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  <front>
    <journal-meta><journal-id journal-id-type="publisher">ACP</journal-id><journal-title-group>
    <journal-title>Atmospheric Chemistry and Physics</journal-title>
    <abbrev-journal-title abbrev-type="publisher">ACP</abbrev-journal-title><abbrev-journal-title abbrev-type="nlm-ta">Atmos. Chem. Phys.</abbrev-journal-title>
  </journal-title-group><issn pub-type="epub">1680-7324</issn><publisher>
    <publisher-name>Copernicus Publications</publisher-name>
    <publisher-loc>Göttingen, Germany</publisher-loc>
  </publisher></journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.5194/acp-21-1325-2021</article-id><title-group><article-title>Ozonolysis of fatty acid monolayers at the air–water interface: organic films may persist at the surface of atmospheric aerosols</article-title><alt-title>Ozonolysis of fatty acid monolayers at the air–water interface</alt-title>
      </title-group><?xmltex \runningtitle{Ozonolysis of fatty acid monolayers at the air--water interface}?><?xmltex \runningauthor{B. Woden et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Woden</surname><given-names>Benjamin</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Skoda</surname><given-names>Maximilian W. A.</given-names></name>
          
        <ext-link>https://orcid.org/0000-0003-0086-2965</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Milsom</surname><given-names>Adam</given-names></name>
          
        <ext-link>https://orcid.org/0000-0003-3875-9015</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Gubb</surname><given-names>Curtis</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff4">
          <name><surname>Maestro</surname><given-names>Armando</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Tellam</surname><given-names>James</given-names></name>
          
        <ext-link>https://orcid.org/0000-0001-9243-1323</ext-link></contrib>
        <contrib contrib-type="author" corresp="yes" rid="aff3 aff5">
          <name><surname>Pfrang</surname><given-names>Christian</given-names></name>
          <email>c.pfrang@bham.ac.uk</email>
        <ext-link>https://orcid.org/0000-0001-9023-5281</ext-link></contrib>
        <aff id="aff1"><label>1</label><institution>Department of Chemistry, University of Reading, Whiteknights, Reading, RG6 6AD, UK</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>ISIS Neutron and Muon Source, Science and Technology Facilities
Council,<?xmltex \hack{\break}?> Rutherford Appleton Laboratory, Didcot, OX11 0QX, UK</institution>
        </aff>
        <aff id="aff3"><label>3</label><institution>School of Geography, Earth and Environmental Sciences, University of Birmingham, Edgbaston, Birmingham, B15 2TT, UK</institution>
        </aff>
        <aff id="aff4"><label>4</label><institution>Institut Laue–Langevin (ILL), 71 Avenue des Martyrs, Grenoble, 38000, France</institution>
        </aff>
        <aff id="aff5"><label>5</label><institution>Department of Meteorology, University of Reading, Whiteknights Road, Reading, RG6 6BG, UK</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Christian Pfrang (c.pfrang@bham.ac.uk)</corresp></author-notes><pub-date><day>1</day><month>February</month><year>2021</year></pub-date>
      
      <volume>21</volume>
      <issue>2</issue>
      <fpage>1325</fpage><lpage>1340</lpage>
      <history>
        <date date-type="received"><day>16</day><month>July</month><year>2020</year></date>
           <date date-type="rev-request"><day>12</day><month>August</month><year>2020</year></date>
           <date date-type="rev-recd"><day>29</day><month>October</month><year>2020</year></date>
           <date date-type="accepted"><day>20</day><month>November</month><year>2020</year></date>
      </history>
      <permissions>
        <copyright-statement>Copyright: © 2021 </copyright-statement>
        <copyright-year>2021</copyright-year>
      <license license-type="open-access"><license-p>This work is licensed under the Creative Commons Attribution 4.0 International License. To view a copy of this licence, visit <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">https://creativecommons.org/licenses/by/4.0/</ext-link></license-p></license></permissions><self-uri xlink:href="https://acp.copernicus.org/articles/.html">This article is available from https://acp.copernicus.org/articles/.html</self-uri><self-uri xlink:href="https://acp.copernicus.org/articles/.pdf">The full text article is available as a PDF file from https://acp.copernicus.org/articles/.pdf</self-uri>
      <abstract><title>Abstract</title>
    <p id="d1e164">Ozonolysis of fatty acid monolayers was studied to understand the
fate of organic-coated aerosols under realistic atmospheric conditions.
Specifically, we investigated the effects of temperature and salinity on the degradation of oleic acid at the air–water interface and the persistence of
the aged surfactant film at the surface. The presence of a residual film is
of atmospheric importance, as surface monolayers affect the physical
properties of the droplets and because of the role they play in cloud
formation. This occurs via several effects, most notably via surface tension
reduction. The interplay between atmospheric aerosol loading and the
formation, nature, and persistence of clouds is a key uncertainty in climate
modelling.</p>
    <p id="d1e167">Our data show that a residual surface film, which we suspect to be formed of
nonanoic acid and a mixture of azelaic and 9-oxononanoic acids, is retained
at the interface after ozonolysis at near-zero temperatures but not at room
temperature. Given the low-temperature conditions used here are
atmospherically realistic, the persistence of a product film must be
considered when assessing the impact of unsaturated fatty acid partitioned
to the air–water interface. The presence of stable (non-oxidisable)
reaction products also opens the possibility of build-up of inert monolayers
during the aerosol life cycle with potential implications for cloud
formation. Furthermore, we measured the kinetic behaviour of these films and
found that the reactions are not significantly affected by the shift to a
lower temperature with rate coefficients determined to be (2.2 <inline-formula><mml:math id="M1" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.4) <inline-formula><mml:math id="M2" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M3" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M4" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M5" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at 21 <inline-formula><mml:math id="M6" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M7" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C and
(2.2 <inline-formula><mml:math id="M8" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.2) <inline-formula><mml:math id="M9" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M10" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M11" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M12" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at 2 <inline-formula><mml:math id="M13" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M14" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Introduction</title>
      <p id="d1e307">Organic films are formed at the surfaces of aerosol particles in the
atmosphere (Gill et al.,
1983; Ellison et al., 1999; Sareen et al., 2013; Nozière et al., 2014 
Kroflič et al., 2018; Geŕard et al., 2019), and the partitioning of organic
components in this manner changes the physical properties of the aerosol
particle and its chemical reactivity (Rudich, 2003; Ruehl et al., 2016;
Ovadnevaite et al., 2017). A key review
(Donaldson and Vaida, 2006) has brought
together various emerging trends in the study of these films and their
relevance to atmospheric processes. An important area of interest regarding
these films concerns the interactions between atmospheric aerosol particles
and clouds. This relationship is complex and difficult to measure or predict
(Stevens and Feingold, 2009), and resolving the role
played by organic monolayers at the surface of aerosol particles is part of
solving this puzzle. The organic species that are contained in these surface
films oxidise in the atmosphere and may produce low-volatility products that
form secondary organic aerosols. If the oxidation of these species is
prevented, accelerated, or otherwise modified by the partitioning of the
reactant into a surface monolayer, then this will have<?pagebreak page1326?> implications for the
contribution of that reactant to aerosol loading. More importantly, the
presence of a surface monolayer changes the physical and chemical properties
of the aerosol particle itself.</p>
      <p id="d1e310">The present study focuses on monolayers at the air–water interface as would
be seen on aqueous aerosol droplets, but the concept is broadly
transferrable to any aerosol particle with an organic film coating. These
monolayers are relevant, as they decrease the surface tension of water
(Donaldson and Vaida, 2006;
Ambaum, 2010); the surface tension of aqueous droplets plays a key role in
the growth and formation of clouds (Ambaum, 2010;
Ovadnevaite et al., 2017). Furthermore, the monolayer can act as a barrier
to water uptake, retard droplet evaporation, and inhibit the transfer of
atmospheric species between the air and water phases
(Rideal,
1924; La Mer, 1962; La Mer et al., 1964; Gaines, 1966; Garrett, 1971; Ray et al., 1991;
Benjamin, 1996; Barnes, 1997; Li et al., 2019). It can also act as a 2D
solvent for normally water-insoluble species that could not partition to a
water aerosol or modify the solvation behaviour of soluble species
(Tomoaia-Cotisel
and Cadenhead, 1991; Cohen Stuart et al., 1996; Mmereki and Donaldson, 2002;
Mmereki et al., 2003; Gilman et al., 2004). Organic monolayers can also act
as efficient ice-nucleating particles (see Knopf et al., 2018; Knopf and
Forrester, 2011; Zobrist et al., 2007; Cantrell and Robinson, 2006).</p>
      <p id="d1e313">This catalogue of effects upon the aerosol particle caused by the presence
of an organic monolayer coating shows the importance of establishing the
lifetime and ageing of these monolayers in the atmosphere, and this has been
the focus of previous research
(e.g.
Thornton and Abbatt, 2005; Hung et al., 2005; Knopf et al., 2005; McNeill et
al., 2006; Voss et al., 2007; Knopf et al., 2007; Cosman et al., 2008; Gross
et al., 2009; King et al., 2009; Pfrang et al., 2014; Sebastiani et al.,
2018).</p>
      <p id="d1e316">Oleic acid has been a monolayer component of particular interest, as it is a
major contributor to both anthropogenic organic emissions – it is mostly
produced by meat cooking (Shrivastava et al., 2007) and
is the dominant component of such emissions
(Allan et al., 2010) – and
biogenic marine aerosols
(Tervahattu
et al., 2002; Fu et al., 2013). Its ubiquity in such aerosols has allowed it
to serve as a benchmark molecule for more complex mixtures of organic
surfactant produced by such anthropogenic activity
(Zahardis and Petrucci, 2007). While there are
numerous studies of pure oleic acid or high-oleic-acid-content droplets and
their oxidation reactions (e.g. King et al.,
2004; Voss et al., 2007; Last et al., 2009; Pfrang et al., 2011, 2017a), work on
the oxidation of an oleic acid monolayer at the air–water interface in
particular has been comparatively scarce
(King
et al., 2009; Skoda et al., 2017; Sebastiani et al., 2018).</p>
      <p id="d1e320">Ozone (O<inline-formula><mml:math id="M15" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>) and nitrate radicals (NO<inline-formula><mml:math id="M16" display="inline"><mml:mrow><mml:msubsup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn><mml:mi mathvariant="normal" class="Radical">⚫</mml:mi></mml:msubsup></mml:mrow></mml:math></inline-formula>) are important
night-time oxidants
(e.g.
Hung et al., 2005; Gross et al., 2009; Sebastiani et al., 2018; Woden et
al., 2018), while O<inline-formula><mml:math id="M17" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> and hydroxyl radicals (<inline-formula><mml:math id="M18" display="inline"><mml:msup><mml:mi/><mml:mi mathvariant="normal" class="Radical">⚫</mml:mi></mml:msup></mml:math></inline-formula>OH) are the
key daytime oxidants (see Chen et al., 2020, for a recent study of
heterogenous OH reactions on organic aerosols). Of these three primary
atmospheric oxidants O<inline-formula><mml:math id="M19" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> is the only one present during the day and night, and the present study is focused on ozonolysis, i.e. oxidation by
O<inline-formula><mml:math id="M20" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>.</p><?xmltex \setfigures?><?xmltex \setschemes?><?xmltex \floatpos{t}?><fig id="Ch1.F1" specific-use="star"><?xmltex \currentcnt{1}?><?xmltex \def\figurename{Scheme}?><label>Scheme 1</label><caption><p id="d1e384">Oleic acid ozonolysis reaction scheme. We used both fully and
half-deuterated oleic acid samples, granting us the ability to create
different contrasts for analysis by neutron reflectometry. In the fully
deuterated (<inline-formula><mml:math id="M21" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>) variant of oleic acid, both the head portion (purple)
and tail portion (teal) of the molecule are deuterated. In the partially
deuterated (<inline-formula><mml:math id="M22" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>) variant of oleic acid, only the tail portion (teal) is
deuterated. The colouring of the products and intermediates indicates the
fate of the two portions of the oleic acid molecule and demonstrates that,
when <inline-formula><mml:math id="M23" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid is oxidised, two products (nonanal and nonanoic
acid) are deuterated and two (azelaic acid and 9-oxononanoic acid) are not.</p></caption>
        <?xmltex \igopts{width=483.69685pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-s01.png"/>

      </fig>

      <p id="d1e426">The initial reaction of O<inline-formula><mml:math id="M24" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> with oleic acid is chemically well
understood and is laid out in Scheme 1
(compare King et al., 2009;
see also Gallimore et al., 2017). It proceeds via an attack on the
carbon–carbon double bond at the centre of the molecule. The two reaction
pathways resulting from the two possible collapses of the molozonide lead to
a total of four initial reaction products. These products are nonanoic acid,
nonanal, 9-oxononanoic acid, and azelaic acid
(Zahardis and Petrucci, 2007). One
detailed kinetic study on bulk-like oleic acid (Thornberry and Abbatt, 2004)
identifies nonanal as major product with a yield of 0.50 (<inline-formula><mml:math id="M25" display="inline"><mml:mo lspace="0mm">±</mml:mo></mml:math></inline-formula>0.10) for
the oleic acid ozonolysis using a coated-wall tube (0.6 mm thick oleic acid
layer). The authors found only a small temperature dependence of the uptake
coefficients down to 263 K. The fate of these products after the ozonolysis
of an oleic acid monolayer however is the subject of debate
(Voss et al., 2007;
King et al., 2009).</p>
      <p id="d1e445">The presence of a product partitioned to the (air–water) interface after
reaction is the most important question for atmospheric impact, as a
monolayer remaining after ozonolysis may perpetuate the modifications to the
properties of an aerosol droplet due to the persistence of the organic
character at the air–water interface even after ozonolysis
(Ellison et al.,
1999; Donaldson and Vaida, 2006).</p>
      <p id="d1e448">The aim of this study is to extend the understanding of oleic acid monolayer
ozonolysis under atmospherically relevant conditions by investigating the
impact of low temperatures and saline subphases. King et al. (2009)
investigated a variety of saline subphases but did not study differences in
ozonolysis behaviour between the monolayers spread upon them at room
temperature, and to our knowledge no studies have yet investigated the
effects of low temperatures (<inline-formula><mml:math id="M26" display="inline"><mml:mo lspace="0mm">&lt;</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M27" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>), which are common in
the lower troposphere (Grotjahn, 2015), where these
reactions occur. To this end, we investigated the behaviour at ca. 0<inline-formula><mml:math id="M28" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>, i.e. near the ice melting temperature (referred to as
near-zero temperatures in this paper), but it should be noted that
aqueous NaCl solutions will experience a slight ice melting point depression
(see phase diagram and previous studies, in particular Koop et al., 2000a, b) and that water droplets in the atmosphere will
freeze at significantly lower temperatures. Near-zero temperatures are more
frequently encountered in the atmosphere than room-temperature conditions
used in other studies, especially in temperate and polar regions as well as
in the free troposphere, possibly with the exception of the boundary layer in
the tropics. Our neutron reflectometry (NR) study also incorporates
simultaneous characterisation by infrared reflection absorption spectroscopy
(IRRAS) as a secondary analysis technique, using a bespoke reaction/analysis
chamber recently developed for this purpose
(Skoda et al., 2017).</p>
</sec>
<?pagebreak page1327?><sec id="Ch1.S2">
  <label>2</label><title>Methodology</title>
      <p id="d1e484">This research was performed on the specular neutron reflectometry
instruments INTER at the ISIS Neutron and Muon Source and FIGARO at Institut Laue–Langevin (ILL) and builds on previous work by this research group on
the oxidation of floating monolayers at the air–water interface performed
at these facilities
(Pfrang
et al., 2014; Sebastiani et al., 2015; Skoda et al., 2017; Sebastiani et
al., 2018; Woden et al., 2018).</p>
<sec id="Ch1.S2.SS1">
  <label>2.1</label><title>Neutron reflectometry</title>
      <p id="d1e494">A review paper (Lu et al., 2000) details how
neutron reflectometry can be used to determine the surface concentration of
organic films present as a monolayer at the air–water interface. In short,
neutron reflectivity depends on the differences between concentrations of
atoms with a characteristic neutron scattering length in adjacent thin
layers of material. Simplifications of the equations describing this system
are possible when studying just one layer (the organic monolayer) at the
interface between air – which essentially has a scattering length density
(SLD) of zero – and a “null-reflecting” or “air-contrast-matched” subphase (a
subphase prepared to have a neutron SLD of zero, matching that of air). The null-reflecting matched water was prepared as a solution of D<inline-formula><mml:math id="M29" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O (99.9 %
atom D; Sigma-Aldrich) 8.8 % <inline-formula><mml:math id="M30" display="inline"><mml:mrow><mml:mi>v</mml:mi><mml:mo>/</mml:mo><mml:mi>v</mml:mi></mml:mrow></mml:math></inline-formula> in 18.2 M<inline-formula><mml:math id="M31" display="inline"><mml:mi mathvariant="normal">Ω</mml:mi></mml:math></inline-formula> H<inline-formula><mml:math id="M32" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O. Null-reflecting sodium chloride solution subphase was prepared with 35 g NaCl
(<inline-formula><mml:math id="M33" display="inline"><mml:mo lspace="0mm">&lt;</mml:mo></mml:math></inline-formula> 99 %; Sigma-Aldrich) in 900 mL H<inline-formula><mml:math id="M34" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O and 58 mL D<inline-formula><mml:math id="M35" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O.
This preparation compensates for the scattering length of the salt ions with
a slightly different H<inline-formula><mml:math id="M36" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O <inline-formula><mml:math id="M37" display="inline"><mml:mo>/</mml:mo></mml:math></inline-formula> D<inline-formula><mml:math id="M38" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O ratio.</p>
      <p id="d1e585">Details of the experimental setup and procedure can be found in Skoda et al. (2017). In short, a purpose-built aluminium gas flow cell with a volume of
approximately 1.5 L was used, which accommodated a PTFE liquid trough with
inner dimensions of 238 mm <inline-formula><mml:math id="M39" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 70 mm. The sample stage was equipped
with passive and active anti-vibration control. The reaction chamber was
mounted on the sample stage and interfaced with the gas setup. The PTFE
trough was filled with 90 mL of null-reflecting water. Monolayers were spread using 20–40 <inline-formula><mml:math id="M40" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L of the spreading solutions in chloroform, leaving a monolayer of the
dissolved species after evaporation of the solvent. A dry oxygen flow of 1.2 L min<inline-formula><mml:math id="M41" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> was continuously present, providing a low (<inline-formula><mml:math id="M42" display="inline"><mml:mo lspace="0mm">&lt;</mml:mo></mml:math></inline-formula> 10 %) relative humidity (RH) and
avoiding any build-up of gas-phase products that would not be consistent
with atmospheric conditions.<?pagebreak page1328?> Thanks to the low RH, we did not observe any
condensation within the reaction chamber or windows throughout the
experiments. Data were recorded for a few minutes before O<inline-formula><mml:math id="M43" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> was
admitted into the chamber. O<inline-formula><mml:math id="M44" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> was then generated continuously by
exposing the O<inline-formula><mml:math id="M45" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula> flow to UV light. The height of the air–liquid
interface was aligned with respect to the neutron beam using a Keyence
laser displacement sensor (model no. LK-G402), which was coupled into the
sample chamber via a quartz window to allow automated height adjustment
during the measurements. Height adjustments over a 2 h experiment were
always less than 0.15 mm for a water height of ca. 5 mm in the trough. The
reflectivity (fraction of incident neutrons reflected; <inline-formula><mml:math id="M46" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula>) varies as a
function of the energy and reflection angle of the incident neutrons
(expressed as momentum transfer, <inline-formula><mml:math id="M47" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula>) and the SLD (<inline-formula><mml:math id="M48" display="inline"><mml:mi mathvariant="italic">ρ</mml:mi></mml:math></inline-formula>) and thickness
(<inline-formula><mml:math id="M49" display="inline"><mml:mi mathvariant="italic">τ</mml:mi></mml:math></inline-formula>) of the monolayer as expressed in Eq. (1)
(based on Lu et al., 2000).
            <disp-formula id="Ch1.E1" content-type="numbered"><label>1</label><mml:math id="M50" display="block"><mml:mrow><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mrow><mml:msup><mml:mi>Q</mml:mi><mml:mn mathvariant="normal">4</mml:mn></mml:msup><mml:mi>R</mml:mi></mml:mrow><mml:mrow><mml:mn mathvariant="normal">16</mml:mn><mml:msup><mml:mi mathvariant="italic">π</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:mrow></mml:mfrac></mml:mstyle><mml:mo>≅</mml:mo><mml:mn mathvariant="normal">4</mml:mn><mml:msup><mml:mi mathvariant="italic">ρ</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup><mml:msup><mml:mi mathvariant="normal">sin</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mrow><mml:mi>Q</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow><mml:mn mathvariant="normal">2</mml:mn></mml:mfrac></mml:mstyle></mml:mrow></mml:math></disp-formula>
          The SLD and layer thickness characteristic of the system can then be
inferred from the relationship between reflectivity and momentum transfer as
measured by the instrument. The two parameters are fitted over the whole
<inline-formula><mml:math id="M51" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> range as a combined <inline-formula><mml:math id="M52" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> value, which corresponds to a surface
concentration of scattering length, from which the surface concentration of
oleic acid can be determined as the scattering length of oleic acid is known
(<inline-formula><mml:math id="M53" display="inline"><mml:mrow><mml:mi>b</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">315</mml:mn></mml:mrow></mml:math></inline-formula> fm). Reflectivity curves of <inline-formula><mml:math id="M54" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M55" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> are collected at 20 s intervals
throughout the reaction and fitted using MOTOFIT
(Nelson, 2006) to give <inline-formula><mml:math id="M56" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> values for
each time slice. These fitted <inline-formula><mml:math id="M57" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> values can be converted into
surface concentration (<inline-formula><mml:math id="M58" display="inline"><mml:mrow><mml:mi mathvariant="normal">Γ</mml:mi><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula> values for oleic acid
(Eq. 2, based on Lu et al., 2000).
            <disp-formula id="Ch1.E2" content-type="numbered"><label>2</label><mml:math id="M59" display="block"><mml:mrow><mml:mi mathvariant="normal">Γ</mml:mi><mml:mo>=</mml:mo><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mrow><mml:mi mathvariant="italic">τ</mml:mi><mml:mi mathvariant="italic">ρ</mml:mi></mml:mrow><mml:mi>b</mml:mi></mml:mfrac></mml:mstyle></mml:mrow></mml:math></disp-formula>
          In order for the layer to stand out sufficiently from the other phases, a
deuterated form, <inline-formula><mml:math id="M60" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid, was used. Spreading onto an aqueous
subphase will cause the acidic deuterium to be exchanged with the subphase,
so we use the scattering length of oleic acid with 33 deuterium atoms (315 fm) to calculate the surface concentration from <inline-formula><mml:math id="M61" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> values. For
product identification studies, we used custom-synthesised half-deuterated
<inline-formula><mml:math id="M62" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid.</p>
</sec>
<sec id="Ch1.S2.SS2">
  <label>2.2</label><title>Reaction chamber for simultaneous infrared reflection absorption
spectroscopy (IRRAS)</title>
      <p id="d1e860">The reactions were carried out in a bespoke chamber developed by this
research group. The chamber is designed to provide a controlled and confined
environment in which the monolayer can be oxidised by a gas-phase oxidant
while under analysis by both neutron reflectometry and IRRAS. The
integration of IRRAS analysis in situ during the neutron reflectometry experiment
is non-trivial, and the entire analysis and reaction setup is described in
detail in a method paper (Skoda et al.,
2017). For this study it had been further developed to allow for cooling of
the subphase in order to access relevant atmospheric temperature
conditions. IRRAS integration is primarily intended to facilitate the study
of mixed monolayers, in which one component can be deuterated (for neutron
reflectometry) and the other left non-deuterated (and thus easily measurable
by IRRAS). This work focuses on a film composed solely of oleic acid, so the
IRRAS analysis served as an additional semi-quantitative method to follow
the oleic acid component rather than as a method to follow non-deuterated
film components (Skoda et al., 2017).
During experiments using <inline-formula><mml:math id="M63" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid, IRRAS data were sensitive to
the deuterated and non-deuterated halves of the molecule (via the C–D and
C–H absorption bands, respectively). The IRRAS equipment was only available
at the INTER beamline, given the large and flexible sample environment
available at that instrument.</p>
      <p id="d1e874">Baseline-corrected integrations under C–D peaks (symmetric and asymmetric
stretch) provide a series of peak area against time traces for each
reaction, which reflect the presence or absence of C–D chains at the surface
and traces their evolution throughout the reaction.</p>
      <p id="d1e877">While IRRAS can measure deuterated components (the infrared absorbance bands are
shifted to a lower wavenumber, distinguishing them from the absorbance bands
associated with non-deuterated components), the sensitivity in this region
is much lower, as these bands are weaker and more affected by the gas-phase
atmosphere above the organic film. This meant that the IRRAS measurements
could not distinguish the residues left at low temperatures from background
noise. Figure S13 in the Supplement shows an example of IRRAS
data from an ozonolysis experiment on INTER.</p>
</sec>
<sec id="Ch1.S2.SS3">
  <label>2.3</label><title>Materials</title>
      <p id="d1e888"><inline-formula><mml:math id="M64" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid was used (one batch custom synthesised by the ISIS
Deuteration Facility and one batch purchased from Sigma-Aldrich at 98 %
atom D; 99.9 %); the half-deuterated <inline-formula><mml:math id="M65" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid was produced by
the ISIS Deuteration Facility; O<inline-formula><mml:math id="M66" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> was produced for the reaction using a
commercial Pen-Ray ozoniser (UVP Ltd, Cambridge) to ozonise a stream of
O<inline-formula><mml:math id="M67" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula> (99.999 %; BOC Ltd) regulated to a flow of 1.2 L min<inline-formula><mml:math id="M68" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> (20 cm<inline-formula><mml:math id="M69" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M70" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) using an electronic mass flow controller to an O<inline-formula><mml:math id="M71" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>
concentration of (1.43 <inline-formula><mml:math id="M72" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.05) <inline-formula><mml:math id="M73" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M74" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">13</mml:mn></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M75" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>; the
ozoniser was calibrated offline using UV–Vis absorption at 254 nm and an
absorption cross-section value of 1.13 <inline-formula><mml:math id="M76" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M77" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">17</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M78" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>
(Daumont et al., 1992). Mixing ratios of ozone (in
O<inline-formula><mml:math id="M79" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>) in the chamber were in the range 126–2010 ppb, so that we were
working in large excess of O<inline-formula><mml:math id="M80" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> compared to the organic monolayer, and
[O<inline-formula><mml:math id="M81" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>] remained approximately constant during the reaction.</p><?xmltex \hack{\newpage}?>
</sec>
</sec>
<?pagebreak page1329?><sec id="Ch1.S3">
  <label>3</label><title>Results and discussion</title>
      <p id="d1e1077">Prior to the ozonolysis studies we characterised the stability of the oleic
acid monolayers at room and reduced temperatures (see Sect. S1 of the
Supplement with <inline-formula><mml:math id="M82" display="inline"><mml:mi mathvariant="italic">π</mml:mi></mml:math></inline-formula>-A isotherms presented as Figs. S1 and
S2). After confirming the reactant film's stability, we exposed the
monolayers to ozone following the reaction by neutron reflectometry and
IRRAS in the conditions described below.</p>
<sec id="Ch1.S3.SS1">
  <label>3.1</label><title>Pure water subphase – room temperature</title>
      <p id="d1e1094">At room temperature, on a pure water subphase, we found that the removal of
deuterated material from the surface is consistent with complete oxidation.
The remaining reflectivity signal is not distinguishable from zero and
cannot be fitted except by using a fixed background. This is consistent with
the results of Voss et al. (2007), but not with those of
King et al. (2009), where a
stable product film was reported.</p>
      <p id="d1e1097">Figure 1 shows a time series of fitted <inline-formula><mml:math id="M83" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> values (proportional
to surface concentration) for 120 s time slices of the reaction, with an
O<inline-formula><mml:math id="M84" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> concentration of 323 <inline-formula><mml:math id="M85" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 9 ppb introduced at <inline-formula><mml:math id="M86" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s. The
absence of points after ca. 800 s indicates that the numerical fits fail to
converge after this point, demonstrating that the reflectivity is not
consistent with an adsorbed surface layer (i.e. not measurably different
from the background). Figure S3 in the Supplement illustrates
this as a pair of before/after <inline-formula><mml:math id="M87" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M88" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> reflectivity curves. The figure also shows
data for a salt subphase reaction, which will be discussed below.</p><?xmltex \setfigures?><?xmltex \floatpos{t}?><fig id="Ch1.F2"><?xmltex \currentcnt{1}?><?xmltex \def\figurename{Figure}?><label>Figure 1</label><caption><p id="d1e1155">Ozonolysis of an oleic acid monolayer floating on pure vs. salt
water. Time evolution plot for ozonolysis of 29 <inline-formula><mml:math id="M89" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M90" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>
<inline-formula><mml:math id="M91" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA (CHCl<inline-formula><mml:math id="M92" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure water (green circles) and 25 <inline-formula><mml:math id="M93" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M94" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M95" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA 36 g L<inline-formula><mml:math id="M96" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> NaCl(aq) (purple squares)
subphases by 323 <inline-formula><mml:math id="M97" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 29 ppb O<inline-formula><mml:math id="M98" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M99" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 21 <inline-formula><mml:math id="M100" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M101" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f01.png"/>

        </fig>

      <p id="d1e1294">This result of no measurable residue was reproducible across 11 different
ozonolysis runs carried out across an [O<inline-formula><mml:math id="M102" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>] range of 126 <inline-formula><mml:math id="M103" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 15 to
2010 <inline-formula><mml:math id="M104" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 238 ppb as parts of three different beamline experiments at two
different neutron facilities (ISIS INTER RB 1810793 and RB 1710483; ILL
FIGARO 9-10-1518).</p>
</sec>
<sec id="Ch1.S3.SS2">
  <label>3.2</label><title>Salt water subphase – room temperature</title>
      <p id="d1e1328">Sea spray aerosol will naturally be salty, and a simple monovalent common
salt, sodium chloride (aq; 36 g L<inline-formula><mml:math id="M105" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>), was used as a rough model
of sea spray for this experiment.</p>
      <p id="d1e1343">At room temperature, the reaction also proceeded to completion, with no
residual deuterated material detectable at the interface. King et al. (2009)
found that there was no detectable difference in the nature of the reaction
between a room-temperature pure water subphase and a room-temperature salted
subphase (across a wider variety of salts than studied here), and these
results support that comparative conclusion (though King et al. (2009) actually
measured a residual layer in both conditions while the present study has
measured no residual layer in either condition; this experiment supports
their finding that no difference between the reaction in the two conditions is
detectable using this method). Figure 1 shows the results in these
conditions as a time series of 120 s time slices (a lack of points
indicates no convergence in the numerical fit; a pair of before/after <inline-formula><mml:math id="M106" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M107" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula>
reflectivity curves can be found as Fig. S4 in the Supplement).</p>
</sec>
<sec id="Ch1.S3.SS3">
  <label>3.3</label><title>Near-zero temperature conditions: pure water subphase</title>
      <p id="d1e1368">Experiments were then undertaken to determine if the reaction proceeds in a
similar manner at atmospherically more relevant temperatures of 3 <inline-formula><mml:math id="M108" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M109" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. A clear difference between this reaction and the reaction at
room temperature is observable. At the lower temperature, the neutron
reflectometry data clearly show a residual signal from deuterated material
at the interface after the initial reaction of oleic acid and ozone. On
heating the subphase to room temperature, this residue disappears. This is
inferred from the fact that, after heating, the reflectivity signal is
consistent with that for a null-reflecting water surface (i.e. background),
meaning that no deuterated material remains at the surface (or so little
that it cannot be distinguished from this background condition<fn id="Ch1.Footn1"><p id="d1e1387">The
exact value of this cut-off point varies depending on measurement conditions
and count time, but <inline-formula><mml:math id="M110" display="inline"><mml:mrow><mml:mi mathvariant="italic">ρ</mml:mi><mml:mi mathvariant="italic">τ</mml:mi></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M111" display="inline"><mml:mo>∼</mml:mo></mml:math></inline-formula> 5 <inline-formula><mml:math id="M112" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M113" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M114" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>, corresponding to ca. 5 % of the oleic acid concentration
spread initially, have been reliably measured with this experimental
setup.</p></fn>); the reflectivity data for such a null-reflecting air–water
interface are included in the Supplement (Fig. S11).</p>
      <p id="d1e1436">The kinetics of the reaction, however, do not seem to differ markedly in the
two temperature conditions. A fuller treatment of the kinetics of the
reaction (in which we confirm no significant difference in second-order
rate coefficients for the two temperature conditions) will follow in Sect. 3.9.</p>
      <?pagebreak page1330?><p id="d1e1439">Figure 2 shows a time evolution plot for these conditions. It demonstrates
that a stable residual layer remaining after ozonolysis for more than 1 h can be measured and fitted over 120 s counting periods and that this
is no longer the case after heating to 20 <inline-formula><mml:math id="M115" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. The figure also
shows data from a salt subphase reaction, which will be discussed below.
Figure 3 draws particular attention to the distinction between the situation
after ozonolysis and the situation after heating by showing <inline-formula><mml:math id="M116" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M117" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> reflectivity
curves before ozonolysis, after ozonolysis, and after heating (the analogous
plot for the salt water condition is included in the Supplement
as Fig. S5).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3"><?xmltex \currentcnt{2}?><?xmltex \def\figurename{Figure}?><label>Figure 2</label><caption><p id="d1e1468">Ozonolysis of an oleic acid monolayer at low temperatures floating
on pure vs. salt water. Time evolution plot for ozonolysis of 25 <inline-formula><mml:math id="M118" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L
1.0 g L<inline-formula><mml:math id="M119" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M120" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA (CHCl<inline-formula><mml:math id="M121" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure water (green
circles) and 36 g L<inline-formula><mml:math id="M122" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> NaCl(aq) (purple squares) subphases by 323 <inline-formula><mml:math id="M123" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 29 ppb O<inline-formula><mml:math id="M124" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M125" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 3 <inline-formula><mml:math id="M126" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M127" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
(pure water) or <inline-formula><mml:math id="M128" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M129" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M130" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (salt water).</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f02.png"/>

        </fig>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4"><?xmltex \currentcnt{3}?><?xmltex \def\figurename{Figure}?><label>Figure 3</label><caption><p id="d1e1600">Neutron reflectivity signal from the air–water interface before
ozonolysis (blue circles – signal from the pristine oleic acid monolayer),
after ozonolysis (red squares – clear signal remaining), and after heating
(orange triangles – no measurable signal) for ozonolysis of 25 <inline-formula><mml:math id="M131" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M132" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M133" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA (CHCl<inline-formula><mml:math id="M134" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure water subphase by
323 <inline-formula><mml:math id="M135" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 29 ppb O<inline-formula><mml:math id="M136" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M137" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 3 <inline-formula><mml:math id="M138" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M139" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f03.png"/>

        </fig>

      <p id="d1e1694">This measurable residue after ozonolysis is reproducible across 18
experiments carried out with a wide [O<inline-formula><mml:math id="M140" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>] range from 126 <inline-formula><mml:math id="M141" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 15
to 2010 <inline-formula><mml:math id="M142" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 238 ppb. The lower end of this range is close to mixing
ratios of 100 ppb that have been observed in polluted conditions
(Warneck, 1999) and thus approaches atmospherically realistic
concentrations as far as feasible within the time constraints of beam-time
experiments for such a rigorous study.</p>
      <p id="d1e1720">Twelve of these runs (those obtained at the high-flux instrument FIGARO at
ILL; experiment 9-10-1518) were carried out to determine the kinetic
behaviour of this reaction and were therefore performed using a high
<inline-formula><mml:math id="M143" display="inline"><mml:mrow><mml:mi mathvariant="normal">d</mml:mi><mml:mi>Q</mml:mi><mml:mo>/</mml:mo><mml:mi>Q</mml:mi></mml:mrow></mml:math></inline-formula> fast (5 s per measurement) chopper and slit setup optimised for kinetic
measurements of the fast reactions afforded by high [O<inline-formula><mml:math id="M144" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]. These runs
were used to measure second-order rate constants for the reaction (cf.
Sect. 3.9) rather than to precisely quantify the residual material.
Therefore, these 12 runs support the qualitative conclusion that a residue
remains after ozonolysis but were not used to quantify this residue.</p>
      <p id="d1e1746">Four runs (INTER; experiment RB 1810793) were carried out with the precise
and reproducible temperature control system and with the neutron
reflectometry setup optimised to facilitate precise measurement of a low-intensity reflectivity signal (low <inline-formula><mml:math id="M145" display="inline"><mml:mrow><mml:mi mathvariant="normal">d</mml:mi><mml:mi>Q</mml:mi><mml:mo>/</mml:mo><mml:mi>Q</mml:mi></mml:mrow></mml:math></inline-formula>, low background). These were assumed
to be sampling from a Gaussian distribution of residue intensities, and on
that basis a mean deuterated residue fraction of 11.1 % of the initial
spread material was calculated, with a 95 % confidence interval of
<inline-formula><mml:math id="M146" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula>1.9 % (absolute).</p>
</sec>
<sec id="Ch1.S3.SS4">
  <label>3.4</label><title>Atmospheric ageing simulation</title>
      <p id="d1e1779">In order to provide further assurance that the measured residue was a
genuine product monolayer and not, for example, a temperature-dependent
fitting artefact, an experiment was performed in which, after ozonolysis of
an oleic acid monolayer, more oleic acid was added and another ozonolysis
reaction carried out, and then yet more oleic was added, and a third
ozonolysis reaction carried out. If the measured residual reflectivity is
due to a product monolayer, then this should build up over multiple
spreading and ozonolysis cycles. This was indeed observed, adding further
weight to the conclusion that the measured residual reflectivity stems from
the presence of a product monolayer that is not susceptible to further
ozonolysis.</p>
      <p id="d1e1782">Figure 4 shows a time series representing reflectivity from the air–water
interface at 120 s time slices throughout this process and clearly
demonstrates the gradual build-up of a product monolayer. As well as
illustrating that this is a real product, not a temperature-dependent
measurement artefact, this represents a possible process in the real
atmosphere, in which reactive species could be repeatedly adsorbed to the
surface and engage in reactions which leave a small amount of unreactive
material behind, gradually building up an unreactive monolayer. The
atmospheric implications of this, which are potentially significant, are
discussed in Sect. 4.2.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F5"><?xmltex \currentcnt{4}?><?xmltex \def\figurename{Figure}?><label>Figure 4</label><caption><p id="d1e1787">Experiment mimicking an aqueous aerosol droplet exposed to
multiple cooking emission peaks and demonstrating the associated build-up of
an inert organic film at the air–water interface at low temperatures. Time
evolution plot for ozonolysis of 25 <inline-formula><mml:math id="M147" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M148" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M149" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA
(CHCl<inline-formula><mml:math id="M150" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure water subphase by 323 <inline-formula><mml:math id="M151" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 29 ppb
O<inline-formula><mml:math id="M152" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M153" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s and after two additional spreadings of 25 <inline-formula><mml:math id="M154" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M155" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M156" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA at 3 <inline-formula><mml:math id="M157" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M158" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f04.png"/>

        </fig>

      <p id="d1e1914">Figure 5 further illustrates this as a series of <inline-formula><mml:math id="M159" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M160" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> reflectivity curves for
each spreading and ozonolysis (as well as for a final heating step; data for
second and third<?pagebreak page1331?> spreading steps are omitted, and only fits shown as all
three data series heavily overlap), and Fig. S6 in the Supplement focuses in on the build-up of the product monolayer by excluding
the spreading <inline-formula><mml:math id="M161" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M162" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> curves from the plot and zooming in on the post-ozonolysis
reflectivity data. In Fig. 5, the data points for the spreading of
additional material (two series) are removed for clarity (they very closely
overlap the initial spreading data), and only the fits are shown.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F6"><?xmltex \currentcnt{5}?><?xmltex \def\figurename{Figure}?><label>Figure 5</label><caption><p id="d1e1947">Neutron reflectivity signal from the air–water interface before
ozonolysis (blue circles; data only shown for first spreading; fits shown
for all three spreadings – clear and consistent signal from the oleic acid
monolayers across the three simulated cooking emission peaks), after
ozonolysis (red squares – demonstrating the build-up of organic residue at the
air–water interface during repeated exposure to cooking emission), and after
heating (orange triangles – removal of organic residue at room temperature)
for the multi-ozonolysis reaction shown as a time evolution plot in Fig. 4.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f05.png"/>

        </fig>

<?xmltex \hack{\newpage}?>
</sec>
<sec id="Ch1.S3.SS5">
  <label>3.5</label><title>Near-zero temperature conditions: salt water subphase</title>
      <p id="d1e1966">Ozonolysis reaction was also carried out on a simple monovalent sea salt
solution model subphase. At the same temperatures where a residue was
observed on pure water (3 <inline-formula><mml:math id="M163" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M164" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C), a residue was not
reproducibly measurable for the salt-water subphase: only one out of five
runs carried out with the temperature control setup produced a measurable
residue, and it is possible that this residue was not stable but was still slowly disappearing – see discussion below on the unexpected kinetics of
the reaction in these conditions. This could be because no residue remains
under these conditions or because whatever residue does remain is close to
the detection limit for this technique.</p>
      <p id="d1e1985">However, at still colder temperatures not accessible on a pure water
subphase (<inline-formula><mml:math id="M165" display="inline"><mml:mo lspace="0mm">-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M166" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M167" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C), a residue is reliably measurable.
Figure 2 shows a time evolution for a reaction in these conditions, and
Fig. S5 in the Supplement shows the corresponding <inline-formula><mml:math id="M168" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M169" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> plots for
spreading, ozonolysis, and heating.</p>
      <p id="d1e2025">This result was produced in duplicate (INTER experiment RB 1810793). Using
the same assumption of sampling from a Gaussian distribution of measured
residues as a fraction of initially deposited deuterated material as used in
the pure water at 3 <inline-formula><mml:math id="M170" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M171" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, the mean deuterated residue
fraction of 7.3 % was calculated, with a 95 % confidence interval of
<inline-formula><mml:math id="M172" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula>0.45 % (absolute). The upper confidence bound of this mean lies
below the lower confidence bound of the mean for the pure water at 2 <inline-formula><mml:math id="M173" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M174" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. This supports the conclusion that a little less product
monolayer remains at the interface in the salt water at <inline-formula><mml:math id="M175" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M176" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M177" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C condition than in the pure water at 3 <inline-formula><mml:math id="M178" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M179" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
condition.</p>
      <p id="d1e2107">A basic visual appraisal of the time evolution of this reaction (see Fig. 2) also suggests a considerable difference in the kinetics of the reaction
compared with those seen at room temperature and on pure water at low
temperatures. Instead of the linear-to-exponential decay (either to no
signal or to a residual signal) seen under other conditions, the reaction
appears to follow a linear-to-exponential decay at first, before switching
to a much slower roughly linear decay to the final residual monolayer. This
shape was reproducible across three runs under these conditions, as well as
in five runs with the salt subphase at 3 <inline-formula><mml:math id="M180" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M181" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. One of
these five runs in which a residue was detectable may have simply been a
slow linear decay that was not allowed to run to completion – as this
arresting of exponential decay and replacement with a much slower linear
decay was unexpected, it was initially difficult to distinguish from the
stable residual monolayer, as seen in pure water at 3 <inline-formula><mml:math id="M182" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M183" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C and after the slow linear decay in salt water at <inline-formula><mml:math id="M184" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M185" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M186" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p>
      <p id="d1e2167">We can currently only speculate about what exactly is causing this deviation
from expected stretched exponential decay in the low-temperature salt water
conditions. The most likely explanation seems to be that some deuterated
products<?pagebreak page1332?> are building up on the surface throughout the reaction and then
slowly partitioning away from the interface (in a process which goes to
completion at 3 <inline-formula><mml:math id="M187" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M188" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C but not at <inline-formula><mml:math id="M189" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M190" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M191" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C).</p>
</sec>
<sec id="Ch1.S3.SS6">
  <label>3.6</label><title>Product elucidation with partially deuterated reactants at near-zero temperatures: pure water subphase</title>
      <p id="d1e2217">In order to understand what the atmospheric impacts of this product
monolayer are likely to be, it is important to understand its composition.
The ozonolysis of oleic acid (see Scheme 1) produces four initial products:
nonanoic acid (estimated vapour pressure at 25 <inline-formula><mml:math id="M192" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C: 0.0 <inline-formula><mml:math id="M193" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.5 mm Hg; all estimated vapour pressures are from ChemSpider), nonanal
(estimated vapour pressure at 25 <inline-formula><mml:math id="M194" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C: 0.5 <inline-formula><mml:math id="M195" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.4 mm Hg),
azelaic acid (estimated vapour pressure at 25 <inline-formula><mml:math id="M196" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C: 0.0 <inline-formula><mml:math id="M197" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1.8 mm Hg), and 9-oxononanoic acid (estimated vapour pressure at 25 <inline-formula><mml:math id="M198" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C:
0.0 <inline-formula><mml:math id="M199" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1.4 mm Hg). It should be noted that recent work has reported that
Criegee intermediates not only re-arrange to form carboxylic acids, but may
also react with species such as carboxylic acids, leading to formation of
hydroperoxide esters (see e.g. work at the air–water interface by Enami
and Colussi, 2017, on reactions of <italic>cis</italic>-pinonic acid with Criegee
intermediates produced from the ozonolysis of sesquiterpenes and by Zhou et
al., 2019, on reactions of condensed-phase Criegee intermediates with
carboxylic acids and perfluoroalkyl carboxylic acids). To our knowledge
there are no studies on oleic acid reacting with Criegee intermediates, but
it is clearly possible that the simple four products presented here are not
the only products given the potential for secondary chemistry. For our
specific approach of studying a floating monolayer on water, secondary
reactions seem comparably unlikely given the geometry and relatively low
concentration of oleic acid compared to ozone in the conditions applied.
Future studies as a function of oleic acid surface coverage could
disentangle this chemistry to some extent and potentially provide evidence
for Criegee intermediates reacting with oleic acid.</p>
      <p id="d1e2288">Out of the four initial products described in Scheme 1, nonanoic acid is the
most obviously amphiphilic product and thus the prime candidate picked out
in the past for possible membership in a post-ozonolysis monolayer
(King et al., 2009). Nonanal
has been reported as partitioning to the gas phase upon oxidation of methyl
oleate monolayers (McNeill et al.,
2007). The surfactant activity of azelaic acid is under debate, with Voss et al. (2007) suggesting no surfactant activity
and Tuckermann (2007) taking the opposite view. The room-temperature solubility of azelaic acid (2.4 g L<inline-formula><mml:math id="M200" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>; Tuckermann, 2007) is much higher than that of nonanoic
acid (0.28 g L<inline-formula><mml:math id="M201" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>; Gilman et al.,
2004), so, in a reaction producing both products, azelaic acid is more
likely to partition into the bulk rather than to the interface, although
there is no conclusive evidence that it does not partition to the interface.
King et al. (2009) suggest
that it most likely partitions to the bulk. 9-Oxononanoic acid is not as
well studied as the other products and therefore is the hardest to predict
as regards to its partitioning. King et al. (2009)
suggest tentatively that it does not partition to the interface.</p>
      <p id="d1e2315">From the results discussed so far and knowledge of the volatility,
solubility, and amphiphilicity of the candidate species, it is reasonable to
dismiss nonanal from consideration due to its measured partition to the gas
phase in a very similar reaction and due to the lack of any obvious
significant amphiphilicity in the structure of the molecule. The results
discussed so far do not allow discernment between nonanoic acid, azelaic
acid, and 9-oxononanoic acid, all of which, if present as product monolayers,
could produce the observed results.</p>
      <p id="d1e2318">However, the use of a partially deuterated form of oleic acid allows for
some discernment between possibilities. Deuteration of only the tail side of
the double bond of the oleic acid molecule (shown in teal in Scheme 1)
facilitates an ozonolysis reaction in which two of the products (nonanal and
nonanoic acid) will be deuterated (and thus detectable via neutron
reflectometry) and the other two (9-oxononanoic acid and azelaic acid) will
not be deuterated (and thus will not be detectable via neutron
reflectometry).</p>
      <p id="d1e2322">Depending on the makeup of the product monolayer, the measured residue (as a
fraction of initial deuterated material) will vary from nothing (signifying
a product monolayer made up entirely of azelaic acid and/or 9-oxononanoic
acid) to twice the relative amount (the same absolute amount if the same
initial surface concentration of oleic acid is assumed) as in the <inline-formula><mml:math id="M202" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>
case (signifying a product monolayer made up entirely of nonanoic acid).</p>
      <p id="d1e2336">This experiment was carried out on a pure water subphase at 3 <inline-formula><mml:math id="M203" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M204" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and the result was intermediate between these two possible
extremes. The fraction of deuterated material remaining at the interface was
calculated for five ozonolysis reactions, and the mean deuterated residue
fraction was 9.8 %, with a 95 % confidence interval (assuming sampling
from a Gaussian distribution as before) of <inline-formula><mml:math id="M205" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula>2.0 % (absolute). The
confidence interval here heavily overlaps with the confidence interval for
the mean deuterated residue fraction for the <inline-formula><mml:math id="M206" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment, so the two
values are not significantly different. Indistinguishable fractional
deuterated residue means that, from the same oleic acid surface
concentration starting point, the deuterated residue present in a <inline-formula><mml:math id="M207" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>
experiment is half of what it is in a <inline-formula><mml:math id="M208" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment. This implies a
product monolayer made up of roughly equal molar amounts of nonanoic acid
and azelaic and/or 9-oxononanoic acids (the ratio between these latter two
cannot be determined by this method, as both are deuterated in a <inline-formula><mml:math id="M209" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>
experiment and non-deuterated in a <inline-formula><mml:math id="M210" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment). While there are
limited data available on the temperature dependence of the solubilities of
these three products, the solubility of azelaic acid has been reported to
reduce to 1.0 g L<inline-formula><mml:math id="M211" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at 1 <inline-formula><mml:math id="M212" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C from 2.4 g L<inline-formula><mml:math id="M213" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at 20 <inline-formula><mml:math id="M214" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
(O'Neil, 2006), which suggests that azelaic acid may be lost to the subphase
at room temperature while being retained at the air–water interface at
near-zero temperatures.</p>
      <?pagebreak page1333?><p id="d1e2461">Figure 6 shows a representative example of a time series of 120 s time
slices for this reaction on pure water, as well as the reaction on a salt
subphase. The absolute amount of deuterated material in the residue is about
half of that seen for the <inline-formula><mml:math id="M215" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment in the same conditions (see
Fig. 2), and this comes close to the detection limit for 120 s count times
in this neutron reflectometry setup. This results in many non-converging
fits for the product monolayer, making its identification via this method of
analysis alone difficult. However, taking longer time slices allows for a
reliable discernment of a product monolayer, as the quality of the
reflectivity statistics scales with the square root of count time (assuming
a constant neutron flux). This is also illustrated in the stage-by-stage <inline-formula><mml:math id="M216" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula>
vs. <inline-formula><mml:math id="M217" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> reflectivity plots displayed in Fig. S7 in the Supplement.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F7"><?xmltex \currentcnt{6}?><?xmltex \def\figurename{Figure}?><label>Figure 6</label><caption><p id="d1e2491">Ozonolysis of a partially deuterated oleic acid monolayer floating
on pure vs. salt water. Time evolution plot for ozonolysis of 17 <inline-formula><mml:math id="M218" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L
1.3 g L<inline-formula><mml:math id="M219" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M220" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA (CHCl<inline-formula><mml:math id="M221" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure water (green
circles) and 36 g L<inline-formula><mml:math id="M222" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> NaCl(aq) (purple squares) subphases by 323 <inline-formula><mml:math id="M223" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 29 ppb O<inline-formula><mml:math id="M224" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M225" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 3 <inline-formula><mml:math id="M226" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M227" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
(pure water) or <inline-formula><mml:math id="M228" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M229" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M230" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (salt water).</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f06.png"/>

        </fig>

      <p id="d1e2621">A topping-up and re-oxidisation experiment was also carried out with
<inline-formula><mml:math id="M231" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid, and the results were analogous to those for the
<inline-formula><mml:math id="M232" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid experiment (except scaled down by a factor of 2). This
demonstrates that both the nonanoic acid and azelaic/9-oxononanoic acid
components of the product monolayer can be built up over time (if only
nonanoic acid were to build up, then the build-up of fractional deuterated
residue would be faster in the <inline-formula><mml:math id="M233" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment; if only
azelaic/9-oxononanoic acid were to build up, then no build-up would be
observed in the <inline-formula><mml:math id="M234" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiment). These data are included in the
Supplement (Figs. S9 and S10).</p>
</sec>
<sec id="Ch1.S3.SS7">
  <label>3.7</label><title>Product elucidation at near-zero temperatures with partially deuterated reactants: salt water subphase</title>
      <p id="d1e2676">A series of <inline-formula><mml:math id="M235" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> experiments was also run for the salt water subphase at
<inline-formula><mml:math id="M236" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M237" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M238" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C in which measurable residue was observed for
<inline-formula><mml:math id="M239" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-oleic acid ozonolysis. This allowed investigation of the likely
makeup of the product monolayer in the same way as under the pure water 3 <inline-formula><mml:math id="M240" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M241" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C conditions. However, the yet lower absolute amounts
of residual deuterated material in this experiment posed sensitivity
problems for this method of measuring the residue, and therefore the
conclusions that can be drawn about the composition of the product monolayer
in the salt water <inline-formula><mml:math id="M242" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M243" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M244" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C conditions are less secure than
those that can be drawn about the composition of the product monolayer on
pure water at 3 <inline-formula><mml:math id="M245" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M246" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C discussed above.</p>
      <p id="d1e2781">In two out of three runs, a residue was detected. This could be because the
residue was genuinely absent in the third run or because it was simply
below the detection threshold. Treating the run in which no residue was
measurable as a measurement of zero residue yields a mean fractional
deuterated residue of 5.6 % with a 95 % confidence interval of <inline-formula><mml:math id="M247" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula>2.9 % (absolute) for this system. This may be a slight underestimate of
the true value due to the treatment of below-threshold residue as zero
residue.</p>
      <p id="d1e2791">Based on our analysis, the product monolayer cannot be predominantly
composed of nonanoic acid, as that would produce a significantly higher
fractional deuterated residual in the <inline-formula><mml:math id="M248" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> case than in the <inline-formula><mml:math id="M249" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> case, which can be ruled out by our data. It is not possible to say with
confidence that the composition of this product monolayer is similar to that
observed in the pure water 3 <inline-formula><mml:math id="M250" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M251" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C conditions (a roughly
equal mixture of nonanoic acid and azelaic/9-oxononanoic acids), as the data
are also consistent with somewhat lower relative levels of nonanoic acid
(though not none at all, as that would produce no measurable residue).</p>
      <p id="d1e2832">It must be noted that, in this particular case, an assumption had to be made
that the reaction would have proceeded to completion within 4000 s and that
anything measured after that point was a stable residue. This is because the
residue was, in all these <inline-formula><mml:math id="M252" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> salt water <inline-formula><mml:math id="M253" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M254" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M255" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
cases, below the detection threshold for a 120 s count time. This meant that
the reaction could not be followed to ascertain at which point the system
was stable in order to define a period over which the residue could be more
accurately measured using a single reflectivity curve compiled over a long
count time. As the saltwater trace in Fig. 2 (low temperature) shows, the
reaction on salt water at low temperatures proceeds to completion over a
much longer time frame than the pure water equivalent.</p>
      <p id="d1e2870">In order to measure the stable residue, the 120 s interval time series
graph is first prepared, and the slope of that graph is then used to
determine at what point a stable residue has formed, and the time period
during which that graph is flat is then averaged over to create the single
after-ozonolysis reflectivity curve which is shown in the <inline-formula><mml:math id="M256" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M257" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula> reflectivity
graphs and used to determine the fractional deuterated residue values. For
instance, Fig. 2 shows that the signal is no longer declining after 4000 s, so the time period used for the after-ozonolysis reflectivity curve
in Fig. S4 is 4000–4500 s (heating began at 4500 s). For all fractional
deuterated residue calculations except these last (for <inline-formula><mml:math id="M258" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> salt water <inline-formula><mml:math id="M259" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M260" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M261" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C), the 120 s time series interval graphs have<?pagebreak page1334?> been
able to guide the time integration ranges for the step-by-step <inline-formula><mml:math id="M262" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M263" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula>
reflectivity curves (see Fig. S7 in the Supplement).</p>
      <p id="d1e2936">However, for the <inline-formula><mml:math id="M264" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">18</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> salt water <inline-formula><mml:math id="M265" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M266" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M267" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C experiment,
the absolute signal from the residue was so low that 120 s count times were
not sufficient. As a result, the reaction was assumed to have completed by
4000 s (longer than any observed reaction times), and signal was averaged
from this point until heating in order to quantify the residue.</p>
      <p id="d1e2973">Figures 6 and S8 (in the Supplement) show a time series and <inline-formula><mml:math id="M268" display="inline"><mml:mi>R</mml:mi></mml:math></inline-formula> vs. <inline-formula><mml:math id="M269" display="inline"><mml:mi>Q</mml:mi></mml:math></inline-formula>
reflectivity plots for these conditions. The time series plot demonstrates
that any residue is below the detection limit for 120 s of counting;
however, the 500 s over which the after-ozonolysis reflectivity
curve is calculated affords good enough data to discern a residue.</p>
</sec>
<sec id="Ch1.S3.SS8">
  <label>3.8</label><title>Atmospheric product stability: temperature threshold</title>
      <p id="d1e2998">It has been demonstrated that a residue remains at the interface after
ozonolysis (2 h timescale) of an oleic acid monolayer by gas-phase ozone at
3 <inline-formula><mml:math id="M270" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M271" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C on a pure water subphase and at <inline-formula><mml:math id="M272" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>2 <inline-formula><mml:math id="M273" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M274" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C on a 36 g L<inline-formula><mml:math id="M275" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> NaCl aqueous solution. However, it would be
useful to establish across what ranges of temperature this product monolayer
persists.</p>
      <p id="d1e3053">In order to investigate this, a product monolayer was gradually heated (1<inline-formula><mml:math id="M276" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> every 5 min) to see if there was a critical threshold
temperature above which it would be rapidly removed from the interface.</p>
      <p id="d1e3065">Figure 7 shows the temperature-ramping experiment in detail. The temperature
of the subphase is controlled by varying the temperature of a coupled
coolant bath. For the experiments discussed thus far, the temperature of the
subphase can be measured before each experiment, allowing the offset between
bath and subphase to be measured and an accurate assessment of the subphase
temperature via direct measurement used for each experiment. For this
ramping experiment, it was not practical to measure the subphase temperature
directly for every step. Instead, the relationship between bath and subphase
temperatures was used to define a linear relationship between bath and
subphase temperatures that was deemed sufficiently accurate given the
existing <inline-formula><mml:math id="M277" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula>1 <inline-formula><mml:math id="M278" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C uncertainty. Diurnal temperature variations
that could have disturbed this relationship were largely eliminated using
air conditioning to maintain the temperature of the experimental area at
around 15 <inline-formula><mml:math id="M279" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, which was also key in reducing the impact of
condensation. The bath was set to <inline-formula><mml:math id="M280" display="inline"><mml:mo>-</mml:mo></mml:math></inline-formula>1 <inline-formula><mml:math id="M281" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C for ozonolysis and then increased by 1 <inline-formula><mml:math id="M282" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C at <inline-formula><mml:math id="M283" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">1035</mml:mn></mml:mrow></mml:math></inline-formula> s and every 300 s following until
5 <inline-formula><mml:math id="M284" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (corresponding to a measured subphase temperature of 7 <inline-formula><mml:math id="M285" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C) was reached after 2535 s. A single step to a bath temperature
of 11 <inline-formula><mml:math id="M286" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, which corresponds to a subphase temperature of around
12 <inline-formula><mml:math id="M287" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, was performed at <inline-formula><mml:math id="M288" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">3260</mml:mn></mml:mrow></mml:math></inline-formula> s.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F8"><?xmltex \currentcnt{7}?><?xmltex \def\figurename{Figure}?><label>Figure 7</label><caption><p id="d1e3183">Gradual loss of residue due to increase in temperature. Time
evolution plot for ozonolysis of 29 <inline-formula><mml:math id="M289" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 1.0 g L<inline-formula><mml:math id="M290" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M291" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA
(CHCl<inline-formula><mml:math id="M292" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure subphase by 754 <inline-formula><mml:math id="M293" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 89 ppb O<inline-formula><mml:math id="M294" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>
introduced at <inline-formula><mml:math id="M295" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 2 <inline-formula><mml:math id="M296" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M297" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, with temperature
ramping (described in detail in the text) from <inline-formula><mml:math id="M298" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">1035</mml:mn></mml:mrow></mml:math></inline-formula> s; error bars are
omitted for visual clarity.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f07.png"/>

        </fig>

      <p id="d1e3289"><?xmltex \hack{\newpage}?>This experiment was performed on the FIGARO reflectometer at the ILL
(experiment 9-10-1518) and showed that the product film was stable at up to
7 <inline-formula><mml:math id="M299" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M300" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, though there was a slight linear decay in product
monolayer surface concentration with increasing temperature. On further
heating to 12 <inline-formula><mml:math id="M301" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M302" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, no threshold temperature was
observed, but, at this higher temperature, the linear decay ran into the
detection limits of the neutron reflectometry setup. This could mean that
the monolayer is not stable at or above 12 <inline-formula><mml:math id="M303" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M304" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, or it
could mean that it simply continues to gradually linearly decay with rising
temperature above 12 <inline-formula><mml:math id="M305" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M306" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, but passed the detection limit
of the setup used for this experiment. Either way, the product monolayer is
certainly stable up to 7 <inline-formula><mml:math id="M307" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M308" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C but definitely not above
12 <inline-formula><mml:math id="M309" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M310" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (upper limit).</p>
      <p id="d1e3391">It is important to note that a monolayer produced at 3 <inline-formula><mml:math id="M311" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M312" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C and then being stable at up to around 12 <inline-formula><mml:math id="M313" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M314" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C does not
mean that a reaction carried out at 12 <inline-formula><mml:math id="M315" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M316" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C would
definitely produce a stable monolayer. However, this temperature-ramping
experiment at least provides a hint for the range of temperatures over which
these product monolayers might persist. Most of the troposphere is below 10 <inline-formula><mml:math id="M317" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, so these conditions are highly atmospherically relevant.</p>
      <p id="d1e3452">Hung and Tang (2010) suggested that the
physical state of products from the ozonolysis of solid state oleic acid
particles by O<inline-formula><mml:math id="M318" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> might be temperature dependent across a 4–9 <inline-formula><mml:math id="M319" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C temperature range, and it is worth considering whether the
effect we report in present work is linked to this phenomenon, as there is
overlap between this transition temperature range and the 6–13 <inline-formula><mml:math id="M320" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C transition range we observe.</p>
</sec>
<sec id="Ch1.S3.SS9">
  <label>3.9</label><title>Kinetic analysis of oleic acid ozonolysis</title>
      <p id="d1e3490">Experiments were performed on the FIGARO reflectometer at the ILL
(experiment 9-10-1518) to elucidate the<?pagebreak page1335?> effect of temperature changes on the
kinetics of the reaction. The ozonolysis reaction was performed with
[O<inline-formula><mml:math id="M321" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M322" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">gas</mml:mi></mml:msub></mml:math></inline-formula> ranging between 126 <inline-formula><mml:math id="M323" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 15 and 1005 <inline-formula><mml:math id="M324" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 119 ppb. A
pseudo-first-order rate coefficient (<inline-formula><mml:math id="M325" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>) for each reaction was
calculated by fitting a modified exponential developed in previous work by
this group in order to account for the fact that [O<inline-formula><mml:math id="M326" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M327" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">gas</mml:mi></mml:msub></mml:math></inline-formula> initially
builds up in the reaction chamber and thus rises steeply at the start of the
reaction as initial mixing occurs within the chamber
(Pfrang et al., 2014). The traditional
first-order exponential equation that describes a second-order reaction
occurring with an excess of one reactant (in this case, O<inline-formula><mml:math id="M328" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>) is modified
to (Pfrang et al., 2014)
            <disp-formula id="Ch1.E3" content-type="numbered"><label>3</label><mml:math id="M329" display="block"><mml:mrow><mml:mi mathvariant="normal">Γ</mml:mi><mml:mfenced close=")" open="("><mml:mi>t</mml:mi></mml:mfenced><mml:mo>=</mml:mo><mml:msub><mml:mi mathvariant="normal">Γ</mml:mi><mml:mn mathvariant="normal">0</mml:mn></mml:msub><mml:msup><mml:mi>e</mml:mi><mml:mrow><mml:mo>-</mml:mo><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub><mml:mfenced close=")" open="("><mml:mrow><mml:mi>t</mml:mi><mml:mo>-</mml:mo><mml:mstyle scriptlevel="+1"><mml:mfrac><mml:mi>v</mml:mi><mml:mi>f</mml:mi></mml:mfrac></mml:mstyle><mml:mfenced close=")" open="("><mml:mrow><mml:mn mathvariant="normal">1</mml:mn><mml:mo>-</mml:mo><mml:msup><mml:mi>e</mml:mi><mml:mrow><mml:mo>-</mml:mo><mml:mstyle scriptlevel="+1"><mml:mfrac><mml:mi>f</mml:mi><mml:mi>v</mml:mi></mml:mfrac></mml:mstyle><mml:mi>t</mml:mi></mml:mrow></mml:msup></mml:mrow></mml:mfenced></mml:mrow></mml:mfenced></mml:mrow></mml:msup><mml:mo>.</mml:mo></mml:mrow></mml:math></disp-formula>
          The expected exponential relationship between surface concentration (<inline-formula><mml:math id="M330" display="inline"><mml:mi mathvariant="normal">Γ</mml:mi></mml:math></inline-formula>) and time (<inline-formula><mml:math id="M331" display="inline"><mml:mi>t</mml:mi></mml:math></inline-formula>) is modified by the inclusion of a second exponential function
that includes constants for the gas flow rate (<inline-formula><mml:math id="M332" display="inline"><mml:mi>f</mml:mi></mml:math></inline-formula>), which is 20 cm<inline-formula><mml:math id="M333" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M334" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> for these experiments, and chamber volume (<inline-formula><mml:math id="M335" display="inline"><mml:mi>v</mml:mi></mml:math></inline-formula>), which is 2.1 <inline-formula><mml:math id="M336" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M337" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M338" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msup></mml:math></inline-formula>, but which requires replacement with an
effective chamber volume. The derivation of Eq. (3) is presented in
previous work (Pfrang et al., 2014).</p>
      <p id="d1e3703">It is important to note that this analytical treatment is not a complete
description of the processes at work throughout the reaction. Transient
reaction products at the interface are, due to their deuterated nature,
measured along with the reactant film throughout the reaction if and when
they are present (this is why the technique is sensitive to a residual
product film). As a result, fitting this analytical model to the data needs
to take this into account. A number of assumptions have to be made about the
precise way in which ozone mixes into the chamber. These are discussed in
detail in Sect. S3 of the Supplement. Here, we present and
discuss the results of this fitting procedure.</p>
      <p id="d1e3706">Figure 8 displays fitted <inline-formula><mml:math id="M339" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> values for reactions under a variety of
[O<inline-formula><mml:math id="M340" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M341" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:math></inline-formula> conditions at 21 and 2 <inline-formula><mml:math id="M342" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, as well as 95 % confidence intervals for fits of <inline-formula><mml:math id="M343" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> values (<inline-formula><mml:math id="M344" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msub><mml:mo>=</mml:mo><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub><mml:mo>/</mml:mo><mml:mo>[</mml:mo><mml:msub><mml:mrow class="chem"><mml:mi mathvariant="normal">O</mml:mi></mml:mrow><mml:mn mathvariant="normal">3</mml:mn></mml:msub><mml:msub><mml:mo>]</mml:mo><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>) to these data.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F9"><?xmltex \currentcnt{8}?><?xmltex \def\figurename{Figure}?><label>Figure 8</label><caption><p id="d1e3795">Kinetics of ozonolysis of the oleic acid monolayer on pure water
at room and low temperatures. Fitted <inline-formula><mml:math id="M345" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> pseudo-first-order rate constants
against [O<inline-formula><mml:math id="M346" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M347" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:math></inline-formula> at 21 <inline-formula><mml:math id="M348" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M349" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (orange) and 2 <inline-formula><mml:math id="M350" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M351" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (aqua).</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f08.png"/>

        </fig>

      <p id="d1e3866">[O<inline-formula><mml:math id="M352" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M353" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:math></inline-formula> values were calculated from [O<inline-formula><mml:math id="M354" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M355" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">gas</mml:mi></mml:msub></mml:math></inline-formula> values by
using a Henry's law solubility constant for O<inline-formula><mml:math id="M356" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> in organics of
[organic] <inline-formula><mml:math id="M357" display="inline"><mml:mo>/</mml:mo></mml:math></inline-formula> [gas] <inline-formula><mml:math id="M358" display="inline"><mml:mo>=</mml:mo></mml:math></inline-formula> 11.7 (unitless) and assuming the same layer thickness of
2 nm. This solubility constant is consistent with the value used previously
in ozonolysis experiments by King et al. (2009)
and is informed by the work of Smith et al. (2002).</p>
      <p id="d1e3929">The error in each fitted <inline-formula><mml:math id="M359" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> value, as noted in Sect. S3 of the
Supplement, is dominated by uncertainty in model fitting at the
start of each reaction. Uncertainty in [O<inline-formula><mml:math id="M360" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M361" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:math></inline-formula> arises from
uncertainties in the calibration of the Pen-Ray ozoniser, which was
performed using Beer–Lambert law UV absorbance at 254 nm using an extinction
coefficient of 1.13 <inline-formula><mml:math id="M362" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M363" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">17</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M364" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> (Daumont et
al., 1992).</p>
      <p id="d1e3993"><?xmltex \hack{\newpage}?>The fitted <inline-formula><mml:math id="M365" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> values for these two conditions (<inline-formula><mml:math id="M366" display="inline"><mml:mo lspace="0mm">±</mml:mo></mml:math></inline-formula> a 95 %
confidence interval) are (2.2 <inline-formula><mml:math id="M367" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.4) <inline-formula><mml:math id="M368" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M369" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> and (2.2 <inline-formula><mml:math id="M370" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.2) <inline-formula><mml:math id="M371" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M372" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M373" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M374" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at
21 and 2 <inline-formula><mml:math id="M375" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, respectively.</p>
      <p id="d1e4098">Our experiments observe either no difference or a difference too small to
be reliably detected (a difference of <inline-formula><mml:math id="M376" display="inline"><mml:mo>&lt;</mml:mo></mml:math></inline-formula> 10 % might not be
noticeable given the uncertainty in fitted <inline-formula><mml:math id="M377" display="inline"><mml:mrow><mml:msub><mml:mi>k</mml:mi><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> parameters and [O<inline-formula><mml:math id="M378" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]
calibration). This is a similar situation to that found by Hung and Tang (2010), who observed, for ozonolysis of liquid
oleic acid, a very slight dependence on temperature based on their point
estimates of reaction rate that was within their margins of error (although
they observed a strong temperature dependence for the ozonolysis of solid
oleic acid).</p>
      <p id="d1e4128">It is important to note that, as this reflectivity-based method for
calculating surface concentration of oleic acid is not sensitive only to
oleic acid, but also to reaction products that may remain at the interface,
it is possible that the rate of reaction does differ across this temperature
range but that changes in product build-up and distribution conspire to
entirely mask this, leading to a similar trend in total adsorbed deuterated
material at the interface. It seems highly unlikely that counterbalancing
effects would conspire to so well balance each other out across a range of
[O<inline-formula><mml:math id="M379" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>] conditions. In any case, from an atmospheric perspective, the key
question is not how fast oleic acid reacts but how fast the monolayer is
removed from the interface. These experiments confirm that changing the
temperature from room temperature to a more atmospherically realistic
near-zero temperature does not notably alter the rate of monolayer removal
from the interface.</p>
      <p id="d1e4141">Figure 9 shows time series of the product of SLD and thickness for the
lowest and highest [O<inline-formula><mml:math id="M380" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]<inline-formula><mml:math id="M381" display="inline"><mml:msub><mml:mi/><mml:mi mathvariant="normal">surf</mml:mi></mml:msub></mml:math></inline-formula> concentrations used at the two
temperatures studied, to provide a clearer visual confirmation of the
similar rates of the two reactions.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F10"><?xmltex \currentcnt{9}?><?xmltex \def\figurename{Figure}?><label>Figure 9</label><caption><p id="d1e4164">Comparison of time-dependent loss of material from the air–water
interface during oleic acid ozonolysis at room and low temperatures and at
highest and lowest [O<inline-formula><mml:math id="M382" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>]. Time evolution plot for ozonolysis of 39 <inline-formula><mml:math id="M383" display="inline"><mml:mrow class="unit"><mml:mi mathvariant="normal">µ</mml:mi></mml:mrow></mml:math></inline-formula>L 0.75 g L<inline-formula><mml:math id="M384" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M385" display="inline"><mml:mrow><mml:msub><mml:mi>d</mml:mi><mml:mn mathvariant="normal">34</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>-OA (CHCl<inline-formula><mml:math id="M386" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> spreading solution) on pure
subphase by O<inline-formula><mml:math id="M387" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> introduced at <inline-formula><mml:math id="M388" display="inline"><mml:mrow><mml:mi>t</mml:mi><mml:mo>=</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula> s at 21 <inline-formula><mml:math id="M389" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M390" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
(orange) and 2 <inline-formula><mml:math id="M391" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M392" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (aqua); error bars are omitted for
visual clarity.</p></caption>
          <?xmltex \igopts{width=241.848425pt}?><graphic xlink:href="https://acp.copernicus.org/articles/21/1325/2021/acp-21-1325-2021-f09.png"/>

        </fig>

      <p id="d1e4276">It can be seen from these two comparisons that the rates of these reactions
do not differ appreciably. Indeed, the offset<?pagebreak page1336?> between the two curves is due
in both cases to slight differences in starting concentration. These plots
also further corroborate the main result of this study – that a residue
remains after ozonolysis at near-zero temperature but not at room
temperature.</p>
      <p id="d1e4279">The rate coefficients determined here are about 3 times higher than
those previously reported for ozonolysis of oleic acid monolayers
(King et al., 2009).
Significant variability between experiments to determine rates for these
heterogeneous reactions is not unprecedented. When Hung and Tang (2010) investigated heterogeneous ozonolysis
of liquid oleic acid, they measured a rate coefficient that was 3 times
higher than the highest value they could find in previous work
(Moise and Rudich, 2002) and up to
10 times higher than the lowest. For solid state ozonolysis, the discrepancy
was up to a factor of 40 (Hung and Tang,
2010).</p>
      <p id="d1e4282">The most important conclusions here, however, are not the absolute rate
coefficients measured but the fact that there is not a notable difference
between them. Despite the qualitative differences between the ozonolysis of
an oleic acid monolayer at room temperature and more atmospherically
relevant near-zero temperatures (namely the presence of a residual monolayer
in the latter case), the kinetics of the reaction does not appear to be
altered substantially in these two conditions.</p><?xmltex \hack{\newpage}?>
</sec>
</sec>
<sec id="Ch1.S4" sec-type="conclusions">
  <label>4</label><title>Conclusions</title>
<sec id="Ch1.S4.SS1">
  <label>4.1</label><title>Atmospheric surface chemistry</title>
      <p id="d1e4302">Based on our neutron reflectometry data, we conclude that the ozonolysis of
an oleic acid monolayer on a pure water subphase (a basic model of an
atmospheric water droplet) does not leave behind a product at the interface
at room temperature but does leave such a residual product film at more
atmospherically relevant near-zero temperatures and may do so at
temperatures of up to 7–12 <inline-formula><mml:math id="M393" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. Data from an experiment
involving re-deposition and re-ozonolysis of oleic acid showing the build-up
of this product monolayer convince us that this is a genuine product of the
reaction.</p>
      <p id="d1e4314">Further to this, we conclude that the ozonolysis of an oleic acid monolayer
film on a 36 g L<inline-formula><mml:math id="M394" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> NaCl aqueous solution subphase (a basic model of a
sea spray droplet) does not leave a product film at the interface at room
temperature but does leave such a residual product film behind at
temperatures below freezing. Such a residual product film probably is not
left behind after ozonolysis at the 3 <inline-formula><mml:math id="M395" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M396" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C temperature
condition at which stable product films were observed on pure water.</p>
      <p id="d1e4345">Based on data from experiments performed with a partially deuterated form of
oleic acid together with a knowledge of the expected major products of the
ozonolysis, we conclude that, for the pure water subphase, this product film
is roughly half nonanoic acid, with the other half being azelaic acid or
9-oxononanoic acid, or a mixture of the two. For the salt subphase case, the
data are less conclusive on the ratio between these components, though very
high or very low fractions of nonanoic acid can be ruled out.</p>
      <p id="d1e4348">Experiments performed at a variety of O<inline-formula><mml:math id="M397" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> concentrations demonstrate
that the rate of monolayer removal does not differ significantly between the
two temperatures studied, despite the clear qualitative differences in the
end state of the reaction; rate coefficients were determined to be (2.2 <inline-formula><mml:math id="M398" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.4) <inline-formula><mml:math id="M399" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M400" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> and (2.2 <inline-formula><mml:math id="M401" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 0.2) <inline-formula><mml:math id="M402" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 10<inline-formula><mml:math id="M403" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> cm<inline-formula><mml:math id="M404" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> s<inline-formula><mml:math id="M405" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> at 21 <inline-formula><mml:math id="M406" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 and 2 <inline-formula><mml:math id="M407" display="inline"><mml:mo>±</mml:mo></mml:math></inline-formula> 1 <inline-formula><mml:math id="M408" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, respectively.</p>
</sec>
<sec id="Ch1.S4.SS2">
  <label>4.2</label><title>Atmospheric implications</title>
      <p id="d1e4466">Almost regardless of the chemical nature of the surface film, the result
from an atmospheric physics perspective is very similar: a film remains at
the surface after ozonolysis of an oleic acid monolayer at atmospherically
realistic temperatures. The presence of such a film means that the physical
effects of a surface monolayer, such as reduced water uptake, reduced
surface pressure, and reduced evaporation, will still be present, albeit not
to the same extent, as they were in the original oleic-acid-coated aerosol
droplet. This means the fact that an oleic acid film will oxidise in the
atmosphere does not render such a film irrelevant to the physical properties
of the droplet in the long term, as would be the case if no residual film
remained after ozonolysis.</p>
      <?pagebreak page1337?><p id="d1e4469"><?xmltex \hack{\newpage}?>Furthermore, our re-oxidation experiments demonstrate that an inert product
film may build up during the droplet ageing process in the atmosphere, even
if only ordinarily short-lived reactive species (such as oleic acid and
other unsaturated compounds) were initially emitted into the atmosphere. It
is entirely possible that, given suitably cold conditions, an entirely
saturated “full” monolayer could be built up by repeated deposition and
ozonolysis of entirely unsaturated precursor surfactants. More generally,
long-lived inert films could develop even if only short-lived reactive
species are emitted, provided a suitable processing mechanism is available.
The ozonolysis of oleic acid studied here is such a mechanism; therefore
emissions of oleic acid and similar unsaturated fatty acids may well result
in the build-up of saturated monolayers inert to further ozonolysis. This
provides a way to reconcile the observation that anthropogenic activity
emits significant quantities of unsaturated fatty acids
(Shrivastava et al., 2007) with
the observation that aerosol particles collected from the atmosphere seem to
host monolayers entirely inert to ozonolysis
(Jones et al., 2017).</p>
      <p id="d1e4473">The presence of these long-lived films is atmospherically significant. The
surface pressure reduction in particular may have an impact on cloud
lifetimes via the stabilisation of lower diameter droplets associated with
this change under Köhler theory (Ambaum, 2010). Other
possible effects include reduced water uptake (and therefore growth) of the
droplet, inhibited evaporation from the droplet, reduced transfer of species
between the droplet and the wider atmosphere (alternative processes leading
to this effect have been discussed in earlier work by this research group
and others; King
et al., 2004; Pfrang et al., 2014, 2017a), and modified surface solubility
of other atmospheric species (Barnes,
1997; Benjamin, 1996; Cohen Stuart et al., 1996; Gaines, 1966; Garrett,
1971; Gilman et al., 2004; La Mer, 1962; La Mer et al., 1964; Mmereki et al., 2003; Mmereki
and Donaldson, 2002; Ray et al., 1991; Rideal, 1924; Tomoaia-Cotisel and
Cadenhead, 1991).</p>
      <p id="d1e4476">In summary, this work provides evidence that even the emission of reactive
surfactant species such as unsaturated fatty acids could alter the physical
properties of water droplets in the atmosphere (including in clouds) over a
much longer timeframe than the atmospheric lifetime of these species would
suggest, via the build-up of inert monolayers on the surface of such
droplets composed of the products of the oxidative processing of such fatty
acids in the atmosphere.</p>
</sec>
</sec>

      
      </body>
    <back><notes notes-type="dataavailability"><title>Data availability</title>

      <p id="d1e4485">The data presented in this paper can be obtained from the corresponding author upon request. The underlying data are archived at ILL (<ext-link xlink:href="https://doi.org/10.5291/ILL-DATA.9-10-1518" ext-link-type="DOI">10.5291/ILL-DATA.9-10-1518</ext-link>, Thomas et al., 2018) and ISIS (<ext-link xlink:href="https://doi.org/10.5286/ISIS.E.87020742" ext-link-type="DOI">10.5286/ISIS.E.87020742</ext-link>, Pfrang et al., 2017b; <ext-link xlink:href="https://doi.org/10.5286/ISIS.E.92919810" ext-link-type="DOI">10.5286/ISIS.E.92919810</ext-link>, Pfrang et al., 2018).</p>
  </notes><app-group>
        <supplementary-material position="anchor"><p id="d1e4497">The supplement related to this article is available online at: <inline-supplementary-material xlink:href="https://doi.org/10.5194/acp-21-1325-2021-supplement" xlink:title="pdf">https://doi.org/10.5194/acp-21-1325-2021-supplement</inline-supplementary-material>.</p></supplementary-material>
        </app-group><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e4506">CP and MWAS initiated the research project. CP, MWAS, and BW designed the
experiments and carried them out. BW analysed the data with support from
MWAS and CP. AMi and CG supported the work during beam-time
experiments, and AMi also helped with the offline calibrations. AMa provided support during the FIGARO beam time. JT synthesised
deuterated oleic acid. BW, CP, and MWAS prepared the manuscript.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e4512">The authors declare that they have no conflict of interest.</p>
  </notes><ack><title>Acknowledgements</title><p id="d1e4518">The authors acknowledge the following people for their contributions to this
work: Sophie Ayscough (University of Edinburgh) and Evita Hartmane (University of
Reading) for assistance on beamline experiments at ILL and ISIS; Philipp
Gutfreund (ILL) for help with the FIGARO beamline operation; Simon Wood (ILL)
for technical assistance on the FIGARO beamline; Jacob Simms (ISIS) for
reaction chamber design and assembly partnership; Richard Haynes (ISIS) for
support of the reaction chamber design, assembly, and deployment, plus
technical assistance on the INTER beamline; John Crawford (ISIS) for
assistance with the reactor chamber assembly; Jeff Vine (ISIS), Tom Charleston
(ISIS), and Andy Church (ISIS) for technical assistance on the INTER beamline.</p></ack><notes notes-type="financialsupport"><title>Financial support</title>

      <p id="d1e4523">This research has been supported by the Natural Environment Research Council (grant no. NE/L002566/1).</p>
  </notes><notes notes-type="reviewstatement"><title>Review statement</title>

      <p id="d1e4529">This paper was edited by Jason Surratt and reviewed by four anonymous referees.</p>
  </notes><ref-list>
    <title>References</title>

      <ref id="bib1.bib1"><label>1</label><?label 1?><mixed-citation>Allan, J. D., Williams, P. I., Morgan, W. T., Martin, C. L., Flynn, M. J., Lee, J., Nemitz, E., Phillips, G. J., Gallagher, M. W., and Coe, H.: Contributions from transport, solid fuel burning and cooking to primary organic aerosols in two UK cities, Atmos. Chem. Phys., 10, 647–668, <ext-link xlink:href="https://doi.org/10.5194/acp-10-647-2010" ext-link-type="DOI">10.5194/acp-10-647-2010</ext-link>, 2010.</mixed-citation></ref>
      <ref id="bib1.bib2"><label>2</label><?label 1?><mixed-citation>
Ambaum, M. H. P.: Thermal Physics of the Atmosphere, 1st edn.,
Wiley-Blackwell, Reading, UK, 2010.</mixed-citation></ref>
      <ref id="bib1.bib3"><label>3</label><?label 1?><mixed-citation>Barnes, G. T.: Permeation through monolayers, Colloid. Surface. A, 126, 149–158, <ext-link xlink:href="https://doi.org/10.1016/S0927-7757(96)03926-X" ext-link-type="DOI">10.1016/S0927-7757(96)03926-X</ext-link>, 1997.</mixed-citation></ref>
      <ref id="bib1.bib4"><label>4</label><?label 1?><mixed-citation>Benjamin, I.: Chemical Reactions and Solvation at Liquid Interfaces: A
Microscopic Perspective Chemical Reactions and Solvation at Liquid
Interfaces: A Microscopic Perspective, Chem. Rev., 96, 1449–1476,
<ext-link xlink:href="https://doi.org/10.1021/cr950230" ext-link-type="DOI">10.1021/cr950230</ext-link>, 1996.</mixed-citation></ref>
      <?pagebreak page1338?><ref id="bib1.bib5"><label>5</label><?label 1?><mixed-citation>Cantrell, W. and Robinson, C.: Heterogeneous freezing of ammonium sulfate
and sodium chloride solutions by long chain alcohols, Geophys. Res. Lett.,
33, L07802, <ext-link xlink:href="https://doi.org/10.1029/2005gl024945" ext-link-type="DOI">10.1029/2005gl024945</ext-link>, 2006.</mixed-citation></ref>
      <ref id="bib1.bib6"><label>6</label><?label 1?><mixed-citation>Chen, Y., Zhang, Y., Lambe, A. T., Xu, R., Lei, Z., Olson, N. E., Zhang, Z.,
Szalkowski, T., Cui, T., Vizuete, W., Gold, A., Turpin, B. J., Ault, A. P.,
Chan, M. N., and Surratt, J. D.: Heterogeneous Hydroxyl Radical Oxidation of
Isoprene-Epoxydiol-Derived Methyltetrol Sulfates: Plausible Formation
Mechanisms of Previously Unexplained Organosulfates in Ambient Fine
Aerosols, Environ. Sci. Technol. Lett., 7, 460–468,
<ext-link xlink:href="https://doi.org/10.1021/acs.estlett.0c00276" ext-link-type="DOI">10.1021/acs.estlett.0c00276</ext-link>, 2020.</mixed-citation></ref>
      <ref id="bib1.bib7"><label>7</label><?label 1?><mixed-citation>Cohen Stuart, M. A., Wegh, R. A. J., Kroon, J. M., and Sudhölter, E. J.
R.: Design and Testing of a Low-Cost and Compact Brewster Angle Microscope,
Langmuir, 12, 2863–2865, <ext-link xlink:href="https://doi.org/10.1021/la9507592" ext-link-type="DOI">10.1021/la9507592</ext-link>, 1996.</mixed-citation></ref>
      <ref id="bib1.bib8"><label>8</label><?label 1?><mixed-citation>Cosman, L. M., Knopf, D. A., and Bertram, A. K.: N<inline-formula><mml:math id="M409" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O<inline-formula><mml:math id="M410" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">5</mml:mn></mml:msub></mml:math></inline-formula> reactive
uptake on aqueous sulfuric acid solutions coated with branched and
straight-chain insoluble organic surfactants, J. Phys. Chem. A, 112,
2386–2396, <ext-link xlink:href="https://doi.org/10.1021/jp710685r" ext-link-type="DOI">10.1021/jp710685r</ext-link>, 2008.</mixed-citation></ref>
      <ref id="bib1.bib9"><label>9</label><?label 1?><mixed-citation>
Daumont, D., Brion, J., Charbonnier, J., and Malicet, J.: Ozone UV
spectroscopy I: Absorption cross sections at room temperature, J. Atmos.
Chem., 15, 135–155, 1992.</mixed-citation></ref>
      <ref id="bib1.bib10"><label>10</label><?label 1?><mixed-citation>Donaldson, D. J. and Vaida, V.: The influence of organic films at the
air-aqueous boundary on atmospheric processes, Chem. Rev., 106,
1445–1461, <ext-link xlink:href="https://doi.org/10.1021/cr040367c" ext-link-type="DOI">10.1021/cr040367c</ext-link>, 2006.</mixed-citation></ref>
      <ref id="bib1.bib11"><label>11</label><?label 1?><mixed-citation>Ellison, G. B., Tuck, A. F., and Vaida, V.: Atmospheric processing of organic
aerosols, J. Geophys. Res., 104, 11633–11641, <ext-link xlink:href="https://doi.org/10.1029/1999JD900073" ext-link-type="DOI">10.1029/1999JD900073</ext-link>,
1999.</mixed-citation></ref>
      <ref id="bib1.bib12"><label>12</label><?label 1?><mixed-citation>
Enami, S. and Colussi, A. J.: Efficient scavenging of Criegee intermediates
on water by surface-active cis-pinonic acid, Phys. Chem. Chem. Phys., 19,
17044–17051, 2017.</mixed-citation></ref>
      <ref id="bib1.bib13"><label>13</label><?label 1?><mixed-citation>Fu, P. Q., Kawamura, K., Chen, J., Charrière, B., and Sempéré, R.: Organic molecular composition of marine aerosols over the Arctic Ocean in summer: contributions of primary emission and secondary aerosol formation, Biogeosciences, 10, 653–667, <ext-link xlink:href="https://doi.org/10.5194/bg-10-653-2013" ext-link-type="DOI">10.5194/bg-10-653-2013</ext-link>, 2013.</mixed-citation></ref>
      <ref id="bib1.bib14"><label>14</label><?label 1?><mixed-citation>
Gaines, G. L.: Insoluble Monolayers at the Liquid Gas Interface,
Interscience Publishers, New York, USA, 1966.</mixed-citation></ref>
      <ref id="bib1.bib15"><label>15</label><?label 1?><mixed-citation>Gallimore, P. J., Griffiths, P. T., Pope, F. D., Reid, J. P., and Kalberer,
M.: Comprehensive modeling study of ozonolysis of oleic acid aerosol based
on real-time, online measurements of aerosol composition, J. Geophys. Res.-Atmos., 122, 4364–4377, <ext-link xlink:href="https://doi.org/10.1002/2016JD026221" ext-link-type="DOI">10.1002/2016JD026221</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib16"><label>16</label><?label 1?><mixed-citation>Garrett, W. D.: Retardation of Water Drop Evaporation with Monomolecular
Surface Films, J. Atmos. Sci., 28, 816–819,
<ext-link xlink:href="https://doi.org/10.1175/1520-0469(1971)028&lt;0816:rowdew&gt;2.0.co;2" ext-link-type="DOI">10.1175/1520-0469(1971)028&lt;0816:rowdew&gt;2.0.co;2</ext-link>,
1971.</mixed-citation></ref>
      <ref id="bib1.bib17"><label>17</label><?label 1?><mixed-citation>Geŕard, V., Noziere, B., Fine, L., Ferronato, C., Singh, D. K., Frossard, A.
A., Cohen, R. C., Asmi, E., Lihavainen, H., Kivekas̈, N., Aurela, M., Brus,
D., Frka, S., Kusǎn, A. C.: Concentrations and Adsorption Isotherms for
Amphiphilic Surfactants in PM<inline-formula><mml:math id="M411" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">1</mml:mn></mml:msub></mml:math></inline-formula> Aerosols from Different Regions of Europe,
Environ. Sci. Technol., 53, 21, 12379–12388, 2019.</mixed-citation></ref>
      <ref id="bib1.bib18"><label>18</label><?label 1?><mixed-citation>Gill, P. S., Graedel, T. E., and Weschler, C. J.: Organic films on
atmospheric aerosol particles, fog droplets, cloud droplets, raindrops, and
snowflakes, Rev. Geophys., 21, 903, <ext-link xlink:href="https://doi.org/10.1029/RG021i004p00903" ext-link-type="DOI">10.1029/RG021i004p00903</ext-link>, 1983.</mixed-citation></ref>
      <ref id="bib1.bib19"><label>19</label><?label 1?><mixed-citation>Gilman, J. B., Eliason, T. L., Fast, A., and Vaida, V.: Selectivity and
stability of organic films at the air-aqueous interface, J. Colloid
Interf. Sci., 280, 234–43, <ext-link xlink:href="https://doi.org/10.1016/j.jcis.2004.07.019" ext-link-type="DOI">10.1016/j.jcis.2004.07.019</ext-link>, 2004.</mixed-citation></ref>
      <ref id="bib1.bib20"><label>20</label><?label 1?><mixed-citation>Gross, S., Iannone, R., Xiao, S., and Bertram, A. K.: Reactive uptake studies
of NO<inline-formula><mml:math id="M412" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula> and N<inline-formula><mml:math id="M413" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O<inline-formula><mml:math id="M414" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">5</mml:mn></mml:msub></mml:math></inline-formula> on alkenoic acid, alkanoate, and polyalcohol
substrates to probe nighttime aerosol chemistry, Phys. Chem. Chem. Phys.,
11, 7792–7803, 2009.</mixed-citation></ref>
      <ref id="bib1.bib21"><label>21</label><?label 1?><mixed-citation>
Grotjahn, R.: General Circulation of the Atmosphere, Mean
Characteristics, in: Encyclopedia of Atmospheric Sciences, 2nd edn.,
edited by: North, G. R., Pyle, J., and Zhang, F., 73–89, Academic Press,
Oxford, UK, 2015.</mixed-citation></ref>
      <ref id="bib1.bib22"><label>22</label><?label 1?><mixed-citation>Hung, H.-M. and Tang, C.-W.: Effects of Temperature and Physical State on
Heterogeneous Oxidation of Oleic Acid Droplets with Ozone, J. Phys. Chem. A,
114, 13104–13112, <ext-link xlink:href="https://doi.org/10.1021/jp105042w" ext-link-type="DOI">10.1021/jp105042w</ext-link>, 2010.</mixed-citation></ref>
      <ref id="bib1.bib23"><label>23</label><?label 1?><mixed-citation>Hung, H.-M., Katrib, Y., and Martin, S. T.: Products and mechanisms of the
reaction of oleic acid with ozone and nitrate radical, J. Phys. Chem. A.,
109, 4517–4530, <ext-link xlink:href="https://doi.org/10.1021/jp0500900" ext-link-type="DOI">10.1021/jp0500900</ext-link>, 2005.</mixed-citation></ref>
      <ref id="bib1.bib24"><label>24</label><?label 1?><mixed-citation>Jones, S. H., King, M. D., Ward, A. D., Rennie, A. R., Jones, A. C., and
Arnold, T.: Are organic films from atmospheric aerosol and sea water inert
to oxidation by ozone at the air-water interface?, Atmos. Environ., 161,
274–287, <ext-link xlink:href="https://doi.org/10.1016/J.ATMOSENV.2017.04.025" ext-link-type="DOI">10.1016/J.ATMOSENV.2017.04.025</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib25"><label>25</label><?label 1?><mixed-citation>King, M. D., Thompson, K. C., and Ward, A. D.: Laser Tweezers Raman Study of
Optically Trapped Aerosol Droplets of Seawater and Oleic Acid Reacting with
Ozone: Implications for Cloud-Droplet Properties, J. Am. Chem. Soc.,
126, 16710–16711, <ext-link xlink:href="https://doi.org/10.1021/ja044717o" ext-link-type="DOI">10.1021/ja044717o</ext-link>, 2004.</mixed-citation></ref>
      <ref id="bib1.bib26"><label>26</label><?label 1?><mixed-citation>King, M. D., Rennie, A. R., Thompson, K. C., Fisher, F. N., Dong, C. C.,
Thomas, R. K., Pfrang, C., and Hughes, A. V.: Oxidation of oleic acid at the
air-water interface and its potential effects on cloud critical
supersaturations., Phys. Chem. Chem. Phys., 11, 7699–7707,
<ext-link xlink:href="https://doi.org/10.1039/b906517b" ext-link-type="DOI">10.1039/b906517b</ext-link>, 2009.</mixed-citation></ref>
      <ref id="bib1.bib27"><label>27</label><?label 1?><mixed-citation>
Knopf, D. A. and Forrester, S. M.: Freezing of Water and Aqueous NaCl
Droplets Coated by Organic Monolayers as a Function of Surfactant Properties
and Water Activity, J. Phys. Chem. A, 115, 5579–5591, 2011.</mixed-citation></ref>
      <ref id="bib1.bib28"><label>28</label><?label 1?><mixed-citation>Knopf, D. A., Anthony, L. M., and Bertram, A. K.: Reactive uptake of O<inline-formula><mml:math id="M415" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msub></mml:math></inline-formula>
by multicomponent and multiphase mixtures containing oleic acid, J. Phys.
Chem. A, 109, 5579–5589, 2005.</mixed-citation></ref>
      <ref id="bib1.bib29"><label>29</label><?label 1?><mixed-citation>Knopf, D. A., Cosman, L. M., Mousavi, P., Mokamati, S., and Bertram, A. K.: A
novel flow reactor for studying reactions on liquid surfaces coated by
organic monolayers: Methods, validation, and initial results, J. Phys. Chem.
A, 111, 11021–11032, <ext-link xlink:href="https://doi.org/10.1021/Jp075724c" ext-link-type="DOI">10.1021/Jp075724c</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib30"><label>30</label><?label 1?><mixed-citation>Knopf, D. A., Alpert, P. A., and Wang, B.: The Role of Organic Aerosol in
Atmospheric Ice Nucleation: A Review, ACS Earth Space Chem., 2, 168–202,
<ext-link xlink:href="https://doi.org/10.1021/acsearthspacechem.7b00120" ext-link-type="DOI">10.1021/acsearthspacechem.7b00120</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib31"><label>31</label><?label 1?><mixed-citation>
Koop, T., Kapilashrami, A., Molina, L. T., and Molina, M. J.: Phase transitions
of sea-salt/water mixtures at low temperatures: Implications for ozone
chemistry in the polar marine boundary layer, J. Geophys. Res., 105,
26393–26402, 2000a.</mixed-citation></ref>
      <ref id="bib1.bib32"><label>32</label><?label 1?><mixed-citation>Koop, T., Luo, B. P., Tsias, A., and Peter, T.: Water activity as the
determinant for homogeneous ice nucleation in aqueous solutions, Nature,
406, 611–614, <ext-link xlink:href="https://doi.org/10.1038/35020537" ext-link-type="DOI">10.1038/35020537</ext-link>, 2000b.</mixed-citation></ref>
      <?pagebreak page1339?><ref id="bib1.bib33"><label>33</label><?label 1?><mixed-citation>
Kroflič, A., Frka, S., Simmel, M., Wex, H., and Grgič, I.: Size-Resolved
Surface-Active Substances of Atmospheric Aerosol: Reconsideration of the
Impact on Cloud Droplet Formation, Environ. Sci. Technol., 52,
9179–9187, 2018.</mixed-citation></ref>
      <ref id="bib1.bib34"><label>34</label><?label 1?><mixed-citation>
La Mer, V. K.: Retardation of Evaporation by Monolayers: Transport
Processes, Academic Press Inc., London, UK, 1962.</mixed-citation></ref>
      <ref id="bib1.bib35"><label>35</label><?label 1?><mixed-citation>
La Mer, V. K., Healy, T. W., and Aylmore, L. A. G.: The transport of water through monolayers of long-chain
n-paraffinic alcohols, J. Colloid Sci., 19, 673–684, 1964.</mixed-citation></ref>
      <ref id="bib1.bib36"><label>36</label><?label 1?><mixed-citation>Last, D. J., Nájera, J. J., Wamsley, R., Hilton, G., McGillen, M.,
Percival, C. J., and Horn, A. B.: Ozonolysis of organic compounds and
mixtures in solution. Part I: Oleic, maleic, nonanoic and benzoic acids,
Phys. Chem. Chem. Phys., 11, 1427–1440, <ext-link xlink:href="https://doi.org/10.1039/b815425b" ext-link-type="DOI">10.1039/b815425b</ext-link>, 2009.</mixed-citation></ref>
      <ref id="bib1.bib37"><label>37</label><?label 1?><mixed-citation>Li, S., Cheng, S., Du, L., and Wang, W.: Establishing a model organic film of
low volatile compound mixture on aqueous aerosol surface, Atmos. Environ.,
200, 15–23, <ext-link xlink:href="https://doi.org/10.1016/j.atmosenv.2018.11.052" ext-link-type="DOI">10.1016/j.atmosenv.2018.11.052</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib38"><label>38</label><?label 1?><mixed-citation>Lu, J. R., Thomas, R. K., and Penfold, J.: Surfactant layers at the air/water
interface: structure and composition, Adv. Colloid Interfac., 84,
143–304, <ext-link xlink:href="https://doi.org/10.1016/S0001-8686(99)00019-6" ext-link-type="DOI">10.1016/S0001-8686(99)00019-6</ext-link>, 2000.</mixed-citation></ref>
      <ref id="bib1.bib39"><label>39</label><?label 1?><mixed-citation>McNeill, V. F., Patterson, J., Wolfe, G. M., and Thornton, J. A.: The effect of varying levels of surfactant on the reactive uptake of N<inline-formula><mml:math id="M416" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O<inline-formula><mml:math id="M417" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">5</mml:mn></mml:msub></mml:math></inline-formula> to aqueous aerosol, Atmos. Chem. Phys., 6, 1635–1644, <ext-link xlink:href="https://doi.org/10.5194/acp-6-1635-2006" ext-link-type="DOI">10.5194/acp-6-1635-2006</ext-link>, 2006.</mixed-citation></ref>
      <ref id="bib1.bib40"><label>40</label><?label 1?><mixed-citation>McNeill, V. F., Wolfe, G. M., and Thornton, J. A.: The Oxidation of Oleate in
Submicron Aqueous Salt Aerosols: Evidence of a Surface Process, J. Phys.
Chem. A, 111, 1073–1083, <ext-link xlink:href="https://doi.org/10.1021/JP066233F" ext-link-type="DOI">10.1021/JP066233F</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib41"><label>41</label><?label 1?><mixed-citation>Mmereki, B. T. and Donaldson, D. J.: Laser induced fluorescence of pyrene at
an organic coated air-water interface, Phys. Chem. Chem. Phys., 4,
4186–4191, <ext-link xlink:href="https://doi.org/10.1039/b204754c" ext-link-type="DOI">10.1039/b204754c</ext-link>, 2002.</mixed-citation></ref>
      <ref id="bib1.bib42"><label>42</label><?label 1?><mixed-citation>Mmereki, B. T., Chaudhuri, S. R., and Donaldson, D. J.: Enhanced Uptake of
PAHs by Organic-Coated Aqueous Surfaces, J. Phys. Chem. A, 107,
2264–2269, <ext-link xlink:href="https://doi.org/10.1021/jp027361g" ext-link-type="DOI">10.1021/jp027361g</ext-link>, 2003.</mixed-citation></ref>
      <ref id="bib1.bib43"><label>43</label><?label 1?><mixed-citation>Moise, T. and Rudich, Y.: Reactive Uptake of Ozone by Aerosol-Associated
Unsaturated Fatty Acids: Kinetics, Mechanism, and Products, J. Phys. Chem.
A, 106, 6469–6476, <ext-link xlink:href="https://doi.org/10.1021/jp025597e" ext-link-type="DOI">10.1021/jp025597e</ext-link>, 2002.</mixed-citation></ref>
      <ref id="bib1.bib44"><label>44</label><?label 1?><mixed-citation>Nelson, A.: Co-refinement of multiple-contrast neutron/X-ray reflectivity
data using MOTOFIT, J. Appl. Crystallogr., 39, 273–276,
<ext-link xlink:href="https://doi.org/10.1107/S0021889806005073" ext-link-type="DOI">10.1107/S0021889806005073</ext-link>, 2006.</mixed-citation></ref>
      <ref id="bib1.bib45"><label>45</label><?label 1?><mixed-citation>Nozière, B., Baduel, C., and Jaffrezo, J.-L.: The dynamic surface tension of
atmospheric aerosol surfactants reveals new aspects of cloud activation,
Nat. Commun., 5, 3335, <ext-link xlink:href="https://doi.org/10.1038/ncomms4335" ext-link-type="DOI">10.1038/ncomms4335</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib46"><label>46</label><?label 1?><mixed-citation>
O'Neil, M. J. (Ed.): The Merck Index – An Encyclopedia of Chemicals, Drugs,
and Biologicals, Merck and Co., Inc., Whitehouse Station, NJ, USA, p. 153, 2006.</mixed-citation></ref>
      <ref id="bib1.bib47"><label>47</label><?label 1?><mixed-citation>
Ovadnevaite, J., Zuend, A., Laaksonen, A., Sanchez, K. J., Roberts, G.,
Ceburnis, D., Decesari, S., Rinaldi, M., Hodas, N., Facchini, M. C.,
Seinfeld, J. H., and O'Dowd, C.: Surface tension prevails over solute effect in organic-influenced cloud droplet activation, Nature, 546, 637–641,
2017.</mixed-citation></ref>
      <ref id="bib1.bib48"><label>48</label><?label 1?><mixed-citation>Pfrang, C., Shiraiwa, M., and Pöschl, U.: Chemical ageing and transformation of diffusivity in semi-solid multi-component organic aerosol particles, Atmos. Chem. Phys., 11, 7343–7354, <ext-link xlink:href="https://doi.org/10.5194/acp-11-7343-2011" ext-link-type="DOI">10.5194/acp-11-7343-2011</ext-link>, 2011.</mixed-citation></ref>
      <ref id="bib1.bib49"><label>49</label><?label 1?><mixed-citation>Pfrang, C., Sebastiani, F., Lucas, C. O. M., King, M. D., Hoare, I. D.,
Chang, D., and Campbell, R. A.: Ozonolysis of methyl oleate monolayers at the
air–water interface: oxidation kinetics, reaction products and atmospheric
implications, Phys. Chem. Chem. Phys., 16, 13220–13228,
<ext-link xlink:href="https://doi.org/10.1039/c4cp00775a" ext-link-type="DOI">10.1039/c4cp00775a</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib50"><label>50</label><?label 1?><mixed-citation>Pfrang, C., Rastogi, K., Cabrera-Martinez, E. R., Seddon, A. M., Dicko, C.,
Labrador, A., Plivelic, T. S., Cowieson, N., and Squires, A. M.: Complex
three-dimensional self-assembly in proxies for atmospheric aerosols, Nat.
Commun., 8, 1724, <ext-link xlink:href="https://doi.org/10.1038/s41467-017-01918-1" ext-link-type="DOI">10.1038/s41467-017-01918-1</ext-link>, 2017a.</mixed-citation></ref>
      <ref id="bib1.bib51"><label>51</label><?label 1?><mixed-citation>Pfrang, C., Woden, B., Skoda, M., and Gubb, C.: More than the sum – oxidation behaviour of mixed fatty acid monolayers, STFC ISIS Neutron and Muon Source, <ext-link xlink:href="https://doi.org/10.5286/ISIS.E.87020742" ext-link-type="DOI">10.5286/ISIS.E.87020742</ext-link>, 2017b.</mixed-citation></ref>
      <ref id="bib1.bib52"><label>52</label><?label 1?><mixed-citation>Pfrang, C., Skoda, M., Woden, B., and Hartmane, E.: Closer to Reality: Studies of Mixed Organic Monolayer Ozonolysis at Atmospherically Relevant Temperature and Salinity Conditions, STFC ISIS Neutron and Muon Source, <ext-link xlink:href="https://doi.org/10.5286/ISIS.E.92919810" ext-link-type="DOI">10.5286/ISIS.E.92919810</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib53"><label>53</label><?label 1?><mixed-citation>Ray, A. K., Devakottai, B., Souyri, A., and Huckaby, J. L.: Evaporation
characteristics of droplets coated with immiscible layers of nonvolatile
liquids, Langmuir, 7, 525–531, <ext-link xlink:href="https://doi.org/10.1021/la00051a019" ext-link-type="DOI">10.1021/la00051a019</ext-link>, 1991.</mixed-citation></ref>
      <ref id="bib1.bib54"><label>54</label><?label 1?><mixed-citation>Rideal, E. K.: On the Influence of Thin Surface Films on the Evaporation of
Water, J. Phys. Chem., 29, 1585–1588, <ext-link xlink:href="https://doi.org/10.1021/j150258a011" ext-link-type="DOI">10.1021/j150258a011</ext-link>, 1924.</mixed-citation></ref>
      <ref id="bib1.bib55"><label>55</label><?label 1?><mixed-citation>
Rudich, Y.: Laboratory perspectives on the chemical transformations of
organic matter in atmospheric particles, Chem. Rev., 103, 5097–5124,
2003.</mixed-citation></ref>
      <ref id="bib1.bib56"><label>56</label><?label 1?><mixed-citation>
Ruehl, C. R., Davies, J. F., and Wilson, K. R.: An interfacial mechanism for
cloud droplet formation on organic aerosols, Science, 351, 1447–1450,
2016.</mixed-citation></ref>
      <ref id="bib1.bib57"><label>57</label><?label 1?><mixed-citation>
Sareen, N., Schwier, A. N., Lathem, T. L., Nenes, A., and McNeill, V. F.:
Surfactants from the gas phase may promote cloud droplet formation, P.
Natl. Acad. Sci. USA, 110, 2723–2728, 2013.</mixed-citation></ref>
      <ref id="bib1.bib58"><label>58</label><?label 1?><mixed-citation>Sebastiani, F., Campbell, R. A., and Pfrang, C.: Complementarity of neutron
reflectometry and ellipsometry for the study of atmospheric reactions at the
air–water interface, RSC Adv., 5, 107105–107111,
<ext-link xlink:href="https://doi.org/10.1039/C5RA22725A" ext-link-type="DOI">10.1039/C5RA22725A</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib59"><label>59</label><?label 1?><mixed-citation>Sebastiani, F., Campbell, R. A., Rastogi, K., and Pfrang, C.: Nighttime oxidation of surfactants at the air–water interface: effects of chain length, head group and saturation, Atmos. Chem. Phys., 18, 3249–3268, <ext-link xlink:href="https://doi.org/10.5194/acp-18-3249-2018" ext-link-type="DOI">10.5194/acp-18-3249-2018</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib60"><label>60</label><?label 1?><mixed-citation>Shrivastava, M. K., Subramanian, R., Rogge, W. F., and Robinson, A. L.:
Sources of organic aerosol: Positive matrix factorization of molecular
marker data and comparison of results from different source apportionment
models, Atmos. Environ., 41, 9353–9369,
<ext-link xlink:href="https://doi.org/10.1016/j.atmosenv.2007.09.016" ext-link-type="DOI">10.1016/j.atmosenv.2007.09.016</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib61"><label>61</label><?label 1?><mixed-citation>Skoda, M. W. A., Thomas, B., Hagreen, M., Sebastiani, F., and Pfrang, C.:
Simultaneous neutron reflectometry and infrared reflection absorption
spectroscopy (IRRAS) study of mixed monolayer reactions at the air-water
interface, RSC Adv., 7, 34208–34214, <ext-link xlink:href="https://doi.org/10.1039/C7RA04900E" ext-link-type="DOI">10.1039/C7RA04900E</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib62"><label>62</label><?label 1?><mixed-citation>Smith, G. D., Woods, E., DeForest, C. L., Baer, T., and Miller, R. E.:
Reactive uptake of ozone by oleic acid aerosol particles: Application of
single-particle mass spectrometry t<?pagebreak page1340?>o heterogeneous reaction kinetics, J.
Phys. Chem. A, 106, 8085–8095, <ext-link xlink:href="https://doi.org/10.1021/jp020527t" ext-link-type="DOI">10.1021/jp020527t</ext-link>, 2002.</mixed-citation></ref>
      <ref id="bib1.bib63"><label>63</label><?label 1?><mixed-citation>Stevens, B. and Feingold, G.: Untangling aerosol effects on clouds and
precipitation in a buffered system, Nature, 461, 607–613,
<ext-link xlink:href="https://doi.org/10.1038/nature08281" ext-link-type="DOI">10.1038/nature08281</ext-link>, 2009.</mixed-citation></ref>
      <ref id="bib1.bib64"><label>64</label><?label 1?><mixed-citation>Tervahattu, H., Juhanoja, J., and Kupiainen, K.: Identification of an organic
coating on marine aerosol particles by TOF-SIMS, J. Geophys. Res.-Atmos., 107, ACH 18-1–ACH 18-7, <ext-link xlink:href="https://doi.org/10.1029/2001JD001403" ext-link-type="DOI">10.1029/2001JD001403</ext-link>, 2002.</mixed-citation></ref>
      <ref id="bib1.bib65"><label>65</label><?label 1?><mixed-citation>Thomas, B., Maestro, A., Milsom, A., Pfrang, C., and Skoda, M.: Oxidation Kinetics of Oleic Acid in Mixed Fatty Acid Monolayers: Miscible Vs Immiscible Mixtures, Institut Laue-Langevin (ILL), <ext-link xlink:href="https://doi.org/10.5291/ILL-DATA.9-10-1518" ext-link-type="DOI">10.5291/ILL-DATA.9-10-1518</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib66"><label>66</label><?label 1?><mixed-citation>
Thornberry, T. and Abbatt, J. P. D.: Heterogeneous reaction of ozone with
liquid unsaturated fatty acids: detailed kinetics and gas-phase product
studies, Phys. Chem. Chem. Phys., 6, 84–93, 2004.</mixed-citation></ref>
      <ref id="bib1.bib67"><label>67</label><?label 1?><mixed-citation>Thornton, J. A. and Abbatt, J. P. D.: N<inline-formula><mml:math id="M418" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msub></mml:math></inline-formula>O<inline-formula><mml:math id="M419" display="inline"><mml:msub><mml:mi/><mml:mn mathvariant="normal">5</mml:mn></mml:msub></mml:math></inline-formula> reaction on submicron
sea salt aerosol: Kinetics, products, and the effect of surface active
organics, J. Phys. Chem. A, 109, 10004–10012, <ext-link xlink:href="https://doi.org/10.1021/jp054183t" ext-link-type="DOI">10.1021/jp054183t</ext-link>,
2005.</mixed-citation></ref>
      <ref id="bib1.bib68"><label>68</label><?label 1?><mixed-citation>Tomoaia-Cotisel, M. and Cadenhead, D. A.: The interaction of procaine with
stearic acid monolayers at the air/water interface, Langmuir, 7,
964–974, <ext-link xlink:href="https://doi.org/10.1021/la00053a025" ext-link-type="DOI">10.1021/la00053a025</ext-link>, 1991.</mixed-citation></ref>
      <ref id="bib1.bib69"><label>69</label><?label 1?><mixed-citation>Tuckermann, R.: Surface tension of aqueous solutions of water-soluble
organic and inorganic compounds, Atmos. Environ., 41, 6265–6275,
<ext-link xlink:href="https://doi.org/10.1016/j.atmosenv.2007.03.051" ext-link-type="DOI">10.1016/j.atmosenv.2007.03.051</ext-link>, 2007.
</mixed-citation></ref><?xmltex \hack{\newpage}?>
      <ref id="bib1.bib70"><label>70</label><?label 1?><mixed-citation>Voss, L. F., Bazerbashi, M. F., Beekman, C. P., Hadad, C. M., and Allen, H.
C.: Oxidation of oleic acid at air/liquid interfaces, J. Geophys. Res.,
112, D06209, <ext-link xlink:href="https://doi.org/10.1029/2006JD007677" ext-link-type="DOI">10.1029/2006JD007677</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib71"><label>71</label><?label 1?><mixed-citation>Warneck, P.: Chemistry of the Natural Atmosphere, vol. 71, 2nd edn.,
available at:
<uri>https://www.elsevier.com/books/chemistry-of-the-natural-atmosphere/warneck/978-0-12-735632-7</uri> (last access: 6 December 2020),
1999.</mixed-citation></ref>
      <ref id="bib1.bib72"><label>72</label><?label 1?><mixed-citation>Woden, B., Skoda, M. W. A., Hagreen, M., and Pfrang, C.: Night-Time Oxidation
of a Monolayer Model for the Air–Water Interface of Marine Aerosols – A
Study by Simultaneous Neutron Reflectometry and in Situ Infra-Red Reflection
Absorption Spectroscopy (IRRAS), Atmosphere, 9, 471,
<ext-link xlink:href="https://doi.org/10.3390/atmos9120471" ext-link-type="DOI">10.3390/atmos9120471</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib73"><label>73</label><?label 1?><mixed-citation>Zahardis, J. and Petrucci, G. A.: The oleic acid-ozone heterogeneous reaction system: products, kinetics, secondary chemistry, and atmospheric implications of a model system – a review, Atmos. Chem. Phys., 7, 1237–1274, <ext-link xlink:href="https://doi.org/10.5194/acp-7-1237-2007" ext-link-type="DOI">10.5194/acp-7-1237-2007</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib74"><label>74</label><?label 1?><mixed-citation>
Zhou, S., Joudan, S., Forbes, M. W., Zhou, Z., and Abbatt, J. P. D., Reaction
of Condensed-Phase Criegee Intermediates with Carboxylic Acids and
Perfluoroalkyl Carboxylic Acids, Environ. Sci. Technol. Lett., 6,
243–250, 2019.</mixed-citation></ref>
      <ref id="bib1.bib75"><label>75</label><?label 1?><mixed-citation>Zobrist, B., Koop, T., Luo, B. P., Marcolli, C., and Peter, T.: Heterogeneous
ice nucleation rate coefficient of water droplets coated by a nonadecanol
monolayer, J. Phys. Chem. C, 111, 2149–2155, <ext-link xlink:href="https://doi.org/10.1021/Jp066080w" ext-link-type="DOI">10.1021/Jp066080w</ext-link>,
2007.</mixed-citation></ref>

  </ref-list></back>
    <!--<article-title-html>Ozonolysis of fatty acid monolayers at the air–water interface: organic films may persist at the surface of atmospheric aerosols</article-title-html>
<abstract-html><p>Ozonolysis of fatty acid monolayers was studied to understand the
fate of organic-coated aerosols under realistic atmospheric conditions.
Specifically, we investigated the effects of temperature and salinity on the degradation of oleic acid at the air–water interface and the persistence of
the aged surfactant film at the surface. The presence of a residual film is
of atmospheric importance, as surface monolayers affect the physical
properties of the droplets and because of the role they play in cloud
formation. This occurs via several effects, most notably via surface tension
reduction. The interplay between atmospheric aerosol loading and the
formation, nature, and persistence of clouds is a key uncertainty in climate
modelling.</p><p>Our data show that a residual surface film, which we suspect to be formed of
nonanoic acid and a mixture of azelaic and 9-oxononanoic acids, is retained
at the interface after ozonolysis at near-zero temperatures but not at room
temperature. Given the low-temperature conditions used here are
atmospherically realistic, the persistence of a product film must be
considered when assessing the impact of unsaturated fatty acid partitioned
to the air–water interface. The presence of stable (non-oxidisable)
reaction products also opens the possibility of build-up of inert monolayers
during the aerosol life cycle with potential implications for cloud
formation. Furthermore, we measured the kinetic behaviour of these films and
found that the reactions are not significantly affected by the shift to a
lower temperature with rate coefficients determined to be (2.2&thinsp;±&thinsp;0.4)&thinsp; × &thinsp;10<sup>−10</sup>&thinsp;cm<sup>2</sup>&thinsp;s<sup>−1</sup> at 21&thinsp;±&thinsp;1&thinsp;°C and
(2.2&thinsp;±&thinsp;0.2)&thinsp; × &thinsp;10<sup>−10</sup>&thinsp;cm<sup>2</sup>&thinsp;s<sup>−1</sup> at 2&thinsp;±&thinsp;1&thinsp;°C.</p></abstract-html>
<ref-html id="bib1.bib1"><label>1</label><mixed-citation>
Allan, J. D., Williams, P. I., Morgan, W. T., Martin, C. L., Flynn, M. J., Lee, J., Nemitz, E., Phillips, G. J., Gallagher, M. W., and Coe, H.: Contributions from transport, solid fuel burning and cooking to primary organic aerosols in two UK cities, Atmos. Chem. Phys., 10, 647–668, <a href="https://doi.org/10.5194/acp-10-647-2010" target="_blank">https://doi.org/10.5194/acp-10-647-2010</a>, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib2"><label>2</label><mixed-citation>
Ambaum, M. H. P.: Thermal Physics of the Atmosphere, 1st edn.,
Wiley-Blackwell, Reading, UK, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib3"><label>3</label><mixed-citation>
Barnes, G. T.: Permeation through monolayers, Colloid. Surface. A, 126, 149–158, <a href="https://doi.org/10.1016/S0927-7757(96)03926-X" target="_blank">https://doi.org/10.1016/S0927-7757(96)03926-X</a>, 1997.
</mixed-citation></ref-html>
<ref-html id="bib1.bib4"><label>4</label><mixed-citation>
Benjamin, I.: Chemical Reactions and Solvation at Liquid Interfaces: A
Microscopic Perspective Chemical Reactions and Solvation at Liquid
Interfaces: A Microscopic Perspective, Chem. Rev., 96, 1449–1476,
<a href="https://doi.org/10.1021/cr950230" target="_blank">https://doi.org/10.1021/cr950230</a>, 1996.
</mixed-citation></ref-html>
<ref-html id="bib1.bib5"><label>5</label><mixed-citation>
Cantrell, W. and Robinson, C.: Heterogeneous freezing of ammonium sulfate
and sodium chloride solutions by long chain alcohols, Geophys. Res. Lett.,
33, L07802, <a href="https://doi.org/10.1029/2005gl024945" target="_blank">https://doi.org/10.1029/2005gl024945</a>, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib6"><label>6</label><mixed-citation>
Chen, Y., Zhang, Y., Lambe, A. T., Xu, R., Lei, Z., Olson, N. E., Zhang, Z.,
Szalkowski, T., Cui, T., Vizuete, W., Gold, A., Turpin, B. J., Ault, A. P.,
Chan, M. N., and Surratt, J. D.: Heterogeneous Hydroxyl Radical Oxidation of
Isoprene-Epoxydiol-Derived Methyltetrol Sulfates: Plausible Formation
Mechanisms of Previously Unexplained Organosulfates in Ambient Fine
Aerosols, Environ. Sci. Technol. Lett., 7, 460–468,
<a href="https://doi.org/10.1021/acs.estlett.0c00276" target="_blank">https://doi.org/10.1021/acs.estlett.0c00276</a>, 2020.
</mixed-citation></ref-html>
<ref-html id="bib1.bib7"><label>7</label><mixed-citation>
Cohen Stuart, M. A., Wegh, R. A. J., Kroon, J. M., and Sudhölter, E. J.
R.: Design and Testing of a Low-Cost and Compact Brewster Angle Microscope,
Langmuir, 12, 2863–2865, <a href="https://doi.org/10.1021/la9507592" target="_blank">https://doi.org/10.1021/la9507592</a>, 1996.
</mixed-citation></ref-html>
<ref-html id="bib1.bib8"><label>8</label><mixed-citation>
Cosman, L. M., Knopf, D. A., and Bertram, A. K.: N<sub>2</sub>O<sub>5</sub> reactive
uptake on aqueous sulfuric acid solutions coated with branched and
straight-chain insoluble organic surfactants, J. Phys. Chem. A, 112,
2386–2396, <a href="https://doi.org/10.1021/jp710685r" target="_blank">https://doi.org/10.1021/jp710685r</a>, 2008.
</mixed-citation></ref-html>
<ref-html id="bib1.bib9"><label>9</label><mixed-citation>
Daumont, D., Brion, J., Charbonnier, J., and Malicet, J.: Ozone UV
spectroscopy I: Absorption cross sections at room temperature, J. Atmos.
Chem., 15, 135–155, 1992.
</mixed-citation></ref-html>
<ref-html id="bib1.bib10"><label>10</label><mixed-citation>
Donaldson, D. J. and Vaida, V.: The influence of organic films at the
air-aqueous boundary on atmospheric processes, Chem. Rev., 106,
1445–1461, <a href="https://doi.org/10.1021/cr040367c" target="_blank">https://doi.org/10.1021/cr040367c</a>, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib11"><label>11</label><mixed-citation>
Ellison, G. B., Tuck, A. F., and Vaida, V.: Atmospheric processing of organic
aerosols, J. Geophys. Res., 104, 11633–11641, <a href="https://doi.org/10.1029/1999JD900073" target="_blank">https://doi.org/10.1029/1999JD900073</a>,
1999.
</mixed-citation></ref-html>
<ref-html id="bib1.bib12"><label>12</label><mixed-citation>
Enami, S. and Colussi, A. J.: Efficient scavenging of Criegee intermediates
on water by surface-active cis-pinonic acid, Phys. Chem. Chem. Phys., 19,
17044–17051, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib13"><label>13</label><mixed-citation>
Fu, P. Q., Kawamura, K., Chen, J., Charrière, B., and Sempéré, R.: Organic molecular composition of marine aerosols over the Arctic Ocean in summer: contributions of primary emission and secondary aerosol formation, Biogeosciences, 10, 653–667, <a href="https://doi.org/10.5194/bg-10-653-2013" target="_blank">https://doi.org/10.5194/bg-10-653-2013</a>, 2013.
</mixed-citation></ref-html>
<ref-html id="bib1.bib14"><label>14</label><mixed-citation>
Gaines, G. L.: Insoluble Monolayers at the Liquid Gas Interface,
Interscience Publishers, New York, USA, 1966.
</mixed-citation></ref-html>
<ref-html id="bib1.bib15"><label>15</label><mixed-citation>
Gallimore, P. J., Griffiths, P. T., Pope, F. D., Reid, J. P., and Kalberer,
M.: Comprehensive modeling study of ozonolysis of oleic acid aerosol based
on real-time, online measurements of aerosol composition, J. Geophys. Res.-Atmos., 122, 4364–4377, <a href="https://doi.org/10.1002/2016JD026221" target="_blank">https://doi.org/10.1002/2016JD026221</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib16"><label>16</label><mixed-citation>
Garrett, W. D.: Retardation of Water Drop Evaporation with Monomolecular
Surface Films, J. Atmos. Sci., 28, 816–819,
<a href="https://doi.org/10.1175/1520-0469(1971)028&lt;0816:rowdew&gt;2.0.co;2" target="_blank">https://doi.org/10.1175/1520-0469(1971)028&lt;0816:rowdew&gt;2.0.co;2</a>,
1971.
</mixed-citation></ref-html>
<ref-html id="bib1.bib17"><label>17</label><mixed-citation>
Geŕard, V., Noziere, B., Fine, L., Ferronato, C., Singh, D. K., Frossard, A.
A., Cohen, R. C., Asmi, E., Lihavainen, H., Kivekas̈, N., Aurela, M., Brus,
D., Frka, S., Kusǎn, A. C.: Concentrations and Adsorption Isotherms for
Amphiphilic Surfactants in PM<sub>1</sub> Aerosols from Different Regions of Europe,
Environ. Sci. Technol., 53, 21, 12379–12388, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib18"><label>18</label><mixed-citation>
Gill, P. S., Graedel, T. E., and Weschler, C. J.: Organic films on
atmospheric aerosol particles, fog droplets, cloud droplets, raindrops, and
snowflakes, Rev. Geophys., 21, 903, <a href="https://doi.org/10.1029/RG021i004p00903" target="_blank">https://doi.org/10.1029/RG021i004p00903</a>, 1983.
</mixed-citation></ref-html>
<ref-html id="bib1.bib19"><label>19</label><mixed-citation>
Gilman, J. B., Eliason, T. L., Fast, A., and Vaida, V.: Selectivity and
stability of organic films at the air-aqueous interface, J. Colloid
Interf. Sci., 280, 234–43, <a href="https://doi.org/10.1016/j.jcis.2004.07.019" target="_blank">https://doi.org/10.1016/j.jcis.2004.07.019</a>, 2004.
</mixed-citation></ref-html>
<ref-html id="bib1.bib20"><label>20</label><mixed-citation>
Gross, S., Iannone, R., Xiao, S., and Bertram, A. K.: Reactive uptake studies
of NO<sub>3</sub> and N<sub>2</sub>O<sub>5</sub> on alkenoic acid, alkanoate, and polyalcohol
substrates to probe nighttime aerosol chemistry, Phys. Chem. Chem. Phys.,
11, 7792–7803, 2009.
</mixed-citation></ref-html>
<ref-html id="bib1.bib21"><label>21</label><mixed-citation>
Grotjahn, R.: General Circulation of the Atmosphere, Mean
Characteristics, in: Encyclopedia of Atmospheric Sciences, 2nd edn.,
edited by: North, G. R., Pyle, J., and Zhang, F., 73–89, Academic Press,
Oxford, UK, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib22"><label>22</label><mixed-citation>
Hung, H.-M. and Tang, C.-W.: Effects of Temperature and Physical State on
Heterogeneous Oxidation of Oleic Acid Droplets with Ozone, J. Phys. Chem. A,
114, 13104–13112, <a href="https://doi.org/10.1021/jp105042w" target="_blank">https://doi.org/10.1021/jp105042w</a>, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib23"><label>23</label><mixed-citation>
Hung, H.-M., Katrib, Y., and Martin, S. T.: Products and mechanisms of the
reaction of oleic acid with ozone and nitrate radical, J. Phys. Chem. A.,
109, 4517–4530, <a href="https://doi.org/10.1021/jp0500900" target="_blank">https://doi.org/10.1021/jp0500900</a>, 2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib24"><label>24</label><mixed-citation>
Jones, S. H., King, M. D., Ward, A. D., Rennie, A. R., Jones, A. C., and
Arnold, T.: Are organic films from atmospheric aerosol and sea water inert
to oxidation by ozone at the air-water interface?, Atmos. Environ., 161,
274–287, <a href="https://doi.org/10.1016/J.ATMOSENV.2017.04.025" target="_blank">https://doi.org/10.1016/J.ATMOSENV.2017.04.025</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib25"><label>25</label><mixed-citation>
King, M. D., Thompson, K. C., and Ward, A. D.: Laser Tweezers Raman Study of
Optically Trapped Aerosol Droplets of Seawater and Oleic Acid Reacting with
Ozone: Implications for Cloud-Droplet Properties, J. Am. Chem. Soc.,
126, 16710–16711, <a href="https://doi.org/10.1021/ja044717o" target="_blank">https://doi.org/10.1021/ja044717o</a>, 2004.
</mixed-citation></ref-html>
<ref-html id="bib1.bib26"><label>26</label><mixed-citation>
King, M. D., Rennie, A. R., Thompson, K. C., Fisher, F. N., Dong, C. C.,
Thomas, R. K., Pfrang, C., and Hughes, A. V.: Oxidation of oleic acid at the
air-water interface and its potential effects on cloud critical
supersaturations., Phys. Chem. Chem. Phys., 11, 7699–7707,
<a href="https://doi.org/10.1039/b906517b" target="_blank">https://doi.org/10.1039/b906517b</a>, 2009.
</mixed-citation></ref-html>
<ref-html id="bib1.bib27"><label>27</label><mixed-citation>
Knopf, D. A. and Forrester, S. M.: Freezing of Water and Aqueous NaCl
Droplets Coated by Organic Monolayers as a Function of Surfactant Properties
and Water Activity, J. Phys. Chem. A, 115, 5579–5591, 2011.
</mixed-citation></ref-html>
<ref-html id="bib1.bib28"><label>28</label><mixed-citation>
Knopf, D. A., Anthony, L. M., and Bertram, A. K.: Reactive uptake of O<sub>3</sub>
by multicomponent and multiphase mixtures containing oleic acid, J. Phys.
Chem. A, 109, 5579–5589, 2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib29"><label>29</label><mixed-citation>
Knopf, D. A., Cosman, L. M., Mousavi, P., Mokamati, S., and Bertram, A. K.: A
novel flow reactor for studying reactions on liquid surfaces coated by
organic monolayers: Methods, validation, and initial results, J. Phys. Chem.
A, 111, 11021–11032, <a href="https://doi.org/10.1021/Jp075724c" target="_blank">https://doi.org/10.1021/Jp075724c</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib30"><label>30</label><mixed-citation>
Knopf, D. A., Alpert, P. A., and Wang, B.: The Role of Organic Aerosol in
Atmospheric Ice Nucleation: A Review, ACS Earth Space Chem., 2, 168–202,
<a href="https://doi.org/10.1021/acsearthspacechem.7b00120" target="_blank">https://doi.org/10.1021/acsearthspacechem.7b00120</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib31"><label>31</label><mixed-citation>
Koop, T., Kapilashrami, A., Molina, L. T., and Molina, M. J.: Phase transitions
of sea-salt/water mixtures at low temperatures: Implications for ozone
chemistry in the polar marine boundary layer, J. Geophys. Res., 105,
26393–26402, 2000a.
</mixed-citation></ref-html>
<ref-html id="bib1.bib32"><label>32</label><mixed-citation>
Koop, T., Luo, B. P., Tsias, A., and Peter, T.: Water activity as the
determinant for homogeneous ice nucleation in aqueous solutions, Nature,
406, 611–614, <a href="https://doi.org/10.1038/35020537" target="_blank">https://doi.org/10.1038/35020537</a>, 2000b.
</mixed-citation></ref-html>
<ref-html id="bib1.bib33"><label>33</label><mixed-citation>
Kroflič, A., Frka, S., Simmel, M., Wex, H., and Grgič, I.: Size-Resolved
Surface-Active Substances of Atmospheric Aerosol: Reconsideration of the
Impact on Cloud Droplet Formation, Environ. Sci. Technol., 52,
9179–9187, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib34"><label>34</label><mixed-citation>
La Mer, V. K.: Retardation of Evaporation by Monolayers: Transport
Processes, Academic Press Inc., London, UK, 1962.
</mixed-citation></ref-html>
<ref-html id="bib1.bib35"><label>35</label><mixed-citation>
La Mer, V. K., Healy, T. W., and Aylmore, L. A. G.: The transport of water through monolayers of long-chain
n-paraffinic alcohols, J. Colloid Sci., 19, 673–684, 1964.
</mixed-citation></ref-html>
<ref-html id="bib1.bib36"><label>36</label><mixed-citation>
Last, D. J., Nájera, J. J., Wamsley, R., Hilton, G., McGillen, M.,
Percival, C. J., and Horn, A. B.: Ozonolysis of organic compounds and
mixtures in solution. Part I: Oleic, maleic, nonanoic and benzoic acids,
Phys. Chem. Chem. Phys., 11, 1427–1440, <a href="https://doi.org/10.1039/b815425b" target="_blank">https://doi.org/10.1039/b815425b</a>, 2009.
</mixed-citation></ref-html>
<ref-html id="bib1.bib37"><label>37</label><mixed-citation>
Li, S., Cheng, S., Du, L., and Wang, W.: Establishing a model organic film of
low volatile compound mixture on aqueous aerosol surface, Atmos. Environ.,
200, 15–23, <a href="https://doi.org/10.1016/j.atmosenv.2018.11.052" target="_blank">https://doi.org/10.1016/j.atmosenv.2018.11.052</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib38"><label>38</label><mixed-citation>
Lu, J. R., Thomas, R. K., and Penfold, J.: Surfactant layers at the air/water
interface: structure and composition, Adv. Colloid Interfac., 84,
143–304, <a href="https://doi.org/10.1016/S0001-8686(99)00019-6" target="_blank">https://doi.org/10.1016/S0001-8686(99)00019-6</a>, 2000.
</mixed-citation></ref-html>
<ref-html id="bib1.bib39"><label>39</label><mixed-citation>
McNeill, V. F., Patterson, J., Wolfe, G. M., and Thornton, J. A.: The effect of varying levels of surfactant on the reactive uptake of N<sub>2</sub>O<sub>5</sub> to aqueous aerosol, Atmos. Chem. Phys., 6, 1635–1644, <a href="https://doi.org/10.5194/acp-6-1635-2006" target="_blank">https://doi.org/10.5194/acp-6-1635-2006</a>, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib40"><label>40</label><mixed-citation>
McNeill, V. F., Wolfe, G. M., and Thornton, J. A.: The Oxidation of Oleate in
Submicron Aqueous Salt Aerosols: Evidence of a Surface Process, J. Phys.
Chem. A, 111, 1073–1083, <a href="https://doi.org/10.1021/JP066233F" target="_blank">https://doi.org/10.1021/JP066233F</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib41"><label>41</label><mixed-citation>
Mmereki, B. T. and Donaldson, D. J.: Laser induced fluorescence of pyrene at
an organic coated air-water interface, Phys. Chem. Chem. Phys., 4,
4186–4191, <a href="https://doi.org/10.1039/b204754c" target="_blank">https://doi.org/10.1039/b204754c</a>, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib42"><label>42</label><mixed-citation>
Mmereki, B. T., Chaudhuri, S. R., and Donaldson, D. J.: Enhanced Uptake of
PAHs by Organic-Coated Aqueous Surfaces, J. Phys. Chem. A, 107,
2264–2269, <a href="https://doi.org/10.1021/jp027361g" target="_blank">https://doi.org/10.1021/jp027361g</a>, 2003.
</mixed-citation></ref-html>
<ref-html id="bib1.bib43"><label>43</label><mixed-citation>
Moise, T. and Rudich, Y.: Reactive Uptake of Ozone by Aerosol-Associated
Unsaturated Fatty Acids: Kinetics, Mechanism, and Products, J. Phys. Chem.
A, 106, 6469–6476, <a href="https://doi.org/10.1021/jp025597e" target="_blank">https://doi.org/10.1021/jp025597e</a>, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib44"><label>44</label><mixed-citation>
Nelson, A.: Co-refinement of multiple-contrast neutron/X-ray reflectivity
data using MOTOFIT, J. Appl. Crystallogr., 39, 273–276,
<a href="https://doi.org/10.1107/S0021889806005073" target="_blank">https://doi.org/10.1107/S0021889806005073</a>, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib45"><label>45</label><mixed-citation>
Nozière, B., Baduel, C., and Jaffrezo, J.-L.: The dynamic surface tension of
atmospheric aerosol surfactants reveals new aspects of cloud activation,
Nat. Commun., 5, 3335, <a href="https://doi.org/10.1038/ncomms4335" target="_blank">https://doi.org/10.1038/ncomms4335</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib46"><label>46</label><mixed-citation>
O'Neil, M. J. (Ed.): The Merck Index – An Encyclopedia of Chemicals, Drugs,
and Biologicals, Merck and Co., Inc., Whitehouse Station, NJ, USA, p. 153, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib47"><label>47</label><mixed-citation>
Ovadnevaite, J., Zuend, A., Laaksonen, A., Sanchez, K. J., Roberts, G.,
Ceburnis, D., Decesari, S., Rinaldi, M., Hodas, N., Facchini, M. C.,
Seinfeld, J. H., and O'Dowd, C.: Surface tension prevails over solute effect in organic-influenced cloud droplet activation, Nature, 546, 637–641,
2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib48"><label>48</label><mixed-citation>
Pfrang, C., Shiraiwa, M., and Pöschl, U.: Chemical ageing and transformation of diffusivity in semi-solid multi-component organic aerosol particles, Atmos. Chem. Phys., 11, 7343–7354, <a href="https://doi.org/10.5194/acp-11-7343-2011" target="_blank">https://doi.org/10.5194/acp-11-7343-2011</a>, 2011.
</mixed-citation></ref-html>
<ref-html id="bib1.bib49"><label>49</label><mixed-citation>
Pfrang, C., Sebastiani, F., Lucas, C. O. M., King, M. D., Hoare, I. D.,
Chang, D., and Campbell, R. A.: Ozonolysis of methyl oleate monolayers at the
air–water interface: oxidation kinetics, reaction products and atmospheric
implications, Phys. Chem. Chem. Phys., 16, 13220–13228,
<a href="https://doi.org/10.1039/c4cp00775a" target="_blank">https://doi.org/10.1039/c4cp00775a</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib50"><label>50</label><mixed-citation>
Pfrang, C., Rastogi, K., Cabrera-Martinez, E. R., Seddon, A. M., Dicko, C.,
Labrador, A., Plivelic, T. S., Cowieson, N., and Squires, A. M.: Complex
three-dimensional self-assembly in proxies for atmospheric aerosols, Nat.
Commun., 8, 1724, <a href="https://doi.org/10.1038/s41467-017-01918-1" target="_blank">https://doi.org/10.1038/s41467-017-01918-1</a>, 2017a.
</mixed-citation></ref-html>
<ref-html id="bib1.bib51"><label>51</label><mixed-citation>
Pfrang, C., Woden, B., Skoda, M., and Gubb, C.: More than the sum – oxidation behaviour of mixed fatty acid monolayers, STFC ISIS Neutron and Muon Source, <a href="https://doi.org/10.5286/ISIS.E.87020742" target="_blank">https://doi.org/10.5286/ISIS.E.87020742</a>, 2017b.
</mixed-citation></ref-html>
<ref-html id="bib1.bib52"><label>52</label><mixed-citation>
Pfrang, C., Skoda, M., Woden, B., and Hartmane, E.: Closer to Reality: Studies of Mixed Organic Monolayer Ozonolysis at Atmospherically Relevant Temperature and Salinity Conditions, STFC ISIS Neutron and Muon Source, <a href="https://doi.org/10.5286/ISIS.E.92919810" target="_blank">https://doi.org/10.5286/ISIS.E.92919810</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib53"><label>53</label><mixed-citation>
Ray, A. K., Devakottai, B., Souyri, A., and Huckaby, J. L.: Evaporation
characteristics of droplets coated with immiscible layers of nonvolatile
liquids, Langmuir, 7, 525–531, <a href="https://doi.org/10.1021/la00051a019" target="_blank">https://doi.org/10.1021/la00051a019</a>, 1991.
</mixed-citation></ref-html>
<ref-html id="bib1.bib54"><label>54</label><mixed-citation>
Rideal, E. K.: On the Influence of Thin Surface Films on the Evaporation of
Water, J. Phys. Chem., 29, 1585–1588, <a href="https://doi.org/10.1021/j150258a011" target="_blank">https://doi.org/10.1021/j150258a011</a>, 1924.
</mixed-citation></ref-html>
<ref-html id="bib1.bib55"><label>55</label><mixed-citation>
Rudich, Y.: Laboratory perspectives on the chemical transformations of
organic matter in atmospheric particles, Chem. Rev., 103, 5097–5124,
2003.
</mixed-citation></ref-html>
<ref-html id="bib1.bib56"><label>56</label><mixed-citation>
Ruehl, C. R., Davies, J. F., and Wilson, K. R.: An interfacial mechanism for
cloud droplet formation on organic aerosols, Science, 351, 1447–1450,
2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib57"><label>57</label><mixed-citation>
Sareen, N., Schwier, A. N., Lathem, T. L., Nenes, A., and McNeill, V. F.:
Surfactants from the gas phase may promote cloud droplet formation, P.
Natl. Acad. Sci. USA, 110, 2723–2728, 2013.
</mixed-citation></ref-html>
<ref-html id="bib1.bib58"><label>58</label><mixed-citation>
Sebastiani, F., Campbell, R. A., and Pfrang, C.: Complementarity of neutron
reflectometry and ellipsometry for the study of atmospheric reactions at the
air–water interface, RSC Adv., 5, 107105–107111,
<a href="https://doi.org/10.1039/C5RA22725A" target="_blank">https://doi.org/10.1039/C5RA22725A</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib59"><label>59</label><mixed-citation>
Sebastiani, F., Campbell, R. A., Rastogi, K., and Pfrang, C.: Nighttime oxidation of surfactants at the air–water interface: effects of chain length, head group and saturation, Atmos. Chem. Phys., 18, 3249–3268, <a href="https://doi.org/10.5194/acp-18-3249-2018" target="_blank">https://doi.org/10.5194/acp-18-3249-2018</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib60"><label>60</label><mixed-citation>
Shrivastava, M. K., Subramanian, R., Rogge, W. F., and Robinson, A. L.:
Sources of organic aerosol: Positive matrix factorization of molecular
marker data and comparison of results from different source apportionment
models, Atmos. Environ., 41, 9353–9369,
<a href="https://doi.org/10.1016/j.atmosenv.2007.09.016" target="_blank">https://doi.org/10.1016/j.atmosenv.2007.09.016</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib61"><label>61</label><mixed-citation>
Skoda, M. W. A., Thomas, B., Hagreen, M., Sebastiani, F., and Pfrang, C.:
Simultaneous neutron reflectometry and infrared reflection absorption
spectroscopy (IRRAS) study of mixed monolayer reactions at the air-water
interface, RSC Adv., 7, 34208–34214, <a href="https://doi.org/10.1039/C7RA04900E" target="_blank">https://doi.org/10.1039/C7RA04900E</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib62"><label>62</label><mixed-citation>
Smith, G. D., Woods, E., DeForest, C. L., Baer, T., and Miller, R. E.:
Reactive uptake of ozone by oleic acid aerosol particles: Application of
single-particle mass spectrometry to heterogeneous reaction kinetics, J.
Phys. Chem. A, 106, 8085–8095, <a href="https://doi.org/10.1021/jp020527t" target="_blank">https://doi.org/10.1021/jp020527t</a>, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib63"><label>63</label><mixed-citation>
Stevens, B. and Feingold, G.: Untangling aerosol effects on clouds and
precipitation in a buffered system, Nature, 461, 607–613,
<a href="https://doi.org/10.1038/nature08281" target="_blank">https://doi.org/10.1038/nature08281</a>, 2009.
</mixed-citation></ref-html>
<ref-html id="bib1.bib64"><label>64</label><mixed-citation>
Tervahattu, H., Juhanoja, J., and Kupiainen, K.: Identification of an organic
coating on marine aerosol particles by TOF-SIMS, J. Geophys. Res.-Atmos., 107, ACH 18-1–ACH 18-7, <a href="https://doi.org/10.1029/2001JD001403" target="_blank">https://doi.org/10.1029/2001JD001403</a>, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib65"><label>65</label><mixed-citation>
Thomas, B., Maestro, A., Milsom, A., Pfrang, C., and Skoda, M.: Oxidation Kinetics of Oleic Acid in Mixed Fatty Acid Monolayers: Miscible Vs Immiscible Mixtures, Institut Laue-Langevin (ILL), <a href="https://doi.org/10.5291/ILL-DATA.9-10-1518" target="_blank">https://doi.org/10.5291/ILL-DATA.9-10-1518</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib66"><label>66</label><mixed-citation>
Thornberry, T. and Abbatt, J. P. D.: Heterogeneous reaction of ozone with
liquid unsaturated fatty acids: detailed kinetics and gas-phase product
studies, Phys. Chem. Chem. Phys., 6, 84–93, 2004.
</mixed-citation></ref-html>
<ref-html id="bib1.bib67"><label>67</label><mixed-citation>
Thornton, J. A. and Abbatt, J. P. D.: N<sub>2</sub>O<sub>5</sub> reaction on submicron
sea salt aerosol: Kinetics, products, and the effect of surface active
organics, J. Phys. Chem. A, 109, 10004–10012, <a href="https://doi.org/10.1021/jp054183t" target="_blank">https://doi.org/10.1021/jp054183t</a>,
2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib68"><label>68</label><mixed-citation>
Tomoaia-Cotisel, M. and Cadenhead, D. A.: The interaction of procaine with
stearic acid monolayers at the air/water interface, Langmuir, 7,
964–974, <a href="https://doi.org/10.1021/la00053a025" target="_blank">https://doi.org/10.1021/la00053a025</a>, 1991.
</mixed-citation></ref-html>
<ref-html id="bib1.bib69"><label>69</label><mixed-citation>
Tuckermann, R.: Surface tension of aqueous solutions of water-soluble
organic and inorganic compounds, Atmos. Environ., 41, 6265–6275,
<a href="https://doi.org/10.1016/j.atmosenv.2007.03.051" target="_blank">https://doi.org/10.1016/j.atmosenv.2007.03.051</a>, 2007.

</mixed-citation></ref-html>
<ref-html id="bib1.bib70"><label>70</label><mixed-citation>
Voss, L. F., Bazerbashi, M. F., Beekman, C. P., Hadad, C. M., and Allen, H.
C.: Oxidation of oleic acid at air/liquid interfaces, J. Geophys. Res.,
112, D06209, <a href="https://doi.org/10.1029/2006JD007677" target="_blank">https://doi.org/10.1029/2006JD007677</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib71"><label>71</label><mixed-citation>
Warneck, P.: Chemistry of the Natural Atmosphere, vol. 71, 2nd edn.,
available at:
<a href="https://www.elsevier.com/books/chemistry-of-the-natural-atmosphere/warneck/978-0-12-735632-7" target="_blank"/> (last access: 6 December 2020),
1999.
</mixed-citation></ref-html>
<ref-html id="bib1.bib72"><label>72</label><mixed-citation>
Woden, B., Skoda, M. W. A., Hagreen, M., and Pfrang, C.: Night-Time Oxidation
of a Monolayer Model for the Air–Water Interface of Marine Aerosols – A
Study by Simultaneous Neutron Reflectometry and in Situ Infra-Red Reflection
Absorption Spectroscopy (IRRAS), Atmosphere, 9, 471,
<a href="https://doi.org/10.3390/atmos9120471" target="_blank">https://doi.org/10.3390/atmos9120471</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib73"><label>73</label><mixed-citation>
Zahardis, J. and Petrucci, G. A.: The oleic acid-ozone heterogeneous reaction system: products, kinetics, secondary chemistry, and atmospheric implications of a model system – a review, Atmos. Chem. Phys., 7, 1237–1274, <a href="https://doi.org/10.5194/acp-7-1237-2007" target="_blank">https://doi.org/10.5194/acp-7-1237-2007</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib74"><label>74</label><mixed-citation>
Zhou, S., Joudan, S., Forbes, M. W., Zhou, Z., and Abbatt, J. P. D., Reaction
of Condensed-Phase Criegee Intermediates with Carboxylic Acids and
Perfluoroalkyl Carboxylic Acids, Environ. Sci. Technol. Lett., 6,
243–250, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib75"><label>75</label><mixed-citation>
Zobrist, B., Koop, T., Luo, B. P., Marcolli, C., and Peter, T.: Heterogeneous
ice nucleation rate coefficient of water droplets coated by a nonadecanol
monolayer, J. Phys. Chem. C, 111, 2149–2155, <a href="https://doi.org/10.1021/Jp066080w" target="_blank">https://doi.org/10.1021/Jp066080w</a>,
2007.
</mixed-citation></ref-html>--></article>
