Document RjM151R8yZx3qGd4xQ1aKdejn
AR226-2700
AR226-2700
TORONTO WORKSHOP MATERIALS
Septem ber 13-14,2004
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A n (E-Tate (Perspective
John Gannon DuPont Central Research & Development,
Wilmington, DE
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isiderations for Thou
What is the Source of PFCA's in the Environment?
What is the potential contribution of emissions from direct PFCA Sources?
What is the potential for degradation of the Fluorotelomer-based polymers as an indirect source?
es What is the potential contribution of Fluorotelomer raw material residuals as an indirect source?
Potential PFCA Sources : F(CF2)n COO
1950's - present
Fluoropolymer Manufacture
F(CF2)?COONH4+
7uoropoly*re*' Dispersions
F(CF2)nC O O N H 4 T
Fluoropolymer Manufacture
F(CF2)nCOONH4+ n = 6 -12
APFO Manufacture
1950's - present
ECF AFFF Agents PFCA-based
Indirect Sources
P F C A 's in the
Environment
AX X
X X
AFFF Agents C-6 Telomer-based
19705s - present
I elomer nufacture, Indus & Consumer Use otential Degra
AFFF agents PFOS-based
1 Q 7 rj*3 - p r e s e n t
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PFCA Impurities in
POSF Materials
POSF Materials Potential
Breakdown to PFCA5s
1950 s - present
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Emissions from Point Sources
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Influence of Particle Size Distribution
Particle size categories:
Particle diameter
(Dp):
Dominant Removal M echanism :
Typical residence time:
Coarse mode
D p > 2.5 pm
Gravitational settling
minutes to days
Accumulation mode
< 0.1 urn < D p < 2.5 pm
W et deposition
days to weeks
Aitkens nuclei mode
<0.1 pm
Dry deposition
minutes to days
Wet Deposition
What Happens Next?:
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After material deposited on soil/ in water via gravitational settling / dry deposition: Materials that are volatile or sublime may evaporate back to atmosphere The dominant particle sources (by mass) in air are mineral dust from wind-blown
soils and sea-salt particles from wave-breaking.
r : .>:ypo;3g X-a/i?: Presence of Rain Event
After Material deposited on soil and in water via wet deposition: Water soluble/miscible materials will move with water (e.g., PFCAs) * Water insoluble materials with high adsorption coefficients may adsorb to soil
matrix at or near the surface (e.g., fluorotelomer alcohols (FtOH))
Note: TRP soil adsorption studies showed essentially full recovery of FtOH in test soils and soil pore water, but no FtOH in air traps. Adsorption clearly dominant
Questions: Would FtOH adsorbed to wind-blown soils be: reactive in the atmosphere? deposited in remote locations as wind-blown soil with adsorbed FtOH?
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Hypothesis
Wind-blown soils may:
account for transport of PFCAs and FtOH from surface of soils to the atmosphere.
enhance rate of sublimation for PFCAs from soil surfaces. limit potential for FtOH transformation in atmosphere deposit FtOH in remote locations as wind-blown soil with
adsorbed FtOH.
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-ja -S a lts '. -/t asis
1. PFCAs and FtOH may be deposited in marine boundary layer of ocean and associated with sea-salts.
2. Wave-breaking and winds move sea-salts into atmosphere.
3. PFCAs may enter atmosphere via transport on sea-salts or perhaps evaporate/sublime from marine boundary layer.
4. FtOH may enter atmosphere via transport on sea-salts or volatility, or perhaps it is transformed in marine boundary layer and/or it may be deposited to sediments.
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Interpolated Animation of Global Winds as rom tike NASA SeaWinis Instrument
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Potential Distribution via Oceanic Surface Currents
Currents flow in complex patterns affected by wind, salinity, heat content, bottom topography, and earth's rotation.
Source: Physical Geography .Net
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Warm Current
flohnson Pi
Cold Curent
Grasshopper Effect & Global Fractionation
S t o r e v o l s * l e s*tfts*r*ee
Grasshopper Effect: series of air-surface exchange events following an initial emission-deposition event. involves cycles of evaporation/sublimation to the atmosphere, carried by
winds for a distance, and then wet deposition (i.e., rain, snow events) to land or water. Global Fractionation: differing behaviors of chemicals as transported phys.-chem. prop, influence residence time and hop probability.
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Potential PFCA Sources : F(CF2)n COO
1950's - prese
l-' Sources
Fluoropolymer Manufacture
F(CF2)7COO-NH4+
APFO
Manufacture 1950's - present
/ ECF
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/ AFFF Agents /
/ PFCA-based / / /1960's-70's
Indirect Sources
AFFF Agent C-6 Telomer-based
970's - present
Fluoropolymer Dispersions
F(CF2)nC O O N H 4 +
Fluoropolymer Manufacture
F(CF2)nCOO-NH4+ n = 6 -12
A AFFF agents PFOS-based 1970's - present
PFCA Impurities in
POSF Materials
1950's - 2002
HH1elome
nufacture, Indus & Consumer Use
tial Degra1 PS-
POSF Material Potential
Breakdown t PFCA's
1950's - preset
Are " telomer-Based
ilfitiers Potential Source of PFCAs?
To evaluate Fluorotelomer-based Polymers (FTBP) as a potential contributor, we will need to look at the potential for the FTBP to be degraded.
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Evaluating Degradation Potential o f Ftuoro-TeSomer-Based Polymers (FTBP)
Abiotic Transformation
Hydrolysis * Thermal (incineration Studies) > Photochemical Stability under Industrial & Consumer
Use conditions
Biodegradability: Sewage Treatment Plant
Modified Zahn-Wellens Test per OECD 302B STP Simulation Test per OECD 303A Anaerobic Biodegradability of Organic Compounds in
Digested Sludge per OECD 311
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Evaluating Degradation Potential of Fluoro-Telomer-Based Polymers (FTBP)
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Biodegradability: Soils and Sediments Aerobic and Anaerobic Biodegradation Studies Range of soils and sediments to allow for evaluation of differences in physical-chemical parameters that may influence biodegradability potential. Expected Duration: 1 year Determine Kinetics (if possible)
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Summary
Cannot fully answer questions about PFCA sources in environment and biota without understanding contributions of emissions from all PFCA sources:
Need to develop a global distribution model to evaluate relationship of 50 yrs. of PFCA emissions with presence in environment and biota.
Need to Understand if Fluorotelomer-based Polymers Transform
Potential Distribution Via Air- Global Winds: Circulation Cells and Prevailing Wind Beits
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