<?xml version='1.0' encoding='utf-8'?>
<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>Nancy C. Nelson</dc:contributor>
  <dc:contributor>Cathy A. Smith</dc:contributor>
  <dc:creator>Gary A. Wedemeyer</dc:creator>
  <dc:date>1978</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Ozone and chlorine inactivation curves were determined in three water types at 10 &amp;deg;C for the fish pathogenic viruses infectious hematopoietic necrosis (IHNV) and infectious pancreatic necrosis (IPNV). In phosphate-buffered, distilled water (PBDW) an ozone dose of 0.01&amp;ensp;mg/L for 30 or 60&amp;ensp;s inactivated IHNV or IPNV, respectively, suspended at a tissue culture 50% infective dose (TCID50) of 10&lt;/span&gt;&lt;sup&gt;4&lt;/sup&gt;&lt;span&gt;&amp;ndash;10&lt;/span&gt;&lt;sup&gt;5&lt;/sup&gt;&lt;span&gt;/mL. In hard (120&amp;ensp;mg/L as CaCO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;span&gt;) and soft water (30&amp;ensp;mg/L) lake waters, an ozone application rate of 70&amp;ensp;mg∙h&lt;/span&gt;&lt;sup&gt;&amp;minus;1&lt;/sup&gt;&lt;span&gt;∙L&lt;/span&gt;&lt;sup&gt;&amp;minus;1&lt;/sup&gt;&lt;span&gt;&amp;nbsp;for 10&amp;ensp;min destroyed IHNV. IPNV inactivation in hard water required 90&amp;ensp;mg∙O&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;span&gt;∙h&lt;/span&gt;&lt;sup&gt;&amp;minus;1&lt;/sup&gt;&lt;span&gt;∙L&lt;/span&gt;&lt;sup&gt;&amp;minus;1&lt;/sup&gt;&lt;span&gt;&amp;nbsp;for 10&amp;ensp;min but only a 30-s contact time in soft water. The IPNV was also somewhat more resistant to chlorine. In PBDW, a residual of 0.1&amp;ensp;mg/L with contact times of 30 and 60&amp;ensp;s, respectively, destroyed IHNV and IPNV. In soft lake water IHNV was destroyed within 5&amp;ensp;min at 0.5&amp;ensp;mg/L, while in hard water a 10-min contact time was required. For IPNV disinfection in soft water, 0.2&amp;ensp;mg/L for 10&amp;ensp;min was sufficient but this chlorine residual had essentially no effect on IPNV in hard water. Increasing this dose to 0.7&amp;ensp;mg/L destroyed IPNV in hard water within 2&amp;ensp;min. In untreated waters, IPNV was stable for at least 8&amp;ensp;wk in either distilled, soft, or hard lake waters. However, IHNV survived only about 2&amp;ensp;wk in distilled and 7&amp;ensp;wk in the soft or hard lake waters. We suggest the serious consideration of ozone as a fish disease control agent.&amp;nbsp;&lt;/span&gt;&lt;i&gt;Key words&lt;/i&gt;&lt;span&gt;: ozone, chlorine disinfection, fish pathogens, viruses&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1139/f78-140</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>NRC Research Press</dc:publisher>
  <dc:title>Survival of the salmonid viruses infectious hematopoietic necrosis (IHNV) and infectious pancreatic necrosis (IPNV) in ozonated, chlorinated, and Untreated waters</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>