured in wells down gradient from the flooding basins (0.17 ug/L) during rapid infiltration of primary sewage (containing 4-(1,1,3,3-tetramethylbutyl)phenol at 0.79 ug/L) at a kame site(4). Sorption processes did not appear to completely control the movement of this compound through soil(4). This compound was again present in wells down gradient from the initial site(at 0.01-0.017 ug/L) at another rapid infiltration site in Arizona (4-(1,1,3,3-tetramethylbutyl)phenol initially present at 0.757 ug/L); here, removal of 4-(1,1,3,3-tetramethylbutyl)phenol was attributed mainly to sorption processes as the sewage had been through secondary treatment(5).
Literature: (1) Meylan WM, Howard PH; J Pharm Sci 84: 83-92 (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 23 (1983) (4) Hutchins SR et al; Water Res 18: 1025-36 (1984) (5) Tomson MB et al; Water Res 15: 1109-16 (1981)