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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics Discussions</journal_title>
		<journal_url>www.atmos-chem-phys-discuss.net</journal_url>
		<issn>1680-7367</issn>
		<eissn>1680-7375</eissn>
		<volume_number>2</volume_number>
		<issue_number>6</issue_number>
		<publication_year>2002</publication_year>
	</journal>
	<doi>10.5194/acpd-2-1809-2002</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/2/1809/2002/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/2/1809/2002/acpd-2-1809-2002.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/2/1809/2002/acpd-2-1809-2002.pdf</fulltext_pdf>
	<start_page>1809</start_page>
	<end_page>1845</end_page>
	<publication_date>2002-11-05</publication_date>
	<article_title content_type="html">Ozone decomposition on Saharan dust: an experimental investigation</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>F. Hanisch</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>J. N. Crowley</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Max-Planck-Institut für Chemie, Division of Atmospheric Chemistry, Postfach 3060, 55020 Mainz, Germany</affiliation>
	</affiliations>
	<abstract content_type="html">The heterogeneous reaction between
      O&lt;sub&gt;3&lt;/sub&gt; and authentic Saharan dust surfaces was investigated in a Knudsen reactor
      at approx 296 K. O&lt;sub&gt;3&lt;/sub&gt;
      was destroyed on the dust surface and O&lt;sub&gt;2&lt;/sub&gt;
      was formed with conversion efficiencies of 1.0 and 1.3 molecules O&lt;sub&gt;2&lt;/sub&gt;
      per O&lt;sub&gt;3&lt;/sub&gt; molecule destroyed for
      unheated and heated samples, respectively. No O&lt;sub&gt;3&lt;/sub&gt;
      desorbed from exposed dust samples, showing that the uptake was irreversible. The uptake coefficients for the irreversible
      destruction of O&lt;sub&gt;3&lt;/sub&gt;
      on (unheated) Saharan dust surfaces depended on the O&lt;sub&gt;3&lt;/sub&gt;
      concentration and varied between 3.5 x10&lt;sup&gt;-4&lt;/sup&gt; and 5.5 x10&lt;sup&gt;-6&lt;/sup&gt; for the initial uptake coefficient
      (&lt;font face=&quot;Symbol&quot;    &gt;g&lt;/font&gt;&lt;sub&gt;0&lt;/sub&gt;
      approx 3 x10&lt;sup&gt;-5&lt;/sup&gt; at 30 ppbv O&lt;sub&gt;3&lt;/sub&gt;
      STP) and between 4.8 x10&lt;sup&gt;-5&lt;/sup&gt; and 2.2 x10&lt;sup&gt;-6&lt;/sup&gt; for the steady-state uptake coefficient
      (&lt;font face=&quot;Symbol&quot;    &gt;g&lt;/font&gt;&lt;sub&gt;ss&lt;/sub&gt;
      approx 7 x10&lt;sup&gt;-6&lt;/sup&gt; at 30 ppbv O&lt;sub&gt;3&lt;/sub&gt;
      STP). At very high O&lt;sub&gt;3&lt;/sub&gt;
      concentrations the surface was deactivated, and O&lt;sub&gt;3&lt;/sub&gt;
      uptake ceased after a certain exposure period. Sample re-activation (i.e.
      de-passivation) was found to occur over periods of hours, after exposure to
      O&lt;sub&gt;3&lt;/sub&gt;
      had ceased, suggesting that re-activation processes play a role both in the laboratory and in the atmosphere.</abstract>
	<references>
	</references>
</article>

