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NEW HORIZONS 2008

Consumer Acceptable Surface
Modification and Hard Surface
Cleaners
Hydrophilic or Hydrophobic ?
David R. Scheuing
Mona M. Knock
Colloid and Interface Science Group
Clorox Technical Center
Consumers Want Cleaning Products
that  Are efficacious
 Are convenient to use, saving time and effort – Wipes
 Are pleasant to use – Orange
 Preserve or enhance household surfaces, garments
 Fall within definite price ranges

Therefore
Innovative Surfactants, Polymers, Additives and
Formulations Will Continue to Appear !
981 US patents issued in “Home Cleaning” in 2003
(All US universities =3181, IBM=3457)
Hard Surface Cleaning with RTU Products =
Complex Kinetics
 Spraying/wiping occurs within seconds – No washing bath
 Applicator chemistry – Polymer and surfactant loss onto paper
towels, etc.
 Wiping is high shear environment (>1000 s-1)
 Soils are spatially heterogeneous
 High energy surfaces = glass, porcelain,tiles,aluminum
 Lower energy = appliance/plumbing coatings,PVC
flooring,poly(styrene) and related ABS plastics
 Evaporation of cleaner = evolution of a wide range of
surfactant/oil/water phases
Surface Modification Technology Can Deliver
New Consumer Benefits
 “Stays Cleaner, Longer” = delay formation of soap scum,
hard water spots on sink, shower.
 “Easier Next Time Cleaning” = faster, less effort
 Delivery from a familiar cleaner format
 Trigger sprayer, toilet cleaner liquid, disposable Wipe

 Or a novel format –
 Disposable head/nonwoven with a tool
 Reasonable pricing
Hydrophilic Surface Modification = Approach #1
To Deliver New Benefits
 Adsorb very thin (<100 nm) layers of hydrophilic polymers
during cleaning process
 Polymers that incorporate significant amounts of water
molecules in equilibrium with ambient air  Yield a disordered surface that is Gel-like
Hydrophilic Layers Can Deliver Both –
Hydrophilic Layers Can Deliver Both –
Soil resistance = poor wetting of household surfaces by
Soil resistance = poor wetting of household surfaces by
greases = lower adhesion energy
greases = lower adhesion energy
Soil release = easier cleaning
Soil release = easier cleaning
Deliver Soil Resistance with Hydrophilic
Polymers

γ LA cos θ= (γ SA – γ SL) Young – Dupre’
cos θ= (γ SA – γ SL) / γ LA

cos θ = 0 (at θ =90º)

γ LA = liquid oil/air tension (can measure !)
γ SA = solid/air tension γ SL = solid/liquid tension
γ LA of oil is fixed ! To prevent good wetting of the surface with oil, need to
decrease the difference term
“Polar” polymers raise γ SL- surface “resists” non-polar oil !
“Polar” polymer increases θ, decreasing adhesion

Liquid
Oil

Air
Solid

Air

Liquid
θ Oil
Solid
Improve Soil Release with Polymer/Water
Layers
 Reduce Work of Adhesion Under water –
∆ Wa = γ SO – γ OW – γ SW
 SO = solid/oil OW=oil/water SW=solid/water tensions

γ OW is fixed and large (40 mN/m)
 If γ SW small or vanishes, the energy change is driven by
how large γ SO gets !
 Oil release spontaneous at ∆ Wa = 0 !
Adsorbed polymer layers swollen with liquid water (“gels”)
affect both “controlled” tensions.
Water only “displacement” of oil possible.
Delivery of Polymers from Cleaners –
Challenges
 Bulk sacrificial films not of interest – poor aesthetics
 Polymer must compete with surfactants for surface
sites
 Polymer must not interfere with detergency
 Ideal polymer or mix of polymers will modify glass
and plastic surfaces
 Polymer adsorption onto emulsified oils, particulate
soils, or applicator is a waste
 Price/performance always an issue
Fourier Transform Infrared Spectroscopy Can
Guide Polymer Selection and Formulation
 Attenuated Total Reflectance (ATR) optical rig
 Characterize monolayers, sub-monolayers of surfactants, polymers
– adsorbed directly on internal reflection element (IRE)
 In thin film case (<200 nm) Absorbance ~ layer thickness

 Substrate for adsorption = Ge surface (model polar surface) = the
IRE ! (500 mm2)
 Adsorption time controlled, 5 min typical
 Remove solution, rinse with water
 (2.5 ml/rinse)
Internal Reflection Optics Key To Analysis of Surfaces – Including the
IRE Surface Itself !

IRE
(Ge)

Air

Refractive index = n1=
4.0

θ

Refractive index = n2 = 1.5

n21=n2/n1

Sampling depth, dp= 736
nm at 1650 cm-1

dp = λ/2π (sin2 θ − n21 2 )1/2
Multiple Reflections Aid Sensitivity with
Versatile Horizontal IRE
Ge surface can also
bear thin film of a
plastic polymer, i.e.,
polystyrene

Trough on Horizon rig

Classical multiple IRE

50 mm
Commercial Optics & Chamber Control
Atmosphere Over Adsorbed Layers
Trough – 2.5 ml capacity

Dry Nitrogen/Air
Input
Examples of Copolymers for Hydrophilic
Surface Modification
Dimethylacrylamide co - acrylic acid
DMA – AA

Tristyryl phenol ethoxylate ester of
methacrylic acid co - acrylic (or
methacrylic) acid
“Bigfoot” types

Y

X
O
O

O

OH

O

25

Monitor Amide & Acid Groups in
Spectra of Adsorbed Layers

Monitor EO & Acid Groups in
Spectra of Adsorbed Layers

And – Intense H-O-H stretching and bending bands in
And – Intense H-O-H stretching and bending bands in
FT-IR spectra = Water Uptake Monitoring
FT-IR spectra = Water Uptake Monitoring
DMA co AA stds on Ge from MeOH
Amide

CH3-N

Linear (Amide)

0.14

0.035

ATR spectra
resemble
transmission
spectra when film
thickness << dp.

0.1
0.08

0.03
0.025
0.02

0.06

0.015

0.04

0.01

0.02

0.005

0

0
0

5

10

micrograms applied to IRE

15

Absorbance CH3-N

Absorbance AMide I

0.12
DMA-AA Copolymer Takes Up Water from
Atmosphere At All Layer Thicknesses
DMA co-AA films on Ge IRE - calibration with cast films
.12

13.3 ug, approx 35 nm thickness - ambient air

Absorbance

.1

13.3 ug - under nitrogen purge

.08

.06

0.133 ug stds, approx 0.35 nm
thickness, purge and ambient air

.04

H-O-H
.02

0
4000

3500

3000

2500

Wavenumber (cm-1)

2000

1500

1000
Shifts in Amide I Consistent with Hydration in Air
– Leverage Literature on Proteins for Details
DMA co-AA films on Ge IRE - calibration with cast films

Amide I and H-O-H deform.

Not to same scale

Absorbance

.1

CH3-N

.05

13 ug - 35 nm "thick" film under nitrogen purge

COOH

0

-.05

0.133 ug - 0.35 nm "thin" film under purge
Thick film - ambient air

-.1

Thin film ambient air
1700

1600

1500

1400

1300

Wavenumber (cm-1)

1200

1100

1000

900
Reversible Water Uptake - Blanks vs. minimum DMA
2

co-AA 0.035 ug/cm (0.35 nm thickness)
Amide +Water

H-O-H

0.003
0.0025

Absorbance

0.002
0.0015
0.001
0.0005
0
-0.0005

Purge
blank

In air blank In air blank
immed
5 min

#2 Purge
#2 Purge
blank
blank 5 min

0.035
2

DMA co-AA 3.57 ug/cm on Ge (35.7 nm thickness) - Reversible
Water Uptake
Amide + Water

H-O-H

Purge
2

#2 In
air 5
min

0.16
0.14

Absorbance

0.12
0.1
0.08
0.06
0.04
0.02
0
Purge
In air In air 5
1
immed
min

#2 In
air
immed

Purge
3

#3 In
air
immed

#3 In
air 5
min
DMA co-AA on Ge - Water Uptake at 5 min in Air Effect of Polymer weight - ug/cm 2
H-O-H
0.14

Water uptake increases
with amount of polymer
present. None of these
layers are visible to the
eye !

0.12

Absorbance

0.1
0.08
0.06
0.04
0.02
0
0, blank

0.035

3.57

14.24

49.06
Performance of Hydrophilic Polymer
Layers – FT-IR Also Useful
 Example – Bathroom Cleaning Formulations
 Resistance to build-up of soap scum desired
 Track soap scum formation via several FT-IR protocols
• Multiple Exposure
• Kinetic Exposure
Interactions of Hydrophilic Polymer
Layers with Soaps
 Sodium laurate = model soap


Phase behavior known – “soluble” at ambient temperature
• CMC = 20mM, pH > 8.5, T>23 C
• Forms crystal structures, adsorbed layers, etc. similar
to longer chain analogs

 C14,C16,C18 saturated acids
• Similar phase behavior, solubility, but at higher
temperatures = less convenient

 Oleate (cis 9,11 octadecenoate) soluble at ambient T
Use 1mM NaLaurate exposure to distinguish performance of
different polymers
 Multiple Exposure Protocol –
 Deliver an adsorbed polymer layer or product.
 Expose to NaLaurate 5 min, then vacuum off solution
 Dry under purge 1 min. Record spectrum
 Do four successive exposures.
 Then start rinse study. One “rinse” = fill trough with water, then vacuum off.

 Kinetic Exposure Protocol
 Deliver adsorbed polymer layer
 Fill trough with 1mM NaLaurate. Record spectrum every 2 minutes for 12
minutes
 Vacuum off NaL, record spectrum
 Fill trough with water. Record spectrum every 2 minutes during “desorption”
.8

Solid Na Laurate reference - 20 ul of 100mM solution dried on Ge IRE

COO - asymm

Absorbance

.6

CH2 str. asymm, symm
.4

.2

0
4000

3500

3000

2500

Wavenumber (cm-1)

2000

1500

1000
Solid Na Laurate reference - 20 ul of 100mM solution dried on Ge IRE
COO - asymmetric str

.7

.6

Absorbance

.5

.4

.3

CH2-C=O
CH2 def

COO- symm str

.2

CH2 wagging
.1

1600

1500

1400

1300

Wavenumber (cm-1)

1200

1100

1000
Net Scum Adsorption Depends on
Exposure/Rinse Protocol
Ge IRE Exposed to 1 mM NaLaurate - "Soap Scum" Buildup Test
Run 2 no rinse

Absorbance

.15

Run 2 12x water rinse

.1

Run 2 24x water rinse

.05

Run 1 no rinse
Run 1 12x water rinse
Run 1 24x water rinse

0
4000

3500

3000

2500

Wavenumber (cm-1)

2000

1500

1000
Crystalline Lauric Acid Adsorbs from Dilute
Solutions
Ge IRE Exposed to 1 mM NaLaurate - "Soap Scum" Buildup Test

.1

COO- asymm

Absorbance

.08

COOH
.06

no rinse

Na Laurate dried reference from 100 mM solution "bulk film"
.04

12x rinse

.02

Lauric acid adsorbed from 1 mM NaLaurate solution pH 8.5

CH2 def

C-OH acid
24x rinse
0
1800

1700

1600

1500

1400

1300

Wavenumber (cm-1)

1200

1100

1000

900
Lauric Acid Adsorbs, Then Crystallizes on
Surface – Kinetic Run Spectra, Under Water
1mM NaLaurate pH 7.8 Adsorbing on Ge
All to same scale
Liquid Water subtracted (0-12 min)

Final - dry

.08

12 min

Absorbance

10 min

.06

.04

8 min
6 min

4 min
2 min
0 min

.02

Wavenumber (cm-1)
3000

2950

2900

2850
1mM NaLaurate pH 7.8 Adsorbing on Ge
All to same scale
Liquid Water subtracted (0-12 min)

Final - dry
12 min
10 min

Absorbance

.04

8 min
6 min
.02

4 min
2 min

0 min

0

-.02
1700

1600

1500

1400

Wavenumber (cm-1)

1300

1200

1100
Adsorbed Species Depends on pH
Ge Exposed to 1mM NaLaurate Effect of pH
Dried Layers in Air
Not to same scale

pH 6.5

.1

pH 7.8
pH 8.8

Absorbance

.08

.06

pH 9.8
.04

.02

0

2980

2960

2940

2920

2900

2880

Wavenumber (cm-1)

2860

2840

2820
Laurate Adsorbs Only from high pH
Monomeric Solutions
Ge Exposed to 1mM NaLaurate Effect of pH
Dried Layers in Air
Not to same scale

pH 6.5
pH 7.8

.06

pH 8.8

Absorbance

.04

pH 9.8

.02

0

-.02

Wavenumber (cm-1)
1700

1600

1500

1400

1300

1200

1100

1000

900
Exposure to 1 mM NaLaurate indicates  Lauric acid is adsorbed, not soap, at bulk conc. < cmc and “low” pH
 Consistent with early FT-IR studies of sodium laurate on Ge *
 Net amount of acid adsorbed depends on number of rinses between
exposures
 Real world soiling of surfaces with fatty acids and soaps begins at very
low concentrations during rinsing of basins, showers, and wiping of
countertops.

Soap scum starts with a hydrophobic layer that is too thin to
Soap scum starts with a hydrophobic layer that is too thin to
see.
see.
A mono-layer is all you need to change the nature of the
A mono-layer is all you need to change the nature of the
surface.
surface.
* Takenaka,T. Higashiyama,T. J.Phys.Chem. 1974,78,9
Significant Differences Between Anionic and
Amphoteric Polymers in Scum Prevention
Ge Surface with Polymers Exposed to 1 mM NaLaurate
Rinsing of Lauric Acid as Evaluated by CH2 Band
Control

Control 2

DMA:AA

Amphoteric Copolymer

Absorbance, CH2 Lauric Acid

0.3

0.25

0.2

0.15

0.1

0.05

0
Run
1

Run
2

Run
3

Run 12x
4
rinse

24x

36x

48x

60x

72x

84x

96x
Kinetic Protocol Probes Resistance of DMA
-AA and Others to Lauric Acid Adsorption
Polymers on Ge (0.5%, 5 min ads time) Exposed
to 1mM NaLaurate
No polymer

Polymer Mix A

DMA-AA

Polymer B

Polymer C

Absorbance, CH2 lauric acid

0.12
0.1
0.08
0.06
No Polymer

0.04
DMA-AA

0.02
0
0

2

4

6
time, mins

8

10

12
Polystyrene Surfaces Rendered Hydrophilic via
Adsorbed Layers of “Bigfoot” co – AA Polymers
.007

C-O-C, EO groups
all to same scale
.006

Under Water, Cycles 1,2,3
ps
ps

Absorbance

.005

C=O, ester,acid

.004

.003

ps

.002

Under purge, Cycles 1,2,3
.001

0
1800

1700

1600

1500

1400

1300

1200

1100

1000

Wavenumber (cm-1)

Copolymer layer is unchanged after 40x rinses/3 water immersions. Band
shifts show EO chains are not crystalline and readily hydrate !
Scum Resistance of Polymers on
Polystyrene/Ge Screened Via FT-IR
Polymers on Polystyrene Exposed to 1mM
NaLaurate
Bigfoot copolymer run1

Bigfoot run2

Polymer B

No polymer

Absorbance, CH2 Lauric acid

0.12
0.1
0.08
0.06
0.04
0.02
0
0

2

4

6
Time (min)

8

10

12
Macroscopic Perfomance – Black Acrylic Exposed to Bar
Soap & Hard Water – 5 Cycles

Untreated

Treated

Original Product Contact Time = 90 seconds, Then First Soap Exposure
Macroscopic Perfomance – Black Acrylic Exposed to
Bar Soap & Hard Water – 10 Cycles

Untreated

Treated
Macroscopic Perfomance – Black Acrylic Exposed to Bar
Soap & Hard Water – 15 Cycles

Untreated

Treated
Summary – Hydrophilic Approach
 Adsorbed monolayers of hydrophilic polymers can modify surfaces to
deliver consumer benefits - “Easier Cleaning” and “Stays Cleaner,
Longer”
 Uptake of atmospheric water into adsorbed layers is reversible and
essential to performance
 Control of the interactions of soluble soaps with surfaces needed in
bathroom applications
 Soap – surface interactions can be engineered with appropriate
polymers
 FT-IR is routinely used in evaluation of –
 Amounts of polymer adsorbed and water uptake
 Interaction of the polymer with oils, soaps, etc.
Approach #2 – Hydrophobic/Oleophobic
Modification
 Oleophobic = Deliver Adsorbed Layers of Anionic
Fluorosurfactant/Cationic Polymer Complexes
 Most useful = Reduced adhesion of oily soils

 Hydrophobic = Ordinary Anionic Surfactant/Cationic
Polymer Complexes
 Formulate in a RTU cleaner format
 Surfactant system = Mixed Nonionic/Anionic micelles
 Cationic polymer – Example DADMAC
Stepping Back a Moment - -

 Does everyone agree on what hydrophobic means ??
Surface Modification for Soil-Repellancy:
Defining Success
 High Contact Angle: Oil, Water
 Slide-off (roll-off, low hysteresis): Oil, Water

γL
γS

θ

γSL

air
solid

Young’s equation: γS = γSL + γL cos θ
Contact Angles and Sliding Droplets –
Common Truisms
θ

θ

smaller

Common
advancing / receding
contact angle
measurement

larger

better

wettability

worse

better

adhesiveness

worse

larger

Not always true!

contact angle

surface free energy

smaller
Drop Shape Analysis
 Equilibrium sessile drop contact angles obtained with Krüss
DSA-10L with tilting table feature

Test fluids
•Ultrapure H2O
•Anhydrous C16
For non-pinned
drops:
•Sliding angle, α
•θA and θR

γ

(A)
cing
van
L ad

γ

(R)
ding
e
L rec

θR

θA

α

air
solid
Hysteresis – the basics
Hysteresis: ∆θ = θA – θR for liquid on surface
 Liquid-solid adhesive bond
created during spreading
 Homogeneous smooth surface
may exhibit less hysteresis
 Recession of contact line can
break adhesive bond.

 θR > 0: liquid debonds from
solid; adhesive failure.
 θR ≈ 0: liquid – solid
adhesion > cohesive
strength of liquid; drop
ruptures and leaves a trail
= sheeting

mg sin α

θr

θa

α

mg cos α
mg
More on Hysteresis
 Hysteresis is particularly detrimental to hydrophobic surfaces.
 For minimum surface tilt of α, a droplet of surface tension γLV
with mass, m, and width, w, will spontaneously move:

m g (sin α) / w = γLV (cos θR – cos θA)
 Difference between θA & θR (hysteresis) is more important to
hydrophobicity than the absolute values of the contact angles!
Only water molecules on 3-phase
Only water molecules on 3-phase
contact line must move for drop to
contact line must move for drop to
move.
move.

DROP
TOP
VIEW
Hydrophobicity and Hysteresis
Pinned drops with any θ not very
useful !
Sliding drops are ideal to deliver
real consumer benefits !
Control of the composition and
uniformity of the adsorbed layers is
critical !
Both Fluorosurfactants Soluble @ 1% in Water – AT-1002
Has Fewer, More Hydrophobic Tines than PF 156
 Polyfox PF-156A from Omnova

 Polyfox AT-1002 (experimental)

Thomas, R.R., et. al, Langmuir, 2002, 18, 5933-5938

C-F stretching yields
intense IR
absorbance

Cationic Polymer
= pDADMAC
pDADMAC Binding To Micelles Depends on
Micelle Charge and Electrolyte
Mixed Nonionic/Ionic micelles interacting with a
Polyelectrolyte (opposite charge)
Micelle Charge Defined by “Y”
Y = [Ionic]
[Ionic] + [Nonionic]
A “critical charge” (σ crit) required for polymermicelle binding !!
σcrit ~ κb / q
κ= Debye-Huckel parameter, (nm )
-1

+
+

+

+

+
+

+
+

q = polymer charge spacing
b varies with micelle shape, polymer type
NH4+

Cl-

Mixed Anionic
Fluoro /
Surfonic micelle

Anionic
Fluorinated
Oxetane

+

+
+
+

+
+ +

+
+ +

+

+

+
+

+
+ +
+
+ +
+
+
+ +
+ +
+
Nonionic
Binding of micelles required to form
coacervate and precipitate
 Precipitate = polymer/surfactant phase, solid, no water
 Coacervate = polymer/surfactant – rich phase, with water
 Critical MW/size & near neutral overall charge
 Intrapolymer complexes yield interpolymer complexes
 Complexes reject some water, settle (“bottom” phase)

 Coacervation depends on
 Micelle Charge (“Y”)
 Polymer MW
 Screening” of charges by electrolyte (Debye length)
Critical [Polymer] Needed To Form Large
Complexes for Coacervation
System = p(DADMAC) / Triton X100 / SDS
Coacervate Formed at >
0.01% DADMAC, Aggregates
> 45 nm radius

Complexes But No Coacervates
– Aggregates Too Small !
Intrapolymer Complexes Only
Phase Behavior Variables = [DADMAC] &
Ratio of Anionic/Cationic groups = R
 Systems Made on 20 ml Scale – Rapid/Easy Mixing
 Nonionic = Surfonic L12-8, Constant @ 2 wt% (39 mM)
 Poly(DADMAC) Level Varied  @ Low = 0.3 mM (50 ppm)
 @ High = 3.0 mM (500 ppm)

 Anionic Fluoro-oxetane Varied  Cover R= Anionic/Cationic Equivalents – 0.04 to 8.0
 At low [DADMAC] = [Oxetane] = 0.001 to 0.25 %
 At high [DADMAC] = [Oxetane] = 0.01 to 2.2%
Surface Compositions Assessed With FT-IR

How Does Modification of Surfaces (within 5 minutes)
Depend on Location in Phase Boundary Diagram ?
Poly(DADMAC) Adsorbed on Ge – Adequate
Detection Limit < 0.5 mg/m2
Detection Limit (CH3-N+) < 0.3 mAU
Dried
Reference,
Not to
same scale

Dried, Rinsed
Freely Adsorbed
from 3 mM Solution
Intense Bands Available for Detection of
Fluorinated Oxetanes in Adsorbed Layers
Bands due to Coupled C-F, S-O, C-O-C stretching

C4F9 oxetane
C2F5 oxetane

SDS, hydrated

S-O Asymm.
Stretch
S-O Symm.
Stretch
PF156 (C2F5 chains) Systems Yield
Coacervates but No Precipitates
PF 156/Surfonic Interactions
with 3.0 mM DADMAC
clr

PF 156/Surfonic Interactions
with 3.0 mM DADMAC

2, clr+coacervate

clr

0.5

0.4

0.4
NaCl, M

0.6

0.5

NaCl, M

0.6

2, clr+coacervate

0.3

Net Cationic
Complexes

Net Anionic
Complexes

1

4

0.3

0.2

0.2

0.1

0.1

0

0
0

0.05

0.1

0.15

0.2

0.25

Y, Mole Fraction Anionic in Micelle

0.3

0

2

3

5

6

7

R= Anionic/Cationic Equivalents

8
AT 1002 (C4F9) Systems Show Collision of Precipitate
and Coacervate Regions. How does R Affect Surface
Modification ?
AT 1002/Surfonic
Interactions with 3.0 mM
DADMAC
clr
2, clr+ppt

AT 1002/Surfonic
Interactions with 3.0 mM
DADMAC

2, clr+ coacervate
2, coacervate+ppt

clr
2, clr+ppt

0.4
NaCl, M

0.5

0.4

2, coacervate+ppt

0.6

0.5

NaCl, M

0.6

2, clr+ coacervate

0.3

0.3

0.2

0.2

0.1

0.1

0

0
0

0.1

0.2

Y, Mole Fraction Anionic

0

1

2

3

4

5

6

7

R=Anionic/Cationic Equivalents

8
AT 1002/ 3.0 mM DADMAC – Adsorption Increases Near
Coacervate Boundary For Net Cationic Complexes @ R
< 1, High [Salt], 2-Phase Systems Reduce Adsorption
DADMAC CH3-N

0.008
0.006
0.004
0.002

=0
R .19
=0 3
R .37 0 M
=1 6
.9 0 Na
9 M C
R 70 N l
=4
a
.0 M Cl
R R= 0 Na
=0 8. M C
R .19 0 0 Na l
=0 5 M C
R .39 0 .1 Na l
=0 2 M C
.5 0 . N l
1
R 82 M aC
R =4. 0 .1 Na l
=0 0 M C
R .09 0.1 Na l
=0 9 M C
. 0
N l
R 217 .5 M aC
=
R 0.4 0 .5 Na l
=0 2 M C
.9 0
l
R 89 .5 M NaC
=7 0
.9 .5 Na l
4 M C
0. N l
5
M aC
Na l
C
l

0

R

No Drying Step !

C-F @ 1130

0.01

Absorbance

Adsorption conditions
= 5 minutes’
exposure of Ge IRE,
Then Rinsed 50x with
water

C-F @ 1236
At Low [DADMAC], Coacervate Region Reduced. How
Does Adsorption Change with R?
AT 1002/Surfonic Interactions
with 0.3 mM DADMAC
clr

2, clr + coacervate

AT 1002/Surfonic Interactions
with 0.3 mM DADMAC

2, clr+ppt

clr

0.6

1

2

2, clr+ppt

0.6

0.5

0.5

0.4

0.4
NaCl, M

NaCl, M

2, clr + coacervate

0.3
0.2

0.3
0.2

0.1

0.1

0
0

0.01

0.02

0.03

Y, Mole Fraction Anionic

0
0

3

4

5

6

Equivalents, Anionic/Cationic

7

8
AT1002 at Low [DADMAC] = Maximum Adsorption Near
Boundaries, But High [Salt], Net Anionic Complexes
Inhibit Adsorption
DADMAC CH3-N

C-F 1236

C-F 1136

0.01
0.008
0.006
0.004
0.002
0

R
=0
.
R 40
=0 0
.9 M
N
R 8,
= 7 0 aC
R .86 M N l
=0
a
0
R .40 M Cl
=0 0
N
.9 .1 aC
l
R 4, M
=1 0. N
.7 1 M aC
l
R 0
=0 0. N
.4 1 M aC
R
l
=0 0 0
N
.9 .5 aC
R 8, 0 M N l
=1
.8 .5 M aC
l
6
0. Na
5
M Cl
N
aC
l

Absorbance

Equal
Fluorosurfactant
Adsorption at 1/10
the Level - $$
Surfonic L12-8 is Absent From Adsorbed
Layers
Not to same scale

C-F, S-O
Stretching

Adsorbed Layer Spectra – AT 1002/Surfonic
@ low DADMAC
CH2 Stretching
of CH2-O

Adsorbed
Layer, R=1.70

CH3-N+

Adsorbed
Layer, R=0.94

CH2 Stretching
of Methylenes
in Tail

Reference Spectrum
Surfonic L12-8 Dried on
Ge

C-O-C
Stretching
Oil Repellancy with Sliding Drops is Possible via AT1002 Complexes, but not with Largest Contact Angle !
Contact Angle of Hexadecane in degrees

70
60
50

C16 Theta 0 M NaCl
C16 Theta 0.1 M NaCl
C16 Theta 0.5 M NaCl
C16 Theta(A) 0 M NaCl
C16 Theta(R) 0 M NaCl
C16 Theta(A) 0.1 M NaCl
C16 Theta(R) 0.1 M NaCl
C16 Theta(A) 0.5 M NaCl
C16 Theta(R) 0.5 M NaCl

40
30
20
10
0

0.3 mM pDADMAC

0.0

0.5

3 mM pDADMAC

3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5

[PF1002] in mM
Water Repellancy Possible with PF AT-1002
Complexes, But Many Drops are Pinned !
100

0.3 mM pDADMAC

3 mM pDADMAC

Contact Angle of Water in degrees

90
80
70

W
W
W
W
W
W
W
W
W

60
50
40
30

Theta 0 M NaCl
Theta 0.1 M NaCl
Theta 0.5 M NaCl
Theta(A) 0 M NaCl
Theta(R) 0 M NaCl
Theta(A) 0.1 M NaCl
Theta(R) 0.1 M NaCl
Theta(A) 0.5 M NaCl
Theta(R) 0.5 M NaCl

20
10
0
0.0

0.5

3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5

[PF1002] in mM
Proximity to Coacervate Drives Adsorption –
Factors
+

++

+

+
+

+

PE with bound micelles yield low charge density, thick
layers.

+

+
+ + +
+
+
+ + +
+ +
+
+
+
+ +
+
+
+
+ +
+ +
+
+

++
+

Micelles solubilize PE segments = More loops and tails
of PE = More flexible PE chains
Surf. Monomer - micelle exchange remains fast
Oxetane - DADMAC – Surface becomes hydrophobic =
Significant tail exposure
Adsorbed Layers of PEs Almost Never at Equilibrium
Significant
Lateral
Interactions of
Surfactants

++ ++ +
++
+ +
+
+
+ ++ ++ ++ + - - - - - - - - -

Nonionic
Anionic
surf

Na+

Mixed anionic /nonionic
micelle

Cl-
Conclusions – Hydrophobic Approach
 Complete drop slide-off demonstrates water- and/or oilrepellancy
 High contact angles (~ 90°) do not necessarily confer
repellancy
 Higher complex concentrations produce repellancy at
short adsorption times (5 minutes)
 Salt concentrations > 0.1 M NaCl are detrimental to
repellancy
 PF AT-1002 complexes at 3 mM pDADMAC and 0 – 0.1
M NaCl are able to achieve both water- and oilrepellancy
Conclusions – Hydrophobic Approach
 Control of Complex Size & Composition Critical
 Adsorption Kinetics Important (5 minutes or Hours?)
 Understanding structures formed important – cost$

 Oleophobic Modification Performance Correlates With
Fluorosurfactant Adsorption !
 AT 1002 (C4F9 groups) Far Superior
 Best performers are Compositions Near Coacervate Boundary

 FT-IR Useful for Monitoring Composition of Adsorbed Layers
Final Thoughts
 Hydrophilic Approach May Be Easier
 Depends on Anticipated Soil Types – Beware Soaps !

 Hydrophobic/Oleophobic Modification Possible !
 Understanding of Coacervate Boundaries Helps !
 Adjust Compositions to Avoid Pinning Oil & Water Drops
 Assess Performance via Drop Hysterisis
 “Targeted” Use of Expensive Materials

 Consumer-perceivable benefits from invisible (thin) layers !
 RTU Cleaning Formulations Possible – One Step

 Industrial/Professional Products Possible
 Labor Reduction in Janitorial Products – but Familiar Formats
 Aesthetic Improvements of Surfaces Encountered By Public
Thanks !
 Clorox Management
 Consumer Specialty Products Association
 Mona Knock

You – The Audience &
Consumer !!!

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New Horizons Conference Consumer Specialty Products Association 2008 - Scheuing

  • 1. NEW HORIZONS 2008 Consumer Acceptable Surface Modification and Hard Surface Cleaners Hydrophilic or Hydrophobic ? David R. Scheuing Mona M. Knock Colloid and Interface Science Group Clorox Technical Center
  • 2. Consumers Want Cleaning Products that  Are efficacious  Are convenient to use, saving time and effort – Wipes  Are pleasant to use – Orange  Preserve or enhance household surfaces, garments  Fall within definite price ranges Therefore Innovative Surfactants, Polymers, Additives and Formulations Will Continue to Appear ! 981 US patents issued in “Home Cleaning” in 2003 (All US universities =3181, IBM=3457)
  • 3. Hard Surface Cleaning with RTU Products = Complex Kinetics  Spraying/wiping occurs within seconds – No washing bath  Applicator chemistry – Polymer and surfactant loss onto paper towels, etc.  Wiping is high shear environment (>1000 s-1)  Soils are spatially heterogeneous  High energy surfaces = glass, porcelain,tiles,aluminum  Lower energy = appliance/plumbing coatings,PVC flooring,poly(styrene) and related ABS plastics  Evaporation of cleaner = evolution of a wide range of surfactant/oil/water phases
  • 4. Surface Modification Technology Can Deliver New Consumer Benefits  “Stays Cleaner, Longer” = delay formation of soap scum, hard water spots on sink, shower.  “Easier Next Time Cleaning” = faster, less effort  Delivery from a familiar cleaner format  Trigger sprayer, toilet cleaner liquid, disposable Wipe  Or a novel format –  Disposable head/nonwoven with a tool  Reasonable pricing
  • 5. Hydrophilic Surface Modification = Approach #1 To Deliver New Benefits  Adsorb very thin (<100 nm) layers of hydrophilic polymers during cleaning process  Polymers that incorporate significant amounts of water molecules in equilibrium with ambient air  Yield a disordered surface that is Gel-like Hydrophilic Layers Can Deliver Both – Hydrophilic Layers Can Deliver Both – Soil resistance = poor wetting of household surfaces by Soil resistance = poor wetting of household surfaces by greases = lower adhesion energy greases = lower adhesion energy Soil release = easier cleaning Soil release = easier cleaning
  • 6. Deliver Soil Resistance with Hydrophilic Polymers γ LA cos θ= (γ SA – γ SL) Young – Dupre’ cos θ= (γ SA – γ SL) / γ LA cos θ = 0 (at θ =90º) γ LA = liquid oil/air tension (can measure !) γ SA = solid/air tension γ SL = solid/liquid tension γ LA of oil is fixed ! To prevent good wetting of the surface with oil, need to decrease the difference term “Polar” polymers raise γ SL- surface “resists” non-polar oil ! “Polar” polymer increases θ, decreasing adhesion Liquid Oil Air Solid Air Liquid θ Oil Solid
  • 7. Improve Soil Release with Polymer/Water Layers  Reduce Work of Adhesion Under water – ∆ Wa = γ SO – γ OW – γ SW  SO = solid/oil OW=oil/water SW=solid/water tensions γ OW is fixed and large (40 mN/m)  If γ SW small or vanishes, the energy change is driven by how large γ SO gets !  Oil release spontaneous at ∆ Wa = 0 ! Adsorbed polymer layers swollen with liquid water (“gels”) affect both “controlled” tensions. Water only “displacement” of oil possible.
  • 8. Delivery of Polymers from Cleaners – Challenges  Bulk sacrificial films not of interest – poor aesthetics  Polymer must compete with surfactants for surface sites  Polymer must not interfere with detergency  Ideal polymer or mix of polymers will modify glass and plastic surfaces  Polymer adsorption onto emulsified oils, particulate soils, or applicator is a waste  Price/performance always an issue
  • 9. Fourier Transform Infrared Spectroscopy Can Guide Polymer Selection and Formulation  Attenuated Total Reflectance (ATR) optical rig  Characterize monolayers, sub-monolayers of surfactants, polymers – adsorbed directly on internal reflection element (IRE)  In thin film case (<200 nm) Absorbance ~ layer thickness  Substrate for adsorption = Ge surface (model polar surface) = the IRE ! (500 mm2)  Adsorption time controlled, 5 min typical  Remove solution, rinse with water  (2.5 ml/rinse)
  • 10. Internal Reflection Optics Key To Analysis of Surfaces – Including the IRE Surface Itself ! IRE (Ge) Air Refractive index = n1= 4.0 θ Refractive index = n2 = 1.5 n21=n2/n1 Sampling depth, dp= 736 nm at 1650 cm-1 dp = λ/2π (sin2 θ − n21 2 )1/2
  • 11. Multiple Reflections Aid Sensitivity with Versatile Horizontal IRE Ge surface can also bear thin film of a plastic polymer, i.e., polystyrene Trough on Horizon rig Classical multiple IRE 50 mm
  • 12. Commercial Optics & Chamber Control Atmosphere Over Adsorbed Layers Trough – 2.5 ml capacity Dry Nitrogen/Air Input
  • 13. Examples of Copolymers for Hydrophilic Surface Modification Dimethylacrylamide co - acrylic acid DMA – AA Tristyryl phenol ethoxylate ester of methacrylic acid co - acrylic (or methacrylic) acid “Bigfoot” types Y X O O O OH O 25 Monitor Amide & Acid Groups in Spectra of Adsorbed Layers Monitor EO & Acid Groups in Spectra of Adsorbed Layers And – Intense H-O-H stretching and bending bands in And – Intense H-O-H stretching and bending bands in FT-IR spectra = Water Uptake Monitoring FT-IR spectra = Water Uptake Monitoring
  • 14. DMA co AA stds on Ge from MeOH Amide CH3-N Linear (Amide) 0.14 0.035 ATR spectra resemble transmission spectra when film thickness << dp. 0.1 0.08 0.03 0.025 0.02 0.06 0.015 0.04 0.01 0.02 0.005 0 0 0 5 10 micrograms applied to IRE 15 Absorbance CH3-N Absorbance AMide I 0.12
  • 15. DMA-AA Copolymer Takes Up Water from Atmosphere At All Layer Thicknesses DMA co-AA films on Ge IRE - calibration with cast films .12 13.3 ug, approx 35 nm thickness - ambient air Absorbance .1 13.3 ug - under nitrogen purge .08 .06 0.133 ug stds, approx 0.35 nm thickness, purge and ambient air .04 H-O-H .02 0 4000 3500 3000 2500 Wavenumber (cm-1) 2000 1500 1000
  • 16. Shifts in Amide I Consistent with Hydration in Air – Leverage Literature on Proteins for Details DMA co-AA films on Ge IRE - calibration with cast films Amide I and H-O-H deform. Not to same scale Absorbance .1 CH3-N .05 13 ug - 35 nm "thick" film under nitrogen purge COOH 0 -.05 0.133 ug - 0.35 nm "thin" film under purge Thick film - ambient air -.1 Thin film ambient air 1700 1600 1500 1400 1300 Wavenumber (cm-1) 1200 1100 1000 900
  • 17. Reversible Water Uptake - Blanks vs. minimum DMA 2 co-AA 0.035 ug/cm (0.35 nm thickness) Amide +Water H-O-H 0.003 0.0025 Absorbance 0.002 0.0015 0.001 0.0005 0 -0.0005 Purge blank In air blank In air blank immed 5 min #2 Purge #2 Purge blank blank 5 min 0.035
  • 18. 2 DMA co-AA 3.57 ug/cm on Ge (35.7 nm thickness) - Reversible Water Uptake Amide + Water H-O-H Purge 2 #2 In air 5 min 0.16 0.14 Absorbance 0.12 0.1 0.08 0.06 0.04 0.02 0 Purge In air In air 5 1 immed min #2 In air immed Purge 3 #3 In air immed #3 In air 5 min
  • 19. DMA co-AA on Ge - Water Uptake at 5 min in Air Effect of Polymer weight - ug/cm 2 H-O-H 0.14 Water uptake increases with amount of polymer present. None of these layers are visible to the eye ! 0.12 Absorbance 0.1 0.08 0.06 0.04 0.02 0 0, blank 0.035 3.57 14.24 49.06
  • 20. Performance of Hydrophilic Polymer Layers – FT-IR Also Useful  Example – Bathroom Cleaning Formulations  Resistance to build-up of soap scum desired  Track soap scum formation via several FT-IR protocols • Multiple Exposure • Kinetic Exposure
  • 21. Interactions of Hydrophilic Polymer Layers with Soaps  Sodium laurate = model soap  Phase behavior known – “soluble” at ambient temperature • CMC = 20mM, pH > 8.5, T>23 C • Forms crystal structures, adsorbed layers, etc. similar to longer chain analogs  C14,C16,C18 saturated acids • Similar phase behavior, solubility, but at higher temperatures = less convenient  Oleate (cis 9,11 octadecenoate) soluble at ambient T
  • 22. Use 1mM NaLaurate exposure to distinguish performance of different polymers  Multiple Exposure Protocol –  Deliver an adsorbed polymer layer or product.  Expose to NaLaurate 5 min, then vacuum off solution  Dry under purge 1 min. Record spectrum  Do four successive exposures.  Then start rinse study. One “rinse” = fill trough with water, then vacuum off.  Kinetic Exposure Protocol  Deliver adsorbed polymer layer  Fill trough with 1mM NaLaurate. Record spectrum every 2 minutes for 12 minutes  Vacuum off NaL, record spectrum  Fill trough with water. Record spectrum every 2 minutes during “desorption”
  • 23. .8 Solid Na Laurate reference - 20 ul of 100mM solution dried on Ge IRE COO - asymm Absorbance .6 CH2 str. asymm, symm .4 .2 0 4000 3500 3000 2500 Wavenumber (cm-1) 2000 1500 1000
  • 24. Solid Na Laurate reference - 20 ul of 100mM solution dried on Ge IRE COO - asymmetric str .7 .6 Absorbance .5 .4 .3 CH2-C=O CH2 def COO- symm str .2 CH2 wagging .1 1600 1500 1400 1300 Wavenumber (cm-1) 1200 1100 1000
  • 25. Net Scum Adsorption Depends on Exposure/Rinse Protocol Ge IRE Exposed to 1 mM NaLaurate - "Soap Scum" Buildup Test Run 2 no rinse Absorbance .15 Run 2 12x water rinse .1 Run 2 24x water rinse .05 Run 1 no rinse Run 1 12x water rinse Run 1 24x water rinse 0 4000 3500 3000 2500 Wavenumber (cm-1) 2000 1500 1000
  • 26. Crystalline Lauric Acid Adsorbs from Dilute Solutions Ge IRE Exposed to 1 mM NaLaurate - "Soap Scum" Buildup Test .1 COO- asymm Absorbance .08 COOH .06 no rinse Na Laurate dried reference from 100 mM solution "bulk film" .04 12x rinse .02 Lauric acid adsorbed from 1 mM NaLaurate solution pH 8.5 CH2 def C-OH acid 24x rinse 0 1800 1700 1600 1500 1400 1300 Wavenumber (cm-1) 1200 1100 1000 900
  • 27. Lauric Acid Adsorbs, Then Crystallizes on Surface – Kinetic Run Spectra, Under Water 1mM NaLaurate pH 7.8 Adsorbing on Ge All to same scale Liquid Water subtracted (0-12 min) Final - dry .08 12 min Absorbance 10 min .06 .04 8 min 6 min 4 min 2 min 0 min .02 Wavenumber (cm-1) 3000 2950 2900 2850
  • 28. 1mM NaLaurate pH 7.8 Adsorbing on Ge All to same scale Liquid Water subtracted (0-12 min) Final - dry 12 min 10 min Absorbance .04 8 min 6 min .02 4 min 2 min 0 min 0 -.02 1700 1600 1500 1400 Wavenumber (cm-1) 1300 1200 1100
  • 29. Adsorbed Species Depends on pH Ge Exposed to 1mM NaLaurate Effect of pH Dried Layers in Air Not to same scale pH 6.5 .1 pH 7.8 pH 8.8 Absorbance .08 .06 pH 9.8 .04 .02 0 2980 2960 2940 2920 2900 2880 Wavenumber (cm-1) 2860 2840 2820
  • 30. Laurate Adsorbs Only from high pH Monomeric Solutions Ge Exposed to 1mM NaLaurate Effect of pH Dried Layers in Air Not to same scale pH 6.5 pH 7.8 .06 pH 8.8 Absorbance .04 pH 9.8 .02 0 -.02 Wavenumber (cm-1) 1700 1600 1500 1400 1300 1200 1100 1000 900
  • 31. Exposure to 1 mM NaLaurate indicates  Lauric acid is adsorbed, not soap, at bulk conc. < cmc and “low” pH  Consistent with early FT-IR studies of sodium laurate on Ge *  Net amount of acid adsorbed depends on number of rinses between exposures  Real world soiling of surfaces with fatty acids and soaps begins at very low concentrations during rinsing of basins, showers, and wiping of countertops. Soap scum starts with a hydrophobic layer that is too thin to Soap scum starts with a hydrophobic layer that is too thin to see. see. A mono-layer is all you need to change the nature of the A mono-layer is all you need to change the nature of the surface. surface. * Takenaka,T. Higashiyama,T. J.Phys.Chem. 1974,78,9
  • 32. Significant Differences Between Anionic and Amphoteric Polymers in Scum Prevention Ge Surface with Polymers Exposed to 1 mM NaLaurate Rinsing of Lauric Acid as Evaluated by CH2 Band Control Control 2 DMA:AA Amphoteric Copolymer Absorbance, CH2 Lauric Acid 0.3 0.25 0.2 0.15 0.1 0.05 0 Run 1 Run 2 Run 3 Run 12x 4 rinse 24x 36x 48x 60x 72x 84x 96x
  • 33. Kinetic Protocol Probes Resistance of DMA -AA and Others to Lauric Acid Adsorption Polymers on Ge (0.5%, 5 min ads time) Exposed to 1mM NaLaurate No polymer Polymer Mix A DMA-AA Polymer B Polymer C Absorbance, CH2 lauric acid 0.12 0.1 0.08 0.06 No Polymer 0.04 DMA-AA 0.02 0 0 2 4 6 time, mins 8 10 12
  • 34. Polystyrene Surfaces Rendered Hydrophilic via Adsorbed Layers of “Bigfoot” co – AA Polymers .007 C-O-C, EO groups all to same scale .006 Under Water, Cycles 1,2,3 ps ps Absorbance .005 C=O, ester,acid .004 .003 ps .002 Under purge, Cycles 1,2,3 .001 0 1800 1700 1600 1500 1400 1300 1200 1100 1000 Wavenumber (cm-1) Copolymer layer is unchanged after 40x rinses/3 water immersions. Band shifts show EO chains are not crystalline and readily hydrate !
  • 35. Scum Resistance of Polymers on Polystyrene/Ge Screened Via FT-IR Polymers on Polystyrene Exposed to 1mM NaLaurate Bigfoot copolymer run1 Bigfoot run2 Polymer B No polymer Absorbance, CH2 Lauric acid 0.12 0.1 0.08 0.06 0.04 0.02 0 0 2 4 6 Time (min) 8 10 12
  • 36. Macroscopic Perfomance – Black Acrylic Exposed to Bar Soap & Hard Water – 5 Cycles Untreated Treated Original Product Contact Time = 90 seconds, Then First Soap Exposure
  • 37. Macroscopic Perfomance – Black Acrylic Exposed to Bar Soap & Hard Water – 10 Cycles Untreated Treated
  • 38. Macroscopic Perfomance – Black Acrylic Exposed to Bar Soap & Hard Water – 15 Cycles Untreated Treated
  • 39. Summary – Hydrophilic Approach  Adsorbed monolayers of hydrophilic polymers can modify surfaces to deliver consumer benefits - “Easier Cleaning” and “Stays Cleaner, Longer”  Uptake of atmospheric water into adsorbed layers is reversible and essential to performance  Control of the interactions of soluble soaps with surfaces needed in bathroom applications  Soap – surface interactions can be engineered with appropriate polymers  FT-IR is routinely used in evaluation of –  Amounts of polymer adsorbed and water uptake  Interaction of the polymer with oils, soaps, etc.
  • 40. Approach #2 – Hydrophobic/Oleophobic Modification  Oleophobic = Deliver Adsorbed Layers of Anionic Fluorosurfactant/Cationic Polymer Complexes  Most useful = Reduced adhesion of oily soils  Hydrophobic = Ordinary Anionic Surfactant/Cationic Polymer Complexes  Formulate in a RTU cleaner format  Surfactant system = Mixed Nonionic/Anionic micelles  Cationic polymer – Example DADMAC
  • 41. Stepping Back a Moment - -  Does everyone agree on what hydrophobic means ??
  • 42. Surface Modification for Soil-Repellancy: Defining Success  High Contact Angle: Oil, Water  Slide-off (roll-off, low hysteresis): Oil, Water γL γS θ γSL air solid Young’s equation: γS = γSL + γL cos θ
  • 43. Contact Angles and Sliding Droplets – Common Truisms θ θ smaller Common advancing / receding contact angle measurement larger better wettability worse better adhesiveness worse larger Not always true! contact angle surface free energy smaller
  • 44. Drop Shape Analysis  Equilibrium sessile drop contact angles obtained with Krüss DSA-10L with tilting table feature Test fluids •Ultrapure H2O •Anhydrous C16 For non-pinned drops: •Sliding angle, α •θA and θR γ (A) cing van L ad γ (R) ding e L rec θR θA α air solid
  • 45. Hysteresis – the basics Hysteresis: ∆θ = θA – θR for liquid on surface  Liquid-solid adhesive bond created during spreading  Homogeneous smooth surface may exhibit less hysteresis  Recession of contact line can break adhesive bond.  θR > 0: liquid debonds from solid; adhesive failure.  θR ≈ 0: liquid – solid adhesion > cohesive strength of liquid; drop ruptures and leaves a trail = sheeting mg sin α θr θa α mg cos α mg
  • 46. More on Hysteresis  Hysteresis is particularly detrimental to hydrophobic surfaces.  For minimum surface tilt of α, a droplet of surface tension γLV with mass, m, and width, w, will spontaneously move: m g (sin α) / w = γLV (cos θR – cos θA)  Difference between θA & θR (hysteresis) is more important to hydrophobicity than the absolute values of the contact angles! Only water molecules on 3-phase Only water molecules on 3-phase contact line must move for drop to contact line must move for drop to move. move. DROP TOP VIEW
  • 47. Hydrophobicity and Hysteresis Pinned drops with any θ not very useful ! Sliding drops are ideal to deliver real consumer benefits ! Control of the composition and uniformity of the adsorbed layers is critical !
  • 48. Both Fluorosurfactants Soluble @ 1% in Water – AT-1002 Has Fewer, More Hydrophobic Tines than PF 156  Polyfox PF-156A from Omnova  Polyfox AT-1002 (experimental) Thomas, R.R., et. al, Langmuir, 2002, 18, 5933-5938 C-F stretching yields intense IR absorbance Cationic Polymer = pDADMAC
  • 49. pDADMAC Binding To Micelles Depends on Micelle Charge and Electrolyte Mixed Nonionic/Ionic micelles interacting with a Polyelectrolyte (opposite charge) Micelle Charge Defined by “Y” Y = [Ionic] [Ionic] + [Nonionic] A “critical charge” (σ crit) required for polymermicelle binding !! σcrit ~ κb / q κ= Debye-Huckel parameter, (nm ) -1 + + + + + + + + q = polymer charge spacing b varies with micelle shape, polymer type NH4+ Cl- Mixed Anionic Fluoro / Surfonic micelle Anionic Fluorinated Oxetane + + + + + + + + + + + + + + + + + + + + + + + + + + + Nonionic
  • 50. Binding of micelles required to form coacervate and precipitate  Precipitate = polymer/surfactant phase, solid, no water  Coacervate = polymer/surfactant – rich phase, with water  Critical MW/size & near neutral overall charge  Intrapolymer complexes yield interpolymer complexes  Complexes reject some water, settle (“bottom” phase)  Coacervation depends on  Micelle Charge (“Y”)  Polymer MW  Screening” of charges by electrolyte (Debye length)
  • 51. Critical [Polymer] Needed To Form Large Complexes for Coacervation System = p(DADMAC) / Triton X100 / SDS Coacervate Formed at > 0.01% DADMAC, Aggregates > 45 nm radius Complexes But No Coacervates – Aggregates Too Small ! Intrapolymer Complexes Only
  • 52. Phase Behavior Variables = [DADMAC] & Ratio of Anionic/Cationic groups = R  Systems Made on 20 ml Scale – Rapid/Easy Mixing  Nonionic = Surfonic L12-8, Constant @ 2 wt% (39 mM)  Poly(DADMAC) Level Varied  @ Low = 0.3 mM (50 ppm)  @ High = 3.0 mM (500 ppm)  Anionic Fluoro-oxetane Varied  Cover R= Anionic/Cationic Equivalents – 0.04 to 8.0  At low [DADMAC] = [Oxetane] = 0.001 to 0.25 %  At high [DADMAC] = [Oxetane] = 0.01 to 2.2%
  • 53. Surface Compositions Assessed With FT-IR How Does Modification of Surfaces (within 5 minutes) Depend on Location in Phase Boundary Diagram ?
  • 54. Poly(DADMAC) Adsorbed on Ge – Adequate Detection Limit < 0.5 mg/m2 Detection Limit (CH3-N+) < 0.3 mAU Dried Reference, Not to same scale Dried, Rinsed Freely Adsorbed from 3 mM Solution
  • 55. Intense Bands Available for Detection of Fluorinated Oxetanes in Adsorbed Layers Bands due to Coupled C-F, S-O, C-O-C stretching C4F9 oxetane C2F5 oxetane SDS, hydrated S-O Asymm. Stretch S-O Symm. Stretch
  • 56. PF156 (C2F5 chains) Systems Yield Coacervates but No Precipitates PF 156/Surfonic Interactions with 3.0 mM DADMAC clr PF 156/Surfonic Interactions with 3.0 mM DADMAC 2, clr+coacervate clr 0.5 0.4 0.4 NaCl, M 0.6 0.5 NaCl, M 0.6 2, clr+coacervate 0.3 Net Cationic Complexes Net Anionic Complexes 1 4 0.3 0.2 0.2 0.1 0.1 0 0 0 0.05 0.1 0.15 0.2 0.25 Y, Mole Fraction Anionic in Micelle 0.3 0 2 3 5 6 7 R= Anionic/Cationic Equivalents 8
  • 57. AT 1002 (C4F9) Systems Show Collision of Precipitate and Coacervate Regions. How does R Affect Surface Modification ? AT 1002/Surfonic Interactions with 3.0 mM DADMAC clr 2, clr+ppt AT 1002/Surfonic Interactions with 3.0 mM DADMAC 2, clr+ coacervate 2, coacervate+ppt clr 2, clr+ppt 0.4 NaCl, M 0.5 0.4 2, coacervate+ppt 0.6 0.5 NaCl, M 0.6 2, clr+ coacervate 0.3 0.3 0.2 0.2 0.1 0.1 0 0 0 0.1 0.2 Y, Mole Fraction Anionic 0 1 2 3 4 5 6 7 R=Anionic/Cationic Equivalents 8
  • 58. AT 1002/ 3.0 mM DADMAC – Adsorption Increases Near Coacervate Boundary For Net Cationic Complexes @ R < 1, High [Salt], 2-Phase Systems Reduce Adsorption DADMAC CH3-N 0.008 0.006 0.004 0.002 =0 R .19 =0 3 R .37 0 M =1 6 .9 0 Na 9 M C R 70 N l =4 a .0 M Cl R R= 0 Na =0 8. M C R .19 0 0 Na l =0 5 M C R .39 0 .1 Na l =0 2 M C .5 0 . N l 1 R 82 M aC R =4. 0 .1 Na l =0 0 M C R .09 0.1 Na l =0 9 M C . 0 N l R 217 .5 M aC = R 0.4 0 .5 Na l =0 2 M C .9 0 l R 89 .5 M NaC =7 0 .9 .5 Na l 4 M C 0. N l 5 M aC Na l C l 0 R No Drying Step ! C-F @ 1130 0.01 Absorbance Adsorption conditions = 5 minutes’ exposure of Ge IRE, Then Rinsed 50x with water C-F @ 1236
  • 59. At Low [DADMAC], Coacervate Region Reduced. How Does Adsorption Change with R? AT 1002/Surfonic Interactions with 0.3 mM DADMAC clr 2, clr + coacervate AT 1002/Surfonic Interactions with 0.3 mM DADMAC 2, clr+ppt clr 0.6 1 2 2, clr+ppt 0.6 0.5 0.5 0.4 0.4 NaCl, M NaCl, M 2, clr + coacervate 0.3 0.2 0.3 0.2 0.1 0.1 0 0 0.01 0.02 0.03 Y, Mole Fraction Anionic 0 0 3 4 5 6 Equivalents, Anionic/Cationic 7 8
  • 60. AT1002 at Low [DADMAC] = Maximum Adsorption Near Boundaries, But High [Salt], Net Anionic Complexes Inhibit Adsorption DADMAC CH3-N C-F 1236 C-F 1136 0.01 0.008 0.006 0.004 0.002 0 R =0 . R 40 =0 0 .9 M N R 8, = 7 0 aC R .86 M N l =0 a 0 R .40 M Cl =0 0 N .9 .1 aC l R 4, M =1 0. N .7 1 M aC l R 0 =0 0. N .4 1 M aC R l =0 0 0 N .9 .5 aC R 8, 0 M N l =1 .8 .5 M aC l 6 0. Na 5 M Cl N aC l Absorbance Equal Fluorosurfactant Adsorption at 1/10 the Level - $$
  • 61. Surfonic L12-8 is Absent From Adsorbed Layers Not to same scale C-F, S-O Stretching Adsorbed Layer Spectra – AT 1002/Surfonic @ low DADMAC CH2 Stretching of CH2-O Adsorbed Layer, R=1.70 CH3-N+ Adsorbed Layer, R=0.94 CH2 Stretching of Methylenes in Tail Reference Spectrum Surfonic L12-8 Dried on Ge C-O-C Stretching
  • 62. Oil Repellancy with Sliding Drops is Possible via AT1002 Complexes, but not with Largest Contact Angle ! Contact Angle of Hexadecane in degrees 70 60 50 C16 Theta 0 M NaCl C16 Theta 0.1 M NaCl C16 Theta 0.5 M NaCl C16 Theta(A) 0 M NaCl C16 Theta(R) 0 M NaCl C16 Theta(A) 0.1 M NaCl C16 Theta(R) 0.1 M NaCl C16 Theta(A) 0.5 M NaCl C16 Theta(R) 0.5 M NaCl 40 30 20 10 0 0.3 mM pDADMAC 0.0 0.5 3 mM pDADMAC 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 [PF1002] in mM
  • 63. Water Repellancy Possible with PF AT-1002 Complexes, But Many Drops are Pinned ! 100 0.3 mM pDADMAC 3 mM pDADMAC Contact Angle of Water in degrees 90 80 70 W W W W W W W W W 60 50 40 30 Theta 0 M NaCl Theta 0.1 M NaCl Theta 0.5 M NaCl Theta(A) 0 M NaCl Theta(R) 0 M NaCl Theta(A) 0.1 M NaCl Theta(R) 0.1 M NaCl Theta(A) 0.5 M NaCl Theta(R) 0.5 M NaCl 20 10 0 0.0 0.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 [PF1002] in mM
  • 64. Proximity to Coacervate Drives Adsorption – Factors + ++ + + + + PE with bound micelles yield low charge density, thick layers. + + + + + + + + + + + + + + + + + + + + + + + + + + ++ + Micelles solubilize PE segments = More loops and tails of PE = More flexible PE chains Surf. Monomer - micelle exchange remains fast Oxetane - DADMAC – Surface becomes hydrophobic = Significant tail exposure Adsorbed Layers of PEs Almost Never at Equilibrium Significant Lateral Interactions of Surfactants ++ ++ + ++ + + + + + ++ ++ ++ + - - - - - - - - - Nonionic Anionic surf Na+ Mixed anionic /nonionic micelle Cl-
  • 65. Conclusions – Hydrophobic Approach  Complete drop slide-off demonstrates water- and/or oilrepellancy  High contact angles (~ 90°) do not necessarily confer repellancy  Higher complex concentrations produce repellancy at short adsorption times (5 minutes)  Salt concentrations > 0.1 M NaCl are detrimental to repellancy  PF AT-1002 complexes at 3 mM pDADMAC and 0 – 0.1 M NaCl are able to achieve both water- and oilrepellancy
  • 66. Conclusions – Hydrophobic Approach  Control of Complex Size & Composition Critical  Adsorption Kinetics Important (5 minutes or Hours?)  Understanding structures formed important – cost$  Oleophobic Modification Performance Correlates With Fluorosurfactant Adsorption !  AT 1002 (C4F9 groups) Far Superior  Best performers are Compositions Near Coacervate Boundary  FT-IR Useful for Monitoring Composition of Adsorbed Layers
  • 67. Final Thoughts  Hydrophilic Approach May Be Easier  Depends on Anticipated Soil Types – Beware Soaps !  Hydrophobic/Oleophobic Modification Possible !  Understanding of Coacervate Boundaries Helps !  Adjust Compositions to Avoid Pinning Oil & Water Drops  Assess Performance via Drop Hysterisis  “Targeted” Use of Expensive Materials  Consumer-perceivable benefits from invisible (thin) layers !  RTU Cleaning Formulations Possible – One Step  Industrial/Professional Products Possible  Labor Reduction in Janitorial Products – but Familiar Formats  Aesthetic Improvements of Surfaces Encountered By Public
  • 68. Thanks !  Clorox Management  Consumer Specialty Products Association  Mona Knock You – The Audience & Consumer !!!