Subscriber access provided by UNIV OF NEBRASKA - LINCOLN
Article
The Contribution of Nano- to Micro-scale Roughness to Heterogeneity: Closing the Gap between Unfavorable and Favorable Colloid Attachment Conditions Anna Rasmuson, Eddy Pazmino, Shoeleh Assemi, and William P. Johnson Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.6b05911 • Publication Date (Web): 30 Jan 2017 Downloaded from http://pubs.acs.org on February 5, 2017
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Environmental Science & Technology is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 40
Environmental Science & Technology
1
The Contribution of Nano- to Micro-scale Roughness to Heterogeneity:
2
Closing the Gap between
3
Unfavorable and Favorable Colloid Attachment Conditions
4
Anna Rasmuson1, Eddy Pazmino2, Shoeleh Assemi3, William P. Johnson1,*
5 6 7
1
8
Department of Geology and Geophysics, University of Utah,
9
Salt Lake City, Utah 84112, United States 2
10
Department of Extractive Metallurgy, Escuela Politécnica Nacional, Quito, Ecuador 3
11
Department of Metallurgical Engineering, University of Utah, Salt Lake City, Utah 84112, United States
12 13 14 15 16 17 18
*
Corresponding author. Email:
[email protected]; Tel: (801)585-5033; Fax: (801)5817065.Engineering, University of Utah, Salt Lake City, Utah 84112, United States 1
ACS Paragon Plus Environment
Environmental Science & Technology
19
TOC/Abstract Art
20
2 ACS Paragon Plus Environment
Page 2 of 40
Page 3 of 40
Environmental Science & Technology
21
Abstract
22
Surface roughness has been reported to both increase as well as decrease colloid retention. In
23
order to better understand the boundaries within which roughness operates, attachment of a
24
range of colloid sizes to glass with three levels of roughness was examined under both
25
favorable (energy barrier absent) and unfavorable (energy barrier present) conditions in an
26
impinging jet system. Smooth glass was found to provide the upper and lower bounds for
27
attachment under favorable and unfavorable conditions, respectively. Surface roughness
28
decreased, or even eliminated, the gap between favorable and unfavorable attachment, and
29
did so by two mechanisms: 1) under favorable conditions attachment decreased via increased
30
hydrodynamic slip length and reduced attraction ; 2) under unfavorable conditions attachment
31
increased via reduced colloid-collector repulsion (reduced radius of curvature) and increased
32
attraction (multiple points of contact, and possibly increased surface charge heterogeneity).
33
Absence of a gap where these forces most strongly operate for smaller (< 200 nm) and larger (>
34
2 µm) colloids was observed and discussed. These observations elucidate the role of roughness
35
in colloid attachment under both favorable and unfavorable conditions.
3 ACS Paragon Plus Environment
Environmental Science & Technology
36
Introduction
37
Significant progress has been made in understanding the nature of nanoscale heterogeneity
38
responsible for colloid attachment to bulk repulsive surfaces. 1-4 Colloid-collector repulsion in
39
the environment often arises from like-charged colloids and collectors wherein counter-ions
40
that shield surface charge are “squeezed” between two approaching surfaces.5,6 This repulsion
41
is reduced or eliminated by zones of charge opposite to the colloid/collector surfaces that
42
create local zones of attraction.2,4,7,8 Because the magnitude of repulsion between like-charged
43
colloids and collectors scales directly with their radii of curvature, low radii of curvature of
44
nanoscale asperities (roughness) also locally diminish or eliminate repulsion between like-
45
charged surfaces.1,3,9 Therefore, both nanoscale charge heterogeneity and roughness may
46
counteract repulsion between like-charged surfaces.
47
Experimentally roughness has been shown to increase,10-13 as well as decrease14-16 attachment.
48
This apparent discrepancy may result from different influences of roughness under favorable
49
(energy barrier absent) versus unfavorable (energy barrier present) conditions. Limited studies
50
were conducted under favorable conditions15,17,19 under which the influence of roughness was:
51
1) non-monotonic15 showing a minimum collector efficiency (η = # colloids attached per #
52
colloids introduced) for intermediate roughness (~200 nm root mean square roughness); and 2)
53
monotonic, with η decreasing19 or increasing17 as roughness increased.
54
To understand the seemingly contradictory effects of roughness on particle attachment, its
55
influence needs to be understood via the following mechanisms: 1) interception of the surface,
56
and 2) arrest on the surface (attachment).20 Colloid interception of the surface via fluid drag
4 ACS Paragon Plus Environment
Page 4 of 40
Page 5 of 40
Environmental Science & Technology
57
(fluid streamlines) is enhanced by particle settling and diffusion as encapsulated in colloid
58
filtration theory (CFT).21 Additionally, roughness may diminish interception when the near-
59
surface colloid velocities are increased by the slip layer which is the zone of fluid shear that
60
exists between asperities 22,23 (Figure 1). Roughness may enhance interception18 via local
61
protrusion of the surface into the pore domain, and by decreasing hydrodynamic drag in
62
regions between these asperities.2
63 64
Colloid arrest is governed by the balance of mobilizing and arresting torques, emanating
65
primarily from fluid drag and colloid-collector interaction forces, respectively. 4,21,26,27,31
66
Roughness influences arresting torque in several ways: 1) By decreasing the magnitude of
67
colloid-collector interactions3,9,13,24,25 such that net repulsion (unfavorable conditions) and net
68
attraction (favorable conditions) are decreased since electric double layer (EDL) and van der
69
Waals (VdW) interactions scale to the local radius of curvature of the interacting surfaces;3,19 2)
70
By increasing colloid-collector contact area by establishing multiple points of contact and
71
thereby increasing the arresting torque; 3) By potentially creating additional lever arms
72
associated with contact,27 thereby increasing the arresting torque.
73
The above review demonstrates that roughness has contrasting influences on attachment
74
under unfavorable versus favorable conditions. Experiments performed under these contrasting
75
conditions should help to elucidate these effects of roughness. For this reason, we examined
76
attachment under favorable versus unfavorable conditions for variably rough surfaces.
77
Attachment was examined in pore-scale experiments (impinging jet) where the mode of
5 ACS Paragon Plus Environment
Environmental Science & Technology
78
attachment was directly observed, and motion was tracked in a single focal plane. In contrast,
79
column scale observations do not elucidate the specific modes of attachment, which include
80
immobilization on open surface, wedging in grain-to-grain contacts, and retention without
81
attachment,288 nor do porous media experiments (even direct observation micromodels) allow
82
motion tracking over significant distances because the curved surfaces cross focal planes.
83
Direct observation of attachment on the planar surface therefore allows elucidation of the
84
influence of the hydrodynamic slip layer on near-surface colloid velocities and colloid
85
attachment. The planar surface also eliminates topological complications such as ripening via
86
funneling of colloids into aggregates in grain-to-grain contacts.29 Notably, the experiments of
87
Torkzaban and Bradford19 examined colloid retention in smooth versus rough porous media
88
under high IS conditions where favorable colloid-colloid interaction promote ripening. Such
89
interactions may confound elucidating the influence of roughness on observed colloid release
90
via ionic strength (IS) reduction, since colloid-colloid interactions also respond to IS reduction.
91
The impinging jet system represents only divergent flow at the forward flow stagnation zone,
92
and does not capture Happel sphere-in-cell flow convergence at the rear-flow stagnation zone21
93
representative of porous media. However, by capturing attachment on the open collector
94
surface, the impinging jet allows calibration of the discrete heterogeneity responsible for
95
attachment4,8 and detachment30 under unfavorable conditions. Upon calibrating the
96
contribution of roughness, the resulting representative heterogeneity can be incorporated into
97
other existing collector geometries, such as the Happel sphere-in-cell and Hemisphere-in-cell
98
models.31
6 ACS Paragon Plus Environment
Page 6 of 40
Page 7 of 40
Environmental Science & Technology
99
To ascertain the contribution of roughness, attachment of colloids ranging in diameter from 20
100
nm to 4.4 µm was examined on surfaces with root mean square (RMS) roughness ranging from
101
≤1 nm to 546 nm. This range of asperity/colloid size ratios spans from 1E-5 to 5 (Figure 1),
102
where the largest colloid size (4.4 µm) represents a practical upper limit for stably-suspended
103
non-buoyant colloids in groundwater. The smallest colloid size (20 nm) represents what was
104
possible to resolve optically in our experiments. This colloid size and the largest asperities (546
105
nm RMS) define the largest asperity/colloid size ratio examined here (~5). Above this
106
asperity/colloid size ratio it is reasonable to expect that flow field geometry will be
107
characterized by additional forward and rear flow stagnation zones where impingement and
108
retention may occur as demonstrated in porous media micromodels (e.g., Ausset and Keller32).
109
Because this becomes an issue of resolving a modified flow field (fluid streamlines) rather than
110
the specific influence of roughness on colloid-surface interactions and hydrodynamic slip, we
111
therefore consider larger asperity/colloid size ratios (e.g., > 5) as complex porous media for
112
which the path toward improved prediction is development of corresponding flow fields that
113
represent the associated forward and rear flow stagnation zones.
114
In summary, our goal was to determine the range over which roughness operates (short of
115
creating new impingement surfaces) by defining upper and lower boundaries of attachment
116
which we posit correspond to smooth surfaces under favorable (upper bound attachment) and
117
unfavorable (lower bound attachment) conditions. An additional objective was to understand
118
the influence of roughness not only on attachment but also on detachment.
119
Methods
7 ACS Paragon Plus Environment
Environmental Science & Technology
120
Collector Surfaces
121
Microscope soda lime glass slides and coverslips (Fisher Scientific, Inc.) were used as the
122
impinging surface in the cell, the coverslips were used for smaller colloids that required higher
123
magnification for optical resolution. Three levels of roughness were developed for the glass
124
surfaces by examining them as: 1) untreated; 2) after NaOH-treatment (5 N for 80 min at 90ºC);
125
and 3) after trace metal grade hydrofluoric acid (HF) treatment (27.6 N for 12 hours at 21ºC).
126
Each treatment was followed by extensive rinsing with MilliQ until the rinse solution pH was
127
6.5. The HF treated surface was then heated in air at 250ºC for 2 hours to remove any residual
128
surface impurities. All surfaces were cleaned prior to experiments via the SC-1 procedure. The
129
treatment methods that were used to produce roughness may also introduce defects and
130
uncoordinated atoms on asperities that can increase charge heterogeneity.34 However, it is
131
reasonable to expect that if roughness and charge heterogeneity co-vary on chemically-etched
132
mineral surfaces in the laboratory, then they also co-vary in aquifer media that has undergone
133
natural chemical and mechanical weathering. Our observations are keyed to roughness, since
134
charge heterogeneity is inferred, whereas roughness is measurable.
135
Roughness was measured with an atomic force microscope (model N9451A Agilent
136
Technologies; Santa Clara, CA) following SC-1 cleaning using contact mode in air with silicon
137
nitride probes (type DNP-S10; Bruker Nano, Inc.) with a nominal spring constant of 0.12 N/m.
138
Roughness was evaluated using SPIP software (Image Metrology; Hørsholm Denmark), and was
139
measured as the root mean square height (Figure 2). The minimum scan size for each surface
140
was determined by measuring the RMS roughness over a large area (~50 µm) and then
8 ACS Paragon Plus Environment
Page 8 of 40
Page 9 of 40
Environmental Science & Technology
141
sampling ten random small scan areas (5 µm) within that larger area. If the average RMS
142
roughness of the small scans approximated that of the larger area, the smaller area was
143
accepted and the process was repeated. A minimum of five random locations taken randomly
144
across the observation area of the jet (~500 µm) were used to obtain average values and
145
standard deviations of roughness parameters including: average roughness, root mean square
146
(RMS) roughness, max valley depth, and max peak height. Three dimensional images were
147
generated using Gwyddion software (Czech Metrology Institute, Brno, Czech Republic). The
148
average wavelengths (peak to peak distances) of primary (larger scale) and secondary (small-
149
scale) asperities were measured from five representative profiles (Supplementary Information
150
Figure SI-1) for each surface using the ISO 4287-1997 written standard (ISO; Geneva
151
Switzerland).
152 153
Microsphere Suspensions
154
Carboxylate-modified polystyrene latex (CML) fluorescent (λex = 505, λem = 515 nm)
155
microspheres of six sizes (0.02, 0.1, 0.25, 1.1, 2.0 (Molecular Probes, Inc., Eugene, OR), and 4.4
156
(Polysciences, Washington, PA) μm diameter) were used in the experiments. Colloid
157
suspensions were prepared from stock in relevant solution with concentrations ranging from 5
158
× 106 to 2 × 107 microspheres per milliliter. The microsphere suspension concentration was
159
determined via vacuum filtration of colloid solution (volume adjusted to ensure >20 CML per
160
view area) on 0.05 or 0.1 μm polycarbonate filters (Millipore) followed by averaging counts of
161
25 random observation areas using wide-field fluorescence for colloid illumination and scaling
9 ACS Paragon Plus Environment
Environmental Science & Technology
162
this average to the area of deposition on the filter. Suspension ionic strength (IS) was adjusted
163
using NaCl. Unfavorable solutions (IS 6 mM) were buffered with 2.2 mM MOPS (3-(N-
164
morpholino) propanesulfonic acid, 4-morpholinepropanesulfonic acid; Sigma-Aldrich Corp.)
165
with pH set to 8.0 using NaOH (0.5 M). Favorable solutions were set to pH 2.0 using HCL (1.3 M)
166
and IS 50 mM. Dissolution of the collector surface was not a concern at these pH values as the
167
solubility of amorphous silica is stable and very low at pH values below pH 9.35
168
The Péclet (Pe) and Reynolds (Re) numbers for each colloid size under the relevant fluid
169
velocities are included in the Supplementary Information (Supplementary Information, Table SI-
170
1). Pe numbers all exceed 50,000, corresponding to advection–dominated conditions, and Re
171
numbers range from 1.73 to 5.94, corresponding to laminar creeping flow conditions.
172
The CML electrophoretic mobility (EPM) was measured in suspensions using ζ-potential
173
analyzer (Mobiuζ, Wyatt Technology Corp., Santa Barbara, CA). CML ζ-potentials were
174
calculated from EPM via the Smoluchowski equation for large colloids (i.e. ≥ 100 nm diameter),
175
and the Huckel approximation when the colloid diameter was smaller than the Debye length
176
(i.e. colloids < 100 nm diameter36 (Supplementary Information Table SI-2). The glass slide EPM
177
was measured in the filtrate ( 0.95) was
228
required to quantify η. This initial slope of deposition (across the area of observation, Aobs) was
229
used to calculate the collector efficiency (η) via the following equation:
230
ߟ=
ቀ
#ೌೌ ቁ ಲ
ቀ
#ೕ ቁ ಲ
ೀಳೄ
ಶ
=
#ೌೌ
(1)
ೀ ொ
231
where CO is the injected concentration of colloids and Q is the flow rate of the fluid that enters
232
the cell (across the area of the jet, Ajet). The product COQ is equal to the number of particles
233
injected per unit time across Ajet. This expression was developed specifically for the impinging
234
jet geometry,4 therefore comparison of results with porous media is qualitative. However, note
235
that the conversion of attachment to η as opposed to flux does not change the relative values
236
since the influence of concentration and velocity is equivalent for η (efficiency) and flux (e.g.,
237
dimensionless parameters such as the Sherwood number).
238
Near-surface velocities were determined by tracking particle displacement at the near-surface
239
as a function of time from the images captured using constant streaming (time intervals were
240
less than 1 second between images). Velocities were averaged for 0.25, 1.1 and 2.0 µm colloids
241
for a minimum of 10 particles. Near-surface colloids were distinguished from bulk colloids using
242
TIRF-M (i.e. over the ≤ 1 nm and 38 nm RMS glass surfaces). For the 546 nm RMS surface, a
243
threshold velocity of ~400 µm/min was selected to distinguish particles in the bulk solution.
244
Near-surface velocities were determined under favorable conditions in order to eliminate
245
interactions with the secondary minimum. 13 ACS Paragon Plus Environment
Environmental Science & Technology
246 247
Favorable Simulations
248
A Lagrangian particle trajectory model developed for the smooth impinging jet system was used
249
to predict η under favorable conditions.4 The model accounts for fluid drag, hydrodynamic
250
retardation, gravity, diffusion, colloid−surface interaction forces, and virtual mass. A more
251
detailed description of the force and torque balances including fluid drag, hydrodynamic
252
retardation, gravity, diffusion, steric forces, and virtual mass is described in previous
253
publications. 4,29,31 Favorable conditions were set by assigning measured colloid and collector ζ
254
potentials for the pH 2 50 mM conditions (Supplementary Information, Table SI-2) in the model
255
input.
256
The complete experimental matrix corresponding to the range of collector surfaces (3), colloid
257
sizes (6), fluid velocities (2), IS (2), and pH (2) yielded 72 experiments without replicates and 144
258
experiments with complete replication. In order to produce a tractable set of experiments and
259
simulations, some experimental conditions were not run when the observed trends could be
260
discerned from bracketing experiments, whereas in other cases it was not possible to optically
261
resolve colloids under certain conditions. For example, particles ≤ 100 nm were not examined
262
on the 546 nm RMS surface due to inability to distinguish faint particles from light scattering.
263
Approximately 75 experiments (including replicates) were conducted. Replicates were
264
performed for all experiments conducted on the untreated and NaOH treated slides under the
265
1.7E-3 ms-1 velocity condition. The complete experimental matrix with replicates indicated is
266
shown the Supplementary Information (Supplementary Information Table SI-3).
267
14 ACS Paragon Plus Environment
Page 14 of 40
Page 15 of 40
Environmental Science & Technology
268
Results
269
Roughness
270
Roughness parameters measured using AFM (Figure 2) are summarized in Supplementary
271
Information (Supplementary Information Table SI-4), where untreated, NaOH-treated, and HF-
272
treated glass slides and coverslips showed progressively increasing roughness. The glass slides
273
and coverslips showed similar RMS values for a given treatment. Three levels of roughness
274
were generated on glass slides and coverslips: a) ≤ 1 nm RMS roughness (untreated); b) 38 nm
275
RMS roughness (NaOH-treated); and c) 546 nm RMS roughness (HF-treated). The maximum
276
valley depths and peak heights were approximately a factor of five times the RMS roughness for
277
the untreated and NaOH-treated silica, and approximately a factor of three times the RMS for
278
the HF-treated silica. The primary (large scale) wavelengths were approximately equal to the
279
RMS roughness, suggesting that the asperities were evenly spaced. The untreated glass surface
280
did not exhibit secondary roughness. The secondary wavelengths were similar for both NaOH-
281
treated and HF-treated surfaces (~ 3.5 nm), which indicates that secondary roughness did not
282
change as overall roughness increased, and that roughness appears to follow a fractal
283
relationship.
284
The maximum collector (impinging surface) asperity size was on the order of size of the largest
285
colloids, whereas the smallest collector asperity size was