Sorbaldehyde

Hexadienal

BATOPAZDIZEVQF-MQQKCMAXSA-N

Sorbic aldehyde

2-Propyleneacrolein

3-Propyleneacrolein

AC1LCUHN

2-Propylene acrolein

AC1Q2A3B

AC1Q6PP7

trans,trans-4-Hexadienal

2,4-HEXADIENAL

6992AA

OR6049

LS-840

1,3-Pentadiene-1-carboxaldehyde

878K4I6N7T

C19249

CCRIS 4030

CCRIS 5124

HSDB 7239

trans,trans-2,4-Hexadienal

AK117056

CHEMBL1576086

DTXSID2025391

Hexa-2,4-dienal

OR010857

2,4-Hexadienal, predominantly trans,trans

A807974

CHEBI:82334

DSSTox_CID_5391

UNII-878K4I6N7T

ZINC1733897

AJ-31297

AN-23244

CJ-06962

CJ-29498

DSSTox_GSID_25391

KB-82497

LS-74880

NSC 16184

NSC 68096

ST2419409

trans,trans-2,4-Hexadienal, analytical standard

(2E,4E) hexadienal

(2E,4E)-Hexadienal

DSSTox_RID_77769

e,e-2,4-hexadienal

LMFA06000006

MFCD00007004

t,t-2,4-Hexadienal

trans, trans-2,4-hexadienal

trans,trans-Hexa-2,4-dienal

ZINC01733897

AI3-31142

DB-003137

RT-002647

TC-172853

(e,e)-4-hexadienal

AKOS015915466

I14-6296

J-007704

2,4-Hexadien-1-al

BRN 1698401

FEMA No. 3429

FT-0604957

2,4-Hexadienal, trans,trans-

Tox21_200834

142-83-6

trans,trans-2,4-Hexadien-1-al

(2E)-2,4-Hexadienal

trans,trans-2,4-Hexadienal, >=95%

(E,E)-2,4-hexadienal

2,4-(e-e)-hexadienal

2,4-(E,E)-Hexadienal

4488-48-6

NCGC00090786-01

NCGC00090786-02

NCGC00090786-03

NCGC00258388-01

trans,trans-2,4-Hexadienal, 95%

CAS-142-83-6

EINECS 205-564-3

20432-44-4

53398-76-8

73506-81-7

80466-34-8

(2E,4E)-2,4-Hexadienal

(2e,4z)-2,4-hexadienal

(E,E)-hexa-2,4-dienal

n-Hex-2,4-dienal, trans,trans-

MolPort-001-769-759

(2E,4E)-2,4-Hexadienal #

(2E,4E)-hexa-2,4-dienal

(2E,4E/Z)-2,4-hexadienal

(E)-2,(E)-4-Hexadienal

2,4-Hexadienal, (E,E)-

(E,E)-2,4-Hexadien-1-al

2,4-Hexadienal, (2E,4E)-

Hexa-2,4-dienal, (E,E)-

4-01-00-03545 (Beilstein Handbook Reference)

2,4-Hexadien-1-al, (E,E)-

2,4-Hexadienal (89% trans,trans-, 11% cis,trans-)

2,4-HEXADIENAL (2,4-DECADIENAL (25152-84-5))

InChI=1/C6H8O/c1-2-3-4-5-6-7/h2-6H,1H3/b3-2+,5-4

The Henry's Law constant for 2,4-hexadienal is 9.78X10-6 atm-cu m/mole (1). This Henry's Law constant indicates that 2,4-hexadienal 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 3.8 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 30 days(SRC). 2,4-Hexadienal's Henry's Law constant indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of 2,4-hexadienal from dry soil surfaces may exist(SRC) based upon an estimated vapor pressure of 4.8 mm Hg(SRC), determined from a fragment constant method(3).
Literature: (1) Buttery RG et al; J Agric Food Chem 19: 1045-48 (1971) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Lyman WJ; p. 31 in Environmental Exposure From Chemicals Vol I, Neely WB, Blau GE, eds, Boca Raton, FL: CRC Press (1985)

In water, 8.1X10+3 mg/L @ 25 deg C /Estimated/
Literature: US EPA; Estimation Program Interface (EPI) Suite. Ver.3.11. June 10, 2003. Available from, as of Jul 14, 2004: http://www.epa.gov/oppt/exposure/pubs/episuitedl.htm

Using a structure estimation method based on molecular connectivity indices(1), the Koc for 2,4-hexadienal can be estimated to be 17(SRC). According to a classification scheme(2), this estimated Koc value suggests that 2,4-hexadienal is expected to have very high mobility in soil.
Literature: (1) Meylan WM et al; Environ Sci Technol 26: 1560-67 (1992) (2) Swann RL et al; Res Rev 85: 17-28 (1983)