Niels Timmer1, Steven T J Droge1. 1. Institute for Risk Assessment Sciences, Utrecht University , Utrecht, 3508 TD, The Netherlands.
Abstract
This study reports the distribution coefficient between phospholipid bilayer membranes and phosphate buffered saline (PBS) medium (DMW,PBS) for 19 cationic surfactants. The method used a sorbent dilution series with solid supported lipid membranes (SSLMs). The existing SSLM protocol, applying a 96 well plate setup, was adapted to use 1.5 mL glass autosampler vials instead, which facilitated sampling and circumvented several confounding loss processes for some of the cationic surfactants. About 1% of the phospholipids were found to be detached from the SSLM beads, resulting in nonlinear sorption isotherms for compounds with log DMW values above 4. Renewal of the medium resulted in linear sorption isotherms. DMW values determined at pH 5.4 demonstrated that cationic surfactant species account for the observed DMW,PBS. Log DMW,PBS values above 5.5 are only experimentally feasible with lower LC-MS/MS detection limits and/or concentrated extracts of the aqueous samples. Based on the number of carbon atoms, dialkylamines showed a considerably lower sorption affinity than linear alkylamine analogues. These SSLM results closely overlapped with measurements on a chromatographic tool based on immobilized artificial membranes (IAM-HPLC) and with quantum-chemistry based calculations with COSMOmic. The SSLM data suggest that IAM-HPLC underestimates the DMW of ionized primary and secondary alkylamines by 0.8 and 0.5 log units, respectively.
This study reports the distribution coefficient between phospholipid bilayer membranes and phosphate buffered saline (PBS) medium (DMW,PBS) for 19 cationic surfactants. The method used a sorbent dilution series with solid supported lipid membranes (SSLMs). The existing SSLM protocol, applying a 96 well plate setup, was adapted to use 1.5 mL glass autosampler vials instead, which facilitated sampling and circumvented several confounding loss processes for some of the cationic surfactants. About 1% of the phospholipids were found to be detached from the SSLM beads, resulting in nonlinear sorption isotherms for compounds with log DMW values above 4. Renewal of the medium resulted in linear sorption isotherms. DMW values determined at pH 5.4 demonstrated that cationic surfactant species account for the observed DMW,PBS. Log DMW,PBS values above 5.5 are only experimentally feasible with lower LC-MS/MS detection limits and/or concentrated extracts of the aqueous samples. Based on the number of carbon atoms, dialkylamines showed a considerably lower sorption affinity than linear alkylamine analogues. These SSLM results closely overlapped with measurements on a chromatographic tool based on immobilized artificial membranes (IAM-HPLC) and with quantum-chemistry based calculations with COSMOmic. The SSLM data suggest that IAM-HPLC underestimates the DMW of ionized primary and secondary alkylamines by 0.8 and 0.5 log units, respectively.
Phospholipid membranes
separate (sub)cellular
compartments from surrounding conditions and play an important role
in the uptake, distribution, and toxicity of xenobiotics in multicellular
organisms. Traditionally, the octanol–water partitioning coefficient
(KOW) is used as a predictor for the uptake,
distribution, and accumulation of organic chemicals in various organisms
and their tissues. However, KOW does not
adequately represent the partitioning of ionogenic organic chemicals
(IOCs) between water and phospholipid membranes, because the ionic
solute’s interactions with octanol do not include ionic bonds
that occur with the anionic phosphate groups and cationic choline
groups in phosphatidylcholinephospholipids.[1−3] Cell membranes
are expected to be the dominant sorption site for organic cations
in tissue.[4,5] Just like sorption coefficients to individual
soil components are much more relevant for IOCs than KOW,[6−10] the membrane–water distribution coefficient (DMW) is a logical alternative for KOW as the main model parameter to predict, for example, the
tissue distribution and critical membrane burden in organisms.[4,11] Many IOCs are highly relevant from an ecotoxicological perspective
because of designed bioactive properties and/or continuous input via
wastewater streams.[12,13] Cationic surfactants are hydrophobic
IOCs with a relatively high potential to disrupt cell membranes.[14] Cationic surfactants are commonly used down-the-drain
ingredients in personal care products, because of antistatic properties
(hair conditioner, fabric softener). A variety of quaternary ammoniumsalt cationic surfactants are specifically used as biocide or disinfectants.[15,16] Several cationic surfactants are regularly detected in various aquatic
environments, particularly sediments.[16−20] Quaternarydialkylamines are highly adsorptive and
therefore less accessible for biodegradation processes under certain
conditions, and the longest chain structures such as DODMAC have subsequently
been prohibited in several countries for certain uses.[21] This study aims to measure and model the DMW for cationic surfactants with different alkyl
chain lengths and head groups, in order to improve environmental and
toxicological hazard/risk assessment for this class of IOCs. Since
most common protocols to determine KOW are considered to be impractible for surfactants, the assessment
of DMW would provide a representative
alternative hydrophobicity parameter.Several experimental methods
exist to determine the DMW of IOCs at
physiological pH, such as liposome dispersions, specialized HPLC columns
with phospholipid coatings, and solid supported phospholipid membranes
(SSLM). Methods employing dispersions of freshly prepared liposomes
are most realistic and accurate, but equilibrium dialysis requires
considerable effort and long equilibration times.[2,22] Potentiometric
titrations need substantial concentrations of chemical and phospholipids.[23] Recently, immobilized artificial membrane HPLC
columns (IAM-HPLC) have been used to determine (relative) measures
of lipophilicity in a number of frameworks.[24−27] Confounding pH-dependent surface
charges in IAM-HPLC have recently been recorded in detail.[28] These surface charges can considerably influence
the retention capacity factors of IOCs on IAM-HPLC physiological pH.[28−30] At least for cationic compounds, confounding surface charges can
be avoided by testing at low pH and highly saline eluent medium, and
therewith one can specifically determine the IAM phospholipid–water
distribution coefficient for the ionic form (KIAM,ion).[28] IAM-HPLC consists of
an ordered monolayer of phospholipids covalently linked to a silica
support,[31] instead of a dispersed double
layer of phospholipids. This might reduce its relevance as a surrogate
for the lipid bilayer cellular membrane. Solid supported phospholipid
membranes (SSLMs) are available with macroporous spherical supports
(e.g., silica beads) which are readily separated from the aqueous
phase by mild centrifugation.[32]Recently,
IAM-HPLC was used to determine intrinsic sorption affinities to the
IAM phospholipid monolayer KIAM,intr for
80 different hydrocarbon-based monoprotic cations (CHN+).[24] Remarkably, these KIAM,ion values
did not differ between analogue structures of primary, secondary,
and tertiaryalkylamines with the same alkyl chain length, and were
marginally lower for quaternary ammonium chloride (QAC) analogues
(∼0.2 log units). Quantum-chemistry based molecular calculations
with a model DMPC bilayer (using the COSMOmic module within COSMOtherm software) of KDMPC-W values
for the ionic species closely aligned the full set of KIAM,ion values but predicted a stepwise decrease in KDMPC-W with each methylation of the charged
N, with primary amines at a log unit higher affinity than analogous
QACs. Droge et al.[24] stated that only measurements
on phospholipid bilayers would clarify if either the effect of N-methylation is overpredicted by molecular simulations,
or underpredicted by the IAM monolayer.The main goal of the
present study was to measure partitioning of several series of cationic
surfactants with the molecular formula CHN+ to phospholipid bilayers
using a commercially available SSLM assay, for comparison with IAM-HPLC
results and COSMOmic simulations. We thereby focused on the influence
of the alkyl chain length and different types of charged head groups
but also on the difference between linear single chain alkylamines
and dialkylamines. The applied SSLM assay (trademark TRANSIL) is sold
as a standardized sorbent dilution series assay in a 96 well plate
format[33] but was improved to facilitate
measurements with hydrophobic organic cations.
Materials and Methods
Chemicals,
Sorbent, and Solutions
Nineteen amine based cationic surfactants
compounds were selected. Their molecular structures, physicochemical
properties, purities, and suppliers are listed in the Supporting Information (SI, Table S1). Two secondary
amines contained two linear alkyl chains of equal length (dihexylamine
“S2–C6”, dioctylamine “S2–C8”). Other moieties besides linear alkyl chains include
benzyl in three benzalkonium chloride compounds (BAC), and dodecylpyridinium
(C12-PYR) has the permanently charged nitrogen as part
of an aromatic ring. All stock solutions were prepared as 100 ±
10 mM solutions in methanol, further diluted with methanol as necessary.
All solutions in methanol were stored at −20 °C until
use.TRANSILXL Intestinal Absorption kits and TRANSILXL Intestinal Absorption kits for low affinity compounds were
purchased from Sovicell GmbH (Leipzig, Germany). These kits consist
of a 96 well plate made up of 12 strips with 8 wells each, individual
strips containing two reference wells with phosphate buffered saline
(PBS), and six wells with decreasing amounts (serial dilution factor
of 1.8) of phosphatidylcholine coated macroporous silica beads (“beads”)
suspended in phosphate buffered solution (PBS). The pore diameter
of the silica beads has been specified as 4000 Å in the literature.[47] A 2012 paper by Hou et al. provides SEM images
that give more insight into the three-dimensional structure of the
beads.[48] PBS (Lonza BioWhittaker, Walkersville,
USA; pH 7.4 ± 0.05, without Ca2+ and Mg2+) was used as the test medium for all experiments, unless noted otherwise.
To assess the contribution to the observed DMW of the small neutral fraction present at pH 7.4 for the
ionizableamines (<1%), the DMW was
also determined at pH 5.2 (<0.01% neutral) for several alkylamines.
A 10 mM acetate buffer was used with analytical grade acetic acid
(2.0 mM) and sodium acetate (8.0 mM), dissolved in Milli-Q pure water
(>18.2 MΩ·cm–1, Millipore, Amsterdam,
The Netherlands), and addition of 140 mM NaCl. Additions of all liquids
were checked gravimetrically to record actual volumes.
Adapting the
SSLM Test Protocol for Cationic Surfactants
Cationic surfactants
are notoriously difficult to work with due to relatively high adsorptive
properties and accumulation at the water–air interface. Concentration
dependent sorption to polystyrene well plate material was expected
for several of the tested surfactants, as well as sorption to pipet
tips when transferring supernatant to autosampler vials.[34] To partially avoid these adsorptive challenges,
the SSLM beads were transferred quantitatively to 2 mL glass autosampler
vials. After equilibration of the chemicals with the beads on a roller
bank, the vials were centrifuged and the supernatant in the autosampler
vials could be directly injected by the stainless steel needle of
the autosampler. This reduces pipetting steps and allows for testing
in a larger aqueous volume, of which the composition can be customized.
Whereas the 96 well plate assay applies two PBS reference wells (without
SSLM) serving as 100% references of dissolved concentrations, it was
expected that for several cationic surfactants substantial binding
to the walls of the test vials would compromise a mass balance approach.
We therefore applied quadruplicate methanol solutions as 100% reference
(as calibration standards) and assume that losses due to sorption
to the wall of the test vials in the vials that contain the lipids
does not affect the estimated membrane sorption coefficients. The
validity of this assumption has been validated.A Rainin Pipet-Lite
XLS electronic multichannel pipet with adjustable spacer (Mettler
Toledo BV, Tiel, The Netherlands) was used to transfer the contents
of six wells from one strip with decreasing amounts of phospholipid
coated beads to 2 mL autosampler vials. Wells were flushed six times
with 50 μL of PBS, to transfer all beads to the respective autosampler
vials. Initially, autosampler vials were then filled with additional
400 μL PBS, placed on a Stuart SRT9 roller mixer (Boom BV, Meppel,
The Netherlands) for 15 min at 33 rpm, centrifuged at 750 g (20 °C)
for 10 min. To these test vials, as well as to the four 500 μL
methanol references and four additional 500 μL PBS controls
(to verify the extent of glass binding), 20 μL of spike solution
was added. Overall, our tests were performed in the 1–1000
nM concentration range. We tried to cover isotherms with concentrations
spanning at least a factor of 10, ideally a factor of 100. After addition
of the spike, vials were transferred to a roller mixer for 15 min,
centrifuged at 750 g (20 °C) for 10 min, and stored at 4 °C
until LC-MS/MS analysis.Pilot experiments with longer chain
surfactants showed distinct nonlinear sorption isotherms, while the
shorter chain surfactants showed linear isotherms. Several tests were
performed to evaluate effects of spiking with solvent and bead density.
Since the phospholipid bilayer is not covalently bound to the beads,
we considered that minute—but significant—fractions
of phospholipids might leak from the beads into the test medium during
storage and handling (e.g., thawing) and form small suspended liposomes.
Especially for compounds with high DMW, these liposomes could impact the DMW measurements by artificially increasing measured concentrations
in the aqueous phase being sampled. After transfer of the beads to
the autosampler vials, we therefore added fresh PBS up to 1.8 mL,
centrifuged, and carefully pipetted off 1.7 mL of supernatant to remove
the majority of the detached phospholipids and added 400 μL
of PBS and 20 μL spike solution. Equilibration times of 5, 30,
60, and 240 min were compared with N-methyldodecylamine
(“S12”). A test with dodecylpyridinium (“PYR12”) was performed to assess the tendency of phospholipids
to leak from centrifuged beads while in the autosampler at room temperature,
by injecting the same test series of six vials with washed beads 3,
12, and 21 h after centrifugation.
LC-MS/MS Quantification
and SSLM Data Analysis
All samples were analyzed using a
PerkinElmer (Norwalk, USA) HPLC system with autosampler, coupled to
an MDS Sciex API3000 triple quadrupole mass spectrometer (Applied
Biosystems, Foster City, USA). Retention of test compounds from the
saline test medium was achieved on a Kinetex 5 μm XB-C18 column
(50 × 2.1 mm; 100 Å) with a C18 guard column. The mobile
phase consisted of Milli-Q (pump A) and methanol (pump B), both containing
0.1% formic acid by volume. A solvent switch was employed to flush
PBSsalts into waste, at 10% B for 6 min, before eluting the surfactants
from the column with 90% B. The autosampler needle depth was adjusted
to prevent accidental injection of beads. External calibration standards
in methanol had concentrations ranging from ∼2 nM up to ∼35
μM. Detailed LC and MS/MS parameter settings for each compound
can be found in Table S2.The total
spiked amount (Atotal) of surfactant in
the autosampler will distribute between the aqueous phase (Awater), the phospholipid coating on the beads
(Alipid), and the glass/cap surfaces (Aglass). Atotal is
obtained from the average concentrations in the methanol controls
(CMeOH), and DMW can then be calculated for each sample:Vlipid is the volume of phospholipids
on the beads, as provided by the supplier. Because Aglass is in equilibrium with Awater, then Aglass can be considered negligible
for the calculation of both Alipid and DMW if Alipid is
>90% of Atotal and if Aglass < Awater. Aglass was determined using the PBS reference
samples, which demonstrated the level of equilibrium between glass
sorbed fractions and dissolved fractions (at the spiked concentration).
Samples for decylbenzyldimethylammonium (“BAC10”) were emptied after analysis of Cwater and flushed once with Milli-Q, and glass walls were
extracted with 90% B/10% A eluent mixture. Concentration independent
log DMW values were obtained by fitting
a linear curve on a double logarithmic plot with a forced slope of
1.
IAM-HPLC Measurements of the Phospholipid Monolayer–Water
Distribution Coefficient KIAM,intr for
Cationic Surfactants
The IAM-HPLC procedure described for
strongly sorbing CHN+ cationic amines without UV-absorbing moieties
was followed as described previously.[24] Briefly, a solvent dilution series at pH 5 (10 mM acetate buffer)
was tested in triplicate with LC-MS/MS detection. From a ∼1–5
mg/L surfactant sample in 10% acetonitrile, 5 μL was injected
into an eluent mixtures of ≤30% acetonitrile, at flow rates
of 1.0 mL/min. Multiplying the retention capacity factor kIAM with the column’s phase ratio of 18.9 gives
the apparent distribution coefficient to the IAM phospholipid phase
(KIAM,app) in each tested eluent mixture.[35] Extrapolation of the KIAM,app values to fully aqueous medium buffered at pH 5 gives
the intrinsic KIAM,intr. For each surfactant
at least six measurements were made.
COSMOmic Calculations of
the KDMPC-W for Cationic Surfactants
COSMOmic was run within COSMOtherm Version C30_1501, as described
in the previous comparison between IAM-HPLC and COSMOmic.[24] However, instead of using COSMOmic’s
DMPC example micelle (1,2-dimyristoyl-sn-glycero-3-phosphocholine),
we now used the same time averaged DMPC micelle file and TZVP-optimized
structure of DMPC as used by Bittermann et al.[36] Briefly, the input file to represent a hydrated phospholipid
bilayer is obtained with a molecular dynamics (MD) run, using 128
DMPC molecules equilibrated with thousands of water molecules. COSMOmic
divides the average atomic distribution in the MD simulated DMPC bilayer
into 30 layers for one-half of the hydrated bilayer and uses the lowest
free energy for each surfactant structure at 162 orientations at each
layer to calculate the weighted DMPC–water partition coefficient
(KDMPC-W). The three-dimensional
input
structures for each cationic surfactant were quantum-chemically optimized
for calculations at TZVP level with COSMOmic, including different
conformers (see Table S3 for information
on conformers). COSMOconf version 3.0 was used to
create up to six of the most relevant conformers for all charged surfactants.
Results and Discussion
Measurements of DMW with adapted SSLM Assays
Measured concentrations of the
quadruplicate methanol control samples differed by less than 3.9%
for all compounds tested. For C8-alkylamines and C10-alkylamines, the PBS controls showed 0–30% lower
concentrations than the methanol controls, with exception of the larger
C10-benzalkonium (“C10-BAC”
39%). For C12 surfactants, losses to autosampler surfaces
were between 20 and 60% in PBS. If PBS references would have been
used for C10-BAC as if they represented 100% of the available
compound DMW would have been 0.2 log units
lower than with methanol control samples. Using methanol controls,
measured extracts of the glass walls in vials with beads showed that
the residual impact of glass binding on DMW calculations was insignificant (0.011 log units).Concentrations
of test compound were aimed at keeping the phospholipid/sorbed compound
molar ratio above 60 to prevent possible electrostatic effects due
to the accumulated charge in the membranes.[37,38] As shown in the full matrix of the final sorption isotherms for
all tested compounds in the SI Figure S8, for nearly all of the selected
surfactants, we have tested up to this maximum sorbed concentration
in the membranes of ∼40 mmol/kg to avoid electrostatic effects.
Although the corresponding dissolved concentrations are orders of
magnitude below the critical micelle concentrations (CMC, Table S1), the tested concentrations are most
likely still well above highest environmental concentrations but may
be in the range of adverse effect concentrations. Concentrations of
phospholipid in the test vial should result in sorbed fractions of
at least 30%, to minimize effects of analytical uncertainties of Cwater on the mass balance calculations. The
adapted TRANSILXL Intestinal Absorption kits allows for
measuring DMW values above 1000 with buffer
volumes of ∼525 μL in the autosampler vials. The TRANSILXL Intestinal Absorption kits for low affinity compounds contain
a factor of ∼20 higher levels of beads per well, thereby allowing
for measurements of DMW ≥ 50. The
results from these two kits show overlapping sorption isotherms and
concentration independent DMW, as shown
for dihexylamine (“S2-C6”) in Figure . The sorption isotherms for
C8- and C10-alkylamines also showed concentration
independent DMW values, and overlapping
sorption data with and without PBS renewal (Figure S1).
Figure 1
Sorption data for dihexylamine (S2-C6) obtained with two different
sorbent dilution series and fit of a linear sorption isotherm (slope
of 1), resulting in a log DMW,PBS of 3.15
(95% CI 3.10–3.20).
Sorption data for dihexylamine (S2-C6) obtained with two different
sorbent dilution series and fit of a linear sorption isotherm (slope
of 1), resulting in a log DMW,PBS of 3.15
(95% CI 3.10–3.20).However, for the C12-chain surfactants series
measured without flushing off leaked phospholipids showed distinctly
nonlinear isotherms, with higher DMW values
for the highest concentrations in a series (samples with lowest amounts
of SSLM beads), and no correspondence between two series spiked at
different initial concentrations (Figure S1). For each individual series, the slope of a linear isotherms on
the double logarithmic plots was >1. This result would cause doubt
on the resulting KMW from the SSLM assay,
and an apparent concentration dependent sorption affinity over such
a narrow tested concentration range would have considerable deviations
of the KMW at considerably lower (e.g.,
most environmental) and possibly higher concentrations (e.g., as applied,
or at adverse effect levels). We found no evidence of influence of
solvent from spiking solution, as data for secondary N-methyldodecylamine (“S12”) from methanol
stock solutions overlapped with nonlinear results from stocks dissolved
in water (Figure S2). Instead of a sorbent
dilution series, we then tested primary dodecylamine (“P12”) with two series with constant concentration of
SSLM material, spiked at six different concentrations (accompanied
by six sets of methanol controls). Now, each series indicated concentration
independent DMW (slope of 1 on logarithmic
plot), but again the series with higher amount of SSLM material showed
a lower sorption affinity (Figure S3).
Evidently, higher SSLM material resulted in a higher detached amount
of phospholipids from the beads leaking into the aqueous phase. If
the sorbed amount of cationic surfactants to this phase significantly
increases the measured Cwater, this leads
to underestimation of the DMW. Using a
common extension of eq for third phase systems,[39] we modeled
this effect by assuming a constantly leaked fraction (fleak) of the total amount of lipids coated on the beads,
i.e., where the amount of lipids dispersed in the medium equals Vlipid·fleak:Experimental and
modeled results are plotted for dodecylpyridinium (PYR12) in Figure , combining
data for “unwashed” samples (still including medium
from the well plate, thus with fleak still
present) with “washed” samples (with fleak mostly removed). As shown in Figure , the curve representing 1% of the phospholipids
leaking from bilayers into the test medium (fleak = 0.01) approximated the observed experimental values
that show a nonlinear curve. A modeled curve for fleak =
0.02 overestimated the observations. More plots comparing simulations
for unwashed and washed beads for compounds with log DMW of 4.0, 4.5, and 5.0 can be found in the Supporting Information (Figure S4). All experimental
data and modeling output suggest a phospholipid leakage of approximately
1% from the bilayers on the beads into the medium, which–if
not removed from the test medium–will influence the sorption
isotherms for compounds with a DMW >
log 4.0.
Figure 2
Experimental sorption data and simulated sorption data for dodecylpyridinium
(PYR12) obtained with “unwashed” and “washed”
sorbent dilution series, where unwashed still contains the medium
from the well plates, whereas the medium was replenished with fresh
PBS in “washed” samples. The simulated series show curves
of a lipid leakage fraction of 0%, 1%, and 2%. The fitted linear curve
for the experimental data indicates a log DMW,PBS of 4.89 (95% c.i. 4.84–4.95).
Experimental sorption data and simulated sorption data for dodecylpyridinium
(PYR12) obtained with “unwashed” and “washed”
sorbent dilution series, where unwashed still contains the medium
from the well plates, whereas the medium was replenished with fresh
PBS in “washed” samples. The simulated series show curves
of a lipid leakage fraction of 0%, 1%, and 2%. The fitted linear curve
for the experimental data indicates a log DMW,PBS of 4.89 (95% c.i. 4.84–4.95).Varying the incubation time on the roller mixer (5–240
min) did not have a significant impact for fully dispersed SSLM solutions
(Figure S5); 30 min was kept as standard.
After centrifugation, the autosampler vials may stand for several
hours in the autosampler before injection. The results of analysis
after standing for 3, 12, or 21 h indicated no further leakage of
phospholipids, as the measured surfactant concentrations and resulting
sorption isotherm showed excellent overlap, whereas a significant
fraction of leaked phospholipids would have increased the apparent
concentrations in the medium (Figure S6). In test solution of pH 5.4 (washed), the DMW values of an ionizabletertiaryN,N-dimethyldecylamine (“T10”)
as well as of a permanently charged QACN,N,N-trimethyldecylammonium
(“Q10”) were not statistically different
from the DMW in PBS (pH7.4), indicating
that the <0.5% neutral fraction of T10 is not contributing
to the measured DMW in PBS and that there
were no confounding pH-dependent surface charge effects of the SSLM
material. In contrast, pH-dependent surface charge effects in IAM-HPLC
confound the DMW of organic cations in
saline medium by ∼0.7 log units between pH 5 and 7.4.[28] As a result, the measurements of DMW in PBS of cationic surfactants all relate to the partition
coefficient of the ionic form (KMW,ion) and can thus be directly compared to COSMOmic simulations with
the ionized structures and IAM-HPLC measurements made at pH 5.
Modeling
the DMW by the Structure of Single Chain
Cationic Surfactants
Isotherms were fitted with a fixed slope
of 1 for all data points from tests with washed medium, where fsorbed ≥ 0.3 and the phospholipid/sorbate
ratio was higher than 60 (Figure S8); an
overview of all isotherm details can be found in Table S3. Standard errors were <0.05 log units, and 95%
confidence intervals were <0.17 log units for all tested DMW values. The resulting DMW values (Table ) were used to derive a simple quantitative structure activity relationship
(QSAR) based on binary values for headgroup types and the length of
the alkyl chain:Where ncarbon denotes the number of carbon atoms in
the alkyl chain, NBenz is a binary value
indicating the presence (1) or absence (0) of a complete benzalkonium
headgroup (three compounds included), and NCC (two compounds included), NCCC (three compounds included), and NCCCC (four compounds included) are binary values
indicating the degree of N-alkylation. The NCCCC value for benzalkonium compounds should
be 0 by default. C12-pyridinium was omitted as there was
only one compound with this headgroup. Dialkylamines were omitted
since they are expected to behave differently because the dual alkyl
chain influences their orientation in the phospholipid membrane.[24] Both types are discussed further. As shown in Figure , the regression
model of eq fits all
input compounds within a factor 3 of the experimental values (root-mean-square
error of 0.20). Using binary values on only 3 or 4 compounds for each
parameter in the QSARs of eq results in a fairly low level of redundancy in the data.
However, our main aim of this excercise was to obtain insight in these
simplified headgroup properties (N-methylation) and
not to provide a functional well validated QSAR to predict KMW values for cationic surfactants. Considering
that this data set of cationic surfactants is still structurally relatively
nondiverse and relatively small, no further efforts were made to refine
a QSAR based on other physicochemical or quantum-chemically derived
parameters. Obviously, DMW increases with
longer alkyl chains, with 0.59 ± 0.03 log units per CH2 unit, which can be used to extrapolate DMW predictions to longer chain surfactants. Comparing this fragment
value with the tabulated DMW values (Table ) it seems to be slightly
higher than expected based on the experimental values obtained for
the quaternary ammonium compounds, and slightly lower than expected
based on the secondary and tertiary C12 compounds. Although
we expect a constant CH2 unit contribution for all single
linear alkyl chains, the contributions of CH2 unit in the
chain near the charged amine may be slightly lower, as these may not
all reside in the hydrophobic core, and this is not defined in eq .[24] Effects of pH and possible neutral fraction for ionizableamines
were ruled out based on additional tests at pH 5.4 (above and Figure S7). A consistent trend of decreasing DMW with increasing methylation of the N atom
is observed for the three analogue series of C8-,C10-, and C12-amines. Primary amines have 0.28 ±
0.16 log unit higher DMW than secondary
amines, which are 0.28 ± 0.16 log units higher than tertiaryamines, which are 0.53 ± 16 log units higher than QACs (excluding
benzalkonium compounds). Taking the average over all the C8-,C10-, and C12-amines, primary amines sorbed
1.06 log units stronger than the QAC analogues. Considering that the
quaternary amine has three more CH2 units than the primary
analogue, this is a remarkable feature of IOCs. The benzalkonium compounds
have a DMW of 1.0 ± 0.17 log units
higher than trimethylalkylammonium compounds, which reflects the effect
of an additional benzyl moiety. With an experimental log DMW of 4.89, PYR12 positions in between BAC12 and Q12 compounds, corresponding to the molecular
volume differences. For 16 out of 19 compounds, two or more conjoined
series were tested, demonstrating both consistency of experimental
results and steadiness over multiple orders of magnitude of the DMW estimates.
Table 1
Log DMW Values for All Compounds Tested with the SSLM Assay,a As Well As Uncorrected IAM-HPLC log KIAM,intr Measurements and COSMOmic Predicted log KDMPC-W Values (No Offset Correction)
alkyl chain
method
primary amine (P)
secondary amines (S)
tertiary amines
(T)
trimethyl ammonium (Q)
benzalkonium cations (BAC)
pyridinium cations (PYR)
secondary dialkyl-amines
(S2)
quaternary dialkyl-ammonium (Q2)
C6
SSLM
2.12
3.15
IAM
1.32
2.42
2.88
COSMO
2.63
1.92
1.45
1.08
1.87
2.77
C8
SSLM
3.10
2.76
2.35
2.18
3.11
4.65
IAM
2.30
2.33
2.35
2.18
3.30
5.04
COSMO
3.71
3.01
2.53
2.18
2.96
4.34
C10
SSLM
4.30
3.98
3.65
3.34
4.01
IAM
3.55
3.59
3.59
3.44
4.47
COSMO
4.83
4.14
3.70
3.30
4.05
6.26
7.53
C12
SSLM
5.58
5.39
5.30
4.35
4.89
IAM
4.81
4.57
COSMO
6.01
5.28
4.76
4.47
5.14
4.77
8.40
9.79
C14
SSLM
5.46
COSMO
7.15
6.42
5.89
5.61
6.65
5.90
12.06
C16
COSMO
8.31
7.56
7.07
6.72
7.90
7.03
C16/C18
C18
COSMO
9.43
8.74
8.29
7.94
9.01
15.51
C22
COSMO
10.1
nr of data used, standard errors, and 95% confidence
intervals are presented in SI Table S3.
δIAM-SSLM corrected KMW(IAM) values are presented in SI Table
S3.
Figure 3
Observed and predicted log DMW,PBS values for single linear chain cationic surfactants
using eq (P = primary
amines, S = secondary amines, T = tertiary amines, Q = trimethylalkylammonium
compounds, BAC = benzalkonium chloride compounds).
Observed and predicted log DMW,PBS values for single linear chain cationic surfactants
using eq (P = primary
amines, S = secondary amines, T = tertiaryamines, Q = trimethylalkylammonium
compounds, BAC = benzalkonium chloride compounds).nr of data used, standard errors, and 95% confidence
intervals are presented in SI Table S3.
δIAM-SSLM corrected KMW(IAM) values are presented in SI Table
S3.
Correlation of SSLM Data
with IAM-HPLC Measurements and COSMOmic Predictions
The available KIAM values obtained with IAM-HPLC (see detailed
solvent series data in Figure S9, Table S3) and KDMPC-W values from COSMOmic
(Table S3) are plotted against the experimental DMW results from the SSLM assay in Figure A. Overall, the alternative
data sets and the SSLM data align reasonably well, with RMSE of 0.39
and 0.27 log units, for IAM-HPLC and COSMOmic, respectively. Instead
of eq , now also dialkylamines
and pyridinium compounds can be included. As discussed in Droge et
al.,[24] IAM-HPLC data and COSMOmic predictions
differed in the contributions of the N-methylations
to the sorption affinity. The SSLM DMW values confirm the ordering of primary > secondary > tertiary
> quaternary amine analogues as predicted by COSMOmic and indicate
that IAM-HPLC accounts insufficiently for effects of N-methylation. Considering that the SSLM data are obtained with relatively
fluid phospholipid bilayers, and IAM-HPLC applies a covalently bound
monolayer, we suggest applying corrective increments for the N-methyl headgroup contributions to KIAM values of IAM-HPLC, compared against the SSLM DMW values (δIAM-SSLM). Multiple
linear
regression results in δIAM-SSLM of 0.78 ±
0.07
(se) log units for primary alkylamines (i.e., KIAM values underestimate the KMW in bilayers), and 0.47 ± 0.09 log units for secondary amines.
The δIAM-SSLM for tertiaryamines is insignificant
(−0.03 ± 0.10 log units), and very small for quaternary
alkyltrimethylamines −0.11 ± 0.09. For COSMOmic δDMPC-SSLM amine type corrective increments were derived
similarly.
Interestingly, primary amines tended to be slightly overestimated
by COSMOmic (0.17 ± 0.17 log units), while the other amine types
were slightly underestimated (0.2–0.4 ± 0.16 log units).
COSMOmic seems to be capable of predicting the effect of N-methylation in phospholipid bilayers. Contrary to suggested correction
of COSMOmic values reported previously,[24] the SSLM data support the notion that the IAM-HPLC monolayer is
the most probable source of inconsistency, creating scatter between
IAM-HPLC and COSMOtherm. Using these δIAM-SSLM and
δDMPC-SSLM corrective increments, there is
strong
correspondence between SSLM DMW values,
the corrected IAM-HPLC KMW(IAM) values,
and corrected COSMOmic KDMPC-W values,
as shown in Figure B. All values are well within a factor 2 of the 1:1 line and the
RMSE improved from 0.39 to 0.21 (IAM-HPLC) and from 0.27 to 0.18 (COSMOmic).
Figure 4
Experimental
log DMW,PBS values with TRANSIL bilayers
plotted against experimental log KIAM results
from the IAM-HPLC monolayer and simulated log KDMPC-W values with DMPC bilayers using COSMOmic. In
the graph
on the right, IAM-HPLC values are corrected for 1° amines with
+0.8 log units and 2° amines with +0.5 log units. COSMOmic values
are corrected for 1° amines with −0.5 log units.
Experimental
log DMW,PBS values with TRANSIL bilayers
plotted against experimental log KIAM results
from the IAM-HPLC monolayer and simulated log KDMPC-W values with DMPC bilayers using COSMOmic. In
the graph
on the right, IAM-HPLC values are corrected for 1° amines with
+0.8 log units and 2° amines with +0.5 log units. COSMOmic values
are corrected for 1° amines with −0.5 log units.The three methods attribute similar
effects of alkyl chain length, but also display a striking consistency
in the difference between secondary dialkylamines and linear chain
secondary alkylamine analogues. As discussed in Droge et al.,[24] COSMOmic provides a mechanistic explanation
for the relatively lower contribution of CH2 units to the DMW compared to single chain surfactants. Their
design with two alkyl chains creates a steric effect, where the most
favorable molecular position and orientation is mostly within the
headgroup area of the phospholipid bilayer where—as a compromise—neither
alkyl chain is aligned most favorably into the hydrophobic core region.
The SSLM results confirm the difference in DMW between secondary linear amineN-methyldodecylamine
S12 and secondary dihexylamine S2-C6 by 2.24
log units, as was observed by Droge et al.[24] for IAM-HPLC (1.93 log units) and COSMOmic (2.43 log units). For
all three methods the difference observed is much larger than expected
with one extra CH2 fragment in S12. Between
S2-C6 and dioctylamine (S2-C8), the SSLM DMW increased by 1.5 log units, while the regression
model in eq would predict
a 2.36 log unit increase based on the addition of four CH2 units. COSMOmic also predicts a smaller value (1.73 log units) for
the CH2 increment between S2-C6 and S2-C8, while IAM-HPLC showed a 2.16 log unit difference (Table S3).
DMW Values for Cationic Surfactants Compared to KOW Predictions
The most recent analysis of KMW values of neutral compounds,[40] mostly obtained with liposomes, showed a strong correlation
with KOW:There is only a poor correlation
(R2 = 0.49) between the SSLM measured
log DMW at pH 7.4 and the log KOW of the neutral primary, secondary, and tertiaryamines, as shown in SI Figure S10. The
influence of the methyl units on the charged nitrogen are reversed
for the two distribution coefficients. Each N-methyl
unit increases the log KOW while it reduces
the log DMW. Also, even though the sorption
affinity of the protonated amines to the SSLM bilayer increases with
linear alkyl chain length as the KOW predicts,
the log DMW of the dialkylamines is orders
of magnitude lower than the log KOW (for
S2-C8 4.61 and 7.01, respectively). Typically for studies
on the toxicokinetic properties of ionizable chemicals, a “log D approach” is followed, correcting the log KOW for speciation of the neutral amines at the
tested pH 7.4 (99.9% ionic for primary and secondary amines, 99.7%
for tertiaryamines). To derive a log D, however,
the affinity of the ionic species for octanol needs to be known or
predicted. In the absence of measurements, often either a constant
factor of ∼3 log units lower than log KOW is applied, or the affinity of the ionic species is ignored
and the KOW is multiplied by the fraction
of neutral species. As shown in Figure S10, both such log D approaches underestimate the sorption
affinity to membranes by a up to a factor of 1000 and do not solve
the poor correlation between log DMW and
log KOW. Instead, log KOW could still be used to identify specific scaling factors
to the
difference in sorption affinity to a bilayer between neutral and ionic
species, with the neutral affinity still based on eq . Table S3 lists the KMW values for the neutral
primary, secondary and tertiaryamine species calculated via eq (log KOW predicted by ACD/Laboratories). Accordingly, the average
difference between charged DMW,PBS and
neutral KMW species (ΔMW) for primary amines is −0.05, so the affinity of charged
primary amines is larger than the neutral species. For the three linear
single chain N-methylalkylamines ΔMW is 0.44, for the linear N,N-dimethylalkylamines, the ΔMW is 1.25. These
values closely correspond to the scaling factors suggested for the
bioaccumulation model for ionogenic compounds (BIONIC) proposed by
Armitage et al.,[4] which were 0.3, 0.5,
and 1.25 for primary, secondary and tertiaryamines, respectively,
based on data sets of measured KMW values
for both ionic and neutral species. However, the ΔMW is 1.90 and 2.55 for the two dialkylamines S2-C6 and
S2-C8, respectively, much higher than the 0.44 derived
with the other secondary amines. The examples of the dialkylamines
show that applying a single ΔMW scaling factor for
all secondary amines to calculate the DMW,PBS from the KOW relationship in eq , can lead to erroneous
values. Similarly, this exercise shows that KOW is not an adequate single descriptor to model the DMW values for ionized compounds. Measured KMW values with TRANSIL, KPLIPW values with IAM-HPLC, and even simulated KDMPC values with COSMOmic, provide much more accurate
and more mechanistically sound estimates compared to KOW-based regressions.
Perspective on SSLM Assay
Measurements and Associated DMW Estimates
This study showed that the adapted SSLM protocol, with SSLM beads
transferred from a well plate to autosampler vials, facilitated the
analysis, improved recovery in methanol reference vials, and gained
experimental control over the aqueous phase. The medium renewal removed
third phase liposome artifacts, and allowed for altered pH of the
test medium. The problem of detached phospholipids in the original
SSLM medium became significant for all compounds with a DMW higher than log 4, while using methanol controls instead
of PBS controls seems mostly important for hydrophobic organic cations,
and surfactants in general.[41] The experimental
determination of DMW becomes problematic
above log 5.5, because with the required phospholipid/sorbate molar
ratio >60, the aqueous phase concentrations obtained directly from
the autosampler vials, are nearing LC-MS/MS detection limits. This
means that to measure DMW values for cationic
surfactants with alkyl chains longer than C12, and dialkylamines
with alkyl chains longer than C8, either cumbersome solid
phase extraction steps from larger test volumes are required—which
may include uncontrolled adsorption losses—or sorption affinities
need to be extrapolated with the model, or from series of smaller
analogues. Alternatively, COSMOmic seems to provide a realistic and
accurate predictive tool for cationic surfactants, which allows for
extrapolations to longer chain cationic surfactants (Table ) and slight alterations of
the head groups. For example, the log KDMPC-W for didecyldimethylammonium chloride (DDAC), a commonly used biocide,[42] and cetylpyridinium, a commonly used antiseptic,
are 7.53 and 7.03 (Table ), which are both experimentally not feasible to measure with
currently applied IAM-HPLC and SSLM assays. The log KDMPC-W for behentrimonium, a trimethylalkylammonium
compound with a chain length of C22 which is used in many
hair cair products and which has been detected in marine sediments,[43] is 10.3. The dialkylquat DODMAC (mixed chain
length of C16/C18), banned for certain uses
in the EU,[21] has a predicted log KDMPC-W of 15.5. For these examples, the
very
high predicted sorption affinities to cell membrane should be considered
in risk assessment models (e.g., for bioaccumulation[4]) alongside strong sorption affinities to environmental
particles,[6−9] which strongly reduces the bioavailability, and thus result in relatively
low accumulation from the environment into tissues.[34,44−46]
Authors: Elena Martínez-Carballo; Carmen González-Barreiro; Andrea Sitka; Norbert Kreuzinger; Sigrid Scharf; Oliver Gans Journal: Environ Pollut Date: 2006-09-28 Impact factor: 8.071
Authors: Steven T J Droge; James M Armitage; Jon A Arnot; Patrick N Fitzsimmons; John W Nichols Journal: Environ Toxicol Chem Date: 2021-09-21 Impact factor: 4.218
Authors: Floris A Groothuis; Niels Timmer; Eystein Opsahl; Beate Nicol; Steven T J Droge; Bas J Blaauboer; Nynke I Kramer Journal: Chem Res Toxicol Date: 2019-05-22 Impact factor: 3.739
Authors: Amelie Kierkegaard; Marcus Sundbom; Bo Yuan; James M Armitage; Jon A Arnot; Steven T J Droge; Michael S McLachlan Journal: Environ Sci Technol Date: 2021-06-16 Impact factor: 9.028