Technical Factsheet on: DI (2-ETHYLHEXYL) ADIPATE
List of Contaminants
As part of the Drinking Water and Health pages, this fact sheet is part of a larger publication:
National Primary Drinking Water Regulations
Drinking Water Standards
MCLG: 0.4 mg/L
MCL: 0.4 mg/L
HAL(child): 1 day: 20 mg/L; Longer-term: 20 mg/L
Health Effects Summary
Acute: EPA has no data on the acute toxicity of di
(2-ethylhexyl) adipate, or DEHA, which is relevant to the
drinking water context. Drinking water levels which are
considered "safe" for short-term exposures for a 10-kg (22 lb.)
child consuming 1 liter of water per day: upto a 7-year exposure
to 20 mg/L.
Chronic: DEHA has the potential to cause the following health
effects from long-term exposures at levels above the MCL: reduced
body weight and bone mass; damage to liver and testes.
Cancer: There is some evidence that DEHA may have the potential
to cause cancer from a lifetime exposure at levels above the MCL.
Usage Patterns
Adipate is used primarily as a plasticizer, commonly blended with
general purpose plasticizers in processing polyvinyl and other
polymers. It is also used as a solvent; in aircraft lubricants;
as a hydraulic fluid; as a plasticizer or solvent in the
following cosmetics: bath oils, eye shadow, cologne,
foundations, rouge, blusher, nail-polish remover, moisturizers
and indoor tanning preparations; in meat wrapping operations.
Production of adipates in 1984 was 27.5 million pounds.
Release Patterns
Sources of adipates include fly ash from municipal waste
incineration, wastewater effluents from publicly-owned treatment
works (POTW) and chemical manufacturing plants. Adipates are also
used as a plasticizer in PVC materials and is known to leach from
plumbing made of PVC plastic. Thus, adipates have been recognized
as a potential drinking water contaminant.
From 1987 to 1993, according to EPA's Toxic Chemical Release
Inventory, adipate releases to land and water totalled over
450,000 lbs., of which about 94 percent was to land. These
releases were primarily from gray and ductile iron foundries. The
largest releases occurred in Ohio and Indiana. The largest direct
releases to water occurred in Tennessee.
Environmental Fate
If released to air, di(2-ethylhexyl) adipate (DEHA) can exist in
both vapor and particulate phases. The vapor phase will degrade
relatively rapidly by reaction with photochemically produced
hydroxyl radicals (estimated half-life of 16 hr). The particulate
phase can be physically removed from air by wet and dry
deposition.
If released to soil or water, adipate is expected to biodegrade;
activated sludge screening tests have shown that adipate
biodegrades readily, with a half-life of 2.7 days. Estimated Koc
values of 5004-48,600 suggest that adipate will be relatively
immobile in soil (and not leach) and should partition from the
water column to sediment in the aquatic environment.
Volatilization is expected to be very slow (half-life of 160
days) and not environmentally important; aqueous hydrolysis is
not expected to be important except in very alkaline waters (pH 9
or higher).
Dioctyl adipate was not acutely toxic to algae and fish at or
above its water solubility of 0.78 mg/l. It was acutely and
chronically toxic to Daphnia magna at 480-850 and 24-52 ug/l,
respectively. A comparison of the mean environmental water
concentration of dioctyl adipate (<0.5 ug/L) with laboratory
chronic toxicity values for Daphnia magna showed a safety margin
of approximately 3 under present use and disposal patterns,
dioctyl adipate presents a small hazard to the freshwater aquatic
environment. A whole-fish BCF of 27 was observed for blue-gill
fish was far less than an estimated BCF value in excess of 2700
calculated from a measured log Kow of >6.11; the difference is
thought to be due to metabolism of adipate by the bluegill. This
measured BCF indicates that bioaccumulation and persistence in
fish is not important environmentally but may be important in
aquatic organisms that are unable to metabolize adipate.
Occupational exposure can occur through dermal contact and
inhalation. The general population can be exposed through
consumption of foods stored in plastic films; DEHA is used as
plasticizer in various food storage wraps and it has been shown
to migrate into stored foods. Exposure via drinking water is also
possible since DEHA is also used as a plasticizer in PVC
materials and is known to leach from plumbing made of PVC
plastic.
Chemical/ Physical Properties
CAS Number: 103-23-1
Color/ Form/Odor: Light colored, oily liquid with an aromatic
odor
M.P.: -67.8 C B.P.: 214 C
Vapor Pressure: 8.5x10-7 mmHg at 25 C
Octanol/Water Partition (Kow): Log Kow = >6.11
Density/Spec. Grav.: 0.922 at 25 C
Solubility: 0.78 g/L of water at 22 C; Slightly soluble in
water
Soil sorption coefficient: Koc estimated at 5004 to 48,000;
immobile in soil
Odor/Taste Thresholds: N/A
Bioconcentration Factor: BCF = 27 in fish; not expected to
bioconcentrate in aquatic organisms.
Henry's Law Coefficient: 4.34x10-7 atm-cu m/mole at 20 C;
Trade Names/Synonyms: Adipic acid, bis(2-ethylhexyl) ester;
Bis(2-ethylhexyl) hexanedioate; BEHA; DEHA; Adipol 2EH; Bisoflex
DOA; Dioctyl adipate; Effomoll DOA; Flexol A26; Kodflex DOA;
Monoplex DOA; Octyl adipate; Plastomoll DOA; Sicol 250; Truflex
DOA; Vestinol OA; Wickenol 158; Witamol 320; Ergoplast AdDO;
Kemester 5652; Reomol DOA; Rucoflex plasticizer DOA; Staflex DOA.
Adipate, (2-diethylhexyl)
Other Regulatory Information
Monitoring For Ground/Surface Water Sources:
- Initial Frequency- 4 quarterly samples every 3 years
- Repeat Frequency- If no detections during initial round:
- 2 quarterly per year if serving >3300 persons;
- 1 sample per 3 years for smaller systems
- Triggers - Return to Initial Freq. if detect at >0.0006 mg/L
Analysis:
Reference Source |
Method Numbers |
EPA 600/4-88-039 |
506; 525.2 |
Treatment- Best Available Technologies:
Granular Activated Charcoal
Toxic Release Inventory - Releases to Water and Land, 1987 to
1993 (in pounds):
|
Water |
Land |
TOTALS |
27,471 |
425,230 |
Top Five States* |
OH |
531 |
173,900
|
IN |
5,500 |
93,275
|
VA |
1,886 |
46,102
|
TN |
18,480 |
26,409
|
MI |
250 |
29,750
|
Major Industries* |
Gray iron foundries |
2,263 |
316,438
|
Aluminum foundries |
250 |
50,409
|
Rubber, plastic hose/belts |
10 |
32,078
|
Space propulsion units |
0 |
20,363
|
Misc Indust. organics |
11,996 |
131
|
* Water/Land totals only include facilities with releases greater
than a certain amount - usually 1000 to 10,000 lbs.
For Additional Information:
EPA can provide further regulatory and other general information:
EPA Safe Drinking Water Hotline - 800/426-4791
Other sources of toxicological and environmental fate data include:
Toxic Substance Control Act Information Line - 202/554-1404
Toxics Release Inventory, National Library of Medicine - 301/496-6531
Agency for Toxic Substances and Disease Registry - 404/639-6000
List of Contaminants
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