Document o90Yzw6qBNOe6KXX7VagdXDBE
AR226-2704 26
AR226-2704
TORONTO WORKSHOP MATERIALS
September 13-14,2004
Fluorotelomer Alcohol and
Fluorotelomer-Based Polym
(Bio)degradation
Bob Buck DuPont Chemical Solutions Enterprise
Wilmington, DE
Fluorotelomer-based Polyme
Do polymers "degrade" to form fluorotelomer species that can transform, partition, migrate?
Route(s) to the
Soil
Disposal of articles treated with polymer (i.e. landfill) STP sludge amended to soil
Incinerator
Municipal Waste disposal of articles treated with polym
STP
. Laundering & cleaning activities No transformation expected, short residence time Majority settles in sludge which is amended to soil, remainder as particles in aqueous outflow go to sedime
Sediment
Aqueous outflow from STP
Polymer "Degradation" - Where to Inves
Abiotic Transformation : Hydrolysis, Ph
Industrial Use : Product Dispersion Consumer Use : Cleaning, washing, sunlight ( Disposal: Incineration
Biotic Transforamtion : Sludge, Soil, Se
Disposal Down-the-drain => POTW
e Municipal waste => landfill or incineration
Polymer Hydrolytic Stability : OECD 111 -
e Fluorotelomer-based Acrylate and Urethane Polym
studied
9 Reactions in water are one of the most common me non-biological degradation of substances in the
environment. 9 Aqueous stability tests at environmentally and biolo
relevant pH's and temperatures.
pH 4, 7, 9 at 50C ; pH 1.2 at 37C
9 Four replicates : Analysis at 0 and 5 Days 9 Study
No change , Polymers are hydrolytically stable
Fluorotelomer-Based Acrylic Polymer
Tnnnfimtinn - DuPnnt
e Experimental Approach
Typical municipal waste incineration condition >1000C, 2 seconds
a University of Dayton Research Institute, Advanced The
System
Article treated with Polymer and Polymer itself Studied
9 Study Complete
9 Manuscripts in preparation, To be presented at SETAC N
The polymer is destroyed under typical municipal waste
conditions
a Municipal incineration is not a source ofperfluorocarbo
Polymer Biodegradation Studies - D
Acrylate and Urethane Polymers
Sludge
Ready Biodegradation (OECD 301 B/D) Inherent Biodegradation (OECD 302 B) Work complete. Analysis and reports in-progress
Preliminary evaluation indicates no evidence that po degrading
Screening Studies (commenced Septem
2004)
Soil: Aerobic; Sediment: Anaerobic
For method development Then, commence longer-term studies
Fluorotelomer Alcohols
F(CF2CF2)nCH2CH20H "Telomer B Alcohol"
'^s.i^
Telomer B Alcohol : Physical-Chemical P
Water solubility
~150 mg*L"1 (ppb)
Vapor Pressure
3 pa at 21 C (measured)
Hydrolysis
hydrolytically stable
pH 4, 7, 9 at 50C, pH 1.2 at 37C for five
Photolysis
does not absorb visible light
Highly Sorptive to soils, sediments,
iiSfflaaasBiwasattiisiBil
CATABOL Biodegradation Predic
CgF^Ch^CHzOH
0.0% CgFpCH^CH^OH
75%
CgF^C^COOH
6.8%
"^ C7Fi5CF=CH
13.7% C^r ^cC^=CH.^
1.2%
C^F^C^COOH
3.3%
C^F^CO
The sum of the % values =100 The model predicts this will be the pathway & distribution of tran
products
^w
Chemical Standards
To achieve unequivocal analytical quantitative accuracy and p
Isotopically - Labeled Standards . M+5 : C7Fl513CF2CD2CD20H (internal standard)
. M+2 : C^^CFa^COOH CgFi^CI^COOH
C^FisCF^CHPCOOH "Cold" Standards
. CgF^CHzCOOH C7Fi5CF=CHCOOH . CsFuCOOH
Others are being synthesized for transformation prod observed
8-2 Telomer B Alcohol : CgF^CI-^
Biodegradability Screening
Ready : emulate a POTW
Inherent: favorable, forcing conditions
* Qualitative Identification & Analysis 9 Enable analytical method development
Biodegradation Studies
^C Radiolabeled Study Material
Quantitative Identify stable transformation product(s)
28-Day Ready Biodegradatio Modified OECD 301D
of
^F^CFzCh^CI^OH
Sponsored by the Telomer Research Program
Asahi Glass. Clariant. Daikin, DuPont
Manuscript submitted to Environmental Science & Technolo.
n i'<w7
Results - Day 28 biodegradation
LC/ARC analysis of ^C-labeled transformation p
xW2 Sample: E--61 DR-A
. -
-., ^,,,
3.7
, Vial: 1, lnj.# 1, Channel: ARC(CPM)
..
^
^.
-^
5 paren 1.7
-0.3 0.00
20.00
- ^ L ^^ -^A^-J">?u-CA-~. -r^uAAf^l
"i'
-J L
-1--1----1
]"" I'
I
" 1
1
|
!
i
40.00
60.00
Peaks 1,2, 3, &4are observed transformati
products and peak 5 is the parent.
Ready Biodegradation Potential Biotransformation Rout
8-2 Telomer B Alcohol
56% ^?
i F(CF,),11CF,CH,CH,OH --'27%
PiCP^CP^CH^COOH
F(CF2)714CF=CHCOOH 6%
V
CyF^CI-^CH
^
New, Previousl Transformation
! -?
v
F(CF2)714COOH 2%
4? Other fluorinated substances ?
F(CF2)714C No C9
(Does Not include unidentified minor transformation prod
Accelerated Biodegradatio
90 Days
Acclimated Sludge
FtCFzl^CFsCHzCHzOH
DuPont
unpubli
Time Course of Biotransformati
C7F1,14CF,CH,CH,OH
FtCFzl^COOH
r To be identified FtCFaty^CHzCHzCHzOH
^
"^ ^"
F(CF2)714CF=CHCOOH F(CFo)7 CFoCH^COOH
Unidentified metaboli FtCFzly^CFzCHzCHaO
100 w w
(0 80
(0
60
soP^ 40
20
The m/roctes ofsctence"
Inherent Biodegradation
Potential Biotransformation Route
8-2 Telomer B Alcohol
F(CF2)714CF2CH2CH20H
Undefin
Define
9
F(CF2)714CF2CH2COOH
s--"""
F^F^CF^HCOOH -""l?
C^^CI^CI-^C
?
T
F(CF2)714COOH
F(CF2)sCOOH
F(CF2)714C Not
: :
: :
^ f
; :
T
T
T
Other fluorinated substances ? unp
.&m^&SWSs!sSSfS~.....-,~
Time Course of CF3(CF2)4COOHFor
Test Vessels (Sludge culture + 1160 ppb P.'-O]^ TBA)
Abiotic Control (Killed Sludge culture + 0.5 mM NaCN + 1160 ppb [3,"C]-8-2 TBA) 14 12 10
4
unp
Spike Reco DayO Day 7 Day 14 Day28 Day 56 Day 90
0
20
40
60
80
100
Days after the initiation
Presence of additional hydrocarbon co-metabolites accelerate form
Inherent Biodegradation - 90 Day
_______
CyF^CF^CH^CH^OH_____
e Many Additional ^C containing transformation pro
structural identification in-progress
9 ^CO^ observed 9 C^F^ COO- is a transformation product 9 CyF^COO- is not formed rapidly or in great amoun
the primary transformation product
- No "C9" CsF^COO- observed
OTO -Cfy
fe
unp
^3^5^' v^a^,-'
Presentation Outline
Telomer Alcohol Degradation
Abiotic
e Hydrolytic Stability
Biotic
9 Catabol
9 Sludge : 3M, UT, TRP, DD studies (9, 6)
Soil : DD
@ S02 to COOH
Fluorotelomer-Based Polymer Degradation
a Abiotic
Incineration, Hydrolysis
a Biotic
Zahn-Wellens, Sturm Tests
Release, Fate and Effects Compartm