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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Physiol.</journal-id>
<journal-title>Frontiers in Physiology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Physiol.</abbrev-journal-title>
<issn pub-type="epub">1664-042X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">879401</article-id>
<article-id pub-id-type="doi">10.3389/fphys.2022.879401</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Physiology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Responses of Fungi Maggot (<italic>Bradysia impatiens</italic> Johannsen) to Allyl Isothiocyanate and High CO<sub>2</sub>
</article-title>
<alt-title alt-title-type="left-running-head">Gou et al.</alt-title>
<alt-title alt-title-type="right-running-head">Fumigate <italic>Bradysia impatiens</italic> With AITC&#x002B;CO<sub>2</sub>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Gou</surname>
<given-names>Yu-Ping</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1686429/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Quandahor</surname>
<given-names>Peter</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Mao</surname>
<given-names>Liang</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Li</surname>
<given-names>Chun-Chun</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Zhou</surname>
<given-names>Jing-Jiang</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1325734/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Liu</surname>
<given-names>Chang-Zhong</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/1340347/overview"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>College of Plant Protection</institution>, <institution>Gansu Agricultural University/Biocontrol Engineering Laboratory of Crop Diseases and Pests of Gansu Province</institution>, <addr-line>Lanzhou</addr-line>, <country>China</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>CSIR&#x2014;Savanna Agricultural Research Institute</institution>, <addr-line>Tamale</addr-line>, <country>Ghana</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Forestry and Grassland Bureau of Lintao County</institution>, <addr-line>Dingxi</addr-line>, <country>China</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/382545/overview">Bin Tang</ext-link>, Hangzhou Normal University, China</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/1255487/overview">Samira Kilani-Morakchi</ext-link>, University of Annaba, Algeria</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/622850/overview">Yujie Lu</ext-link>, Henan University of Technology, China</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1046501/overview">Muhammad Hafeez</ext-link>, Zhejiang University, China</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Chang-Zhong Liu, <email>liuchzh@gsau.edu.cn</email>
</corresp>
<fn fn-type="other">
<p>This article was submitted to Invertebrate Physiology, a section of the journal Frontiers in Physiology</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>05</day>
<month>05</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>13</volume>
<elocation-id>879401</elocation-id>
<history>
<date date-type="received">
<day>19</day>
<month>02</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>21</day>
<month>03</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2022 Gou, Quandahor, Mao, Li, Zhou and Liu.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Gou, Quandahor, Mao, Li, Zhou and Liu</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>Botanical pesticide is highly recommended for integrated pest management (IPM), due to its merits such as environmental friendliness, safe to non-target organisms, operators, animals, and food consumers. The experiment was conducted to determine the lethal and sub-lethal effects of allyl isothiocyanate (AITC) on eggs, third instar larvae, pupae, and females and males of <italic>Bradysia impatiens</italic> Johannsen (<italic>B. impatiens</italic>). Different concentrations of AITC under ambient CO<sub>2</sub> by the conical flask sealed fumigation method were used for the experiment. The results showed that there was a significant linear relationship between different concentrations of AITC and the toxicity regression equation of <italic>B. impatiens</italic>. The sub-lethal concentrations of AITC had significant effects on the larval stage, pupal stage, pupation rate, pupal weight, adult emergence rate, and oviposition. The pupation rate, pupal weight, and adult emergency rate were significantly (<italic>p</italic> &#x3c; 0.05) affected by AITC fumigation. The pupation rate was the lowest after fumigation treatment of AITC at LC<sub>50</sub> (36.67%), followed by LC<sub>25</sub> (41.94%), compared with the CK (81.39%). Female longevity was significantly (<italic>p</italic> &#x3c; 0.05) shortened by fumigation at LC<sub>25</sub> (1.75 d) and LC<sub>50</sub> (1.64 d), compared with that of CK (2.94 d). Male longevity was shorter at LC<sub>25</sub> (1.56 d) than at LC<sub>50</sub> (1.25 d) and had no significant difference between these two treatments. The fumigation efficiency of AITC was significantly increased under high CO<sub>2</sub> condition. Furthermore, detoxification enzyme activities and antioxidant enzyme activities were accumulated under high CO<sub>2</sub> condition. The fumigation method in the application of AITC can be useful in areas where <italic>B. impatiens</italic> is a major concern.</p>
</abstract>
<kwd-group>
<kwd>
<italic>Bradysia impatiens</italic> Johannsen</kwd>
<kwd>allyl isothiocyanate</kwd>
<kwd>sub-lethal effects</kwd>
<kwd>high CO<sub>2</sub>
</kwd>
<kwd>detoxification enzyme activity</kwd>
<kwd>antioxidant enzyme activity</kwd>
</kwd-group>
<contract-num rid="cn001">201303027</contract-num>
<contract-num rid="cn002">2018YFD0200405</contract-num>
<contract-sponsor id="cn001">Special Fund for Agro-Scientific Research in the Public Interest<named-content content-type="fundref-id">10.13039/501100010042</named-content>
</contract-sponsor>
<contract-sponsor id="cn002">National Key Research and Development Program of China<named-content content-type="fundref-id">10.13039/501100012166</named-content>
</contract-sponsor>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>
<italic>Bradysia impatiens</italic> Johannsen is an economic important pest globally, which survives on mushrooms, chives, ornamental plants, and humus (<xref ref-type="bibr" rid="B20">Johannsen, 1912</xref>; <xref ref-type="bibr" rid="B35">Menzel et al., 2003</xref>; <xref ref-type="bibr" rid="B41">Santos et al., 2012</xref>; <xref ref-type="bibr" rid="B16">Gou et al., 2019</xref>). The larvae feed on the roots, stems, leaves, flowers, and even the whole seedling of host plants (<xref ref-type="bibr" rid="B15">Gou et al., 2020a</xref>; <xref ref-type="bibr" rid="B12">Gou et al., 2020b</xref>). <italic>B. impatiens</italic> was first reported on mushrooms in China (<xref ref-type="bibr" rid="B43">Shen et al., 2009</xref>). Other host plants of this pest include chive (<italic>Allium tuberosum</italic>) (<xref ref-type="bibr" rid="B13">Gou et al., 2015</xref>), onion (<italic>A. fistulosum</italic>) (<xref ref-type="bibr" rid="B13">Gou et al., 2015</xref>), lily (<italic>Lilium brownie</italic>) (<xref ref-type="bibr" rid="B13">Gou et al., 2015</xref>), carrot (<italic>Daucus carota</italic>) (<xref ref-type="bibr" rid="B1">Arimoto et al., 2018</xref>), poinsettia (<italic>Euphorbia pulcherrima</italic>) (<xref ref-type="bibr" rid="B5">Cheng et al., 2018</xref>), butterfly orchid (<italic>Phalaenopsis aphrodite</italic>) (<xref ref-type="bibr" rid="B5">Cheng et al., 2018</xref>), strawberry (<italic>Fragaria ananassa</italic>) (<xref ref-type="bibr" rid="B47">Sueyoshi and Yoshimatsu, 2019</xref>), and eucalyptus (<italic>Eucalyptus robusta</italic>). <italic>B. impatiens</italic> is an agricultural and forestry pest distributed in areas such as the United States, South Africa, Japan, the Netherlands, Brazil, Hawaiian Islands, the United Kingdom, Russia and other countries (<xref ref-type="bibr" rid="B35">Menzel et al., 2003</xref>; <xref ref-type="bibr" rid="B12">Gou et al., 2020b</xref>).</p>
<p>Botanical pesticide is highly recommended for integrated pest management (IPM) due to its merits of environmental friendliness, safe to non-target organisms, operators, and animal and food consumers. The development of the botanical control method has been proposed as one of the most important strategies for pest management on fruits, vegetables, and ornamental plants (<xref ref-type="bibr" rid="B64">Zhang et al., 2015</xref>; <xref ref-type="bibr" rid="B5">Cheng et al., 2018</xref>; <xref ref-type="bibr" rid="B30">Lu et al., 2020</xref>). AITC, commonly known as horseradish, is a volatile and aliphatic sulfur-containing compound naturally occurring in plants from the family of Cruciferae, such as: horseradish (<italic>Armoracia rusticana</italic>), mustard (<italic>Brassica nigra</italic>), cabbage (<italic>Brassica oleracea</italic>), and wasabi (<italic>Wasabia japonica</italic>) (<xref ref-type="bibr" rid="B33">Mayton et al., 1996</xref>; <xref ref-type="bibr" rid="B57">Wu et al., 2009</xref>; <xref ref-type="bibr" rid="B53">Williams et al., 2015</xref>; <xref ref-type="bibr" rid="B25">Li Y et al., 2018</xref>). AITC could be rapidly adsorbed and degraded in soil with a low risk of persistence (<xref ref-type="bibr" rid="B40">Ren et al., 2018</xref>); thus, it has been considered a potential botanical pesticide. It has been effectively used to control soil-borne fungi (<xref ref-type="bibr" rid="B60">Yim et al., 2016</xref>), plant pathogen (<xref ref-type="bibr" rid="B45">Smolinska et al., 2003</xref>; <xref ref-type="bibr" rid="B48">Troncoso et al., 2005</xref>; <xref ref-type="bibr" rid="B49">Ugolini et al., 2014</xref>), nematodes (<xref ref-type="bibr" rid="B4">Brolsma et al., 2014</xref>), weeds (<xref ref-type="bibr" rid="B2">Bangarwa and Norsworthy, 2014</xref>; <xref ref-type="bibr" rid="B9">Devkota and Norsworthy, 2014</xref>; <xref ref-type="bibr" rid="B32">Matteo et al., 2017</xref>), and pests (<xref ref-type="bibr" rid="B56">Wu H. et al., 2014</xref>; <xref ref-type="bibr" rid="B8">Deguenon et al., 2019</xref>; <xref ref-type="bibr" rid="B63">Zhang et al., 2020</xref>). Some storage pest species, including <italic>Sitophilus oryzae</italic> (<xref ref-type="bibr" rid="B54">Worfel et al., 1997</xref>), <italic>Sitophilus zeamais</italic> (<xref ref-type="bibr" rid="B31">Mansour et al., 2012</xref>), <italic>Callosobruchus maculatus</italic> (<xref ref-type="bibr" rid="B62">Zhang et al., 2016</xref>), <italic>Tribolium confusum</italic> (<xref ref-type="bibr" rid="B24">Li et al., 2011</xref>), and <italic>Plodia interpunctella</italic> (<xref ref-type="bibr" rid="B29">Liang et al., 2013</xref>), are particularly sensitive to AITC and have achieved remarkable fumigation effect. AITC also has good efficacy against adults of <italic>B. odoriphaga</italic> (<xref ref-type="bibr" rid="B44">Shi et al., 2017</xref>).</p>
<p>An increase in atmospheric carbon dioxide (CO<sub>2</sub>) concentration is predicted to continually increase from the current 400&#xa0;ppm to between 750 and 1,300&#xa0;ppm by the end of this century (<xref ref-type="bibr" rid="B10">Erda et al., 2005</xref>; <xref ref-type="bibr" rid="B26">Li et al., 2020</xref>). CO<sub>2</sub> is an important regulator of respiration, and the spiracle of insects are kept open permanently under high concentrations of CO<sub>2</sub> (higher than 10&#x2013;20%) (<xref ref-type="bibr" rid="B36">Miller, 1974</xref>). Accordingly, they are likely to absorb more fumigants when their spiracle is open permanently. A mixture of fumigants and high concentrations of CO<sub>2</sub> enhances toxicity to insects (<xref ref-type="bibr" rid="B36">Miller, 1974</xref>; <xref ref-type="bibr" rid="B17">Haritos et al., 2006</xref>). Several positive effects on various fumigants have been investigated, including methyl bromide, ethanedinitrile (<xref ref-type="bibr" rid="B39">Ramadan et al., 2021</xref>), ethyl formate (<xref ref-type="bibr" rid="B17">Haritos et al., 2006</xref>; <xref ref-type="bibr" rid="B7">Damcevski et al., 2010</xref>), and the essential oils from <italic>Perilla frutescens</italic> (L.) Britt. (Lamiaceae) (<xref ref-type="bibr" rid="B59">Ye et al., 2015</xref>), showing that the control efficacy against the targeted pests had been apparently strengthened under high concentrations of CO<sub>2</sub>. In general, there is a balance between the generation of reactive oxygen species (ROS) and their scavenging. However, when exposed to environmental stress, the balance is disrupted. Insecticidal stress causes an increase in the production of ROS, which causes oxidative damage (<xref ref-type="bibr" rid="B21">Lalouette et al., 2011</xref>). Excess ROS causes lipid peroxidation (LPO) and disrupts cell membrane fluidity, leading to cell lesions. The degree of membrane LPO can be determined indirectly by measuring the concentration of malondialdehyde (MDA) (<xref ref-type="bibr" rid="B34">Meng et al., 2009</xref>). Organisms have evolved complex adaptation-related mechanisms for eliminating ROS, such as molecular antioxidants and antioxidative enzymes (<xref ref-type="bibr" rid="B19">Joanisse and Storey, 1998</xref>), to maintain homeostasis and prevent ROS damage. Superoxide dismutase (SOD), catalase (CAT), peroxidase (POD), and glutathione-S-transferases (GSTs) are the most important components for protecting cells and maintaining homeostasis in various stress conditions by scavenging ROS (<xref ref-type="bibr" rid="B11">Felton and Summers, 1995</xref>). Numerous studies have used antioxidant responses to thermal stress as indicators of important physiological adaptation processes in insects (<xref ref-type="bibr" rid="B11">Felton and Summers, 1995</xref>). Detoxification enzymes in the insect body such as the GSTs, CarE, and cytochrome-b5 (Cyt-b5) are other important factors (<xref ref-type="bibr" rid="B61">Li et al., 2021</xref>; <xref ref-type="bibr" rid="B28">Liang et al., 2017</xref>) that decrease the effectiveness of insecticides by changing the metabolism (<xref ref-type="bibr" rid="B58">Xiao et al., 2009</xref>; <xref ref-type="bibr" rid="B46">Su et al., 2012</xref>).</p>
<p>
<italic>Bradysia impatiens</italic> is considered an economic important pest due to its ability to inhibit the production of a wide range of agricultural crops. Consequently, wide ranges of synthetic insecticides are continuously used for its management in China. This type of strategy has been found to seriously increase environmental contamination and insecticide resistance and endangers the health of farm operators, animals, and food consumers. Botanical pesticides are considered safe in pest control because they have low or no toxic residue, making them safe to people and the environment. Thus, developing botanical control methods for the management of <italic>B. impatiens</italic> is paramount for crop production. This research is based on the hypothesis that the application of AITC and/or CO<sub>2</sub> combination affects the performance of <italic>B. impatiens</italic>. The study is, therefore, conducted to determine the lethal and sub-lethal effects of allyl isothiocyanate (AITC) on eggs, third instar larvae, pupae, and females and males of <italic>B. impatiens</italic> Johannsen (<italic>B. impatiens</italic>).</p>
</sec>
<sec id="s2">
<title>2 Materials and Methods</title>
<sec id="s2-1">
<title>2.1 Experimental Plant</title>
<p>The chive cultivar &#x201c;pingjiu No. 2,&#x201d; which is susceptible to <italic>B. impatiens</italic> (<xref ref-type="bibr" rid="B13">Gou et al., 2015</xref>), was planted in the experimental field of Gansu Agricultural University for 3&#xa0;years. All necessary agronomic practices such as watering, stubble cutting, and farm manure application were carried out regularly, without chemical spraying.</p>
</sec>
<sec id="s2-2">
<title>2.2 Tested Insect</title>
<p>Larvae of <italic>B. impatiens</italic> were collected from chive plants in a greenhouse of the Pan&#x2019;an town (34&#xb0; 45&#x2032;22&#x2032; N, 105&#xb0; 7&#x2032;2 &#x2032;E), Gansu County, Tianshui, China, in April 2019. The individuals of the laboratory population were reared on a self-developed artificial diet (<xref ref-type="bibr" rid="B14">Gou et al., 2020c</xref>). The eggs were collected and placed in transparent plastic rearing containers (upper diameter &#xd7; lower diameter &#xd7; height &#x3d; 12&#xa0;cm &#xd7; 8 cm &#xd7; 8&#xa0;cm). The larvae were fed on chive rhizomes for three constant generations in a light growth chamber under (25 &#xb1; 1)&#xb0;C temperature, 65&#x2013;70% relative humidity (RH), and 16&#xa0;L&#xa0;h: 8D&#xa0;h photoperiod. The eggs, third larvae, pupae, and newly emerged females and males were randomly selected for the analyses.</p>
</sec>
<sec id="s2-3">
<title>2.3. Chemicals</title>
<p>Technical grade AITC (active ingredient &#x3e;98%) was purchased from Sigma, the United States of America GSTs, CarE, Cyt-b5, SOD, CAT, and POD assay kits were purchased from Shanghai Preferred Biotechnology, China.</p>
</sec>
<sec id="s2-4">
<title>2.4 Toxicity Process</title>
<sec id="s2-4-1">
<title>2.4.1 Preparation of Allyl Isothiocyanate Solution</title>
<p>To achieve the mother liquor containing 9.5% AITC, technical grade AITC was dissolved in soybean oil with a volume ratio of 1: 9&#xa0;V/V (<xref ref-type="bibr" rid="B42">Santos et al., 2011</xref>; <xref ref-type="bibr" rid="B38">Paes et al., 2012</xref>) and stored at 4&#xb0;C in dark (maintain chemical activity). Soybean oil did not affect the toxicity tests on <italic>B. impatiens</italic> that was used as the solvent to minimize the volatilization rate of AITC, particularly when used at low quantities (<xref ref-type="bibr" rid="B38">Paes et al., 2012</xref>). Thus, preliminary experiments were conducted, and final concentrations of AITC including 0.0, 3.0, 6.0, 9.0, 12.0, and 15.0&#xa0;&#x3bc;L/L were tested.</p>
</sec>
<sec id="s2-4-2">
<title>2.4.2 Fumigation Test</title>
<p>The experiment was carried out in the fume hood of the laboratory under ambient CO<sub>2</sub> by the conical flask sealed fumigation method (<xref ref-type="bibr" rid="B40">Ren et al., 2018</xref>). A count of 100 eggs (1 day old), third larvae, pupae (1 day old), and unmated females and males were collected each and then placed in corresponding flasks (500&#xa0;ml). Each flask contained fresh chive rhizomes (2-cm length) and had wet absorbent cotton with two filter papers (9-cm diameter) at the bottom. Aliquots of the AITC test solution (30&#xa0;&#x3bc;L) were applied to the filter paper strips (1&#xa0;cm &#xd7; 6&#xa0;cm) plugged at the top of the flask and then sealed with plug and parafilm. The untreated control flask had only soybean oil (30&#xa0;&#x3bc;L). Three replicates were set up for each treatment. All flasks were incubated 24&#xa0;h in the light growth chamber at (25 &#xb1; 1)&#xb0;C, 65%&#x2013;70% RH, and 16: 8 (L: D). The adults and larvae were considered dead with no observable motion when gently touched with a soft brush. The pupae were recorded for 5 d to observe the adult emergence number. The egg hatching numbers were recorded for 7d.</p>
</sec>
</sec>
<sec id="s2-5">
<title>2.5 Effects of Sub-lethal Concentrations of Allyl Isothiocyanate on Growth Parameters of <italic>B. Impatiens</italic>
</title>
<p>The AITC sub-lethal concentrations (LC<sub>25</sub> and LC<sub>50</sub>) against third larvae obtained by fumigation were used to determine the growth parameters of <italic>B. impatiens</italic>. The solvent soybean oil without AITC was used as the control. Each treatment contained 100 third larvae with three replications. After 24&#xa0;h treatment, 60 surviving larvae were transferred into three petri dishes (12-cm, 20 individuals in one dish) containing moistened filter papers and maintained in a growth chamber at 25&#xb0;C, 65%&#x2013;70% RH, and 16L: 8D. Water was added along the edge of the filter paper every day to maintain appropriate humidity and timely supplemented with fresh chive rhizomes without chemicals. The survivals and instars were recorded. The pupae were moved to petri dishes (35-mm, containing moistened filter paper) one by one and weighed within 48&#xa0;h. We weighed the pupae with a single head using a millionth scale. Twenty heads were collected for each treatment and repeated three times. Meanwhile, the survival of pupae was monitored daily. Once an adult emerged, unmated males and females (1:1) were transferred into transparent plastic containers (as described earlier). Each container contained absorbent cottons and filter papers; the male and female longevity and the number of eggs laid by each female were recorded daily. Ten pairs were considered a group, one group was considered a replicate, and three replicates were used for the female oviposition and adult longevity monitoring.</p>
<p>The pupation rate (%) was calculated using the formula [(total number of collected pupae/total number of fourth instar larvae) &#xd7; 100]. The emergence rate (%) was calculated using the formula [(total number of emerged adults/total number of collected pupae) &#xd7; 100].</p>
</sec>
<sec id="s2-6">
<title>2.6 High CO<sub>2</sub> and/or LC<sub>25</sub> Allyl Isothiocyanate Fumigation Stress</title>
<p>To assess the effect of elevated CO<sub>2</sub> on AITC fumigation efficacy against <italic>B. impatiens</italic> larvae, 100 heads third larvae of <italic>B. impatiens</italic> were placed in one conical flask (500&#xa0;ml) with three replicates. The experiment was carried out with LC<sub>25</sub> concentration of AITC as described in the previous paragraph. In addition to the AITC fumigation &#x2b; high CO<sub>2</sub> (AF &#x2b; HC, under high CO<sub>2</sub> concentration about 800&#xa0;ppm with AF stress), the flasks containing the larvae were connected to a high-pressure CO<sub>2</sub> cylinder via plastic tubing. CO<sub>2</sub> was delivered to the flasks for 10&#xa0;s at 50&#xa0;kPa (about 800&#xa0;ppm) (<xref ref-type="bibr" rid="B51">Wang et al., 2018</xref>). The flasks were immediately tightly sealed with plug and parafilm. Larvae without any treatment (CK, under ambient CO<sub>2</sub> concentration about 400&#xa0;ppm without AF stress), larvae treated only with AITC fumigation (AF, under ambient CO<sub>2</sub> concentration about 400&#xa0;ppm with AF stress), and larvae treated with only high CO<sub>2</sub> (HC, under high CO<sub>2</sub> concentration about 800&#xa0;ppm without AF stress) were all placed at the same time. At 24, 48, and 72&#xa0;h after treatment, the larvae were recovered under ambient air for 2&#xa0;h and mortality was examined. The larvae were considered dead if they were immobile after being gently stimulated by a soft brush.</p>
</sec>
<sec id="s2-7">
<title>2.7 Enzyme Activity Assay</title>
<sec id="s2-7-1">
<title>2.7.1 Preparation of Enzyme Sources and Determination and Calculation of Enzyme Activity</title>
<p>Third instar larvae of <italic>B. impatiens</italic> were collected from four treatments (CK, HC, AF, and AF &#x2b; HC), washed with phosphate buffer solution (PBS, pH 7.0) containing 1.0&#xa0;mmol/L ethylene diamide tetra acetic acid (EDTA), and then kept in a 1.5-ml centrifuge tube. Each tube contained 20 heads (about 0.05&#xa0;g) with three replications and marked. Each sample was frozen in liquid nitrogen for 15&#xa0;min and then homogenized in ice in 1.5&#xa0;ml of 0.1&#xa0;M PBS with a high-speed tissue grinder (TIANGEN). The supernatants were collected after the centrifugation of homogenates at 12,000 &#xd7; g for 15&#xa0;min at 4&#xb0;C. The resultant supernatant was stored at &#x2212;80&#xb0;C and used as an enzyme source. We detected three detoxification enzyme activities, such as glutathione-S-transferase (GSTs), carboxylesterase (CarE), and cytochrome-b5 (Cyt-b5); three antioxidant enzyme activities, such as superoxide dismutase (SOD), catalase (CAT), and peroxidase (POD). The methods of determination and calculation for each enzyme were strictly referred to the instructions of the kit (Shanghai Preferred Biotechnology, China).</p>
</sec>
</sec>
<sec id="s2-8">
<title>2.8 Statistical Analysis</title>
<p>The experimental data were statistically analyzed using SPSS23.0 software. The toxicity regression equation and the values of LC<sub>25</sub> and LC<sub>50</sub> were calculated by the Probit module (probability unit regression) (<xref ref-type="bibr" rid="B55">Wu H. H. et al., 2014</xref>). Differences among the treatments were subjected to Tukey&#x2019;s test (<italic>p &#x3c; 0.05</italic>). GraphPad Prism 6.0 software was used for plotting graphs.</p>
</sec>
</sec>
<sec id="s3">
<title>3 Results</title>
<sec id="s3-1">
<title>3.1 Toxicity of Allyl Isothiocyanate to <italic>B. Impatiens</italic>
</title>
<p>The bioassay result indicated that AITC showed significant (<italic>p</italic> &#x3c; 0.05) insecticidal effect on <italic>B. impatiens</italic>. After fumigation in the conical flask for 24&#xa0;h, the values of LC<sub>50</sub> against the female and male adults were 4.79 and 5.47&#xa0;&#x3bc;L/L, respectively, which were significantly lower than those of the eggs (10.23&#xa0;&#x3bc;L/L, <italic>&#x3c7;</italic>
<sup>2</sup> &#x3d; 1.30, <italic>p</italic> &#x3d; 0.71), pupae (10.40&#xa0;&#x3bc;L/L, <italic>&#x3c7;</italic>
<sup>2</sup> &#x3d; 1.92, <italic>p</italic> &#x3d; 0.58), and third larvae (11.27&#xa0;&#x3bc;L/L, <italic>&#x3c7;</italic>
<sup>2</sup> &#x3d; 1.55, <italic>p</italic> &#x3d; 3.38) (<xref ref-type="table" rid="T1">Table 1</xref>).</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Toxicity of the AITC fumigation method to substages of <italic>B. impatiens</italic>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Substage</th>
<th align="center">Toxicity regression equation</th>
<th align="center">
<italic>&#x3c7;</italic>
<sup>2</sup> (Df)</th>
<th align="center">
<italic>p</italic>-value</th>
<th align="center">LC<sub>25</sub> (&#x3bc;L L<sup>&#x2212;1</sup>) (95%confidence limit)</th>
<th align="center">LC<sub>50</sub> (&#x3bc;L L<sup>&#x2212;1</sup>) (95%confidence limit)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Eggs</td>
<td align="char" char="+">
<italic>y</italic> &#x3d; &#x2212;1.14 &#x2b; 1.132<italic>x</italic>
</td>
<td align="char" char="(">1.39 (99)</td>
<td align="char" char=".">0.71</td>
<td align="char" char="(">2.60 (0.692&#x2013;4.101)</td>
<td align="char" char="(">10.23 (7.619&#x2013;16.585)</td>
</tr>
<tr>
<td align="left">3rd larvae</td>
<td align="char" char="+">
<italic>y</italic> &#x3d; &#x2212;1.41 &#x2b; 1.382<italic>x</italic>
</td>
<td align="char" char="(">1.55 (99)</td>
<td align="char" char=".">0.67</td>
<td align="char" char="(">3.38 (1.583&#x2013;4.739)</td>
<td align="char" char="(">10.40 (8.161&#x2013;14.968)</td>
</tr>
<tr>
<td align="left">Pupae</td>
<td align="char" char="+">
<italic>y</italic> &#x3d; &#x2212;2.04 &#x2b; 1.939<italic>x</italic>
</td>
<td align="char" char="(">1.92 (99)</td>
<td align="char" char=".">0.58</td>
<td align="char" char="(">5.06 (2.849&#x2013;6.661)</td>
<td align="char" char="(">11.27 (8.579&#x2013;17.197)</td>
</tr>
<tr>
<td align="left">Female</td>
<td align="char" char="+">
<italic>y</italic> &#x3d; &#x2212;2.40 &#x2b; 3.527<italic>x</italic>
</td>
<td align="char" char="(">1.35 (99)</td>
<td align="char" char=".">0.94</td>
<td align="char" char="(">3.08 (0.622&#x2013;4.677)</td>
<td align="char" char="(">4.79 (2.067&#x2013;6.851)</td>
</tr>
<tr>
<td align="left">Male</td>
<td align="char" char="+">
<italic>y</italic> &#x3d; &#x2212;2.34 &#x2b; 3.175<italic>x</italic>
</td>
<td align="char" char="(">1.38 (99)</td>
<td align="char" char=".">0.81</td>
<td align="char" char="(">3.35 (0.421&#x2013;5.233)</td>
<td align="char" char="(">5.47 (2.087&#x2013;8.179)</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-2">
<title>3.2 Survival Rate</title>
<p>The bioassay results showed that increasing concentrations of AITC significantly (<italic>p</italic> &#x3c; 0.05) decreased the survival rate of <italic>B. impatiens</italic> each stage (<xref ref-type="fig" rid="F1">Figure 1</xref>), that is, significantly increased their mortality rates. Fumigation results showed that AITC had suppressive effects on each stage of <italic>B. impatien</italic>. For example, at 6&#xa0;&#x3bc;L/L concentration of AITC, the survival rate of pupae (69%) was the least affected by AITC, with the highest survival rate and the strongest resistance, followed by eggs (60%) and larvae (58%). A concentration of 15&#xa0;&#x3bc;L/L AITC was fatal to female and male adults, which caused 100% mortality.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Effect of different concentrations of AITC on the survival rate of <italic>B. impatiens</italic>.</p>
</caption>
<graphic xlink:href="fphys-13-879401-g001.tif"/>
</fig>
</sec>
<sec id="s3-3">
<title>3.3 Larval Stage and Pupal Stage</title>
<p>The developmental stage of <italic>B. impatiens</italic> was significantly (<italic>p</italic> &#x3c; 0.05) affected by LC<sub>25</sub> and LC<sub>50</sub> fumigation treatment (<xref ref-type="fig" rid="F2">Figure 2</xref>). The third larval stage was significantly (<italic>p</italic> &#x3c; 0.05) prolonged after LC<sub>25</sub> and LC<sub>50</sub> of AITC stress; however, no obvious changes between those two sub-lethal concentrations were observed. AITC stress of LC<sub>25</sub> prolonged third larval stage of 0.77 d, compared with LC<sub>50</sub>. After AITC treatment, LC<sub>50</sub> prolonged the fourth larval stage by 0.05 d than LC<sub>25,</sub> compared with CK (3.13&#xa0;d). The fumigation treatment prolonged the pupal stage of <italic>B. impatiens</italic> by 0.35&#xa0;d at LC<sub>25</sub> and 0.95&#xa0;d at LC<sub>50</sub>. However, there was no significant difference between CK and LC<sub>25</sub>.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Changes in the third larval stage, fourth larval stage, and pupal stage of <italic>B. impatiens</italic> after sub-lethal concentration fumigation of AITC. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g002.tif"/>
</fig>
</sec>
<sec id="s3-4">
<title>3.4 Pupation Rate, Pupal Weight, and Adult Emergency Rate</title>
<p>The pupation rate, pupal weight, and adult emergency rate were significantly (<italic>p</italic> &#x3c; 0.05) affected by AITC fumigation. The pupation rate was the lowest after fumigation treatment of AITC at LC<sub>50</sub> (36.67%), followed by LC<sub>25</sub> (41.94%), compared with the CK (81.39%) (<xref ref-type="fig" rid="F3">Figure 3A</xref>). Pupal weight was reduced by 0.10&#xa0;mg at LC<sub>25</sub> and by 0.22 at LC<sub>50</sub>; however, there was no significant difference between the two sub-lethal concentrations (<xref ref-type="fig" rid="F3">Figure 3B</xref>). The adult emergency rate in CK was significantly higher (65%; <italic>p</italic> &#x3c; 0.05) than that of LC<sub>25</sub> (50.17%) and LC<sub>50</sub> (40%) treatments (<xref ref-type="fig" rid="F3">Figure 3C</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Changes in the pupation rate <bold>(A)</bold>, pupa weight <bold>(B),</bold> and adult emergence rate <bold>(C)</bold> of <italic>B. impatiens</italic> after sub-lethal concentration fumigation of AITC. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g003.tif"/>
</fig>
</sec>
<sec id="s3-5">
<title>3.5 Adult Longevity and Oviposition</title>
<p>Female longevity was significantly (<italic>p</italic> &#x3c; 0.05) shortened by fumigation at LC<sub>25</sub> (1.75&#xa0;d) and LC<sub>50</sub> (1.64&#xa0;d), compared with that in CK (2.94 d; <xref ref-type="fig" rid="F4">Figure 4A</xref>). Male longevity was shorter at LC<sub>25</sub> (1.56&#xa0;d) than at LC<sub>50</sub> (1.25&#xa0;d) and had no significant difference between the two treatments (<xref ref-type="fig" rid="F4">Figure 4B</xref>). Oviposition was significantly (<italic>p</italic> &#x3c; 0.05) decreased at LC<sub>25</sub> (22 eggs) and at LC<sub>50</sub> (0 eggs) compared to the CK (75.10 eggs; <xref ref-type="fig" rid="F4">Figure 4C</xref>). Obviously, AITC fumigation treatment was significantly inhibited by the oviposition of <italic>B. impatiens</italic>.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Changes in female longevity <bold>(A)</bold>, male lingevity <bold>(B),</bold> and adult oviposition <bold>(C)</bold> of <italic>B. impatiens</italic> after sub-lethal concentration fumigation of AITC. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g004.tif"/>
</fig>
</sec>
<sec id="s3-6">
<title>3.6 Allyl Isothiocyanate Fumigation Efficiency Under High CO<sub>2</sub>
</title>
<p>To determine the effect of high CO<sub>2</sub> on AITC fumigation efficiency against <italic>B. impatiens</italic>, we incorporated high CO<sub>2</sub> exposure of the third larvae during AITC LC<sub>25</sub> treatment (<xref ref-type="fig" rid="F5">Figure 5</xref>). Notably, high CO<sub>2</sub> and/or AITC treatment apparently enhanced the mortality of <italic>B. impatiens</italic> (<italic>p</italic> &#x3c; 0.05) with prolonged time. The larvae subjected to the AITC treatment alone displayed 28.67, 39, and 83.67% mortality at 24, 48, and 72&#xa0;h time points, respectively. Exposure to high concentration of CO<sub>2</sub> during AITC treatment substantially increased the mortality to 48, 59.33, and 99%.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Changes in mortality of <italic>B. impatiens</italic> in three treatment hours under ambient CO<sub>2</sub> or/and high CO<sub>2</sub> conditions with and without AITC fumigation. CK: no AITC fumigation under ambient CO<sub>2</sub> condition; AF: AITC fumigation; HC: high CO<sub>2</sub> stress; AF &#x2b; HC: AITC fumigation under high CO<sub>2</sub> condition. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g005.tif"/>
</fig>
</sec>
<sec id="s3-7">
<title>3.7 Detoxification Enzyme Activity</title>
<p>Generally, AITC fumigation treatments had a significant (<italic>p</italic> &#x3c; 0.05) effect on the detoxification enzyme activities. We measured GST, CraE, and Cyt-b5 activities in third larvae of <italic>B. impatiens</italic> after high CO<sub>2</sub> and/or AITC fumigation for 24&#xa0;h followed by recovery of normal environment for 2&#xa0;h (<xref ref-type="fig" rid="F6">Figure 6</xref>). GST activity was upregulated by either the AITC treatment alone or the combined treatment of AITC with high CO<sub>2</sub>, and the latter induced a higher response (<xref ref-type="fig" rid="F6">Figure 6A</xref>). Similarly, CarE activity was also increased by these treatments (<xref ref-type="fig" rid="F6">Figure 6B</xref>). Substantially higher CarE activity was obtained after the combined treatment than after individual treatment in third larvae. Enhanced Cyt-b5 activity was also detected under various treatments compared to that in the untreated group (<xref ref-type="fig" rid="F6">Figure 6C</xref>), and high CO<sub>2</sub> apparently stimulated these responses than being AITC used alone. Elevated detoxification enzymes may reduce the damage caused by AITC.</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>Changes in GST enzyme activity <bold>(A)</bold>, CarE enzyme activity <bold>(B),</bold> and Cyt-b5 enzyme <bold>(C)</bold> activity of <italic>B. impatiens</italic> after AITC fumigation treatment under ambient CO<sub>2</sub> or high CO<sub>2</sub> conditions with and without AITC fumigation. CK: no AITC fumigation under ambient CO<sub>2</sub> condition; AF: AITC fumigation; HC: high CO<sub>2</sub> stress; AF &#x2b; HC: AITC fumigation under high CO<sub>2</sub> condition. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g006.tif"/>
</fig>
</sec>
<sec id="s3-8">
<title>3.8 Antioxidant Enzyme Activity</title>
<p>High concentration of CO<sub>2</sub> often corresponds to low concentration of O<sub>2</sub>. This environment will stimulate the ROS of organisms and produce oxygen oxidative damage. After being fumigated by AITC and recovered indoors for 2&#xa0;h, the activity of antioxidant enzymes <italic>in vivo</italic> was detected. The results showed that the activities of CAT and POD were inhibited, while the activities of SOD were significantly induced (<italic>p</italic> &#x3c; 0.05; <xref ref-type="fig" rid="F7">Figure 7</xref>). Under high CO<sub>2</sub> concentration condition, the activities of SOD, CAT, and POD were significantly increased (<italic>p</italic> &#x3c; 0.05). The activity of SOD significantly stimulated when treated by AITC under high CO<sub>2</sub> compared with that of CK; however, the degree of activation was weaker than that of the two separate treatments (<xref ref-type="fig" rid="F7">Figure 7A</xref>).</p>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>Changes in SOD enzyme activity <bold>(A)</bold>, CAT enzyme activity <bold>(B)</bold>, and POD enzyme activity <bold>(C)</bold> of <italic>B. impatiens</italic> after AITC fumigation treatment under ambient CO<sub>2</sub> or high CO<sub>2</sub> conditions with and without AITC fumigation. CK: no AITC fumigation under ambient CO<sub>2</sub> condition; AF: AITC fumigation; HC: high CO<sub>2</sub> stress; AF &#x2b; HC: AITC fumigation under high CO<sub>2</sub> condition. Data represent mean &#xb1; SD of three replicates. Different lower-case letters indicate statistically significant difference between sub-lethal concentrations by Tukey&#x2019;s test (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fphys-13-879401-g007.tif"/>
</fig>
</sec>
</sec>
<sec id="s4">
<title>4 Discussion</title>
<p>Plant extracts are considered for pest management because they can be selective, biodegraded to non-toxic products, and have low toxicity to non-target organisms and environment (<xref ref-type="bibr" rid="B40">Ren et al., 2018</xref>). Allyl isothiocyanate (AITC) is a natural product formed from allyl glucosinolate hydrolysis and obtained from the damaged tissues of cruciferous plants (<xref ref-type="bibr" rid="B6">Clarke, 2010</xref>; <xref ref-type="bibr" rid="B53">Williams et al., 2015</xref>). <xref ref-type="bibr" rid="B44">Shi et al. (2017)</xref> reported that AITC has high fumigation bioactivity against eggs, larvae, pupae, and adults of <italic>B. odoriphag</italic>a (<xref ref-type="bibr" rid="B44">Shi et al., 2017</xref>). The application of AITC inhibits <italic>S. zeamai</italic> performance, particularly at the adult stage (<xref ref-type="bibr" rid="B56">Wu H. et al., 2014</xref>). In the present study, the AITC fumigation test showed greater lethal effects on female and male adults of <italic>B. impatiens</italic> than those on eggs, third larvae, and pupae. This is probably because the AITC fumigation contains high toxicity that might have interfered with their respiratory mechanism. We, therefore, speculate that AITC fumigation is more lethal to the adult <italic>B. impatiens</italic> and sub-lethal to its eggs, third larvae, and pupae stages. Consequently, the life cycle of <italic>B. impatiens</italic> should be considered when developing a pesticide application strategy, as its eggs, third larvae, and pupae stages are spent in the growing medium than on the host plant.</p>
<p>In indoor or outdoor field environment, insecticides produce lethal and sub-lethal effects on pests (<xref ref-type="bibr" rid="B23">Leviticus et al., 2020</xref>). Sub-lethal effects refer to ecological, physiological, or behavioral changes in surviving insects after being exposed to sub-lethal insecticide concentrations, which cannot kill them immediately but inhibits their growth, reproduction, and longevity (<xref ref-type="bibr" rid="B27">Li Z et al., 2018</xref>; <xref ref-type="bibr" rid="B52">Wang Q et al., 2019</xref>). The third larvae of <italic>Helicoverpa armigera</italic> when treated with LC<sub>10</sub>, LC<sub>25,</sub> and LC<sub>50</sub> of chlorantraniliprole for 48&#xa0;h showed significantly prolonged larval and pupal stages of the first generation (<xref ref-type="bibr" rid="B37">Ou et al., 2012</xref>). <xref ref-type="bibr" rid="B28">Liang et al. (2017)</xref> reported that the growth, development, and fecundity of <italic>Spodoptera litura</italic> third larvae were significantly inhibited by thiacloprid LC<sub>25</sub> and LC<sub>50</sub> (<xref ref-type="bibr" rid="B28">Liang et al., 2017</xref>). To understand toxicity impact for AITC on <italic>B. impatiens</italic>, its lethal and sub-lethal effects on third larvae were investigated. The results showed that larval and pupal stages were prolonged, pupae weight was lightened, rates of pupation and adult development were reduced, and oviposition was decreased after the third larvae were treated with LC<sub>25</sub> and LC<sub>50</sub> of AITC.</p>
<p>It is well-recognized that CO<sub>2</sub>, as a regulator of respiration, plays very important roles in the life activities of insects (<xref ref-type="bibr" rid="B36">Miller, 1974</xref>). However, when the CO<sub>2</sub> concentration increased by 10&#x2013;20%, insect spiracles remained open permanently (<xref ref-type="bibr" rid="B36">Miller, 1974</xref>), which provided a new idea for the efficient utilization of the fumigant. High CO<sub>2</sub> combined with fumigation against many storage pests has been well-reported. <xref ref-type="bibr" rid="B22">Leelaja et al. (2007)</xref> found that elevated CO<sub>2,</sub> approximately 10&#x2013;20%, could significantly enhance the fumigation effect of allyl acetate on <italic>S. oryzae</italic>, <italic>S. serrulata</italic>, <italic>T. ferrugineus</italic>, <italic>T. castaneum</italic>, and <italic>S. Dominica</italic> (<xref ref-type="bibr" rid="B22">Leelaja et al., 2007</xref>). Similarly, high CO<sub>2</sub> increased the effectiveness of methyl benzoate against the larvae of <italic>Callosobruchus chinensis</italic> (<xref ref-type="bibr" rid="B50">Wang L et al., 2019</xref>) and significantly improved ethyl formate toxicity to <italic>T. castanea</italic> and <italic>Rhizopertha dominica</italic> (<xref ref-type="bibr" rid="B17">Haritos et al., 2006</xref>). Our findings illustrated that the exposed third larvae of <italic>B. impatiens</italic> to AITC under high CO<sub>2</sub> conditions lead to a higher mortality than in normal atmosphere; moreover, these lethal effects were as high as 100% with prolonged time. This indicates that high CO<sub>2</sub> concentration probably contributed greatly to the fumigant formation, which caused a high lethal effect on <italic>B. impatiens</italic>. Accordingly, the presence of CO<sub>2</sub> concentration under green and mushroom houses must be examined when considering the management of <italic>B. impatiens.</italic>
</p>
<p>Insects detoxify the different numerous exogenous and endogenous compounds due to the production of detoxification enzymes, including GSTs, CarE, and Cyt-b5, and their activities are considered to be an effective indicator monitoring the development of insect resistance to pesticides (<xref ref-type="bibr" rid="B61">Li et al., 2021</xref>; <xref ref-type="bibr" rid="B3">Bilal et al., 2020</xref>). The presence of insecticides is reported to stimulate the activities of detoxification enzymes due to the increased production of ROS (<xref ref-type="bibr" rid="B18">Jiang et al., 2020</xref>). The present results show that the enzyme activities of GSTs, CarE, and Cyt-b5 in <italic>B. impatiens</italic> third larvae were induced by the sub-lethal concentrations of AITC (LC<sub>25</sub>) after 24&#xa0;h and significantly enhanced under high CO<sub>2</sub>. These results suggest that the detoxification enzymes may be adaptively activated in <italic>B. impatiens</italic> third larvae as a pro-survival mechanism in response to low concentration of AITC (LC<sub>25</sub>). Although <italic>B. impatiens</italic> developed resistance to some extent, it was not enough to defend them from the lethal effect of the AITC (LC<sub>25</sub>) under high CO<sub>2</sub>. Previous studies reported that increase in AITC exposure could influence the host plant physiology through accumulation of ROS. Although the present study speculates that AITC fumigation shows greater sub-lethal effects on the growth and reproduction of <italic>B. impatiens,</italic> AITC under high CO<sub>2</sub> conditions may lead to host plant cell damage due to high accumulation of ROS. Thus, the level and frequency of AITC fumigation application must be considered in pest management.</p>
</sec>
<sec id="s5">
<title>5 Conclusion</title>
<p>The results of this study indicate that AITC is an effective plant extract which demonstrates greater lethal effects on the various stages of <italic>B. impatiens</italic>. The fumigation method showed effective insecticidal effect on the <italic>B. impatiens</italic>. AITC (LC<sub>25</sub> and LC<sub>50</sub>) greatly showed sub-lethal effects on the growth and reproduction of <italic>B. impatiens</italic>. The AITC fumigation test showed greater lethal effects on female and male adults of <italic>B. impatiens</italic> than those on eggs, third larvae, and pupae. LC<sub>25</sub> and LC<sub>50</sub> of AITC prolonged larval and pupal stages. The rates of pupation and adult development were reduced, and oviposition was decreased after third larvae were under AITC stress. Moreover, high CO<sub>2</sub> enhanced the insecticidal effects of AITC and caused changes in detoxification and antioxidant enzyme activities in <italic>B. impatiens</italic>. The fumigation method in the application of AITC can be useful in areas where <italic>B. impatiens</italic> is a major concern. Although the present study speculates that AITC fumigation shows greater sub-lethal effects on the growth and reproduction of the <italic>B. impatiens,</italic> AITC under high CO<sub>2</sub> conditions may lead to host plant cell damage due to high accumulation of ROS. Thus, the level and frequency of AITC fumigation application must be considered in pest management.</p>
</sec>
</body>
<back>
<sec id="s6">
<title>Data Availability Statement</title>
<p>The original contributions presented in the study are included in the article/Supplementary Materials; further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="s7">
<title>Author Contributions</title>
<p>Y-PG and C-ZL studied the concept and designs. Y-PG and LM analyzed and interpreted the data. PQ, C-CL, and C-ZL investigated and collected the resources. Y-PG drafted the manuscript. PQ and J-JZ reviewed and edited the manuscript. J-JZ critically revised and proofread the manuscript. Y-PG, J-JZ, and C-ZL contributed to statistical analysis. C-ZL funded and supervised the study.</p>
</sec>
<sec id="s8">
<title>Funding</title>
<p>This research was funded by the Special Fund for Agro-scientific Research in the Public Interest (201303027), and the National Key Research and Development Program of China (2018YFD0200405).</p>
</sec>
<sec sec-type="COI-statement" id="s9">
<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="s10">
<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>The authors would like to acknowledge JJ Scientific Consultant Ltd., United Kingdom who provided valuable suggestions and contributed to the quality of this article.</p>
</ack>
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