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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Environ. Sci.</journal-id>
<journal-title>Frontiers in Environmental Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Environ. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-665X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">882284</article-id>
<article-id pub-id-type="doi">10.3389/fenvs.2022.882284</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Environmental Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Fate of Parasites and Viruses in Calcium Hydroxide-Treated Urine in Relation to Temperature and Moisture Content</article-title>
<alt-title alt-title-type="left-running-head">Senecal et al.</alt-title>
<alt-title alt-title-type="right-running-head">Fate of Parasites and Viruses in Treated Urine</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Senecal</surname>
<given-names>Jenna</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<uri xlink:href="https://loop.frontiersin.org/people/849800/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Nordin</surname>
<given-names>Annika Christina</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/941314/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Decrey</surname>
<given-names>Lo&#xef;c</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Kohn</surname>
<given-names>Tamar</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/469789/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Vinner&#xe5;s</surname>
<given-names>Bj&#xf6;rn</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/574661/overview"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Department of Energy and Technology</institution>, <institution>Swedish University of Agricultural Sciences</institution>, <addr-line>Uppsala</addr-line>, <country>Sweden</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Laboratory of Environmental Chemistry</institution>, <institution>School of Architecture, Civil and Environmental Engineering (ENAC)</institution>, <institution>&#xc9;cole Polytechnique F&#xe9;d&#xe9;rale de Lausanne (EPFL)</institution>, <addr-line>Lausanne</addr-line>, <country>Switzerland</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1507161/overview">Susana Segura Munoz</ext-link>, University of S&#xe3;o Paulo, Brazil</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1713531/overview">Marina Smidt Celere Meschede</ext-link>, Federal University of Western Par&#xe1;, Brazil</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1719492/overview">Neni Sintawardani</ext-link>, National Research and Innovation Agency (BRIN), Indonesia</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Jenna Senecal, <email>jenna.senecal@slu.se</email>
</corresp>
<fn fn-type="other">
<p>This article was submitted to Water and Wastewater Management, a section of the journal Frontiers in Environmental Science</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>10</day>
<month>05</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>10</volume>
<elocation-id>882284</elocation-id>
<history>
<date date-type="received">
<day>23</day>
<month>02</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>19</day>
<month>04</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2022 Senecal, Nordin, Decrey, Kohn and Vinner&#xe5;s.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Senecal, Nordin, Decrey, Kohn and Vinner&#xe5;s</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Human urine can be used as fertilizer and technologies, such as alkaline-urine treatment, are being developed to enable easier re-use. There is, however, a risk of pathogens being present in the urine. This hygiene assessment examined inactivation of three model organisms, one parasite (<italic>Ascaris suum</italic>) and two viruses (coliphages MS2 and &#x3a6;X174), during 1) alkaline-urine treatment and 2) drying of the alkalized-urine (<italic>A. suum</italic> only). Fresh human urine was mixed with calcium hydroxide (10&#xa0;g Ca(OH)<sub>2</sub>&#xa0;L<sup>&#x2212;1</sup> urine) and divided into three fractions (Mixed liquor, Supernate, Precipitates). The factions were inoculated with the model organisms and then subjected to three treatments (Drying-storage, Stored and Thermal treatment) at temperatures between 20 and 50&#xb0;C. For <italic>Ascaris</italic>, drying (moisture content (MC) 13&#x2013;33%) the alkaline-urine proved effective in shortening the time required for a 3 log<sub>10</sub> reduction in viable eggs at 20&#xb0;C, but only Partially drying (MC 73&#x2013;82%) the urine led to longer inactivation times compared with Wet (MC &#x3e;90%) or Dry conditions. While virus inactivation took place during the initial addition of Ca(OH)<sub>2</sub>, the viruses that were embedded in feces survived longer compared to the free viruses. At pH 11.5, contact times of 1.5 and 90.7&#xa0;min were required to achieve a 4 log<sub>10</sub> decay of phages in solution and phages embedded in feces respectively. In areas prone to parasites, Thermal treatment (&#x2265;42&#xb0;C) and/or Storage (111&#xa0;days at 20&#xb0;C or 79&#xa0;days at 35&#xb0;C) is recommended in order to meet the WHO and USEPA guidelines for unrestricted fertilizer use. Drying (MC 73&#x2013;82%) can also be used in combination with thermal treatment and/or storage, to accelerate the process.</p>
</abstract>
<kwd-group>
<kwd>alkaline</kwd>
<kwd>urine</kwd>
<kwd>pathogen</kwd>
<kwd>nutrient recycling</kwd>
<kwd>Ascaris</kwd>
</kwd-group>
<contract-num rid="cn001">OPP1111293</contract-num>
<contract-sponsor id="cn001">Bill and Melinda Gates Foundation<named-content content-type="fundref-id">10.13039/100000865</named-content>
</contract-sponsor>
</article-meta>
</front>
<body>
<sec id="s1">
<title>
<bold>Highlights</bold>:</title>
<p>
<list list-type="simple">
<list-item>
<p>&#x2022; In areas prone to parasites, a post-urine-drying-treatment is recommended</p>
</list-item>
<list-item>
<p>&#x2022; Partial drying led to longer inactivation times for <italic>Ascaris</italic> compared to dried</p>
</list-item>
<list-item>
<p>&#x2022; Virus inactivation took place mainly during the initial addition of Ca(OH)<sub>2</sub>
</p>
</list-item>
<list-item>
<p>&#x2022; Viruses embedded in feces survived longer than free viruses in alkaline solutions</p>
</list-item>
</list>
</p>
</sec>
<sec id="s2">
<title>1 Introduction</title>
<p>Urine contains the majority of plant-available nutrients found in household wastewater (<xref ref-type="bibr" rid="B23">J&#xf6;nsson et al., 2005</xref>) and is a contributor to eutrophication and hypoxia in aquatic environments (<xref ref-type="bibr" rid="B47">Smil 2002</xref>; <xref ref-type="bibr" rid="B48">Sp&#xe5;ngberg et al., 2014</xref>; <xref ref-type="bibr" rid="B50">Steffen et al., 2015</xref>; <xref ref-type="bibr" rid="B26">Larsen 2020</xref>). As alternative management of these nutrients, urine can be collected, stored and applied as a fertilizer (<xref ref-type="bibr" rid="B18">Harder et al., 2019</xref>). However, this poses a logistical challenge, with approximately 350&#x2013;1000&#xa0;l urine being produced per person per year (Vinner&#xe5;s et al., 2006). Storing the urine until application as a fertilizer requires either a large storage tank or frequent emptying to a central storage unit, as fertilizers are generally only applied once or twice per growing season. A solution to this is to concentrate the urine, which is &#x3e;95% water. Various techniques for concentrating or extracting the nutrients in urine are being developed (<xref ref-type="bibr" rid="B29">Maurer et al., 2006</xref>; <xref ref-type="bibr" rid="B1">Antonini et al., 2012</xref>; <xref ref-type="bibr" rid="B46">Senecal and Vinner&#xe5;s 2017</xref>; <xref ref-type="bibr" rid="B41">Randall and Naidoo 2018</xref>; <xref ref-type="bibr" rid="B52">Volpin et al., 2018</xref>; <xref ref-type="bibr" rid="B28">Martin 2020</xref>).</p>
<p>When recirculating the nutrients in the urine, there is also a risk of recirculating pathogens. Only a few pathogens are excreted via the urine, compared with feces (<xref ref-type="bibr" rid="B2">Aw 2018</xref>). However, there is a risk of cross-contamination from the feces to the urine during excretion and collection (<xref ref-type="bibr" rid="B21">H&#xf6;glund et al., 2000</xref>; <xref ref-type="bibr" rid="B4">Bischel et al., 2015</xref>). Feces can potentially contain many pathogenic viruses, bacteria, protozoa, and helminths, many of which are immediately infectious upon excretion (<xref ref-type="bibr" rid="B2">Aw 2018</xref>). Cross-contamination of 9.1&#xa0;mg of feces per liter of urine has been estimated for urine-diverting toilets (<xref ref-type="bibr" rid="B43">Sch&#xf6;nning et al., 2002</xref>) (no newer data was found). Due to the cross-contamination with feces, there is a potential health risk for the people handling and/or using diverted urine as a fertilizer (<xref ref-type="bibr" rid="B53">WHO 2006</xref>; <xref ref-type="bibr" rid="B3">Bischel et al., 2019</xref>) hence the importance of hygiene evaluations of emerging technologies.</p>
<p>One method being developed to concentrate urine is the use of alkalizing media to raise the urine&#x2019;s pH and block the biochemical degradation of urea, which then enables dehydration with minimal loss of nitrogen (N) (<xref ref-type="bibr" rid="B11">Dutta and Vinner&#xe5;s 2016</xref>; <xref ref-type="bibr" rid="B40">Randall et al., 2016</xref>; <xref ref-type="bibr" rid="B46">Senecal and Vinner&#xe5;s 2017</xref>; <xref ref-type="bibr" rid="B6">Chipako and Randall 2020</xref>). (<xref ref-type="bibr" rid="B40">Randall et al., 2016</xref> &#x23;371@@author-year) recommends 10&#xa0;g Ca(OH)<sub>2</sub>&#xa0;L<sup>&#x2212;1</sup> of fresh urine to ensure that the urine is always saturated with calcium hydroxide keeping the pH &#x3e; 12, which prevents biochemical hydroxylation of urea to ammonia (<xref ref-type="bibr" rid="B40">Randall et al., 2016</xref>; <xref ref-type="bibr" rid="B16">Geinzer 2017</xref>). The pH must remain &#x3e;11 to minimize urease enzyme activity and temperature during evaporation shall not exceed 60&#xb0;C to minimize thermal degradation of urea (<xref ref-type="bibr" rid="B40">Randall et al., 2016</xref> &#x23;371).</p>
<p>Helminths have shown to be highly resistant to various chemical treatments (<xref ref-type="bibr" rid="B17">Ghiglietti et al., 1997</xref>; <xref ref-type="bibr" rid="B33">Nordin et al., 2009</xref>; <xref ref-type="bibr" rid="B32">Naidoo et al., 2016</xref>; <xref ref-type="bibr" rid="B44">Senecal et al., 2018</xref>; <xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>) and physical treatments (<xref ref-type="bibr" rid="B9">Decrey et al., 2011</xref>). Other pathogenic organisms, such as viruses, are more sensitive to high pH (<xref ref-type="bibr" rid="B34">Nyberg et al., 2011</xref>; <xref ref-type="bibr" rid="B7">Decrey et al., 2016</xref>; <xref ref-type="bibr" rid="B44">Senecal et al., 2018</xref>), however they are secreted in greater number. Thus in the present study, the inactivation of one helminth, <italic>Ascaris suum</italic>, and two virus surrogates, bacteriophage &#x3a6;X174 and MS2, were used to assess the effect of the alkaline pre-treatment and (for helminth only) drying of alkalized urine.</p>
<p>
<italic>Ascaris</italic> eggs were used as a conservative model organism, especially during chemical treatment, to assess the efficiency of treatment, as they are one of the most resilient pathogens excreted (<xref ref-type="bibr" rid="B13">Feachem et al., 1983</xref>; <xref ref-type="bibr" rid="B22">Jim&#xe9;nez 2006</xref>; <xref ref-type="bibr" rid="B37">Pecson et al., 2007</xref>; <xref ref-type="bibr" rid="B30">Maya et al., 2010</xref>). Bacteriophage &#x3a6;X174 (ssDNA virus) and MS2 (ssRNA) were used as conservative surrogates of human and animal viruses in general (<xref ref-type="bibr" rid="B12">Emmoth et al., 2011</xref>; <xref ref-type="bibr" rid="B27">Magri et al., 2015</xref>; <xref ref-type="bibr" rid="B7">Decrey et al., 2016</xref>; <xref ref-type="bibr" rid="B8">Decrey and Kohn 2017</xref>).</p>
<p>The overall aim of the study was to determine inactivation rates in relation to composition of sample, treatment temperature, and dry matter content in order to provide hygienic handling recommendations for the urine/Ca(OH)<sub>2</sub> solution to produce a urine-based fertilizer that meets the existing guidelines <xref ref-type="bibr" rid="B53">WHO (2006)</xref> and <xref ref-type="bibr" rid="B51">USEPA (1994)</xref> for unrestricted fertilizer use.</p>
</sec>
<sec id="s3">
<title>2 Materials and Methods</title>
<p>
<italic>Ascaris</italic> eggs and viruses exhibit different sensitivity to the physical-chemical treatment conditions expected in alkaline-urine treatment. Especially, <italic>Ascaris</italic> eggs&#x2019; survival is more affected by temperature increase and moisture reduction whereas virus fate is mainly driven by pH increase. For viruses, the main driver of inactivation in alkaline-urine treatment is high pH, rather than moisture reduction (<xref ref-type="bibr" rid="B9">Decrey et al., 2011</xref>; <xref ref-type="bibr" rid="B7">Decrey et al., 2016</xref>). In this study, virus inactivation rates were observed in liquids with different alkaline pH at ambient temperature (with and without enmeshment in fecal material), while <italic>Ascaris</italic> inactivation rates were observed in both liquid and dried urine (all eggs were enmeshed in fecal material). Thus, the following experimental methods differ between <italic>Ascaris</italic> and the bacteriophages in order to focus on the most relevant parameters to each given organism.</p>
<sec id="s3-1">
<title>2.1 Urine and Feces Collection and Handling</title>
<p>For study of inactivation of <italic>Ascaris</italic>, &#x3e;10 urine samples were collected by anonymous donations during 1&#xa0;week in 1-L sterile containers at the departments toilet and stored at 4&#xb0;C until use. Human feces (in total 300&#xa0;g) were collected fresh from two people anonymously at the department toilets and stored frozen until use.</p>
<p>For studies of bacteriophage inactivation, fresh feces were obtained from a male adult and stored at 4&#xb0;C less than 1&#xa0;week before experiment. Prior to experiment, the feces were tested and no coliphages detected (detection limit: 100&#xa0;PFU&#xa0;ml<sup>&#x2212;1</sup>).</p>
</sec>
<sec id="s3-2">
<title>2.2 Microorganisms</title>
<p>
<italic>Ascaris suum</italic> eggs were retrieved by sieving feces from inoculated swine (Excelsior Sentinel, Inc., United States) and stored at 4&#xb0;C in diluted formalin solution during transportation and storage prior to use. Coliphages MS2 (DSMZ 13767) and &#x3a6;X174 (DSMZ 4497), and their host <italic>Escherichia coli</italic> (DSMZ 5695 and DSMZ 13127, respectively) were purchased from the German Collection of Microorganisms and Cell Cultures (DSMZ, Braunschweig, Germany). Phages were propagated and purified as described by <xref ref-type="bibr" rid="B38">Pecson et al. (2009)</xref>. Sodium carbonate (Na<sub>2</sub>CO<sub>3</sub>; Fluka), ammonium chloride (NH<sub>4</sub>Cl; Acros), sodium chloride (NaCl; Acros), and sodium phosphate (NaH<sub>2</sub>PO<sub>4</sub>; Acros) were used to make the experimental stock solutions. Stock solutions were kept in virus dilution buffer (VDB; 5&#xa0;mmolL<sup>&#x2212;1</sup> NaH<sub>2</sub>PO<sub>4</sub>, 10&#xa0;mmolL<sup>&#x2212;1</sup> NaCl, pH 7.5), and were stored at 4&#xb0;C. The same stocks were used for all the virus experiments.</p>
</sec>
<sec id="s3-3">
<title>2.3 Experimental Setup and Procedure</title>
<sec id="s3-3-1">
<title>2.3.1 <italic>Ascaris</italic> Study</title>
<p>The inactivation of <italic>Ascaris</italic> eggs was assessed in three fractions of urine/Ca(OH)<sub>2</sub> solution (Supernatant, Mixed liquor and Precipitates&#x2014;<xref ref-type="fig" rid="F1">Figure 1</xref>) and in three solution treatments: 1) drying at 20&#xb0;C with storage at 20 and 35&#xb0;C in sealed containers; 2) storage (no drying) in sealed containers at 20 and 35&#xb0;C; and 3) thermal treatment in sealed containers at 42 and 50&#xb0;C (<xref ref-type="table" rid="T1">Table 1</xref> and <xref ref-type="table" rid="T2">2</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>The three fractions made from the stabilized urine/Ca(OH)2 solution. Mixed liquor being the whole agitated mixture. The Supernate and Precipitate fractions were made by decanting the solution after settling for 3&#xa0;h.</p>
</caption>
<graphic xlink:href="fenvs-10-882284-g001.tif"/>
</fig>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Three solution treatments (Drying and Storage, Storage and Thermal treatment) distributed across temperature and moisture content and the different fractions (described in <xref ref-type="fig" rid="F1">Figure 1</xref>).</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left"/>
<th colspan="2" align="center">Drying and storage</th>
<th colspan="2" align="center">Storage</th>
<th colspan="2" align="center">Thermal treatment</th>
</tr>
<tr>
<th align="left"/>
<th align="center">20&#xb0;C</th>
<th align="center">35&#xb0;C</th>
<th align="center">20&#xb0;C</th>
<th align="center">35&#xb0;C</th>
<th align="center">42&#xb0;C</th>
<th align="center">50&#xb0;C</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Wet (&#x3e;90% MC)</td>
<td align="left"/>
<td align="left"/>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left">Supernatant</td>
<td align="left">Supernatant</td>
</tr>
<tr>
<td align="left">Partially wet<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref> (73&#x2013;82% MC)</td>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">Dry<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref> (13&#x2013;33% MC)</td>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left">Mixed, Supernatant, Precipitate</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn1">
<label>a</label>
<p>Fractions were pre-dried at 20&#xb0;C to targeted moisture content (% MC).</p>
</fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Three solution treatments (Drying and Storage, Storage and Thermal treatment) were applied to the three urine/Ca(OH)2 fractions (Mixed liquor, Supernate, and Precipitate) in which inactivation of <italic>Ascaris</italic> was assessed. Wet conditions had &#x3e;90% moisture content (MC). Partially wet (P. wet) conditions had 73&#x2013;82% MC (no free liquid on the surface); and Dried conditions had 13&#x2013;33% MC. During drying, the containers were open. During storage, the containers were sealed.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Solution Treatment</th>
<th align="center">Storage Temperature (&#xb0;C)</th>
<th align="center">Fraction</th>
<th align="center">Moisture content</th>
<th align="center">Drying (days)</th>
<th align="center">Storage (days)</th>
<th align="center">&#x23; samples</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="12" align="left">Drying (open) followed by storage (closed)</td>
<td rowspan="6" align="center">20</td>
<td rowspan="2" align="left">Supernate</td>
<td align="left">Partially wet</td>
<td align="center">8</td>
<td align="center">91</td>
<td align="center">7</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">2</td>
<td align="center">91</td>
<td align="center">9</td>
</tr>
<tr>
<td rowspan="2" align="left">Mixed liquor</td>
<td align="left">Partially wet</td>
<td align="center">9</td>
<td align="center">90</td>
<td align="center">9</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">2</td>
<td align="center">126</td>
<td align="center">6</td>
</tr>
<tr>
<td rowspan="2" align="left">Precipitates</td>
<td align="left">Partially wet</td>
<td align="center">8</td>
<td align="center">91</td>
<td align="center">10</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">2</td>
<td align="center">91</td>
<td align="center">6</td>
</tr>
<tr>
<td rowspan="6" align="center">35</td>
<td rowspan="2" align="left">Supernate</td>
<td align="left">Partially wet</td>
<td align="center">8</td>
<td align="center">77</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">4</td>
<td align="center">63</td>
<td align="center">5</td>
</tr>
<tr>
<td rowspan="2" align="left">Mixed liquor</td>
<td align="left">Partially wet</td>
<td align="center">8</td>
<td align="center">77</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">4</td>
<td align="center">91</td>
<td align="center">6</td>
</tr>
<tr>
<td rowspan="2" align="left">Precipitates</td>
<td align="left">Partially wet</td>
<td align="center">8</td>
<td align="center">77</td>
<td align="center">6</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="center">2</td>
<td align="center">79</td>
<td align="center">7</td>
</tr>
<tr>
<td rowspan="6" align="left">Storage (closed)</td>
<td rowspan="3" align="center">20</td>
<td align="left">Supernate</td>
<td rowspan="3" align="left">Wet</td>
<td align="center">-</td>
<td align="center">126</td>
<td align="center">10</td>
</tr>
<tr>
<td align="left">Mixed liquor</td>
<td align="left"/>
<td align="left"/>
<td align="center">4</td>
</tr>
<tr>
<td align="left">Precipitates</td>
<td align="left"/>
<td align="left"/>
<td align="center">9</td>
</tr>
<tr>
<td rowspan="3" align="center">35</td>
<td align="left">Supernate</td>
<td align="left"/>
<td align="center">-</td>
<td align="center">49</td>
<td align="center">4</td>
</tr>
<tr>
<td align="left">Mixed liquor</td>
<td align="left"/>
<td align="left"/>
<td align="center">126</td>
<td align="center">4</td>
</tr>
<tr>
<td align="left">Precipitates</td>
<td align="left"/>
<td align="left"/>
<td align="center">77</td>
<td align="center">5</td>
</tr>
<tr>
<td rowspan="2" align="left">Thermal Treatment (closed)</td>
<td align="center">42</td>
<td rowspan="2" align="left">Supernate</td>
<td rowspan="2" align="left">Wet</td>
<td align="center">-</td>
<td align="center">16</td>
<td align="center">4</td>
</tr>
<tr>
<td align="center">50</td>
<td align="left"/>
<td align="center">32&#xa0;h</td>
<td align="center">3</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Moisture content.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The collected urine (&#x3e;10&#xa0;L) was pooled and calcium hydroxide (Ca(OH)<sub>2</sub>; VWR Chemicals, Pennsylvania, United States) was added at a ratio of 10&#xa0;g Ca(OH)<sub>2</sub> per liter urine to achieve pH 12.5. The mixture was agitated for 10&#xa0;min by magnetic stirrer and then left to stand undisturbed in closed containers for 3&#xa0;h at 20&#xb0;C to form what is referred to as stabilized urine.</p>
<p>Urine Fractions</p>
<p>From the stabilized urine/Ca(OH)<sub>2</sub> solution, three fractions were formed (<xref ref-type="fig" rid="F1">Figure 1</xref>). The fraction referred to as Mixed liquor was the whole agitated mixture treated and dried together. The Supernate and Precipitate fractions were made by decanting the solution after standing for 3&#xa0;h. The Supernate represented the situation where after Ca(OH)<sub>2</sub> stabilization the top liquid would be pumped out of the reactor for drying, while the precipitates would be removed and dried separately. All three fractions were stored in sealed containers overnight.</p>
<p>The inactivation of <italic>Ascaris</italic> eggs in the three fractions was assessed by three solution treatments, as described in <xref ref-type="table" rid="T1">Table 1</xref> and <xref ref-type="table" rid="T2">2</xref>. The volumes of the urine fractions for each treatment are described in <xref ref-type="table" rid="T3">Table 3</xref>. All treatments had an addition of 0.1&#xa0;g feces with <italic>Ascaris</italic> eggs (100 000&#xa0;eggs per gram epg).</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Amounts of urine/Ca(OH)<sub>2</sub> used from the three fractions (Supernate, mixed liquor, and precipitates) and procedure applied to the urine-feces mix to reach the target moisture content (MC) for the treatment.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left"/>
<th align="center">Fraction</th>
<th align="left">Dried</th>
<th align="left">Partially Wet</th>
<th align="left">Wet</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="3" align="left">
<bold>Volume of alkalinized urine</bold>
<xref ref-type="table-fn" rid="Tfn2">
<sup>a</sup>
</xref>
</td>
<td align="left">Supernate</td>
<td rowspan="2" align="left">150&#xa0;ml</td>
<td rowspan="2" align="left">45&#xa0;ml</td>
<td rowspan="2" align="left">6&#xa0;ml</td>
</tr>
<tr>
<td align="left">Mixed liquor</td>
</tr>
<tr>
<td align="left">Precipitates</td>
<td align="left">45&#xa0;ml</td>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">
<bold>Procedure</bold>
</td>
<td align="left">All fractions</td>
<td align="left">Vortexed, dried in wax paper boats at 20&#xb0;C, transferred to 7&#xa0;ml&#xa0;PP tubes with O-ring lined caps on reaching target MC</td>
<td align="left">Vortexed, stored in 45&#xa0;ml&#xa0;PP tubes, centrifuged 5&#xa0;min at 3000&#xa0;rpm, dried at 20&#xb0;C, sealed with O-ring lined caps on reaching target MC</td>
<td align="left">Vortexed, stored in 7&#xa0;ml&#xa0;PP tubes with O-ring lined caps</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn2">
<label>a</label>
<p>
<italic>All volumes of alkaline urine had an addition of 0.1&#xa0;g feces with Ascaris eggs</italic>.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>Solution Treatments</p>
<p>Drying-storage: The effect of drying prior to storage was investigated by drying the three urine/Ca(OH)<sub>2</sub> fractions (Mixed liquor, Supernate, and Precipitate) at 20&#xb0;C to either a Partially wet condition (73&#x2013;82% moisture content (MC)) or a Dried condition (13&#x2013;33% MC) followed by storage in sealed containers at 20 or 35&#xb0;C.</p>
<p>Stored: Urine/Ca(OH)<sub>2</sub> fractions were stored directly in sealed containers at 20 and 35&#xb0;C (&#x3e;90% MC).</p>
<p>Thermal Treatment: The third aspect investigated was effect of elevated temperature (42 and 50&#xb0;C) during storage of the Supernate fraction to assess the thermal pre-treatment time required to achieve a 3 log<sub>10</sub> reduction in <italic>Ascaris</italic> egg viability.</p>
<p>Wet Conditions: For setting up the studies of the three urine/Ca(OH)<sub>2</sub> fractions under wet conditions (&#x3e;90% MC), 6&#xa0;ml from each the three different fractions were aliquoted into 7&#xa0;ml polypropylene tubes with O-ring lined screw caps (Sarstedt AG &#x26; Co., Sweden) already containing 0.1&#xa0;g of <italic>Ascaris</italic> eggs in feces. After sealing, the tubes were vortexed for 5&#xa0;s. The capped tubes were then placed at the target temperatures (in incubators or in an insulated box at room temperature) (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
<p>Partially Wet Conditions: urine/Ca(OH)<sub>2</sub> solution of the three different fractions were divided into 45&#xa0;ml aliquots, which were transferred to 50&#xa0;ml centrifuge tubes already containing 0.1&#xa0;g fecal material and vortexed for 3&#xa0;s (or to &#x3c;1&#xa0;mm lumps). The tubes were then centrifuged for 5&#xa0;min at 3000&#xa0;rpm to bring particles, including <italic>Ascaris</italic> eggs, down from the walls. The tubes were placed without lids on a table and dried with a fan at 20&#xb0;C until no liquid was visible (73&#x2013;82% MC) and then the tubes were sealed and stored at target temperature.</p>
<p>Dried conditions: 150&#xa0;ml of the urine/Ca(OH)<sub>2</sub> solution from the Supernate and Mixed liquor fractions and 45&#xa0;ml of the precipitates fraction were added to 0.1&#xa0;g feces with <italic>Ascaris</italic> eggs (the addition of fecal material was made according to the total solids content). After vortexing for 3&#xa0;s, the fractions were transferred to open foil trays lined with waxed paper, which were kept on a table and dried with a fan at room temperature to the target moisture content of &#x3c;33%. The dried material was transferred to 7&#xa0;ml tubes, which were sealed and stored at the target temperature.</p>
<p>The duration of the drying period varied from 2 to 8&#xa0;days (<xref ref-type="table" rid="T1">Table 1</xref>) and the time was included in the duration of the treatment. The variation in drying period was due to the tubes from the Partially wet treatment being dried in smaller containers than the open trays in the Dried treatment. The study was conducted as independent singlets using destructive sampling.</p>
<p>Extraction of Eggs</p>
<p>The extraction procedure for the <italic>A. suum</italic> eggs was a modification of the USEPA (2003) method. To extract the eggs from crystals formed in the three fractions, diluted 0.1&#xa0;N sulphuric acid was added to the vials and they were vortexed for 30&#xa0;s and then centrifuged at 4000&#xa0;rpm for 3&#xa0;min. The Supernate was decanted over Tyler sieves (&#x2300; 38&#xa0;&#x3bc;m, Cat. No. L3-400, and &#x2300; 300&#xa0;&#x3bc;m, Cat. No. L3-50). This was repeated 5&#x2013;10 times, until the crystals formed by the urine and the Ca(OH)<sub>2</sub> were nearly dissolved. Any remaining crystals were decanted over Tyler sieves and further washed with 0.1&#xa0;N sulphuric acid. Sampling frequency depended on the intensity of the treatment and ranged from every 2&#xa0;weeks at 20&#xb0;C to every 8&#xa0;h at 50&#xa0;&#xb0;C.</p>
</sec>
<sec id="s3-3-2">
<title>2.3.2 Virus Study</title>
<p>Experiments were conducted in the presence and absence of feces to assess if fecal matter exerts a protective effect of viruses during alkaline conditions (pH 9, 11.5 and 12.3). Additional control experiment with virus in feces exposed to virus dilution buffer (VDB; 5&#xa0;mmol&#xa0;L<sup>&#x2212;1</sup> NaH<sub>2</sub>PO<sub>4</sub>, 10&#xa0;mmol&#xa0;L<sup>&#x2212;1</sup> NaCl, pH 7.5) were also performed to examine the effect of feces itself on virus survival. Each experimental condition was tested in independent singlet experiments.</p>
<p>Experiments at pH 11.5 and 12.3 were conducted in phosphate buffer. Experiments at pH were conducted in ammonium carbonate buffer. The specific composition of the buffers to attain a given pH was determined with PHREEQC (version 2.18.00) (<xref ref-type="bibr" rid="B35">Parkhurst and Appelo 2013</xref>) and a database using the Pitzer approach for calculating the ion activity. Solutions were made according to SI, <xref ref-type="sec" rid="s11">Supplamentary Table S1</xref>. by mixing salt with sterilized milliQ water, stored at targeted temperature for at least half day, and the solution pH was then measured and adjusted with NaOH/HCl. The pH and electrical conductivity (EC) were measured at experimental temperature with 780 pH Meter with primatrode with NTC no. 6.0228.010 (Metrohm, Herisau, Switzerland) and a Cond315i conductivity meter and a TetraCon 325 probe (WTW, Weilheim, Germany) respectively.</p>
<p>&#x3a6;X174 was used as the test organism at pH 11.5 and 12.3, because MS2 inactivation was too rapid to be measured. Conversely, MS2 were used as the test organism at pH 9.0, because &#x3a6;X174 did not exhibit measurable inactivation over the timescale considered.</p>
<sec id="s3-3-2-1">
<title>2.3.1.4 Virus in Feces</title>
<p>A day prior to the start of the experiment, 50&#xa0;&#xb5;L of &#x223c;10<sup>9</sup>&#xa0;PFU&#xa0;ml<sup>&#x2212;1</sup> virus solution were spiked into &#x223c;5&#xa0;g of feces in a plastic bag, kneaded for a few minutes, and stored overnight at 4&#xb0;C. The following day, 0.05&#x2013;0.2&#xa0;g of feces were transferred into 1&#xa0;ml eppendorf tubes. The tubes were then filled with either 1&#xa0;ml VDB (control sample at circum-neutral pH), 1&#xa0;ml of ammonium carbonate buffer, 0.9&#xa0;ml of phosphate buffer at pH 11.5, or 0.8&#xa0;ml of phosphate buffer at pH 12.3. Sacrificial samples were taken periodically and were mixed with 0.1 and 0.2&#xa0;ml HCl&#xa0;1N for phosphate buffer at pH 11.5 and 12.3 respectively to lower the pH to a range between 6.5&#x2013;7.5. They were then vortexed for 5 min, centrifuged at 10000&#xa0;g for 1&#xa0;min, filtered through a 0.22&#xa0;&#x3bc;m filter (Millipore), diluted in VDB and stored at 4&#xb0;C for no more than 6&#xa0;h prior to enumeration. In control samples with VDB, this method showed a 50% recovery of phages.</p>
</sec>
<sec id="s3-3-2-2">
<title>2.3.1.5 Virus in the Bulk</title>
<p>One milliliter of a virus solution containing 10<sup>9</sup>&#xa0;PFU&#xa0;ml<sup>&#x2212;1</sup> in VDB was added to airtight 116&#xa0;ml glass serum flasks (Infochroma) containing 114&#xa0;ml of experimental solution (as described in <xref ref-type="sec" rid="s3-2">Section 2.2</xref>). After mixing, 1&#xa0;ml of ammonium carbonate buffer, 0.9&#xa0;ml of phosphate buffer at pH 11.5, or 0.8&#xa0;ml of phosphate buffer at pH 12.3 were taken periodically from each flask with a sterile syringe, mixed in an Eppendorf tube with 0.1 and 0.2&#xa0;ml HCl&#xa0;1N for phosphate buffer at pH 11.5 and 12.3 respectively and were filtered through a 0.22&#xa0;&#x3bc;m filter (Millipore), diluted in VDB and stored at 4&#xb0;C for no more than 6&#xa0;h prior to enumeration.</p>
</sec>
</sec>
</sec>
<sec id="s3-4">
<title>2.4 Enumeration</title>
<sec id="s3-4-1">
<title>2.4.1. <italic>Ascaris</italic>
</title>
<p>At the start of the experiment, a sample of the <italic>A. suum</italic> eggs (<italic>n</italic> &#x3d; 100) was observed under a microscope to confirm that the eggs were undeveloped. After extraction from the treatments, 100 eggs were directly examined to assess any development or damage occurring during the treatment period. The viability of the eggs was determined by incubating them at 28&#xb0;C in 0.1&#xa0;N H<sub>2</sub>SO<sub>4</sub> for 28&#xa0;days to allow larval development (Arene, 1986). Viability counts were performed under &#xd7; 10 and &#xd7; 20 magnification and unfertilized eggs, which constituted a minor proportion of all eggs, were excluded from further counting. Eggs developing to the larval stage were considered viable. Initial viability of the <italic>A. suum</italic> eggs was 55% in the treatment applying storage temperatures of 20 and 35&#xb0;C, and 77% in the treatment applying thermal treatment at 42 and 50&#xb0;C.</p>
</sec>
<sec id="s3-4-2">
<title>2.4.2 Virus</title>
<p>Infectivity was assessed using the double agar layer method and was expressed as plaque forming units per mL (PFU ml<sup>&#x2212;1</sup>) (<xref ref-type="bibr" rid="B49">Standard Methods 2018</xref>). The quantification limit for all phages was 100&#xa0;PFU&#xa0;ml<sup>&#x2212;1</sup>. Number of phages in feces (PFU mg<sup>&#x2212;1</sup>) was calculated from the phages in solution PFU&#xa0;mL<sup>&#x2212;1</sup> extracted from feces, multiplied by the total amount of feces in mg&#xa0;mL<sup>&#x2212;1</sup>. Natural presence of MS2 and &#x3a6;X174 used in this study in feces was assessed to be under the fore-mentioned detection limit.</p>
</sec>
</sec>
<sec id="s3-5">
<title>2.5 Data Analysis</title>
<sec id="s3-5-1">
<title>2.5.1 <italic>Ascaris</italic>
</title>
<p>Confidence intervals for proportions of viable <italic>Ascaris</italic> eggs were derived using the Wilson score interval (Minitab Inc., US). The logarithmized egg viability data, which showed a two-phase inactivation pattern, were fitted against a non-linear inactivation model (<xref ref-type="disp-formula" rid="e1">Eq. 1</xref>) from (<xref ref-type="bibr" rid="B19">Harm 1980</xref>). For the treatments that were repeated, the viability data were modelled as a combined dataset:<disp-formula id="e1">
<mml:math id="m1">
<mml:mrow>
<mml:mi>l</mml:mi>
<mml:mi>o</mml:mi>
<mml:msub>
<mml:mi>g</mml:mi>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
</mml:msub>
<mml:msub>
<mml:mi>N</mml:mi>
<mml:mrow>
<mml:mi>t</mml:mi>
<mml:mi>A</mml:mi>
<mml:mi>s</mml:mi>
<mml:mi>c</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>l</mml:mi>
<mml:mi>o</mml:mi>
<mml:msub>
<mml:mi>g</mml:mi>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
</mml:msub>
<mml:msub>
<mml:mi>N</mml:mi>
<mml:mrow>
<mml:mn>0</mml:mn>
<mml:mi>A</mml:mi>
<mml:mi>s</mml:mi>
<mml:mi>c</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mrow>
<mml:mo>[</mml:mo>
<mml:mrow>
<mml:mn>1</mml:mn>
<mml:mo>&#x2212;</mml:mo>
<mml:msup>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mn>1</mml:mn>
<mml:mo>&#x2212;</mml:mo>
<mml:msup>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
<mml:mrow>
<mml:msub>
<mml:mi>k</mml:mi>
<mml:mrow>
<mml:mi>A</mml:mi>
<mml:mi>s</mml:mi>
<mml:mi>c</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x2217;</mml:mo>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msup>
<mml:mo>)</mml:mo>
</mml:mrow>
<mml:mrow>
<mml:msup>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
<mml:mi>n</mml:mi>
</mml:msup>
</mml:mrow>
</mml:msup>
</mml:mrow>
<mml:mo>]</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
<label>(1)</label>
</disp-formula>where log<sub>10</sub>N<sub>t<italic>Ascaris</italic>
</sub> is the log(base 10) proportion of viable eggs at time t (in days), log<sub>10</sub>N<sub>0<italic>Ascaris</italic>
</sub> is the log proportion of viable eggs at start, <italic>k</italic>
<sub>
<italic>Ascaris</italic>
</sub> is the inactivation rate constant, which describes the change in viability over time during the exponential decay phase (log<sub>10</sub> proportion viable eggs day<sup>&#x2212;1</sup>), and <italic>n</italic> is a dimensionless parameter determining lag phase duration. The values of <italic>k</italic>
<sub>
<italic>Ascaris</italic>
</sub> and <italic>n</italic> were determined by non-linear regression using the Gauss-Newton algorithm (Minitab 17, Minitab Inc., US). This enabled calculation of the lag phase, i.e., the initial period where there is no significant inactivation (<xref ref-type="disp-formula" rid="e2">Eq. 2</xref>):<disp-formula id="e2">
<mml:math id="m2">
<mml:mrow>
<mml:mi>L</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>g</mml:mi>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>p</mml:mi>
<mml:mi>h</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>s</mml:mi>
<mml:mi>e</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mi>l</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mfrac>
<mml:mi>n</mml:mi>
<mml:mrow>
<mml:mrow>
<mml:mo>&#x7c;</mml:mo>
<mml:mi>k</mml:mi>
<mml:mo>&#x7c;</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
<label>(2)</label>
</disp-formula>
</p>
<p>Many samples had no lag phase according to this model. For these datasets, the model gave <italic>n</italic> &#x3d; 1, which reduced the model to a linear regression with the <italic>y</italic>-intercept set to zero, i.e., exponential decay.</p>
</sec>
<sec id="s3-5-2">
<title>2.5.2 Virus</title>
<p>Virus inactivation was modelled as a log-linear decay process according to <xref ref-type="disp-formula" rid="e3">Eq. 3</xref>:<disp-formula id="e3">
<mml:math id="m3">
<mml:mrow>
<mml:mi>l</mml:mi>
<mml:mi>o</mml:mi>
<mml:msub>
<mml:mi>g</mml:mi>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
</mml:msub>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:mfrac>
<mml:mrow>
<mml:msub>
<mml:mi>N</mml:mi>
<mml:mrow>
<mml:mi>v</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>u</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
<mml:mrow>
<mml:msub>
<mml:mi>N</mml:mi>
<mml:mrow>
<mml:mn>0</mml:mn>
<mml:mo>,</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>v</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>u</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
<mml:mo>&#xa0;</mml:mo>
<mml:mo>&#x3d;</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mo>&#x2212;</mml:mo>
<mml:msub>
<mml:mi>k</mml:mi>
<mml:mrow>
<mml:mi>v</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>u</mml:mi>
<mml:mi>s</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#xa0;</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo>&#xa0;</mml:mo>
</mml:mrow>
</mml:math>
<label>(3)</label>
</disp-formula>Where <italic>N</italic>
<sub>
<italic>virus</italic>
</sub> and <italic>N</italic>
<sub>
<italic>0,virus</italic>
</sub> are the concentration of infectious viruses at times 0 and t, and <italic>k</italic>
<sub>
<italic>virus</italic>
</sub> is the first-order inactivation rate constant (day<sup>&#x2212;1</sup>). The linear regressions were performed on log<sub>10</sub> transformed data with Excel software. The 95% confidence interval (95% CI) of <italic>k</italic>
<sub>
<italic>viru</italic>s</sub> was calculated from the standard error of the slope from one experiment.</p>
</sec>
</sec>
</sec>
<sec id="s4">
<title>3 Results</title>
<sec id="s4-1">
<title>3.1 <italic>Ascaris</italic>
</title>
<p>The <italic>Ascaris</italic> eggs showed both biphasic inactivation with an initial lag phase and log-linear inactivation. In the Drying-storage treatment at 20&#xb0;C, decreasing the moisture content, from 78 to 82% in the Partially wet condition to 13&#x2013;16% in the Dried condition, decreased the time required for a 3 log<sub>10</sub> reduction by 22&#xa0;days (<xref ref-type="table" rid="T4">Table 4</xref>). The Supernate (98&#xa0;days) and Mixed liquor (102&#xa0;days) fractions that were stored directly at 20&#xb0;C (Wet condition) required similar times for a 3 log<sub>10</sub> reduction to the Partially wet condition (Supernate, 111&#xa0;days; Mixed liquor, 95&#xa0;days). The Precipitates fraction stored directly at 20&#xb0;C (Wet condition) required a similar time (60&#xa0;days) for a 3 log<sub>10</sub> reduction to that in the Dried condition.</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>
<italic>Ascaris</italic> egg inactivation parameters: lag phase (days); inactivation rate constant k (-log<sub>10</sub> d<sup>&#x2212;1</sup>); time required for a 3 log<sub>10</sub> reduction in egg viability (days), derived from <xref ref-type="disp-formula" rid="e1">Eq. 1</xref>, <xref ref-type="disp-formula" rid="e2">2</xref>, for <italic>Ascaris</italic> eggs subjected to the different drying, storage and thermal treatments. Wet conditions had &#x3e;90% MC, Partially wet (P. wet) condition had 73&#x2013;82% MC (no free liquid on the surface); and Dried conditions had 13&#x2013;33% MC.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Treatment</th>
<th align="center">Storage Temperature (&#xb0;C)</th>
<th align="center">Fraction</th>
<th align="center">Moisture content conditions</th>
<th align="center">MC (%)</th>
<th align="center">Lag (d)</th>
<th align="center">k (&#x2212;log<sub>10</sub> d<sup>&#x2212;1</sup>)</th>
<th align="center">3 log<sub>10</sub> (d)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="12" align="left">Drying (open) followed by storage (closed)</td>
<td rowspan="6" align="center">20</td>
<td rowspan="2" align="left">Supernate</td>
<td align="left">P. wet</td>
<td align="char" char=".">78</td>
<td align="char" char=".">56</td>
<td align="char" char=".">0.055</td>
<td align="char" char=".">111</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="char" char=".">13</td>
<td align="char" char=".">14</td>
<td align="char" char=".">0.077</td>
<td align="char" char=".">53</td>
</tr>
<tr>
<td rowspan="2" align="left">Mixed liquor</td>
<td align="left">P. wet</td>
<td align="char" char=".">82</td>
<td align="char" char=".">44</td>
<td align="char" char=".">0.059</td>
<td align="char" char=".">95</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="char" char=".">14</td>
<td align="char" char=".">0.56</td>
<td align="char" char=".">0.052</td>
<td align="char" char=".">58</td>
</tr>
<tr>
<td rowspan="2" align="left">Precipitates</td>
<td align="left">P. wet</td>
<td align="char" char=".">81</td>
<td align="char" char=".">27</td>
<td align="char" char=".">0.043</td>
<td align="char" char=".">97</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="char" char=".">16</td>
<td align="char" char=".">0.0</td>
<td align="char" char=".">0.041</td>
<td align="char" char=".">73</td>
</tr>
<tr>
<td rowspan="6" align="center">35</td>
<td rowspan="2" align="left">Supernate</td>
<td align="left">P. wet</td>
<td align="char" char=".">73</td>
<td align="char" char=".">11</td>
<td align="char" char=".">0.65</td>
<td align="char" char=".">16</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="char" char=".">18</td>
<td align="char" char=".">6.7</td>
<td align="char" char=".">0.59</td>
<td align="char" char=".">12</td>
</tr>
<tr>
<td rowspan="2" align="left">Mixed liquor</td>
<td align="left">P. wet</td>
<td align="char" char=".">78</td>
<td align="char" char=".">16</td>
<td align="char" char=".">0.44</td>
<td align="char" char=".">23</td>
</tr>
<tr>
<td align="left">Dried</td>
<td align="char" char=".">24</td>
<td align="char" char=".">0.23</td>
<td align="char" char=".">0.17</td>
<td align="char" char=".">18</td>
</tr>
<tr>
<td rowspan="1" align="left">Precipitates</td>
<td align="left">P. wet</td>
<td align="char" char=".">77</td>
<td align="char" char=".">0.0</td>
<td align="char" char=".">0.051</td>
<td align="char" char=".">59</td>
</tr>
<tr>
<td align="left"/>
<td align="left">Dried</td>
<td align="char" char=".">33</td>
<td align="char" char=".">0.0</td>
<td align="char" char=".">0.038</td>
<td align="char" char=".">79</td>
</tr>
<tr>
<td rowspan="6" align="left">Storage (closed)</td>
<td rowspan="3" align="center">20</td>
<td align="left">Supernate</td>
<td rowspan="6" align="left">Wet</td>
<td align="char" char=".">97</td>
<td align="char" char=".">28</td>
<td align="char" char=".">0.043</td>
<td align="char" char=".">98</td>
</tr>
<tr>
<td align="left">Mixed liquor</td>
<td align="char" char=".">97</td>
<td align="char" char=".">16</td>
<td align="char" char=".">0.035</td>
<td align="char" char=".">102</td>
</tr>
<tr>
<td align="left">Precipitates</td>
<td align="char" char=".">94</td>
<td align="char" char=".">24</td>
<td align="char" char=".">0.083</td>
<td align="char" char=".">60</td>
</tr>
<tr>
<td rowspan="3" align="center">35</td>
<td align="left">Supernate</td>
<td align="char" char=".">98</td>
<td align="char" char=".">7.4</td>
<td align="char" char=".">0.39</td>
<td align="char" char=".">15</td>
</tr>
<tr>
<td align="left">Mixed liquor</td>
<td align="char" char=".">97</td>
<td align="char" char=".">0.0</td>
<td align="char" char=".">0.063</td>
<td align="char" char=".">48</td>
</tr>
<tr>
<td align="left">Precipitates</td>
<td align="char" char=".">92</td>
<td align="char" char=".">26</td>
<td align="char" char=".">0.11</td>
<td align="char" char=".">53</td>
</tr>
<tr>
<td rowspan="2" align="left">Thermal Treatment (closed)</td>
<td align="center">42</td>
<td rowspan="2" align="left">Supernate</td>
<td rowspan="2" align="left">Wet</td>
<td align="char" char=".">97</td>
<td align="char" char=".">0.05</td>
<td align="char" char=".">0.72</td>
<td align="char" char=".">4.2</td>
</tr>
<tr>
<td align="center">50</td>
<td align="char" char=".">97</td>
<td align="char" char=".">0.00</td>
<td align="char" char=".">8.5</td>
<td align="char" char=".">0.35</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>In the Drying-storage treatment at 35&#xb0;C, the Supernate (12&#x2013;16&#xa0;days) and Mixed liquor (18&#x2013;23&#xa0;days) fractions were quicker to reach a 3 log<sub>10</sub> reduction than in Drying-storage at 20&#xb0;C. The Precipitates at 35&#xb0;C were slower to reach a 3 log<sub>10</sub> reduction than the other two fractions (59&#x2013;79&#xa0;days depending on the moisture content). The Supernate (15&#xa0;days) and Precipitates (53&#xa0;days) fractions that were stored directly at 35&#xb0;C (Wet condition) required a similar time for a 3 log<sub>10</sub> reduction as Partially wet conditions (Supernate, 16&#xa0;days; Precipitates, 59&#xa0;days). The Mixed liquor fraction required twice the time (48&#xa0;days) in comparison with the partially wet conditions in the drying-storage treatment (23&#xa0;days).</p>
<p>In the Thermal treatment, the time required for a 3 log<sub>10</sub> reduction in egg viability was &#x3c;5&#xa0;days at 42&#xb0;C and &#x3c;9&#xa0;h at 50&#xb0;C. Due to fast inactivation in relation to sampling frequency at 50&#xb0;C, the inactivation could only be described by a log-linear relationship and the derived <italic>k</italic> and the time for 3 log<sub>10</sub> reduction in egg viability are conservative values (<xref ref-type="table" rid="T4">Table 4</xref>).</p>
<p>Differences were observed in the inactivation rate constant (<italic>k</italic>) with the varying parameters. The <italic>k</italic> value at 20&#xb0;C was consistent, with a narrow range (&#x2212;0.083&#x2013;&#x2212;0.035&#xa0;day<sup>&#x2212;1</sup>) across the different treatment conditions. At 35&#xb0;C, the Supernate fraction was more sensitive to the heat increase (<italic>k</italic> &#x3d; &#x2212;0.65&#x2212; &#x2212;0.39&#xa0;day<sup>&#x2212;1</sup>) than the Precipitates fraction (<italic>k</italic> &#x3d; &#x2212;0.11&#x2212;&#x2212;0.04&#xa0;day<sup>&#x2212;1</sup>) and the Mixed liquor fraction (<italic>k</italic> &#x3d; &#x2212;0.44&#x2212;&#x2212;0.06&#xa0;day<sup>&#x2212;1</sup>). The smaller <italic>k</italic>-values for the Precipitates at 35&#xb0;C led to longer inactivation time (up to 80&#xa0;days for a 3 log<sub>10</sub> reduction in egg viability, compared with 16&#xa0;days for the Supernate).</p>
</sec>
<sec id="s4-2">
<title>3.2 Virus</title>
<p>In mildly alkaline conditions (pH 9.0), the k-value for MS2 was similar for viruses in the bulk and embedded in feces. In more alkaline buffer, the k-value for &#x3a6;X174 was faster in the bulk than in feces. At pH 11.5, &#x3a6;X174 exhibited k-values of 3.4 &#xb1; 1.1&#xa0;days<sup>&#x2212;1</sup> and 9.7 &#xb1; 2.2 days<sup>&#x2212;1</sup> in feces and in the bulk respectively. This effect was shown to increase with pH. At pH 12.5, &#x3a6;X174 showed k-value of 64 &#xb1; 18&#xa0;days<sup>&#x2212;1</sup> and 3625 &#xb1; 2075&#xa0;days<sup>&#x2212;1</sup>in feces and in the bulk respectively. (<xref ref-type="fig" rid="F2">Figure 2</xref> and see SI, <xref ref-type="sec" rid="s11">Supplementary Table S2</xref>). At pH 11.5, contact times of 9.8 and 28.5&#xa0;h are required to achieve a 4 log<sub>10</sub> decay of phages in solution and embedded in feces respectively. At pH 12.3, these contact times reduce to 1.5 and 90.7&#xa0;min for phages in solution and phages embedded in feces respectively. Control experiments at pH 7.5 showed no inactivating effect of feces at 20&#xb0;C over the course of 4&#xa0;days (see SI, <xref ref-type="sec" rid="s11">Supplementary Figure S1</xref> and <xref ref-type="sec" rid="s11">Supplementary Table S2</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Comparison of inactivation rate constant (k<sub>virus</sub>) at 20&#xb0;C measured within the feces (orange bar) or in a homogenous solution (white bar) of corresponding pH, for MS2 (pH 9.0) and &#x3a6;X174 (pH 11.5 and 12.3). Error bars depict the 95% CI determined from the fit of the data to <xref ref-type="disp-formula" rid="e3">Eq. 3</xref>. Inactivation curves for each experimental condition can be found in SI, <xref ref-type="sec" rid="s11">Supplementary Figure S1</xref>, and values of k<sub>virus</sub> are shown in <xref ref-type="sec" rid="s11">Supplementary Table S2</xref>.</p>
</caption>
<graphic xlink:href="fenvs-10-882284-g002.tif"/>
</fig>
</sec>
</sec>
<sec id="s5">
<title>4 Discussion</title>
<sec id="s5-1">
<title>4.1 <italic>Ascaris</italic>
</title>
<sec id="s5-1-1">
<title>4.1.1 Driving the Inactivation</title>
<p>
<italic>Ascaris</italic> eggs were inactivated at 20&#xb0;C, with times ranging from 53 to 111&#xa0;days for a 3 log<sub>10</sub> reduction in egg viability with shorter time required for inactivation in the dry compared to the wet treatment (<xref ref-type="table" rid="T4">Table 4</xref>). In a related study high pH (12.5) and drying had no effect on the inactivation of <italic>Ascaris</italic> eggs kept for 80&#xa0;days at 20&#xb0;C under similar conditions in terms of pH, moisture, and temperature, but without urine or NH<sub>3</sub> (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>). <xref ref-type="bibr" rid="B37">Pecson et al., 2007</xref> confirmed that pH alone will not affect <italic>Ascaris</italic> egg viability at this temperature whereas <xref ref-type="bibr" rid="B32">Naidoo et al., 2016</xref> showed an effect of moisture content alone, with a 1 log<sub>10</sub> reduction in <italic>Ascaris</italic> egg viability after 6&#xa0;weeks&#xa0;at&#xa0;MC 20%. It is thus likely that presence of NH<sub>3</sub> have contributed to the inactivation in the current study, while any carbonate formation would have been negligible (<xref ref-type="bibr" rid="B14">Fidjeland et al., 2016</xref>). At 35&#xb0;C, the elevated pH of 12.3 and temperature were the driving factors for the inactivation of <italic>Ascaris</italic> eggs, which took between 12 and 79&#xa0;days for a 3 log<sub>10</sub> reduction in egg viability, depending on the fraction and moisture conditions (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>). At 35&#xb0;C, a higher degree of drying had no clear effect on the inactivation rate, an effect that was observed at 20&#xb0;C. In the related study with similar conditions pH, moisture, and temperature levels, but without urine or NH<sub>3</sub>, there was a 3 log<sub>10</sub> reduction in egg viability within 23&#xa0;days (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>).</p>
<p>The <italic>Ascaris</italic> inactivation studies could have been strengthened with controls studying the drying media without urine, to assess whether the medium itself had an effect. Formation and accumulation of ammonia could have been monitored in the different fractions and at different moisture conditions to gain a better understanding of the results.</p>
</sec>
<sec id="s5-1-2">
<title>4.1.2 <italic>Ascaris</italic> Resilience</title>
<p>
<italic>Ascaris</italic> eggs require O<sub>2</sub> during development (<xref ref-type="bibr" rid="B36">Pawlowski 1982</xref>), but are able to remain viable in anaerobic conditions for &#x3e;80&#xa0;days (<xref ref-type="bibr" rid="B15">Gaasenbeek and Borgsteede 1998</xref>). In the present study, lack of oxygen should not have affected the egg inactivation rates at 20&#xb0;C, as demonstrated by no reduction in egg viability after 126&#xa0;days at pH 12.5 in a sealed container (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>). However, the lack of O<sub>2</sub> could have been a compounding stress factor for the <italic>Ascaris</italic> eggs at higher temperatures. The increase in osmotic pressure caused by drying the urine was not likely to have causes stress for the <italic>Ascaris</italic> eggs (<xref ref-type="bibr" rid="B9">Decrey et al., 2011</xref>), as <italic>Ascaris</italic> eggs have been shown to survive in concentrated urine mixed with ash at 20&#xb0;C for &#x3e;100&#xa0;days (<xref ref-type="bibr" rid="B44">Senecal et al., 2018</xref>).</p>
<p>The lag phases were longest in the partially wet condition at 20&#xb0;C, for two probable reasons: 1) this condition had less NH<sub>3</sub> than the Wet and Dried condition (took longer to dry, see <xref ref-type="table" rid="T1">Table 1</xref> and <xref ref-type="table" rid="T2">2</xref> this condition had no moisture stress compared with the dried condition. This difference in the lag phase duration between the conditions was not observed at 35&#xb0;C in this study. However, in another study with similar moisture content (60% MC) and temperature, but no NH<sub>3</sub> present, inactivation time was longer compared with wet (&#x3e;90% MC) and dried (&#x3c;20% MC) conditions (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>). This indicates that partially wet conditions may be ideal for the survival of the <italic>Ascaris</italic> eggs.</p>
<p>The precipitates at 35&#xb0;C seemed to have a protective effect on the <italic>Ascaris</italic> eggs, as the time for a 3 log<sub>10</sub> reduction was longer for this fraction than for the other fractions at 35&#xb0;C (<xref ref-type="table" rid="T4">Table 4</xref>). For the dried precipitate at 35&#xb0;C, the MC was higher than in other dried conditions (33%, compared with 18% for the dried Supernate and 24% for the dried mixed liquor fraction), which could have caused the smaller <italic>k</italic> value. Feces has been shown to have a protective effect on <italic>Ascaris</italic> eggs (<xref ref-type="bibr" rid="B17">Ghiglietti et al., 1997</xref>; <xref ref-type="bibr" rid="B5">Capizzi-Banas et al., 2004</xref>), and the precipitates fraction may have provided some similar protection.</p>
</sec>
</sec>
<sec id="s5-2">
<title>4.2 Viruses</title>
<p>Traditionally studies on fecal-oral transmitted virus survival are conducted with viruses suspended in a solution of interest. Although a fraction of excreted viruses may indeed end up in the bulk, most of them are encountered within large to very small pieces of fecal material (<xref ref-type="bibr" rid="B43">Sch&#xf6;nning et al., 2002</xref>). Viruses are thus embedded in a matrix that can potentially shield them from external stressors, but could also enhance their inactivation.</p>
<p>Our results showed that feces did not enhance virus reduction. On the contrary, viruses embedded in feces survived longer in alkaline solutions compared to free viruses. The higher the pH the greater the difference between survival inside and outside the fecal material (<xref ref-type="fig" rid="F3">Figure 3</xref> and see SI, <xref ref-type="sec" rid="s11">Supplementary Table S2</xref>). Therefore, in order to accurately assess the fate of viruses through the alkaline-urine treatment, we need to consider that most viruses are embedded, and the survival kinetics estimated based on free viruses thus requires a downward correction.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Calculated number of days required for a 3 log<sub>10</sub> reduction in <italic>Ascaris</italic> <bold>[red]</bold> at the given temperature (pH did not impact the inactivation rate). Calculated number of days for a 4 log<sub>10</sub> reduction in virus <bold>[green]</bold> at the given temperature and pH. Solid green line is for virus enmeshed in fecal material and the dotted line is for virus without enmeshment. As the temperature changes, so does the pH of urine/Ca(OH)2 solution (indicated by the blue dots).</p>
</caption>
<graphic xlink:href="fenvs-10-882284-g003.tif"/>
</fig>
<p>The strong protective role of feces is currently poorly understood and deserves further investigation. For example, the size and the type of feces dependent on diet (structure, pH, ion composition) may influence the protective effect. In this work we only investigated feces from a single source. To better capture the extent of virus protection by the fecal matrix, future work should encompass a more diverse array of sources, and should include a thorough physical-chemical characterization of the samples. In addition, we here used phages to demonstrate the protective effect of feces. While we expect this finding to also apply to human viruses, this assumption remains to be confirmed. And finally, the mechanisms underlying the protective role of feces should be clarified. We here propose possible explanations which remain to be tested. First, the feces may form a physical barrier and prevent the exposure of the virus to the inactivating solution. Second, the feces may act as a chemical barrier that buffers the high pH. Or third, the feces matrix (<xref ref-type="bibr" rid="B42">Robinson et al., 2014</xref>; <xref ref-type="bibr" rid="B39">P&#xe9;rez-Rodriguez et al., 2019</xref>) or inner ion composition (<xref ref-type="bibr" rid="B31">Meister et al., 2020</xref>) may increase virus stability towards pH and temperature.</p>
<p>When not protected by feces, however, viruses can be expected to be readily inactivated. An increase of pH from neutral to alkaline drastically increased virus inactivation in solution (see SI, <xref ref-type="sec" rid="s11">Supplementary Figure S2A</xref>). Under the pH conditions expected in alkaline-urine treatment (pH &#x3e; 10.5), MS2 and T4 phages require less than 10&#xa0;days for a 4 log<sub>10</sub> reduction at 20&#xb0;C. This contact time became even shorter at pH &#x3e; 11.5 with only a few seconds required. &#x3a6;X174 revealed to be stable up to pH 12.0, but was also drastically inactivated beyond that pH. Compared to thermal inactivation expected over the temperature range of 4&#x2013;50&#xb0;C, inactivation by alkaline pH is more efficient (<xref ref-type="bibr" rid="B10">Decrey, 2015</xref>). However, temperature nevertheless plays an important role, as the virucidal effects of pH and temperature were found to be synergistic. Inactivation at alkaline pH effect was enhanced by increasing temperature, and vice versa, thermal inactivation was more pronounced at higher pH (SI, <xref ref-type="sec" rid="s11">Supplementary Figure S2B</xref>). In addition, the ion composition and ionic strength of the solution may also influence (enhance or inhibit) the virus stability towards high alkaline pH (<xref ref-type="bibr" rid="B10">Decrey 2015</xref>; <xref ref-type="bibr" rid="B31">Meister et al., 2020</xref>).</p>
</sec>
<sec id="s5-3">
<title>4.3 Safe Nutrient Recycling</title>
<p>When concentrating urine during dehydration, any present pathogens would also be concentrated unless they were inactivated during the dehydration process. Considering the urine-drying temperature applied [0&#x2013;40&#xb0;C; (<xref ref-type="bibr" rid="B40">Randall et al., 2016</xref>)], the treatment duration and the type of fraction treated (precipitates provided some protection), <italic>Ascaris</italic> would likely not be inactivated inside the toilet or during drying. Virus inactivation takes place mainly during the addition of Ca(OH)<sub>2</sub> and would continue during the drying phase of the end products, however, with slower kinetics (<xref ref-type="bibr" rid="B9">Decrey et al., 2011</xref>). Phages are only surrogates of human viruses, but they were more stable in the conditions expected during alkaline-urine treatment and thus serve as a worst-case scenario.</p>
<p>To produce a safe urine-based fertilizer from the alkalized-urine, we modelled the time required for a 4 log<sub>10</sub> reduction in viruses and the time required for a 3 log<sub>10</sub> reduction in <italic>Ascaris</italic> egg viability in order to meet both the <xref ref-type="bibr" rid="B53">WHO (2006)</xref> and <xref ref-type="bibr" rid="B51">USEPA (1994)</xref> guidelines for unrestricted fertilizer (crops consumed raw). The illustration in <xref ref-type="fig" rid="F3">Figure 3</xref> provides a rather conservative storage time requirement regarding both the <italic>Ascaris</italic> and the human virus reduction during alkaline-urine treatment. By collecting and treating the urine separately from the feces, for populations with no <italic>Ascaris</italic> (e.g., the Swedish and the Swiss population), the storage time can be determined by virus inactivation. Assuming a temperature of 20&#xb0;C and a pH of 10, it would then just take 10&#xa0;days for a 4 log<sub>10</sub> virus reduction. In contrast, in populations prone to <italic>Ascaris</italic> infections, <italic>Ascaris</italic> becomes the rate-determining pathogen for alkaline-urine treatment, and 111&#xa0;days of storage in a sealed bag would be required to ensure a 3 log<sub>10</sub> inactivation at 20&#xb0;C. <italic>Ascaris</italic> eggs were able to withstand alkaline environments better than bacteria (<xref ref-type="bibr" rid="B44">Senecal et al., 2018</xref>) and phages, so if <italic>Ascaris</italic> eggs are inactivated, then other pathogens, such as <italic>Salmonella</italic> spp. (<xref ref-type="bibr" rid="B14">Fidjeland et al., 2016</xref>), are also likely to be inactivated.</p>
<p>To enhance <italic>Ascaris</italic> inactivation, two potential post-treatments are thermal treatment and/or storage. In this study, compounding effects of alkaline pH or low moisture content started at temperatures &#x2265;35&#xb0;C, with pH having more of an effect than decreasing moisture content, but it still required 13&#x2013;79&#xa0;days for a 3 log<sub>10</sub> reduction in viable eggs, depending on the urine fraction treated. A final thermal treatment (&#x2265;42&#xb0;C) could be used to ensure faster inactivation (&#x3c;5&#xa0;days for a 3 log<sub>10</sub> reduction) of soil-transmitted helminths. Thermal treatment would be more effective than decreasing the moisture content.</p>
<p>Storing the dried urine in a sealed bag will retain any NH<sub>3</sub> formed and thereby ensure further inactivation of microbial contaminants, especially <italic>Ascaris</italic> spp. In a previous study where <italic>Ascaris</italic> eggs in urine/ash medium were kept in open containers (MC decreased to 1% by day 102), allowing the NH<sub>3</sub> to volatilize, at 20&#xb0;C an estimated 325&#xa0;days were required for a 3 log<sub>10</sub> reduction in viable eggs (<xref ref-type="bibr" rid="B44">Senecal et al., 2018</xref>). In the urine/Ca(OH)<sub>2</sub> solution used in this study, where the <italic>Ascaris</italic> eggs were kept in sealed tubes (no volatilization of NH<sub>3</sub> and stable MC%), a 3 log<sub>10</sub> reduction at 20&#xb0;C required a up to 111&#xa0;days. Additional research has demonstrated that high pH (12.5) and dryness have no effect on the inactivation rate of <italic>Ascaris</italic> at &#x2264; 27&#xb0;C for &#x3e;70&#xa0;days (<xref ref-type="bibr" rid="B45">Senecal et al., 2020</xref>). Based on the measured inactivation times, a minimal storage time of 111&#xa0;days at 20&#xb0;C or 79&#xa0;days at 35&#xb0;C in sealed containers would lead to a 3 log<sub>10</sub> reduction in any <italic>Ascaris</italic> present, ensuring a hygiene safety level meeting existing guidelines <xref ref-type="bibr" rid="B53">WHO (2006)</xref> and <xref ref-type="bibr" rid="B51">USEPA (1994)</xref> guidelines for unrestricted use as fertilizer.</p>
</sec>
</sec>
<sec id="s6">
<title>5 Conclusion</title>
<p>Diverting and collecting urine separately from feces is a good way to retrieve a large fraction of the nutrients from excreta, while excluding the majority of the pathogens. Virus were inactivated during the initial addition of Ca(OH)<sub>2</sub>, while <italic>Ascaris</italic> eggs were not. To ensure, and accelerate, the inactivation of parasites in alkaline treated urine, a post-treatment such as thermal treatment (&#x2265;42&#xb0;C) and/or storage in a sealed container (retaining any NH<sub>3</sub> formed) is ideal. Drying the alkaline urine can also be effective in shorting the time required for a 3 log<sub>10</sub> reduction. However, only partially drying (MC 73&#x2013;82%) the urine at 20&#xb0;C can lead to longer inactivation times than in wet (MV &#x3e;90%) and dried (MC &#x3c;33%) conditions. Finally, parasites should be considered as worst case pathogen organisms and the alkaline-urine treatment should be designed based on preventing their survival to reduce pathogen risks associated with the end products.</p>
</sec>
</body>
<back>
<sec id="s7">
<title>Data Availability Statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec id="s8">
<title>Author Contributions</title>
<p>JS: Designed the <italic>Ascaris</italic> experiment with support from BV and performed the experiment. Wrote the <italic>Ascaris</italic> sections together with AN. JS led the whole paper, with revisions by the co-authors. AN: Wrote the <italic>Ascaris</italic> sections with JS and contributed with revisions. LD: Designed the virus experiment with support from TK and performed the experiment. Wrote the virus sections together with TK. Contributed with revisions. TK: Designed the virus experiment with LD. Supported the writing of the virus sections. Contributed with revisions. BV: TK: Designed the <italic>Ascaris</italic> experiment with JS. Contributed with revisions.</p>
</sec>
<sec id="s9">
<title>Funding</title>
<p>Funding source was the Bill and Melinda Gates Foundation (grant number OPP1111293) which was awarded to the Swiss Federal Institute of Aquatic Science and Technology (EAWAG) which subcontracted the co-authors to perform the work.</p>
</sec>
<sec sec-type="COI-statement" id="s10">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="disclaimer" id="s11">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<ack>
<p>This work was funded by the Bill and Melinda Gates Foundation as part of the Blue Diversion Autarky project (OPP1111293). Thank you to our productive urine and fecal donors from the Department of Energy and Technology at the Swedish University of Agricultural Science.</p>
</ack>
<sec id="s12">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fenvs.2022.882284/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fenvs.2022.882284/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.docx" id="SM1" mimetype="application/docx" xmlns:xlink="http://www.w3.org/1999/xlink"/>
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