Sorption of Cationic Surfactants to Artificial Cell Membranes

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Sorption of Cationic Surfactants to Artificial Cell Membranes: Comparing Phospholipid Bilayers with Monolayer Coatings and Molecular Simulations Niels Timmer, and Steven T.J. Droge Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.6b05662 • Publication Date (Web): 10 Feb 2017 Downloaded from http://pubs.acs.org on February 12, 2017

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Sorption of Cationic Surfactants to Artificial Cell Membranes: Comparing

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Phospholipid Bilayers with Monolayer Coatings and Molecular Simulations.

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Niels Timmer1, Steven T.J. Droge1‡*

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*Corresponding author; E-mail: [email protected]; Tel: +31 205257437

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ABSTRACT

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This study reports the distribution coefficient between phospholipid bilayer membranes and PBS

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medium (DMW,PBS) for 19 cationic surfactants. The method used a sorbent dilution series with solid

Institute for Risk Assessment Sciences, Utrecht University, Utrecht, 3508 TD, The Netherlands

Current address; UvA-IBED, Postbus 94248, 1090 GE Amsterdam, The Netherlands.

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supported lipid membranes (SSLMs). The existing SSLM protocol, applying a 96 well plate set-up, was

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adapted to use 1.5 mL glass autosampler vials instead, which facilitated sampling and circumvented

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several confounding loss processes for some of the cationic surfactants. About 1% of the phospholipids

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were found to be detached from the SSLM beads, resulting in nonlinear sorption isotherms for

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compounds with logDMW values above 4. Renewal of the medium resulted in linear sorption isotherms.

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DMW values determined at pH 5.4 demonstrated that cationic surfactant species account for the observed

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DMW,PBS. LogDMW,PBS values above 5.5 are only experimentally feasible with lower LC-MS/MS detection

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limits and/or concentrated extracts of the aqueous samples. Based on the number of carbon atoms,

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dialkylamines showed a considerably lower sorption affinity than linear alkylamine analogues. These

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SSLM results closely overlapped with measurements on a chromatographic tool based on immobilized

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artificial membranes (IAM-HPLC), and with quantum-chemistry based calculations with COSMOmic. The

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SSLM data suggest that IAM-HPLC underestimates the DMW of ionized primary and secondary alkylamines

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by 0.8 and 0.5 log units, respectively.

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TOC art graphic

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INTRODUCTION

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Phospholipid membranes separate (sub)cellular compartments from surrounding conditions, and play an

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important role in the uptake, distribution and toxicity of xenobiotics in multicellular organisms.

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Traditionally, the octanol-water partitioning coefficient (KOW) is used as a predictor for the uptake,

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distribution and accumulation of organic chemicals in various organisms and their tissues. However, KOW

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does not adequately represent the partitioning of ionogenic organic chemicals (IOCs) between water and

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phospholipid membranes, because the ionic solute’s interactions with octanol do not include ionic bonds

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that occur with the anionic phosphate groups and cationic choline groups in phosphatidylcholine

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phospholipids.1-3 Cell membranes are expected to be the dominant sorption site for organic cations in

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tissue.4, 5 Just like sorption coefficients to individual soil components are much more relevant for IOCs

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than KOW,6-10 the membrane-water distribution coefficient (DMW) is a logical alternative for KOW as the

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main model parameter to predict, for example, the tissue distribution and critical membrane burden in

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organisms.4, 11 Many IOCs are highly relevant from an ecotoxicological perspective because of designed

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bioactive properties and/or continuous input via waste water streams.12, 13 Cationic surfactants are

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hydrophobic IOCs with a relatively high potential to disrupt cell membranes.14 Cationic surfactants are

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commonly used down-the-drain ingredients in personal care products, because of antistatic properties

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(hair conditioner, fabric softener). A variety of quaternary ammonium salt cationic surfactants are

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specifically used as biocide or disinfectants.15, 16 Several cationic surfactants are regularly detected in

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various aquatic environments, particularly sediments.16-20 Quaternary dialkylamines are highly adsorptive

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and therefore less accessible for biodegradation processes under certain conditions, and the longest

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chain structures such as DODMAC have subsequently been prohibited in several countries for certain

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uses.21 This study aims to measure and model the DMW for cationic surfactants with different alkyl chain

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lengths and head groups, in order to improve environmental and toxicological hazard/risk assessment

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for this class of IOCs. Since most common protocols to determine KOW are considered to be impractible

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for surfactants, the assessment of DMW would provide a representative alternative hydrophobicity

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parameter.

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Several experimental methods exist to determine the DMW of IOCs at physiological pH, such as liposome

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dispersions, specialized HPLC columns with phospholipid coatings, and solid supported phospholipid

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membranes (SSLM). Methods employing dispersions of freshly prepared liposomes are most realistic and

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accurate, but equilibrium dialysis requires considerable effort and long equilibration times.2, 22

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Potentiometric titrations need substantial concentrations of chemical and phospholipids.23 Recently,

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immobilized artificial membrane HPLC columns (IAM-HPLC) have been used to determine (relative)

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measures of lipophilicity in a number of frameworks.24-27 Confounding pH-dependent surface charges in

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IAM-HPLC have recently been recorded in detail.28 These surface charges can considerably influence the

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retention capacity factors of IOCs on IAM-HPLC physiological pH.28,29, 30 At least for cationic compounds,

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confounding surface charges can be avoided by testing at low pH and highly saline eluent medium, and

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therewith one can specifically determine the IAM phospholipid-water distribution coefficient for the

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ionic form (KIAM,ion).28 IAM-HPLC consists of an ordered monolayer of phospholipids covalently linked to a

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silica support,31 instead of a dispersed double layer of phospholipids. This might reduce its relevance as a

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surrogate for the lipid bilayer cellular membrane. Solid supported phospholipid membranes (SSLMs) are

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available with macroporous spherical supports (e.g., silica beads) which are readily separated from the

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aqueous phase by mild centrifugation.32

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Recently, IAM-HPLC was used to determine intrinsic sorption affinities to the IAM phospholipid

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monolayer KIAM,intr for eighty different hydrocarbon-based monoprotic cations (CxHyN+).24 Remarkably,

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these KIAM,ion values did not differ between analogue structures of primary, secondary, and tertiary

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alkylamines with the same alkyl chain length, and were marginally lower for quaternary ammonium

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chloride (QAC) analogues (~0.2 log units). Quantum-chemistry based molecular calculations with a model

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DMPC bilayer (using the COSMOmic module within COSMOtherm software) of KDMPC-W values for the

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ionic species closely aligned the full set of KIAM,ion values, but predicted a stepwise decrease in KDMPC-W

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with each methylation of the charged N, with primary amines at a log unit higher affinity than analogous

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QACs. Droge et al.24 stated that only measurements on phospholipid bilayers would clarify if either the

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effect of N-methylation is overpredicted by molecular simulations, or underpredicted by the IAM

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monolayer.

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The main goal of the present study was to measure partitioning of several series of cationic surfactants

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with the molecular formula CxHyN+ to phospholipid bilayers using a commercially available SSLM assay,

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for comparison with IAM-HPLC results and COSMOmic simulations. We thereby focused on the influence

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of the alkyl chain length and different types of charged head groups, but also on the difference between

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linear single chain alkylamines and dialkylamines. The applied SSLM assay (trademark TRANSIL) is sold as

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a standardized sorbent dilution series assay in a 96 well plate format,33 but was improved to facilitate

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measurements with hydrophobic organic cations.

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MATERIALS AND METHODS

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Chemicals, sorbent and solutions

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Nineteen amine based cationic surfactants compounds were selected. Their molecular structures,

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physicochemical properties, purities, and suppliers are listed in the supporting information (SI, Table S1).

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Two secondary amines contained two linear alkyl chains of equal length (dihexylamine “S2-

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C6”,dioctylamine ”S2-C8”). Other moieties besides linear alkyl chains include benzyl in three

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benzalkonium chloride compounds (BAC), and dodecylpyridinium (C12-PYR) has the permanently charged

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nitrogen as part of an aromatic ring. All stock solutions were prepared as 100±10 mM solutions in

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methanol, further diluted with methanol as necessary. All solutions in methanol were stored at -20 °C

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until use.

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TRANSILXL Intestinal Absorption kits, and TRANSILXL Intestinal Absorption kits for low affinity compounds,

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were purchased from Sovicell GmbH (Leipzig, Germany). These kits consist of a 96 wells plate made up of

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12 strips with 8 wells each, individual strips containing two reference wells with phosphate buffered

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saline (PBS) and six wells with decreasing amounts (serial dilution factor of 1.8) of phosphatidylcholine

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coated macroporous silica beads (“beads”) suspended in phosphate buffered solution (PBS). The pore

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diameter of the silica beads has been specified as 4000 Å in literature.47 A 2012 paper by Hou et al.

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provides SEM images that give more insight into the three-dimensional structure of the beads.48 PBS

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(Lonza BioWhittaker, Walkersville, USA; pH 7.4 ± 0.05, without Ca2+ and Mg2+) was used as the test

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medium for all experiments, unless noted otherwise. To assess the contribution to the observed DMW of

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the small neutral fraction present at pH 7.4 for the ionizable amines (90% of Atotal, and if Aglass < Awater. Aglass was determined using the PBS reference samples, which

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demonstrated the level of equilibrium between glass sorbed fractions and dissolved fractions (at the

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spiked concentration). Samples for decylbenzyldimethylammonium (“BAC10”) were emptied after

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analysis of Cwater, flushed once with Milli-Q, and glass walls extracted with 90% B/10% A eluent mixture.

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Concentration independent logDMW values were obtained by fitting a linear curve on a double

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logarithmic plot with a forced slope of 1.

஼ೢೌ೟೐ೝ

=



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ೢೌ೟೐ೝ

=

ಲ೟೚೟ೌ೗ షಲೢೌ೟೐ೝ షಲ೒೗ೌೞೞ



஼ೢೌ೟೐ೝ

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IAM-HPLC measurements of the phospholipid monolayer-water distribution coefficient KIAM,intr for

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cationic surfactants.

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The IAM-HPLC procedure described for strongly sorbing CxHyN+ cationic amines without UV-absorbing

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moieties was followed as described previously.24 Briefly, a solvent dilution series at pH 5 (10 mM acetate

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buffer) was tested in triplicate with LC-MS/MS detection. From a ~1-5 mg/L surfactant sample in 10%

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acetonitrile, 5 μL was injected into an eluent mixtures of ≤30% acetonitrile, at flow rates of 1.0 mL/min.

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Multiplying the retention capacity factor kIAM with the column’s phase ratio of 18.9 gives the apparent

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distribution coefficient to the IAM phospholipid phase (KIAM,app) in each tested eluent mixture.35

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Extrapolation of the KIAM,app values to fully aqueous medium buffered at pH 5 gives the intrinsic KIAM,intr.

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For each surfactant at least 6 measurements were made.

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COSMOmic calculations of the KDMPC-W for cationic surfactants

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COSMOmic was run within COSMOtherm Version C30_1501, as described in the previous comparison

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between IAM-HPLC and COSMOmic.24 However, instead of using COSMOmic’s DMPC example micelle

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(1,2-dimyristoyl-sn-glycero-3-phosphocholine), we now used the same time averaged DMPC micelle file

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and TZVP-optimized structure of DMPC as used by Bittermann et al.36 Briefly, the input file to represent a

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hydrated phospholipid bilayer is obtained with a molecular dynamics (MD) run, using 128 DMPC

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molecules equilibrated with thousands of water molecules. COSMOmic divides the average atomic

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distribution in the MD simulated DMPC bilayer into 30 layers for one half of the hydrated bilayer, and

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uses the lowest free energy for each surfactant structure at 162 orientations at each layer to calculate

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the weighted DMPC-water partition coefficient (KDMPC-W). The three dimensional input structures for each

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cationic surfactant were quantum-chemically optimized for calculations at TZVP level with COSMOmic,

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including different conformers (see Table S3 for information on conformers). COSMOconf Version 3.0

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was used to create up to 6 of the most relevant conformers for all charged surfactants.

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RESULTS AND DISCUSSION

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Measurements of DMW with adapted SSLM assays

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Measured concentrations of the quadruplicate methanol control samples differed by less than 3.9% for

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all compounds tested. For C8-alkylamines and C10-alkylamines, the PBS controls showed 0-30% lower

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concentrations than the methanol controls, with exception of the larger C10-benzalkonium (“C10-BAC”

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39%). For C12 surfactants, losses to autosampler surfaces were between 20 and 60% in PBS. If PBS

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references would have been used for C10-BAC as if they represented 100% of the available compound

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DMW would have been 0.2 log units lower than with methanol control samples. Using methanol controls,

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measured extracts of the glass walls in vials with beads showed that the residual impact of glass binding

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on DMW calculations was insignificant (0.011 log units).

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Concentrations of test compound were aimed at keeping the phospholipid/sorbed compound molar

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ratio above 60 to prevent possible electrostatic effects due to the accumulated charge in the

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membranes.37, 38 As shown in the full matrix of the final sorption isotherms for all tested compounds in

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SI-Figure S8, for nearly all of the selected surfactants, we have tested up to this maximum sorbed

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concentration in the membranes of ~40 mmol/kg to avoid electrostatic effects. Although the

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corresponding dissolved concentrations are orders of magnitude below the critical micelle

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concentrations (CMC, Table S1), the tested concentrations are most likely still well above highest

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environmental concentrations, but may be in the range of adverse effect concentrations. Concentrations

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of phospholipid in the test vial should result in sorbed fractions of at least 30%, to minimize effects of

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analytical uncertainties of Cwater on the mass balance calculations. The adapted TRANSILXL Intestinal

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Absorption kits allows for measuring DMW values above 1000 with buffer volumes of ~525 µL in the

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autosampler vials. The “TRANSILXL Intestinal Absorption kits for low affinity compounds” contains a

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factor of ~20 higher levels of beads per well, thereby allowing for measurements of DMW ≥ 50. The results

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from these two kits show overlapping sorption isotherms and concentration independent DMW, as shown

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for dihexylamine (“S2-C6”) in Figure 1. The sorption isotherms for C8- and C10-alkylamines also showed

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concentration independent DMW values, and overlapping sorption data with and without PBS renewal

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(Figure S1).

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However, for the C12-chain surfactants series measured without flushing off leaked phospholipids

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showed distinctly nonlinear isotherms, with higher DMW values for the highest concentrations in a series

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(samples with lowest amounts of SSLM beads), and no correspondence between two series spiked at

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different initial concentrations (Figure S1). For each individual series, the slope of a linear isotherms on

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the double logarithmic plots was >1. This result would cause doubt on the resulting KMW from the SSLM

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assay, and an apparent concentration dependent sorption affinity over such a narrow tested

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concentration range would have considerable deviations of the KMW at considerably lower (e.g., most

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environmental) and possibly higher concentrations (e.g., as applied, or at adverse effect levels). We

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found no evidence of influence of solvent from spiking solution, as data for secondary N-

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methyldodecylamine (“S12”) from methanol stock solutions overlapped with nonlinear results from

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stocks dissolved in water (Figure S2). Instead of a sorbent dilution series, we then tested primary

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dodecylamine (“P12”) with two series with constant concentration of SSLM material, spiked at six

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different concentrations (accompanied by six sets of methanol controls). Now, each series indicated

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concentration independent DMW (slope of 1 on logarithmic plot), but again the series with higher amount

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of SSLM material showed a lower sorption affinity (Figure S3). Evidently, higher SSLM material resulted

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in a higher detached amount of phospholipids from the beads leaking into the aqueous phase. If the

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sorbed amount of cationic surfactants to this phase significantly increases the measured Cwater, this leads

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to underestimation of the DMW. Using a common extension of Equation 1 for third phase systems 39, we

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modeled this effect by assuming a constantly leaked fraction (ƒleak) of the total amount of lipids coated on

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the beads, i.e., where the amount of lipids dispersed in the medium equals Vlipid ∙ ƒleak: ಲ೟೚೟ೌ೗ ×ವಾೈ ×ೇ೗೔೛೔೏ ಲ೟೚೟ೌ೗ ×ೇೢೌ೟೐ೝ ቇାቆೇ ቇ×௙೗೐ೌೖ ೢೌ೟೐ೝ శ಼ುಽ಺ುೈ ×ೇ೗೔೛೔೏ ೢೌ೟೐ೝ శವಾೈ ×ೇ೗೔೛೔೏

ቆೇ

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‫ܥ‬௪௔௧௘௥ =

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Experimental and modeled results are plotted for dodecylpyridinium (“PYR12“) in Figure 2, combining

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data for ‘unwashed’ samples (still including medium from the well plate, thus with ƒleak still present) with

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‘washed’ samples (with ƒleak mostly removed). As shown in Figure 2, the curve representing 1% of the

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phospholipids leaking from bilayers into the test medium (ƒleak = 0.01) approximated the observed

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experimental values that show a nonlinear curve. A modeled curve for fleak = 0.02 overestimated the

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observations. More plots comparing simulations for unwashed and washed beads for compounds with

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logDMW of 4.0, 4.5 and 5.0 can be found in the supporting information (Figure S4). All experimental data

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and modeling output suggest a phospholipid leakage of approximately 1% from the bilayers on the beads

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into the medium, which – if not removed from the test medium – will influence the sorption isotherms

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for compounds with a DMW > log 4.0.

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Varying the incubation time on the roller mixer (5-240 minutes) did not have a significant impact for fully

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dispersed SSLM solutions (Figure S5); 30 minutes was kept as standard. After centrifugation, the

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autosampler vials may stand for several hours in the autosampler before injection. The results of analysis

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after standing for 3, 12, or 21 h indicated no further leakage of phospholipids, as the measured

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surfactant concentrations and resulting sorption isotherm showed excellent overlap, whereas a

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significant fraction of leaked phospholipids would have increased the apparent concentrations in the

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medium (Figure S6). In test solution of pH 5.4 (“washed”), the DMW values of an ionizable tertiary N,N-

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dimethyldecylamine (“T10”) as well as of a permanently charged QAC N,N,N-trimethyldecylammonium

௏ೢೌ೟೐ೝ

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(“Q10”) were not statistically different from the DMW in PBS (pH7.4), indicating that the quaternary amine

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analogues as predicted by COSMOmic, and indicate that IAM-HPLC accounts insufficiently for effects of

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N-methylation. Considering that the SSLM data are obtained with relatively fluid phospholipid bilayers,

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and IAM-HPLC applies a covalently bound monolayer, we suggest applying corrective increments for the

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N-methyl head group contributions to KIAM values of IAM-HPLC, compared against the SSLM DMW values

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(δIAM-SSLM). Multiple linear regression results in δIAM-SSLM of 0.78 ± 0.07 (s.e.) log units for primary

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alkylamines (i.e.,KIAM values underestimate the KMW in bilayers), and 0.47 ± 0.09 log units for secondary

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amines. The δIAM-SSLM for tertiary amines is insignificant (-0.03 ± 0.10 log units), and very small for

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quaternary alkyltrimethylamines -0.11 ± 0.09. For COSMOmic δDMPC-SSLM amine type corrective

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increments were derived similarly. Interestingly, primary amines tended to be slightly overestimated by

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COSMOmic (0.17 ± 0.17 log units), while the other amine types were slightly underestimated (0.2-

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0.4±0.16 log units). COSMOmic seems to be capable of predicting the effect of N-methylation in

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phospholipid bilayers. Contrary to suggested correction of COSMOmic values reported previously,24 the

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SSLM data support the notion that the IAM-HPLC monolayer is the most probable source of

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inconsistency, creating scatter between IAM-HPLC and COSMOtherm. Using these δIAM-SSLM and δDMPC-SSLM

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corrective increments, there is strong correspondence between SSLM DMW values, the corrected IAM-

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HPLC KMW(IAM) values, and corrected COSMOmic KDMPC-W values, as shown in Figure 4B. All values are well

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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

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0.18 (COSMOmic).

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The three methods attribute similar effects of alkyl chain length, but also display a striking consistency in

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the difference between secondary dialkylamines and linear chain secondary alkylamine analogues. As

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discussed in Droge et al.,24 COSMOmic provides a mechanistic explanation for the relatively lower

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contribution of CH2 units to the DMW compared to single chain surfactants. Their design with two alkyl

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chains creates a steric effect, where the most favorable molecular position and orientation is mostly

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within the head group area of the phospholipid bilayer where – as a compromise – neither alkyl chain is

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aligned most favorably into the hydrophobic core region. The SSLM results confirm the difference in DMW

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between secondary linear amine N-methyldodecylamine “S12” and secondary dihexylamine “S2-C6” by

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2.24 log units, as was observed by Droge et al.24 for IAM-HPLC (1.93 log units), and COSMOmic (2.43 log

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units). For all three methods the difference observed is much larger than expected with one extra CH2

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fragment in S12. Between S2-C6 and dioctylamine (S2-C8), the SSLM DMW increased by 1.5 log units, while

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the regression model in equation 3 would predict a 2.36 log unit increase based on the addition of four

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CH2 units. COSMOmic also predicts a smaller value (1.73 log units) for the CH2 increment between S2-C6

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and S2-C8, while IAM-HPLC showed a 2.16 log unit difference (Table S3).

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DMW values for cationic surfactants compared to KOW predictions

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The most recent analysis of KMW values of neutral compounds,40 mostly obtained with liposomes, showed

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a strong correlation with KOW:

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݈‫ܭ݃݋‬ெௐ = 1.01(±0.02) ⋅ ݈‫ܭ݃݋‬ைௐ + 0.12(±0.07); n=156, SD=0.426, R2= 0.948

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There is only a poor correlation (R2 0.49) between the SSLM measured logDMW at pH 7.4 and the logKOW

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of the neutral primary, secondary, and tertiary amines, as shown in SI-Figure S10. The influence of the

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methyl units on the charged nitrogen are reversed for the two distribution coefficients. Each N-methyl

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unit increases the logKOW while it reduces the logDMW. Also, even though the sorption affinity of the

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protonated amines to the SSLM bilayer increases with linear alkyl chain length as the KOW predicts, the

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logDMW of the dialkylamines is orders of magnitude lower than the logKOW (for S2-C8 4.61 and 7.01,

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respectively). Typically for studies on the toxicokinetic properties of ionizable chemicals, a “logD

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approach” is followed, correcting the logKOW for speciation of the neutral amines at the tested pH 7.4

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(99.9% ionic for primary and secondary amines, 99.7% for tertiary amines). To derive a logD, however,

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the affinity of the ionic species for octanol needs to be known or predicted. In the absence of

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measurements, often either a constant factor of ~3 log units lower than logKOW is applied, or the affinity

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of the ionic species is ignored and the KOW is multiplied by the fraction of neutral species. As shown in

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Figure S10, both such logD approaches underestimate the sorption affinity to membranes by a up to a

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factor of 1000, and do not solve the poor correlation between logDMW and logKOW. Instead, logKOW could

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still be used to identify specific scaling factors to the difference in sorption affinity to a bilayer between

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neutral and ionic species, with the neutral affinity still based on equation 4. Table S3 lists the KMW values

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for the neutral primary, secondary and tertiary amine species calculated via equation 4 (logKOW predicted

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by ACD/Labs). Accordingly, the average difference between charged DMW,PBS and neutral KMW species

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(ΔMW) for primary amines is -0.05, so the affinity of charged primary amines is larger than the neutral

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species. For the three linear single chain N-methylalkylamines ΔMW is 0.44, for the linear N,N-

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dimethylalkylamines, the ΔMW is 1.25. These values closely correspond to the scaling factors suggested

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for the bioaccumulation model for ionogenic compounds (BIONIC) proposed by Armitage et al.,4 which

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were 0.3, 0.5 and 1.25 for primary, secondary and tertiary amines, respectively, based on data sets of

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measured KMW values for both ionic and neutral species. However, the ΔMW is 1.90 and 2.55 for the two

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dialkylamines S2-C6 and S2-C8, respectively, much higher than the 0.44 derived with the other secondary

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amines. The examples of the dialkylamines show that applying a single ΔMW scaling factor for all

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secondary amines to calculate the DMW,PBS from the KOW relationship in equation 4, can lead to erroneous

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values. Similarly, this exercise shows that KOW is not an adequate single descriptor to model the DMW

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values for ionized compounds. Measured KMW values with TRANSIL, KPLIPW values with IAM-HPLC, and

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even simulated KDMPC values with COSMOmic, provide much more accurate and more mechanistically

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sound estimates compared to KOW-based regressions.

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Perspective on SSLM assay measurements and associated DMW estimates

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This study showed that the adapted SSLM protocol, with SSLM beads transferred from a well plate to

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autosampler vials, facilitated the analysis, improved recovery in methanol reference vials, and gained

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experimental control over the aqueous phase. The medium renewal removed third phase liposome

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artefacts, and allowed for altered pH of the test medium. The problem of detached phospholipids in the

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original SSLM medium became significant for all compounds with a DMW higher than log 4, while using

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methanol controls instead of PBS controls seems mostly important for hydrophobic organic cations, and

396

surfactants in general.41 The experimental determination of DMW becomes problematic above log 5.5,

397

because with the required phospholipid/sorbate molar ratio >60, the aqueous phase concentrations

398

obtained directly from the autosampler vials, are nearing LC-MS/MS detection limits. This means that to

399

measure DMW values for cationic surfactants with alkyl chains longer than C12, and dialkylamines with

400

alkyl chains longer than C8, either cumbersome solid phase extraction steps from larger test volumes are

401

required – which may include uncontrolled adsorption losses – or sorption affinities need to be

402

extrapolated with the model, or from series of smaller analogues. Alternatively, COSMOmic seems to

403

provide a realistic and accurate predictive tool for cationic surfactants, which allows for extrapolations to

404

longer chain cationic surfactants (Table 1) and slight alterations of the head groups. For example, the

405

logKDMPC-W for didecyldimethylammonium chloride (DDAC), a commonly used biocide,42 and

406

cetylpyridinium, a commonly used antiseptic, are 7.53 and 7.03 (Table 1), which are both experimentally

407

not feasible to measure with currently applied IAM-HPLC and SSLM assays. The logKDMPC-W for

408

behentrimonium, a trimethylalkylammonium compound with a chain length of C22 which is used in many

409

hair cair products and which has been detected in marine sediments,43 is 10.3. The dialkylquat DODMAC

410

(mixed chainlength of C16/C18), banned for certain uses in the EU,21 has a predicted logKDMPC-W of 15.5. For

411

these examples, the very high predicted sorption affinities to cell membrane should be considered in risk

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assessment models (e.g. for bioaccumulation4) alongside strong sorption affinities to environmental

413

particles,6-9 which strongly reduces the bioavailability, and thus result in relatively low accumulation from

414

the environment into tissues.34,44-46

415

ACKNOWLEDGEMENTS: This study was funded by Unilever, Safety & Environmental Assurance Center

416

(SEAC), Colworth Science Park, Sharnbrook, United Kingdom. We thank Joop Hermens for valuable

417

suggestions and comments.

418

SUPPORTING INFORMATION: Includes additional tables with information on chemicals, LC-MS/MS

419

settings, and sorption isotherm details, as well as Figures with detailed sorption data under various

420

conditions.

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36. Bittermann, K.; Spycher, S.; Endo, S.; Pohler, L.; Huniar, U.; Goss, K. U.; Klamt, A., Prediction of phospholipid-water partition coefficients of ionic organic chemicals using the mechanistic model COSMOmic. .J Phys. Chem. B 2014, 118, (51), 14833-42. 37. Austin, R. P.; Barton, P.; Davis, A. M.; Fessey, R. E.; Wenlock, M. C., The thermodynamics of the partitioning of ionizing molecules between aqueous buffers and phospholipid membranes. Pharm. Res. 2005, 22, (10), 1649-1657. 38. Seelig, A.; Allegrini, P. R.; Seelig, J., Partitioning of local anesthetics into membranes: surface charge effects monitored by the phospholipid head-group. Biochim. Biophys. Acta 1988, 939, (2), 267-76. 39. Schrap, S. M.; Opperhuizen, A., On the contradictions between experimental sorption data and the sorption partitioning model. Chemosphere 1992, 24, (9), 1259-1282. 40. Endo, S.; Escher, B. I.; Goss, K. U., Capacities of membrane lipids to accumulate neutral organic chemicals. Environ. Sci. Technol. 2011, 45, (14), 5912-21. 41. Droge, S. T. J.; Sinnige, T. L.; Hermens, J. L. M., Analysis of freely dissolved alcohol ethoxylate homologues in various seawater matrixes using solid-phase microextraction. Anal. Chem. 2007, 79, (7), 2885-2891. 42. Juergensen, L.; Busnarda, J.; Caux, P.; Kent, R.A., Fate, behavior, and aquatic toxicity of the fungicide DDAC in the Canadian environment. Environ. Toxicol. 2000, 15, 174-200. 43. Lara-Martin, P.A.; Li, X.; Bopp, R.F.; Brownawell, B.J., Occurrence of alkyltrimethylammonium compounds in urban estuarine sediments: behentrimonium as a new emerging contaminant. Environ. Sci. Technol. 2010, 44, (19), 7569-7575. 44. Comber, S.D.W.; Rule, K.L.; Conrad, A.U.; Höss, S.; Webb, S.F.; Marshall, S., Bioaccumulation and toxicity of a cationic surfactant (DODMAC) in sediment dwelling freshwater invertebrates. Environ. Poll. 2008, 153, (1), 184-191. 45. Van Wijk, D.; Gyimesi-Van Den Bos, M.; Garttener-Arends, I.; Geurts, M.; Kamstra, J.; Thomas, P., Bioavailability and detoxification of cationics: I. Algal toxicity of alkyltrimethyl ammonium salts in the presence of suspended sediment and humic acid. Chemosphere 2009, 75, (3), 303-309 46. Thomas, P.C.; Velthoven, K.; Geurts, M.; Van Wijk, D., Bioavailability and detoxification of cationics: II. Relationship between toxicity and CEC of cationic surfactants on Caenorhabditis elegans (Nematoda) in artificial and natural substrates. Chemosphere 2009, 75, (3), 310-318. 47. Hou, W. C.; Moghadam, B. Y.; Corredor, C.; Westerhoff, P.; Posner, J. D., Distribution of functionalized gold nanoparticles between water and lipid bilayers as model cell membranes. Environ. Sci. Technol. 2012, 46, (3), 1869-1875. 48. Loidl-Stahlhofen, A.; Ulrich, A. S.; Kaufmann, S.; Bayerl, T. M., Protein binding to supported lecithin bilayers controlled by the lipid phase state: A new concept for highly selective protein purification. Eur. Biophys. J. 1996, 25, (2), 151-153.

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a

Table 1. LogDMW values for all compounds tested with the SSLM assay , as well as uncorrected IAM-HPLC logKIAM,intr measurements and COSMOmic predicted logKDMPC-W values (no offset correction) Alkyl chain

C6

C8

C10

C12

C14 C16 C18 C22

Method

SSLM IAM COSMO SSLM IAM COSMO SSLM IAM COSMO SSLM IAM COSMO SSLM COSMO COSMO COSMO COSMO

Primary amine (P)

1.32 2.63 3.10 2.30 3.71 4.30 3.55 4.83 5.58

Secondary amines (S)

Tertiary amines (T)

1.45 2.35 2.35 2.53 3.65 3.59 3.70 5.30

6.01

1.92 2.76 2.33 3.01 3.98 3.59 4.14 5.39 4.81 5.28

7.15 8.31 9.43

6.42 7.56 8.74

5.89 7.07 8.29

4.76

Trimethyl Benzalkonium Pyridinium Secondary ammonium cations cations dialkyl(Q) (BAC) (PYR) amines (S2)

1.08 2.18 2.18 2.18 3.34 3.44 3.30 4.35 4.57 4.47 5.46 5.61 6.72 7.94 10.1

2.12 2.42 1.87 3.11 3.30 2.96 4.01 4.47 4.05

3.15 2.88 2.77 4.65 5.04 4.34

6.26

7.53

8.40

9.79

4.89 5.14

4.77

6.65 7.90 9.01

5.90 7.03

a

550

Quaternary dialkylammonium (Q2)

12.06 C16/C18 15.51

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.

551

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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 logDMW,PBS of 3.15 (95% CI 3.10-3.20). Figure 1 73x67mm (300 x 300 DPI)

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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 logDMW,PBS of 4.89 (95% c.i. 4.84-4.95) Figure 2 76x73mm (300 x 300 DPI)

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Caption : Figure 3. Observed and predicted logDMW,PBS values for single linear chain cationic surfactants using equation 3 (P=primary amines, S=secondary amines, T=tertiary amines, Q=trimethylalkylammonium compounds, BAC=benzalkonium chloride compounds). Figure 3 61x46mm (300 x 300 DPI)

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Figure 4. Experimental logDMW,PBS values with TRANSIL bilayers plotted against experimental logKIAM results from the IAM-HPLC monolayer and simulated logKDMPC-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. Figure 4 80x40mm (300 x 300 DPI)

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