Document DMBKpV0jrYbXovebNOZaEgYvB
AMG - iiH-7
DuPont Fluorotelomer Product Stewardship Update
25 Nov. 2002
Presented to
The United States Environmental Protection Agency
November 25, 2002
z?
T. S. Bingman, R. C. Buck, S. H. Korzeniowski, J. C. Stadler
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Presentation Outline
Introduction
- Agenda, desired outcomes - Research approach overview - Overall DuPont Timeline & Milestones
Toxicology & Descriptive Biology Update
- Intermediate : Telomer BA - Polymers : Telomer Urethane, Telomer Acrylate - Surfactants : Telomer Phosphate - Overall Summary & Draft Hazard Assessment
Exposure & Risk Characterization
- Consumer & Occupational Exposure - Risk Characterization
Environmental Fate & Effects
- Environmental Compartments - Environmental Effects - Environmental Fate
Summary, Conclusions, Discussion & Questions
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25 Nov. 2002
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DuPont PS Effort : Product Focused
25 Nov. 2002
Environmental Fate & Effects Physical / chemical properties Environmental compartments Fate (abiotic & biotic) Effects : aquatic, terrestrial 14C Labeled Material
DuPont CCER
E nvironm en tal Risk Assessment
input
Exposure Product Trails Mass Balance Human & Environmental
Exposure Assessment Risk Characterization
DuPont CRG
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25 Nov. 2002
2001 : Feb : DuPont meets with U.S. EPA to review Tox & EFE Plans & Results \ April : DuPont presents Tox Studies at Society of Toxicology (SOT) Annual meeting \ DuPont meets with Environment & Health Canada \ May : DuPont meets with DEFRA, UK Env. Agency
\ Oct : DuPont presents initial data at Soc. Of Env. Tox & Chemistry (SETAC) Meeting \ Dec : DuPont meets with U.S. EPA
2002 : \ April : DuPont presents Tox Study Data at SOT Annual meeting \ May : DuPont meets with UK Env. Agency; Dutch RIKZ / Univ. Amsterdam
\ June : DuPont meets with Environment & Health Canada \ Nov. : DuPont presents at North America SETAC Meeting
DuPont meets with U.S. EPA
DUPONT
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25 Nov. 2002
DuPont Fluorotelomer Product Groups: Intermediates, Surfactants, Polymers
1) Intermediates
CF2=CF2
(TFE)
Sales Products
F(CF2CF2)nI (Telom er A)
n = 2-8
F(CF2CF2)nCH2CH2I (Telom er B)
2) Surfactants / "Molecules" Anionic - Phosphate, Carboxylate, Sulfonate Nonionic - Ethoxvlate Betaine
F(CF2CF2)nCH2CH2OH (Telomer BA)
Straight Chain Alkyl
F(CF2CF2)nCH2CH2OC(O)C(R)=CH2
Zonyl TM (r=ch3) ; Zonyl T A N (r=h)
3) Polymers Acrylic Ester Amide Urethane Urea
5 Test Compounds Represent Large Per
Cent of Product Line
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25 Nov. 2002
Repeated-Dose Study Plan Overview
5 Test Compounds
Structures Represent
Majority of DuPont
Product Line
Products
Intermediate Telomer BA
\
Polymer Telomer Urethane Telomer Acrylate
Surfactant Telomer Phosphate Telomer Ethoxylate /
Repeated-Dose Studies Rat Model 90 Day Subchronic Oral
Study One-Generation
Reproduction Developmental Toxicity
We continue to fill in our database, as we committed 1 May 2001.
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DuPont Toxicology Studies Timeline*
25 Nov. 2002
DUPONT
years
Test Material Telomer Urethane Polymer
Telomer BA Intermediate
Telomer Ethoxylate Surfactant
Telomer Phosphate Surfactant
Telomer Acrylate Polymer
Work 90 Day Oral Repeat Dose, 1Gen Repro (Rat) Developmental Study (Rat) Dermal Permeation (Rat) 90-Day Follow-Up Study 90 Day Range-Finding Study 90 Day Oral Repeat Dose + 1Gen Repro (Rat)___________________ Developmental Study Rangefinder Genetic Toxicity: In Vitro Chrom Ab Developmental Study (Rat) 90 Day Range Finding 90 Day Oral Repeat Dose,1Gen Repro (Rat) Developmental Study Rangefinder Developmental Study (Rat) 90 Day Range Finding 90 Day Oral Repeat Dose (Rat) 1Gen Reproduction Study (Rat) Developmental Range Finder Developmental Study (Rat) 28 Day Dermal Repeat Dose (Rat) 14-Day Inhalation Repeat Dose (Rat) 90-Day Range Finding 90 Day Oral Repeat Dose,1Gen Repro (Rat) Developmental Study Rangefinder Developmental Study (Rat)
Work Complete
Work Underway
Projected Timing
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* This is a proposed timeline and subject to change.
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DuPont Toxicity Studies : Rat Model Multiple Routes of Exposure
25 Nov. 2002
Oral
- 90-day subchronic, reproductive, and developmental toxicity - Dosing by gavage, male and female rats - Full battery of tissues examined
Dermal
- In vitro tests for dermal penetration - rat and human skin - In vivo tests - 28 day study, male rats
Inhalation
- 14/28 day study, male rats
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Intermediate : Telomer BA Study Summary & Timeline
25 Nov. 2002
F ( C F 2 C F 2) nC H 2C H 2 O H n= 3 -6
Test Material Telomer BA Intermediate
Study 90 Day Range-Finding Study 90 Day Oral Repeat Dose + 1Gen Repro (Rat) Developmental Study Rangefinder Genetic Toxicity: In Vitro Chrom Ab Developmental Study (Rat)_______
2000 2001
113Q 4Q 1Q2Q3Q4Q
Work Complete
90 Day Subchronic Oral :
Dose Levels : 25, 100, 250 mg/kg/day
NOEL 25 mg/kg/day
Primary Target : Teeth
Reproductive Toxicity :
Dose Levels : 25, 100, 250 mg/kg/day
NOEL 25 mg/kg/day not a selective reproductive toxin
Developmental Toxicity :
Dose Levels : 25, 200, 500 mg/kg/day
NOEL 200 mg/kg/day not a selective developmental toxin
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Polymer: Telomer Urethane Study Summary & Timeline
25 Nov. 2002
F ( C F 2C F 2) nC H 2C H 2O H ( T e l o m e r B A )
n = 3 _6
Straight Chain Alkyl
^ Telomer Urethane Polymer Aqueous Dispersion with surfactant
Test Material Telomer Urethane Polymer
Work 90 Day Oral Repeat Dose + 1Gen Repro (Rat) Developmental Study (Rat) Dermal Permeation (Rat) Nasal Lesion - Follow-Up Study
2003 Q2Q3Q4Q1Q2Q3Q4Q
Work Complete Work Underway
90 Day Subchronic Oral:
Dose Levels : 50, 250, 1000 mg/kg/day
Reproductive Toxicity:
Dose Levels : 50, 250, 1000 mg/kg/day
Developmental Toxicity:
Dose Levels : 50, 250, 1000 mg/kg/day
LOEL 50mg/kg/day
Primary Target : Nose
No effects on reproduction at any dose not a selective reproductive toxin No abnormalities or birth defects at any dose not a selective developmental toxin
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Polymer: Telomer Urethane 90 Day Oral Study (Rat) : Follow-Up
25 Nov. 2002
Purpose: to determine the cause and establish a no-effect level for nasal lesions (olfactory epithelial degeneration and necrosis)
Primary questions to address
-Are the lesions caused by telomer urethane polymer or surfactant? Reproducible? -Can a NOEL be established?
Study Design 3 dose groups: telomer urethane polymer product, surfactant, and control Animals dosed with equivalent of high dose in 90 day study Sacrifice and evaluate nasal tissue at 2, 4 and 13 weeks as needed
Follow with 3 dose level study with either surfactant or polymer
Study started: 11/01/02
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In Vitro Dermal Permeation with
Telomer Urethane
25 Nov. 2002
Purpose: To determine the permeability of the agent through rat and human skin
Draft Guideline: OECD, 1999; ECETOC, 1993
In vitro technique employing glass (static) diffusion cells have been shown to predict percutaneous absorption of various chemicals in vivo
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25 Nov. 2002
Static Diffusion Cell : In Vitro Dermal Permeation
Saline receptor fluid
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Polymer: Telomer Urethane
In-vitro Dermal Permeation
25 Nov. 2002
Methods
- 20 pl product solution was applied to rat epidermal membrane - Total of 1234 pg fluorine in contact with rat skin for 6 hours - 3 ml receptor fluid analyzed for total fluorine using Wickbold torch
method
Results
- Total fluorine in receptor fluid was below the limit of detection (LOD) of 0.052 ppm; less than 0.013 % of urethane polymer permeated the rat skin
- Input for exposure and risk characterization
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25 Nov. 2002
Aqueous emulsion polymerization of monomer composition : - F(CF2CF2)nCH2CH2OC(O)CH=CH2 n = 4 - 6
CBI Information has been redacted
- MW > 40,000
Test Substance for Acute Studies : product = aqueous dispersion of polymer in water with surfactants
Test Substance for Repeated Dose Studies: - solid polymer washed free of surfactants, composition before and after washing verified as the same
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Polymer : Telomer Acrylate Toxicology Information
Acute Toxicity*:
Oral Rat:
ALD > 11,000 mg/kg
Inhalation Rat:
4 hr: ALC = 590 mg/m3
Skin Irritation:
Non-irritating
Eye Irritation:
Moderate, reversible irritation
Sensitization:
Not an irritant or sensitizer in multiple
human patch tests
Aquatic Toxicity*
Rainbow Trout : 96Hr. LC50= 181 mg/L
Daphnia Magna : 48Hr. EC50= 234 mg/L
Algae : 72Hr. EC50= 36.2 mg/L*
25 Nov. 2002
* data generated on aqueous dispersion product
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Polymer: Telomer Acrylate Subchronic Oral Study Range-Finder
25 Nov. 2002
Test material: Telomer Acrylate Polymer Solids in water vehicle Doses:
- 0, 1, 10, 100, 1000 mg/kg/day - 100% active test substance
No clinical signs or body weight effects after 45 days at any dose Total fluorine levels assessed, steady-state appears to occur
around 20 days into dosing Fluorine levels in blood are low
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Polymer: Telomer Acrylate Study Summary & Timeline
25 Nov. 2002
Test Material Telom er Acrylate Polymer
Work 90-Day Range Finding 90 Day Oral Repeat Dose,1Gen Repro (Rat) Developmental Study Rangefinder Developmental Study (Rat)
Work Complete
4Q Work Underway
90 Day Subchronic Oral:
Dose Levels : 10, 100, 1000 mg/kg/day
Reproductive Toxicity:
Dose Levels : 10, 100, 1000 mg/kg/day
Developmental Toxicity:
Dose Levels : 10, 100, 1000 mg/kg/day
Genetic Toxicity :
In Progress In Progress In Progress Negative Ames, Chom Ab
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Surfactant : Telomer Phosphate _______ Chemistry_______
25 Nov. 2002
F(CF2CF2)nCH2CH2OH (Telomer BA) n = 3 - 6
P2O5, H2O, isopropanol, NR3
[F(CF2 CF2 )n CH2 CH2 O]x P(O)(ONR3 H)3-x
X = 1-3
Products by Process BL, B Telomer Distributions tailored to end-use Mixture of Mono-, Bis- and Pyro- Phosphate Esters Study material contains 25 wt% isopropanol as co-solvent
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25 Nov. 2002
Test Material Telomer Phosphate Surfactant
Surfactant : Telomer Phosphate
Timeline
2000 2001 2002 2003
Work
3Q 4Q 1Q2Q 3Q4Q 1Q2Q3Q4C 1Q2Q3Q4Q
90-Day Range Finding
90 Day Oral Chronic Repeat Dose (Rat)
1Gen Reproduction Study (Rat)
Developm ental Range Finder
Developmental Study
28 Day Dermal Repeat Dose (Rat)
14 Day Inhalation Repeat Dose (Rat)
Work Complete Work Underway
90 Day Subchronic Oral:
Dose Levels : 10, 60, 300 mg/kg/day (35% a.i.)
Reproductive Toxicity:
Dose Levels : 75, 500, 3500 mg/kg/day (20% a.i.)
Developmental Toxicity:
Dose Levels : 625, 1250, 2500 mg/kg/day (20% a.i.)
Genetic Toxicity :
Female NOEL = 60 mg/kg/day Male : NOEL < 10 mg/kg/day
Target : liver
In Progress
In Progress
Negative Ames
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Surfactant : Telomer Phosphate Toxicology Information
Acute Toxicity*
Oral Rat: Inhalation Rat: Skin Irritation: Eye Irritation: Sensitization:
ALD > 17,000 mg/kg; LD50> 25,000 mg/kg 4 hr: ALC = 57 mg/m3 Not a skin irritant Minimal irritant Not an irritant or sensitizer
25 Nov. 2002
Aquatic Toxicity*
Rainbow Trout : 96Hr. LC50> 1,000 mg/L Daphnia Magna : 48Hr. EC50>1,000 mg/L Algae : 1Q2003
Biodegradability* : OECD 301 70%
* studies conducted on 35% active test material containing isopropanol
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25 Nov. 2002
Surfactant : Telomer Phosphate Repeated-Dose Toxicology (Rat) : Summary
(35% a.i.; with isopropanol)
90 Day Subchronic Oral :
Dose Levels : 10, 60, 300 mg/kg/day
Inhalation (Two Week) :
Dose Levels : 0.2, 2.0, 20 mg/m3
Dermal (28 Day) :
Dose Levels : 10, 100, 1000 mg/kg/day
(IPA containing, 35% a.i.) Female NOEL = 60 mg/kg/day Male : NOEL < 10 mg/kg/day Pathology peer review in progress
Study Started 29 Oct. 2002
(20% a.i.; no isopropanol)
Reproductive Toxicity :
Report in Progress
Dose Levels : 75, 500, 3500 mg/kg/day
Developmental Toxicity :
Report in Progress
Dose Levels : 625, 1250, 2500 mg/kg/day
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Surfactant : Telomer Phosphate *
25 Nov. 2002
90 Day Oral Study Results
Study Conclusion: Female (F) : NOEL = 60 mg/kg/day
Male (M) : NOEL < 10 mg/kg/day
300 mg/kg/day (35% active, with isopropanol)
- low body weight, food parameters (M)
- decreased red cell mass (M)
- liver: elevated enzymes, increased weights, necrosis (M&F)
- kidney: increased weights, hypertrophy (M) - thyroid: hypertrophy (M&F)
60 mg/kg/day
- liver: elevated enzymes, increased weights, necrosis (M)
- kidney: increased weights, hypertrophy (M) - thyroid: hypertrophy (M)
10 mg/kg/day
- liver: elevated enzymes, necrosis (M)
* material containing isopropanol
NOTE: Minimally elevated Beta Oxidation at 60 and 300 mg/kg/day
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25 Nov. 2002
Surfactant : Telomer Phosphate Reproduction Study Results
Study Conclusion: Report in Progress (20% a.i., no isopropanol)
Study Design
Doses : 75, 500, 3500 mg/kg/day P1 Pathology
- the same target organs identified from 90-Day Subchronic Study with isopropanol-containing test material will be evaluated
In-life Parameters
- observed body weight effects (M & F) only at the high dose
Study Report Complete: January 2003
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Surfactant : Telomer Phosphate Developmental Study Results
Study Conclusion : Report in progress (20% a.i., no isopropanol)
Study Design Doses : 625, 1250, 2500 mg/kg/day
Study Report Complete: December 2002
25 Nov. 2002
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Surfactant : Telomer Phosphate Two-Week Inhalation Study
Study Status: Report in preparation
25 Nov. 2002
Concentrations: 0.2, 2, and 20 mg/m3 Exposures: 6 hrs/day x 9 days, 2-week recovery Animals: 10 male rats/group Additional Blood Analysis : total fluorine
In-life: observed reduced body weight only at high dose
Necropsy: No increased organ weights at any dose
Microscopic findings: respiratory tract appears to be the most sensitive target
Study Report Complete : 1Q 2003
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Surfactant : Telomer Phosphate 28 Day Dermal Study
Study Status: Study started 29 October 2002
25 Nov. 2002
Doses: 10, 100, 1000 mg/kg/day Application: 6 hrs/day for 28 days Animals: 10 male rats/group Tissues: Skin and target tissues identified from oral study Additional Blood Analysis : total fluorine
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Fluorotelomer Products Repeated-Dose Study Observations
25 Nov. 2002
Common across all DuPont Telomer Product Studies :
- liver and thyroid hypertrophy : physiological response - in the rat : males more sensitive than females
Target endpoints are unique to each test material Plasma and Urine Fluoride values indicate that test
materials are processed differently
- functionality appears to drive the observed unique endpoints
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25 Nov. 2002
Hazard Assessment Example - "Reference Dose
This translates the animal data to a proposed "safe" human exposure level
10A: Animals to Humans
Animal Model
Toxicity Testing
10S: Chronic vs. Subchronic
LOEL* = 50 mg/kg/day Telomer Urethane
* expect NOEL to be near this value
**Using the highest value o f uncertainty factor range (1-10)
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*
10H: Human Variability
Human Criterion
`Reference Dose" = 0.05 mg/kg/day
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25 Nov. 2002
Risk Assessment Framework
Characterize Fate & Transport Properties
Release Estimate
Characterize Distribution in the Environment
fHuman Health
Population Exposure
i
Exposure Assessment
1 Non -Hum an
Population Exposure
Direct Use / Release
Exposure
Measure
Predict
Estimated Human Toxicity
i
Hazard Assessment
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RISK ASSESSMENT
Human Health Ecological
Measure Predict
Estimated EcoToxicity
Risk Management Decisions
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azard Assessment
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25 Nov. 2002
How Did We Approach the Analysis?
What types of products do we sell? Who buys our products? What consumer products contain our products? How do our customers use our products? In what form? How do consumers come in contact with our products? What is the magnitude of potential consumer exposure? How
much? How often? How does exposure compare to what we know about potential
hazard? O Risk Characterization
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Exposure Assessment Overview
25 Nov. 2002
P o te n tia lly Exposed S u b p o p u la tio n C onsum er
Food W rap Paper
* Ingestion
C a rp e ts
* D erm al * Indirect
In g e s tio n
Apparel
* D erm al
P o te n tia lly Exposed S u b p o p u la tio n O c c u p a tio n a l
M edical W o rk e r G arm ent W orker P a in te r
C ustodial W o rke r
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M e d ic a l Fabric
P a in ts
C le a n in g Products
* D erm al * D erm al
* D erm al * Inhalation
* D erm al
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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Critical Exposure Variables
CBI Information has been redacted
25 Nov. 2002
Developed point estimates for all necessary variables:
- (1) C o n cen tratio n o f telo m er u reth an e
- (2) L oss o f p o ly m er
o v er tim e
- (3) E x p o su re p erio d
- (4) S kin su rface area
- (5) D erm al tran sfer co efficien t
- (6) B o d y w eig h t
- (7) F o o d surface area
- (8) B io av ailab ility o f the telo m er u reth an e
Also developed probabilistic inputs for key parameters in the analysis:
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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CBI Information has been redacted
25 Nov. 2002
CBI Information has been redacted
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Exposure Assessment Summary
25 Nov. 2002
We have a great deal of confidence in this assessment and the process we are using.
We believe that this information supports our belief that our products are safe for their intended uses.
We are working to develop information with regard to community, ecological and integrated exposure
We are using this process to identify data needs and to focus our research efforts
We welcome your feedback on our initial efforts and your support in helping us to move forward
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25 Nov. 2002
DuPont Environmental Fate & Effects Work Plan
We began with Physical-Chemical Property characterization for Telomer B and Telomer B Alcohol Intermediates
Methods development progress now enables us to begin fate work on products
Environmental Fate & Effects Study Plans : Product Focus
- Physical- Chemical Properties - Environmental Effects :
A cu te D ata, B C F S creen , C h ro m ic F ish E L S
- Environmental Fate
In term ed iate S u rfactan ts P o ly m ers
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25 Nov. 2002
Physical - Chemical Properties : Water Solubility 6-2, 8-2 Telomer B Alcohols & Iodides
12C
Solubility
25C
37C
60C
C 6 F 13C H 2C H 2OH
12 ppm
17 ppm
C8F17CH2CH2OH 130 + 30 ppb 140 + 50 ppb 318 + 176 ppb 225 + 50 ppb
C 6 F 13C H 2C H 2 I
9 ppb
C 8 F 17C H 2C H 2 I
< 10 ppb (LOQ)
p H 3, 7, 9 ; T = 12, 25, 37, 6 0 C in d eio n ized w a ter see n o d ifferen ces in so lu b ility v ersu s p H
T elo m e r Io d id e w a ter so lu b ility v ery low ; h av e d ecid ed n o t to p u rsu e fu rth er testin g and fo cu s on p ro d u cts
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Release, Fate and Effects Compartments
Release to Air
Volatilization ?
Sources
wwtp
Sludge Amendment
Deposition
Natur. Soil Grassland Agric. Soil
Volatilization ?
25 Nov. 2002
Release to Water -----------------------
Landfill
Direct Discharge
a Surface Water _ J ___
Freshwater Sediment
Incineration
Sea
_____ * _____ Estuary & Marine Sediment
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Potential Environmental Routes of Entry
25 Nov. 2002
A ir Soil
Interm ediates Particle adsorbed or
vapor phase?
Surfactants Fugitive em issions
from W W TP?
P o lym ers
Air Deposition Soil - Landfill Land applied sludge
Landfill Land applied sludge
Landfill Land applied sludge
Sedim ent
WWTP Air Deposition direct discharge
WWTP direct discharge
Direct discharge - point source
W ater
W W TP & Septic direct discharge surface presence?
W W TP & Septic direct discharge surface presence?
W W TP & Septic
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25 Nov. 2002
DuPont : Acute Environmental Effects Data Summary
Telo m er A lcohol Interm ediate Telom er Phosphate S u rfa c ta n t T elo m er E thoxylate S u rfa c ta n t Telom er U rethane* Polym er T elo m er A crylate* Polym er
A cute Fish mg/L
96H r LC 50 = 316 fathead minnow
96H r LC 50 > 1,000 rainbow trout
96H r TL50 = 100-140 rainbow trout
96H r LC 50 > 4,000 fathead minnow
96H r LC 50 = 181 fathead minnow
A cute D aphnid
mg/L
48H r E C 50 = 965
A cute A lgae mg/L
72H r E C 50 = 1,000
48H r E C 50 > 1,000
1Q2003
48H r E C 50 = 72
1Q2003
48H r E C 50 = 500-5,000 72H r EC 50 = 870
48Hr EC50 = 234
72Hr EC50 = 36.2
* tested as sales product including hydrocarbon surfactants
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25 Nov. 2002
O bjective: To conduct screening studies evaluating the bioconcentration
potential fluorotelomer-based products in fish
M ethods: Juvenile fathead minnows, flow-through design
Test Substances (consistent F concentration)
- N eg ativ e C o n tro l - P o sitiv e co n tro l : P F O S - S u rfactan ts : T elo m er P h o sp h ate; T elo m er E th o x y late - In term ed iate : T elo m er A lco h o l - P o ly m er : T elo m er U reth an e
Stock concentrations and tissue residues analysis - (total Fluorine)
- U p tak e phase - days 0, 2, 5, 7, 9, 12, 14 - D ep u ratio n phase - days 16, 19, 21, 23, 26 28
In-life complete, data evaluation on-going (complete 1Q2003)
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Telomer Phosphate Aquatic Chronic Fish (ELS) Toxicity Test
25 Nov. 2002
Objective: To determine a chronic LOEC (lowest observed effect concentration) and a chronic NOEC (no observed effect concentration).
Methods: OECD TG 210, OPPTS 850.1400, (90-d trout ELS) Dose response - dilution water and solvent (IPA) controls, 0.63, 1.25, 2.5, 5, and 10 mg/L Telomer Phosphate (a complex mixture) Analytical confirmation of test concentrations Analysis by LC/MS
Start Date : 8 November 2002 Est. Completion Date (in-life): 8 February 2003
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DuPont Fluorotelomer-based Products Environmental Effects Studies Timeline*
25 Nov. 2002
Test Materials 8-2& 6-2 B, BA Multiple Compounds Intermediate, Surfactant and Polymer
Phosphate Surfactant
Ethoxylate Surfactant
Acrylate Polym er
W ork Physical Properties Bioconcentration Factor (BCF) S creen (Fathead Minnow) I
I2002
2003
1Q 2Q 3Q 4Q 1Q 2Q 3Q 4Q
90 Day Fish ELS (GLP) 72Hr Algae (GLP)
90 Day Fish ELS (GLP) 72Hr Algae (GLP) Acute Aquatic Study Set
Work Complete
Work Underway
-
1
Work Planned
* This is a proposed timeline and subject to change.
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E-Fate Studies Approach
25 Nov. 2002
Intermediates
Surfactants
Abiotic Photolysis - Air
Hydrolytic Stability
Photolysis - Water
Adsorption-Desorption
Hydrolysis
Aging / Sequestration
Adsorption-Desorption (Kd)
Aging / Sequestration
Biotic Aerobic : Ready, Inherent Respiration Inhibition
Anaerobic
Aerobic : Ready, Inherent
Polymers Hydrolytic Stability
Respiration Inhibition Aerobic : Ready, Inherent Anaerobic ?
Telomer Research Program 8-2 Telomer B Alcohol
DuPont Focus on Products
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25 Nov. 2002
Telomer-Based Surfactants & Polymers
Abiotic Transformation : Hydrolytic Stability
Surfactants
Phosphate, Ethoxylate
Polymers
Urethane, Acrylate
Reactions in water are one of the most common means of non biological degradation of substances in the environment.
Aqueous stability tests should be performed at environmentally and biologically relevant pH's and temperatures.
- pH 4, 7, 9 @ 50C -p H 1.2 @ 37C Four replicates at 0 and 5 Days
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8-2 Telomer B Alcohol
Biodegradation Studies
"Ready" Biodegradability Screening "Inherent" Accelerated Biodegradability
Screening "Cold" Study material Qualitative Identification & Analysis Enable method development
25 Nov. 2002
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25 Nov. 2002
The sum o f the % values = 100 The m odel predicts this w ill be the distribution o f transform ation products
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25 Nov. 2002
Accelerated Biodegradation Screening A cclim ated M unicipal S ludge : C8F 17C H 2C H 2OH (8-2T B A )
Growth Medium:
E 2-B S M Y E buffer and
m in erals p lu s 20 g /L y east
ex tract as o rg an ic n u trien t.
In cu b ated at room
tem p eratu re (21-25C )
Inoculum source:
M u n icip al P O T W
( I n c u b a t e d f o r 3 d a y s ) *
Conclusion Test material is
transformed with adapted sludge
0I0 160 IS)
140
Study Period : 3 Days
120
100
03 80
n>o 60
o 40
a 20
a U"
0
Medium + 8-2 TBA
Medium + 8-2 TBA +
4 C-Stored Sludge
Medium + 8-2 TBA + Adapted Sludge Culture
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25 Nov. 2002
Modified "R eady" Aerobic Biodegradation Screening with N on-acclim ated M unicipal S lu d g e : C8F 17C H 2C H 2OH
Growth medium:
O E C D 301D m in eral m ed iu m
+ 4 m g /L y e a st ex tract as
o rg an ic n u trien t
Inoculum source:
M u n icip al P O T W , fresh
sludge; n o n -acclim ated
(In cu b ated fo r 0 - 28 days)
Conclusion Test material decreases No significant fluoride
concentration increase
-
800
600
_Q Q_
400
200
0
Study Period : 28 Days
I---- 1---- 1---- r-
Fluoride
o 8-2 TBA
0 5 10 15 20 25
Days After the Initiation
30
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25 Nov. 2002
Accelerated Aerobic/Anaerobic Biodegradation Screening A cclim ate d Industrial S ludge : C8F 17C H 2C H 2OH
0 8-2 TBA + Fresh Sludge 0 CONTROL : 8-2 TBA, Sludge,2 mM NaCN
00
Growth Medium:
E 2 -B S M Y E (1 g /L y e a s t e x tra c t as o rg an ic n u trien t)
Inoculum source:
In d u strial W W T P ; acclim ated (28 days)
Extraction Efficiency (%):
1 1 5 .8 11.0
Conclusion Test material is readily transformed Significant fluoride formation
0 5 10 15 20 25
Days after the initiation
30
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25 Nov. 2002
Under modified "ready biodegradability" conditions, little de fluorination occurred and C8F17CH2COOH appears to be the primary metabolite.
Under modified accelerated conditions, transformation is rapid
-- Primary transformation products observed are :
C8F17CH22COOH C7F15CF=CHCOOH
Mass balance <50%; Other products/losses?
On-going studies to understand controls, incomplete recoveries,
and other transformation products
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25 Nov. 2002
Telomer-based Surfactants & Polymers
Aerobic "Ready" Biodegradation
25 Nov. 2002
Measured End Points: Time course of CO2evolution rate Time course of [F-] increase Total fluorine at the beginning and the end of the experiment Dissolved Organic Carbon (DOC) at zero (0) and 28 days
Prework:
- Total Organic Carbon (TOC) determination on test substance
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DuPont Fluorotelomer-based Products Environmental Fate Studies Timeline*
25 Nov. 2002
Test Materials C8 F17CH2 CH2 OH
Work Respiration Inhibition
"Ready" Biodegradation Screening "Inherent" Biodegradation Screening
Telomer
Hydrolytic Stability
Phosphate Surfactant Respiration Inhibition
Biodegradation Screening
Telomer
Hydrolytic Stability
Ethoxylate Surfactant Respiration Inhibition
Biodegradation Screening
Telomer Urethane
Hydrolytic Stability
Polymer
Respiration Inhibition
Biodegradation Screening
Telomer Acrylate
Hydrolytic Stability
Polymer
Respiration Inhibition
Biodegradation Screening
Work Complete Work Underway * This is a proposed timeline and subject to change.
Work Planned
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Chemical Standards
25 Nov. 2002
To achieve quantitative precision in transformation studies Isotopically - Labeled Standards
- M+5 : C7F1513CF2CD2CD2OH (internal standard) - M+2 : C6F1313CF213COOH
"Cold" Standards - C8F17CH2COOH - C7F15CF=CHCOOH
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25 Nov. 2002
DuPont Fluorotelomer-Based Products
Product Stewardship Summary
We have been proactive and diligent in meeting our commitments to better understand toxicity, environmental fate & effects and exposure.
We are taking a comprehensive approach to understanding exposure.
We are confident that our products are safe for their intended uses.
We have programs in place to learn more about our products: Toxicology, Environmental Fate & Effect, Exposure
We will continue to have an open & frequent dialogue with Regulators, Customers, and Employees
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25 Nov. 2002
Reflections, Discussion, Questions
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