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			<titleStmt><title level='a'>Transcriptome Responses to Defined Insecticide Selection Pressures in the German Cockroach (Blattella germanica L.)</title></titleStmt>
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				<publisher></publisher>
				<date>02/04/2022</date>
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				<bibl> 
					<idno type="par_id">10327623</idno>
					<idno type="doi">10.3389/fphys.2021.816675</idno>
					<title level='j'>Frontiers in Physiology</title>
<idno>1664-042X</idno>
<biblScope unit="volume">12</biblScope>
<biblScope unit="issue"></biblScope>					

					<author>Michael E. Scharf</author><author>Zachery M. Wolfe</author><author>Kapil R. Raje</author><author>Mahsa Fardisi</author><author>Jyothi Thimmapuram</author><author>Ketaki Bhide</author><author>Ameya D. Gondhalekar</author>
				</bibl>
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		<profileDesc>
			<abstract><ab><![CDATA[Cockroaches are important global urban pests from aesthetic and health perspectives. Insecticides represent the most cost-effective way to control cockroaches and limit their impacts on human health. However, cockroaches readily develop insecticide resistance, which can quickly limit efficacy of even the newest and most effective insecticide products. The goal of this research was to understand whole-body physiological responses in German cockroaches, at the metatranscriptome level, to defined insecticide selection pressures. We used the insecticide indoxacarb as the selecting insecticide, which is an important bait active ingredient for cockroach control. Six generations of selection with indoxacarb bait produced a strain with substantial (&gt;20×) resistance relative to inbred control lines originating from the same parental stock. Metatranscriptome sequencing revealed 1,123 significantly differentially expressed (DE) genes in ≥two of three statistical models (81 upregulated and 1,042 downregulated; FDR              P              &lt; 0.001; log2FC of ±1). Upregulated DE genes represented many detoxification enzyme families including cytochrome-P450 oxidative enzymes, hydrolases and glutathione-              S              -transferases. Interestingly, the majority of downregulated DE genes were from microbial and viral origins, indicating that selection for resistance is also associated with elimination of commensal, pathogenic and/or parasitic microbes. These microbial impacts could result from: (i) direct effects of indoxacarb, (ii) indirect effects of antimicrobial preservatives included in the selecting bait matrix, or (iii) selection for general stress response mechanisms that confer both xenobiotic resistance and immunity. These results provide novel physiological insights into insecticide resistance evolution and mechanisms, as well as novel insights into parallel fitness benefits associated with selection for insecticide resistance.]]></ab></abstract>
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<div xmlns="http://www.tei-c.org/ns/1.0"><head>INTRODUCTION</head><p>The German cockroach, Blattella germanica L. is an international urban pest that affects millions of residences on a global scale <ref type="bibr">(Vargo, 2021)</ref>. B. germanica impacts human health through the production of asthma and rhinitis-causing allergens, transmission of food-borne pathogens and psychological stress <ref type="bibr">(Kopanic et al., 1994;</ref><ref type="bibr">Elgderi et al., 2006;</ref><ref type="bibr">Sohn and Kim, 2012)</ref>. Up to 85% of inner city homes in the United States test positive for cockroach allergens and 60-93% of inner-city children with asthma are sensitized to cockroaches <ref type="bibr">(Gore and Schal, 2007;</ref><ref type="bibr">Do et al., 2016;</ref><ref type="bibr">Pom&#233;s et al., 2017)</ref>. Cockroaches also host pro-and eukaryotic microbes that contribute to house-dust microbiomes that intensify asthma <ref type="bibr">(Roth and Willis, 1960;</ref><ref type="bibr">Pai et al., 2003;</ref><ref type="bibr">Carrasco et al., 2014;</ref><ref type="bibr">Crawford et al., 2015;</ref><ref type="bibr">Thorne et al., 2015;</ref><ref type="bibr">Wada-Katsumata et al., 2015;</ref><ref type="bibr">Lai, 2017;</ref><ref type="bibr">Turturice et al., 2017)</ref>.</p><p>Insecticides are essential for efficiently overcoming health impacts of cockroaches <ref type="bibr">(Schal and Hamilton, 1990;</ref><ref type="bibr">Pom&#233;s et al., 2017)</ref>. However, insecticide resistance has been a formidable recurring barrier to effective cockroach control for decades <ref type="bibr">(Scharf and Gondhalekar, 2021)</ref>. As of 2016, the German cockroach was reported as having developed resistance worldwide to 42 distinct insecticide active ingredients in at least 219 documented cases <ref type="bibr">(Zhu et al., 2016)</ref>. Because cockroaches live in relatively closed populations <ref type="bibr">(Crissman et al., 2010;</ref><ref type="bibr">Vargo et al., 2014;</ref><ref type="bibr">Vargo, 2021)</ref>, resistance can build quickly, even with moderate insecticide selection pressure <ref type="bibr">(Scharf et al., 1997a,b;</ref><ref type="bibr">Gondhalekar et al., 2013;</ref><ref type="bibr">Fardisi et al., 2019)</ref>. Cockroach baits are widely used in management programs and have been an effective tool for controlling cockroaches and reducing pesticide loads in urban housing (e.g., <ref type="bibr">Miller and Smith, 2020)</ref>; however, resistance can readily develop even to bait insecticides <ref type="bibr">(Gondhalekar et al., 2011</ref><ref type="bibr">(Gondhalekar et al., , 2013</ref><ref type="bibr">(Gondhalekar et al., , 2016;;</ref><ref type="bibr">Gondhalekar and</ref><ref type="bibr">Scharf, 2012, 2013;</ref><ref type="bibr">Ko et al., 2016;</ref><ref type="bibr">Fardisi et al., 2019)</ref>.</p><p>The goal of this research was to use a quantitative metatranscriptomics approach to better understand whole-body physiological responses in B. germanica to defined insecticide selection pressures. The insecticide indoxacarb was used as the selecting insecticide, which is an important bait active ingredient for cockroach control <ref type="bibr">(Appel, 2003;</ref><ref type="bibr">Buczkowski et al., 2008;</ref><ref type="bibr">Gondhalekar et al., 2011)</ref>. Through previous studies we documented early stages of resistance evolution to indoxacarb among field populations <ref type="bibr">(Gondhalekar et al., 2011</ref><ref type="bibr">(Gondhalekar et al., , 2013) )</ref> and verified hydrolysis and cytochrome P450-based oxidation as important steps in indoxacarb bioactivation and detoxification <ref type="bibr">(Gondhalekar et al., 2016)</ref>. Our specific objectives here were to: (1) identify whole-body mRNA expression profiles and candidate genes associated with indoxacarb resistance, and (2) investigate a subset of candidate resistance-associated genes in an independent and highly resistant field strain. Our findings reveal novel physiological insights into insecticide resistance evolution in this important global health pest; mainly that resistance evolves rapidly as a complex phenotype with multiple underlying mechanisms that include both xenobiotic detoxification and microbial clearance.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>MATERIALS AND METHODS</head></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Cockroach Strains and Rearing</head><p>The Arbor Park (AP) strain was used for indoxacarb selection experiments within 12 months of its collection and is the source of the "Parental-F0, " "Selected-F6, " and "Control-F6" lines (Figure <ref type="figure">1A</ref>). The AP strain was collected from an apartment in Gainesville, FL, United States after control failures with multiple insecticide products. The highly resistant field-collected "Oviedo-R" strain and the standard susceptible Johnson Wax (JWax-S) strain were included in post hoc validation experiments. The Oviedo-R strain was collected from a restaurant near Orlando, FL, United States, where indoxacarb-containing cockroach baits were used regularly for at least 3-4 years and was tested within 6 months of its collection. The JWax-S strain has been in culture for over 70 years and has never been exposed to synthetic organic insecticides. All of the above cockroach strains were reared in mixed life stages in 1,000 cm &#215; 400 cm &#215; 300 cm (L &#215; W &#215; H) plastic boxes with aerated lids, greased walls, cardboard harborage, and an ad libitum water source and rodent diet (#8604, Harlan Teklad, Madison, WI, United States). Rearing conditions consisted of a 12:12 (L:D) photocycle, 25-27 &#8226; C and &#8764;50% RH.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Chemicals</head><p>Technical grade indoxacarb (99.1% AI), blank bait matrix and formulated gel bait product containing indoxacarb (Advion R ) were provided by DuPont Inc. (Wilmington, DE, United States). All solvents and buffer components were purchased from Fisher Scientific (Pittsburgh, PA, United States) or Sigma (St. Louis, MO, United States). Other chemicals used in enzyme assays and other procedures are detailed in a previous report <ref type="bibr">(Gondhalekar, 2011)</ref>. These chemicals include the P450 substrate p-Nitroanisole, the esterase substrates p-nitrophenyl acetate and naphthyl acetate, the GST substrate chloro-dinitro benzene, protein extraction buffers, and native PAGE reagents and stains.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Selection Procedures</head><p>For selection experiments, &gt;1,200 large nymphs (4th to 5th instar) were separated from the AP lab cultures and divided into six sub populations of ca. 200 nymphs. These life stages were used because they are among the most tolerant cockroach life stages <ref type="bibr">(Koehler et al., 1993)</ref>. A feeding delivery method was used for selections because it exactly represents field exposure to indoxacarb baits <ref type="bibr">(Gondhalekar et al., 2011</ref><ref type="bibr">(Gondhalekar et al., , 2013;;</ref><ref type="bibr">Gondhalekar and Scharf, 2012)</ref>. In brief, pellets of blank gel bait matrix (ca. 5-10 mg wet weight) were prepared manually and treated with a dose of indoxacarb in acetone that provided ca. 60 to 80% mortality (Supplementary Table <ref type="table">1</ref>). Large nymphs that were prestarved for 24-h were held individually with a single indoxacarb treated pellet in 1 oz. (30 mL) cups with vented lids. After 3 days, nymphs that had completely eaten bait pellets were transferred in groups of 100 into 17.8 cm &#215; 17.8 cm &#215; 6 cm disposable plastic Glad R boxes under conditions detailed above, where they remained for 7-10 days. Almost all nymphs exhibited intoxication symptoms at 3 days; however, ca. 25-35% completely recovered over the next 7-10 days. These surviving individuals were reared to adulthood and used as founders for the next generation <ref type="bibr">(Scharf et al., 1997b)</ref>. Selections continued in this manner for six generations (Parental or F0 to F5 generation). The above process happened with three replicate "selected" and "control" lines; control lines received lab diet only. Details of indoxacarb doses used and percent survival for each round of selection are given in Supplementary Table <ref type="table">1</ref>. </p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Bioassays</head><p>Bioassays performed included vial and feeding bioassays, each in two formats.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Vial Bioassays</head><p>Vial bioassays were done in concentration-response and diagnostic-concentration formats. Concentration-response bioassays were done with adult males from the Parental (F0), Control F6 and Selected F6 generations following established protocols <ref type="bibr">(Gondhalekar et al., 2011;</ref><ref type="bibr">Fardisi et al., 2019)</ref>. Four to five concentrations providing 10-90% mortality were used for calculating lethal concentration (LC) estimates and associated parameters using probit analysis (see below). Diagnostic concentration bioassays were done by testing adult males of the JWax-S and Oviedo-R strains at previouslyestablished concentrations of 30 and 60 &#181;g indoxacarb per vial <ref type="bibr">(Gondhalekar et al., 2011</ref><ref type="bibr">(Gondhalekar et al., , 2013))</ref>. Three replicates of ten insects were conducted per concentration and isolate (n = 90). Control vials received acetone only.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Feeding Bioassays</head><p>Feeding bioassays were done in dose-response and no-choice formats. Dose-response bioassays were conducted with Parental (F0), Control F6 and Selected F6 generation adult males using a published protocol <ref type="bibr">(Gondhalekar et al., 2011)</ref>. At least four doses producing 10-90% mortality were tested against each subpopulation. Each replicate had ten insects and bioassays were repeated three times for each dose and sub-population. The dose-response data were analyzed by probit analysis (details below) and used for calculating lethal doses (LD) and associated parameters. Realized heritability (h 2 ) estimation was done on oral dose-response data to determine the proportion of phenotypic variance in resistance caused by additive genetic variation <ref type="bibr">(Falconer, 1989;</ref><ref type="bibr">Tabashnik, 1992)</ref>.</p><p>No-choice assays used formulated indoxacarb gel bait product (0.6% indoxacarb) with adult males of JWax-S strain and the field-selected highly resistant Mid-Florida strain using published protocols <ref type="bibr">(Gondhalekar et al., 2011)</ref>. The same protocols were followed for control treatments that were conducted using blank gel bait without indoxacarb. These tests were done on lab-reared individuals within 6 months of collecting the Oviedo-R strain. In these tests no alternative/competing food other than gel bait was present in the bioassay arenas. No-choice bait feeding assays were preferred for testing the Oviedo-R strain because within 6 months after field collection the population numbers were relatively low and the bait feeding bioassay required less insects as compared to the traditional dose or concentration-response tests. Disposable plastic GladWare boxes (17.8 cm &#215; 17.8 cm &#215; 6 cm; Clorox Co., Oakland, CA, United States) served as bioassay arenas and were provisioned with a water source, harborage and 0.5 g of formulated indoxacarb gel bait product in a plastic dish <ref type="bibr">(Gondhalekar et al., 2011)</ref>. Additional bait or blank matrix was provided if the insects consumed a majority of the initially provided bait. Mortality was recorded at 1, 3, 7, 14, and 21 days. Five replicates with 10 adult males per replicate (n = 50) were performed for each strain.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Enzyme Activity Assays</head><p>Enzyme assay methods were detailed previously <ref type="bibr">(Gondhalekar, 2011)</ref>. Esterase (hydrolysis) and P450 (O-demethylation) activity assays were done on F6-selected and control lines using the model substrates p-nitrophenyl acetate and p-nitroanisole, respectively. Esterase native PAGE was done using the model substrate betanaphthyl acetate. Esterase and P450 investigations were done on soluble and microsomal protein preparations, respectively, made from the same insect homogenates. Protein content was normalized using a commercial Bradford assay (Bio-Rad) with bovine serum albumin as a standard. All enzyme and protein assays were performed in triplicates representing three F6selected and three control lines.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Transcriptome Sequencing</head><p>Total RNA was isolated from three independent biological replicate samples of 10 whole adult male cockroaches from each of F6-selected and control lines. A two-step process was used that included the Promega SV Total RNA Isolation Kit (Madison, WI, United States) followed by the Bioline TRIsure kit (Taunton, MA, United States). Manufacturer protocols were followed for both kits with the exception that DNase treatment was excluded as the final step for the second kit. The use of two kits ensured the RNA samples were free of excess protein.</p><p>Total RNA yields ranged from 5.8-18.6 &#181;g with A260/280 and 260/230 ratios in the range of 1.8-2.1. Sample quality was further assessed using an Agilent Bioanalyzer (Agilent Technologies, Santa Clara, CA, United States) which verified above yields and provided acceptable RIN scores of 7.20-7.76. RNA samples were enhanced for messenger RNA (mRNA) using the Agilent Tru-Seq RNA prep kit before bar-coded sequencing libraries were made. Sequencing was done on the Illumina HiSeq 2000 platform by the Purdue University Genomics Core (West Lafayette, IN, United States). Sequencing reads were filtered using Phred quality scores and other parameters, and de novo transcriptome assembly performed from all six pooled replicate samples (3 selected and 3 control) using Trinity <ref type="bibr">(Grabherr et al., 2011)</ref>. Paired reads for individual replicate samples were then mapped to the de novo transcriptome using Bowtie2 <ref type="bibr">(Langmead and Salzberg, 2012)</ref>, which provided read counts used for differential expression analyses as detailed below. The de novo transcriptome assembly was used because a reference German cockroach genome was not yet available at the time sequencing was completed; however, new blast searches with significant contigs were performed in 2021 which confirmed origins in either the B. germanica genome or from other microbial sources.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>GO and KAAS Annotation Analyses</head><p>The assembled contiguous sequences, i.e., "contigs" were analyzed by BLAST, Blast2GO and KAAS to assign identities and functional annotations. The contigs, as well as singleread "singletons, " were annotated using "Blast2GO" for cellular location (CL), biological process (BP), and molecular function (MF) <ref type="bibr">(Conesa et al., 2005)</ref>. BLAST searches were performed against the Genbank "nr" database available as of May 2012 at www.ncbi.nlm.nih.gov and re-verified in June 2021 (file provided). KAAS analysis was done to gain insights into possible pathways and gene networks involved in resistance <ref type="bibr">(Moriya et al., 2007)</ref>. KAAS is a rapid method that establishes orthologies to genes operating within conserved pathways using best hit information and Smith-Waterman scores.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Differential Expression Analysis Methods</head><p>Basic exploration of the data such as accessing data range, library sizes etc. was performed to ensure data quality. Three models were used for analysis of read-count data obtained for each contig and singleton: edgeR (v 2.9), DESeq (v 1.8.3), and voomlimma (v 1.2.0). An edgeR object was created by combining the counts matrix, library sizes, and experimental design (3 replicates each for selected and control lines, i.e., "samples") using the edgeR package. Normalization factors were calculated for the counts matrix, followed by estimation of common dispersion of counts. An Exact test for differences between the negative binomial distribution of counts for the selected and control replicates resulted in finding differential expression, which was then adjusted for multiple-hypothesis testing to generate a result file. A DESeq object analogous to the aforementioned edgeR object was created and used to generate normalization factors followed by dispersion estimates using DESeq package. The DESeq method tests for differences between the base means of the experimental conditions and differential expression (DE) results were reported in another result file (DE_analysis_DESeq.csv). A third method called 'voom' from the limma package was also used for DE analysis. The 'voom' function carries out log2 transformation of counts followed by mean-variance estimation and assigns weight to each transformed value. Linear model coefficients were then calculated using limma's design matrix and log2 transformed values. The linear model was fitted using an empirical Bayes method and differences between counts between selected and control replicates were calculated, which was then adjusted for multiple-hypothesis testing, and reported as result file. Venn diagrams were generated displaying the DE contigs with false discovery rate (FDR) P &lt; 0.05 that were found to be common among all three analysis methods using the online tool Venny<ref type="foot">foot_2</ref> .</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Quantitative Real-Time PCR</head><p>Expression levels of 48 significantly up-and down-regulated genes identified from Illumina sequencing (Table <ref type="table">1</ref>) were investigated for validative purposes by qRT-PCR in the F6selected and control lines (three biological replicates each). PCR primers for target and reference genes were designed using Primer 3 2 <ref type="bibr">(Untergasser et al., 2012)</ref> and are given in Supplementary Table <ref type="table">2</ref>. The efficiencies of qPCR primers used in this experiment were empirically determined and they were within the recommended range of 90-110%. Validative qRT-PCR was done on aliquots of the same RNA preparations used for Illumina sequencing above using an iCycler iQ real-time PCR detection system (Bio-Rad, Hercules, CA, United States) with Sybr Green product tagging (2x SensiMix Sybr and Fluorescein Kit; Quantace, Norwood, MA, United States). Each 20 &#181;L qRT-PCR reaction in a 96-well format consisted of 10 &#181;L SensiMix (Bioline, Taunton, MA, United States), 7 &#181;L nanopure water, 1 &#181;L each of forward and reverse primer (0.5 &#181;M final concentration) and 1 &#181;L cDNA. A published qRT-PCR temperature program was followed <ref type="bibr">(Scharf et al., 2008)</ref>. Three technical replicates were performed for each gene and cDNA preparation. The resulting critical threshold (Cq) data were analyzed by the 2 -CT CT method <ref type="bibr">(Livak and Schmittgen, 2001)</ref>.</p><p>Expression of a subset of 21 genes (indicated by asterisks * in Table <ref type="table">1</ref> and Supplementary Table <ref type="table">2</ref>) that showed significant differential expression in transcriptome analyses was also quantified in the lab-susceptible JWax-S and resistant Oviedo-R strains. These genes included 13 host cockroach genes (8 P450s, 2 carboxylesterases, 1 chitinase, 1 transposable element, and 1 hypothetical protein) and 8 genes from eukaryotic/viral microbiota (4 virus, 2 gregarine, 1 coccidia, and 1 unknown). Total RNA was extracted from 1 to 2 weeks old adult males in three replicate groups of 10 for the above two strains. RNA extractions were done using the two-step process described under "Transcriptome Sequencing." cDNA synthesis was done from 500 ng total RNA using the iScript TM cDNA synthesis kit (Bio-Rad, Hercules, CA, United States). All qPCR procedures and expression analysis methods were similar to those mentioned above.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Statistical Analyses</head><p>Probit analysis was used for LD and LC determinations using SAS software Version 9.2. Mortality data were corrected for control mortality (&lt;10%) using Abbott's transformation prior to conducting Probit analysis. Resistance ratios (RRs) were calculated by dividing LC or LD estimates for the selected lines by corresponding values for susceptible lines. Significance of RRs was determined according to the procedure outlined by <ref type="bibr">Robertson and Preisler (1992)</ref>. Mean-separation analyses of insecticide toxicity (vial diagnostic and no choice bait feeding bioassays) were done by ANOVA and paired t-tests (P &lt; 0.05) after arcsine transformation of raw mortality data. For enzyme activity assays, specific activity values for the F6-selected and susceptible sub-populations were compared by non-parametric Mann-Whitney U tests (P &lt; 0.05). Methods used for differential gene expression analysis of read-count data from transcriptome sequencing are explained in a separate section above. Regression analyses were done using JMP Pro 15 software (SAS Institute, Cary, NC, United States) to compare (i) qRT-PCR results to Illumina read counts for the F6-selected and control lines (n = 48 2 <ref type="url">https://bioinfo.ut.ee/primer3-0.4.0/</ref> genes), and (ii) the F6-selected and control lines to each other and the Oviedo-R and JWax-S strains (n = 21 genes).</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>RESULTS</head></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Selection and Resistance Evolution</head><p>Six generations of selection of the parental AP strain with indoxacarb bait (Figure <ref type="figure">1A</ref>) resulted in a selected strain having significant levels of resistance in both surface contact (23.8&#215;; Figure <ref type="figure">1B</ref>) and feeding bioassays (4.5&#215;; Supplementary Table <ref type="table">2</ref>). The control strain left to inbreed without selection over the same timeframe acquired no resistance. The selection process led to heritable genetic changes with a realized heritability estimate (h2) of 0.28 (Supplementary Table <ref type="table">3</ref>). Biochemical assays on the F6-selected and control lines revealed &gt;2&#215; elevated esterase activity (P = 0.0004; Figure <ref type="figure">1C</ref>) and &#8764;0.5&#215; decreased P450 O-demethylation activity (P = 0.0004; Figure <ref type="figure">1D</ref>).</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Metatranscriptome Sequencing and Assembly</head><p>From six total libraries representing three replicates each of the selected and control lines, 133 million paired-end sequence reads were obtained that contained &gt;1.3 billion total nucleotide bases having an average read length of 98 base pairs (bp). The resulting overlapping sequences were assembled into 207,672 contiguous sequences, hereafter referred to as "contigs." Sequence reads are deposited in the NCBI GEO archive under accession number GSE188950.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Validation of de novo Transcriptome and Differentially Expressed Contigs</head><p>Contig length ranged from 201 to 30,113 bp with an average length of 1,777 bp and a N50 size of 4,805 bp; i.e., half of the assembled metatranscriptome is covered by contigs &#8805; 4,805 bp. Next, a subset of 48 assembled contigs was chosen for validation analysis by qRT-PCR using the same RNA preparations as were used for Illumina sequencing (Table <ref type="table">1</ref>). A regression plot of log2 transformed Illumina transcriptome read count (X) vs. log2 transformed qRT-PCR Cq values (Y) revealed a highly significant correlation (P &lt; 0.0001, r 2 = 0.51) (Supplementary Figure <ref type="figure">1</ref>). The latter result independently verifies the accuracy of the metatranscriptome results.</p><p>DE analysis by three different models yielded differing numbers of passing contigs (Figure <ref type="figure">2</ref>). Different FDR p-values were considered (P &lt; 0.05, 0.01, 0.001) but the greatest emphasis is placed on the P &lt; 0.001 level. The most stringent analysis model was edgeR with 473 passing contigs (Figure <ref type="figure">2A</ref>), followed by voom-limma with 1,089 (Figure <ref type="figure">2B</ref>) and DESeq with 2,209 (Figure <ref type="figure">2C</ref>). Another interesting feature of the datasets for all three models was the higher ratio of downregulated:upregulated contigs in the selected strain; i.e., 424:49 for edgeR, 960:129 for voom-limma, and 2,083:126 for DESeq. Overall, there were 236 significant DE contigs shared among all three analysis models at the FDR P &lt; 0.01 level and log2FC of &#177;1 (Figure <ref type="figure">2D</ref>). Only  contigs passing in two or more models at the FDR &lt; 0.001 log2FC &#177;1 level were considered for further analysis as detailed below.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>GO Annotation and KAAS Pathway Analyses</head><p>BLAST2GO analyses for gene annotation revealed that 36.6% of contigs were annotated (76,053). For P &lt; 0.001 passing contigs there were 779 GO terms for cellular location (CL; 99 upregulated, 680 downregulated), 1,514 for molecular function (MF; 209 up, 1,305 down) and 1,493 for biological process (BP; 265 up, 1,288 down) (Supplementary Figure <ref type="figure">2A</ref>). CL terms potentially related to insecticide resistance include membrane, ribosome, mitochondria, microsome, endoplasmic reticulum and dendrite (Supplementary Figures <ref type="figure">2B-D</ref>). Potentially relevant MF terms include electron carrier, hydrolase, monooxygenase, oxidoreductase, transferase and catalytic activity; and ATP, calcium, iron, heme, nucleotide and sugar binding. Lastly, relevant BP terms potentially linked to resistance include metabolic, transport, phosphorylation, glutathione conjugation and response to drug. KAAS analysis was used to gain further insights into responsive pathways and gene networks (Supplementary Figure <ref type="figure">3</ref>). Upregulated pathways potentially linked to resistance </p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Candidate Genes and Taxonomic Matches of Differentially Expressed Transcripts</head><p>The blastx identities of many upregulated transcripts had logical links to resistance and detoxification. Upregulated cockroach genes included many gene families commonly associated with insecticide resistance including P450 oxidases and hydrolases (Figure <ref type="figure">3</ref>) and glutathione-S-transferases (GSTs). Table <ref type="table">1</ref> overviews the 21 contigs (shown by asterisks * ) used for post hoc validations and gives a general overview of upregulated transcripts that mainly match the B. germanica genome, along with downregulated transcripts that originate mainly from microbial sources. The identities of sequences from either cockroach or microbial origins were re-verified by Genbank blastX searches performed in September 2021 (Table <ref type="table">1</ref>).</p><p>Taxonomic compositions of significant DE contigs (P &lt; 0.001), based on blastx database queries, indicate the majority of upregulated contigs are from the cockroach genome; whereas, the majority of downregulated contigs come from viruses and eukaryotic microbes (Figure <ref type="figure">4</ref>). Top upregulated taxonomic matches at the domain level were overwhelmingly eukaryotic whereas downregulated contigs had &gt;10-fold more numbers of matches to bacteria, viruses and archaea than insects. At the genera level the top taxonomic matches for upregulated contigs were nearly all insects (Blattella, Cryptotermes, Zootermopsis, Coptotermes, Timema, and Periplaneta). Downregulated transcripts at the genus level were dominated by eukaryotic microbes that are apparently commensal, pathogenic and/or parasitic (Gregarina, Cryptosporidium, Toxoplasma, Vitrella, Plasmodium, Neospora, etc.).</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Post hoc Validations in an Independent Resistant Strain</head><p>An independent resistant strain, Oviedo-R, was collected from the field after indoxacarb bait control failures and assayed alongside the standard susceptible JWax-S strain. The Oviedo-R strain was highly resistant with 0% mortality in vial bioassays on diagnostic concentrations of indoxacarb (Figure <ref type="figure">5A</ref>). These diagnostic concentrations were approximately two and fourfold higher than the indoxacarb LC50 for the Control (F6) strain shown in Figure <ref type="figure">1B</ref>. The JWax-S strain was highly susceptible with 100% mortality in the same assays. When tested in no-choice feeding bioassays with commercially-formulated indoxacarb bait, the Oviedo-R strain displayed exceptionally high resistance (ANOVA df = 1,48, F = 130.50, P &lt; 0.001) (Figure <ref type="figure">5B</ref>). The Oviedo-R strain entirely consumed 0.5 g indoxacarb bait per assay replicate by Days 7 and 14, at which time the bait was replenished. These results show high levels of physiological resistance to indoxacarb in the Oviedo-R strain with no involvement of a behavioral "aversion" component.</p><p>Finally, to test for common patterns of gene expression across strains, qRT-PCR analyses were performed on a subset of 21 significant up-and down-regulated contigs identified from the transcriptome analysis presented above (Table <ref type="table">1</ref> and Supplementary Table <ref type="table">2</ref>). The four strains included in this analysis were Oviedo-R, JWax-S, indoxacarb Selected-F6 and Control-F6. From a series of regression analyses, there was significantly correlated transcript abundance between the Selected-F6 and Oviedo-R strains (Figure <ref type="figure">6A</ref>), but no correlation when comparing Oviedo-R vs. Control-F6 (Figure <ref type="figure">6B</ref>), Control-F6 vs. Selected-F6 (Figure <ref type="figure">6C</ref>), and JWax-S vs. Selected F6 (Figure <ref type="figure">6D</ref>). These results suggest common processes associated with indoxacarb resistance evolution in lab and field-selected cockroach populations.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>DISCUSSION</head></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Overview</head><p>This study reveals new insights into cockroach insecticide resistance evolution from multiple physiological perspectives. Through a combination of approaches including selection for FIGURE 5 | Indoxacarb bioassay results for the highly resistant Oviedo-R strain and the standard susceptible JWax-S strain. (A) Vial diagnostic concentration bioassays at two concentrations showing high-level mortality and the JWax-S strain and 0% mortality in the Oviedo-R strain. (B) No-choice feeding bioassays using commercial formulated indoxacarb bait showing rapid high-level mortality in the JWax-S strain and virtually no mortality in the Oviedo-R strain. * Asterisks indicate significant differences between strains at P &lt; 0.0001.</p><p>resistance via feeding on insecticidal bait, coupled with different bioassay formats and metatranscriptome sequencing, we were able to observe that (1) the host cockroach mainly upregulates a range of detoxification resistance mechanisms, and (2) at the same time decreases its internal virus, parasite and/or pathogen levels. Further investigation of candidate gene expression in the highly resistant Oviedo-R strain suggests common phenomena that underlie resistance evolution. Taken together, these findings support the idea that high-level resistance evolution results from a dual process whereby the host tolerates the selecting insecticide through a number of potential mechanisms, and in parallel, host fitness is further increased as the body is cleared of parasites and pathogens. At present it remains unclear if the microbial impacts result from (i) direct effects of indoxacarb, (ii) indirect effects of antimicrobial preservatives included in the selecting bait matrix, or (iii) selection for general stress response mechanisms that confer both xenobiotic resistance and microbial immunity. With respect to the first two possibilities, it is unclear if these processes are associated generally with all insecticides, or specifically with ingested indoxacarb. Transcriptome sequencing revealed dozens of candidate upregulated genes from the host cockroach potentially involved in resistance, including detoxification enzymes (discussed below), transport mechanisms, host gut penetration barriers, and others. An unanticipated result was the downregulation thereby indicating disappearance of commensal, pathogenic and/or parasitic microbe transcript contigs after insecticide selection (also discussed below). Findings in both categories are corroborated by the GO and KAAS analyses, which provide additional independent confirmation for the sequence composition results relating to detoxification and parasite/pathogen disappearance. The qPCR correlation analyses between resistant and susceptible strains lends further strength to the above findings. Specifically, the regression analyses showed similar trends between independently-selected resistant strains for upregulation and downregulation of host detox mechanisms, and disappearance of a wide range of microbes. However, there appears to be wider variation with respect to disappearance of microbial contigs (right side of Figure <ref type="figure">6A</ref>). This finding is logical given that different environments have different microbiomes associated with them that can, in turn, shape internal microbiomes of higher organisms living within them <ref type="bibr">(Renelies-Hamilton et al., 2021;</ref><ref type="bibr">Tinker and Ottesen, 2021)</ref>.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Detoxification and Metabolism Mechanisms</head><p>In terms of detoxification and metabolism, indoxacarb is a unique pro-insecticide that requires hydrolytic activation to its decarbomethoxyllated "DCJW" metabolite to become an active insecticide <ref type="bibr">(Wing et al., 2000;</ref><ref type="bibr">Alves et al., 2008)</ref>. A prior study investigating indoxacarb metabolism pathways in resistant and susceptible B. germanica strains revealed that hydrolysis and P450-oxidation were important to activation and resistance-associated detoxification, respectively <ref type="bibr">(Gondhalekar et al., 2016)</ref>. The current study reveals candidate genes involved in both oxidative and hydrolytic metabolism of indoxacarb; specifically, 20 differentially expressed (DE) P450 contigs and 14 DE esterase/hydrolase contigs. In theory, resistance could result from both upregulation of P450 oxidative enzymes and downregulation of hydrolases, both of which were detected in the present study.</p><p>With respect to detoxification genes and the B. germanica genome, a targeted analysis revealed 158 P450 genes total, which represents some gene expansions in relation to the available genomes of close insect relatives <ref type="bibr">(Harrison et al., 2018a,b)</ref>. The most expanded P450 families were Cyp4 (n = 59), followed by a subset of Cyp6 (n = 8). The present study identified resistanceassociated changes of expression of 12.6% of the B. germanica "cypome, " with the majority (14) being Cyp6 members and fewer being Cyp4s (4). It is also noteworthy that a transposable element potentially associated with Cyp4 expansion <ref type="bibr">(Harrison et al., 2018b)</ref> had higher resistance-associated expression in both the indoxacarb-selected line and the field-selected Oviedo-R strain. Expansions previously identified for other detoxification genes in the B. germanica genome included 62 E4 esterases and a subgroup of 23 GST genes <ref type="bibr">(Harrison et al., 2018b)</ref>. The present study identified 14 DE esterases (4 up-and 10 down-regulated) and 11 GSTs (6 up-and 5 down-regulated). Significant changes in both P450 and esterase activity were noted with selection (Figure <ref type="figure">1</ref>) but not GST activity <ref type="bibr">(Gondhalekar, 2011)</ref>.</p><p>Numerous DE P450 contigs identified here were close homologs to Cyp6J1 and 6K1 of B. germanica <ref type="bibr">(Wen and Scott, 2001)</ref>, but none were identical matches. Some of these Cyp6 homologs had 20-50&#215; upregulation with indoxacarb selection. Based on these results it is likely that there is Cyp6 involvement in the detoxification pathway for indoxacarb <ref type="bibr">(Gondhalekar et al., 2016)</ref> and more Cyp6 diversity in the B. germanica genome than initially suggested <ref type="bibr">(Wen and Scott, 2001;</ref><ref type="bibr">Harrison et al., 2018b)</ref>. A previous study found Cyp4G19 over expression in association with fipronil and imidacloprid resistance in B. germanica, but not indoxacarb resistance, which agrees with results of the present study finding no change of expression for Cyp4G P450s. Cyp4G19 was also linked to pyrethroid resistance, cuticular hydrocarbon production and cuticular penetrationbased resistance <ref type="bibr">(Pridgeon et al., 2003;</ref><ref type="bibr">Guo et al., 2010;</ref><ref type="bibr">Pei et al., 2019;</ref><ref type="bibr">Chen et al., 2020;</ref><ref type="bibr">Hu et al., 2021)</ref>, which are seemingly unrelated to the ingestion and gut uptake that occurred during the six generations of indoxacarb selection that were done in the present study.</p><p>The current study also identified DE homologs of Cyp9e2 and Cyp4C21 with possible roles in indoxacarb biotransformation. Both Cyp9e2 and Cyp4C21 were previously identified from B. germanica along with apparent homologous pseudogenes that may confound gene identification <ref type="bibr">(Wen et al., 2001)</ref>. Another upregulated P450 in the present study was Cyp15F1, which catalyzes the last step in juvenile hormone biosynthesis <ref type="bibr">(Maestro et al., 2010;</ref><ref type="bibr">Tarver et al., 2012;</ref><ref type="bibr">Zhou et al., 2014)</ref>. The Cyp15F1 homolog identified in the present study had a strong match to its corresponding genomic sequence reported in the B. germanica genome <ref type="bibr">(Harrison et al., 2018a,b)</ref>. It is not clear if Cyp15F1 participates in indoxacarb detoxification or another physiological process related to gut tissue remodeling after indoxacarb exposure, or in response to clearance of gut microbes (e.g., <ref type="bibr">Sen et al., 2015)</ref>. A previous study identified the P450 protein "P450MA" from a multi-resistant B. germanica strain <ref type="bibr">(Scharf et al., 1998)</ref>. P450MA was overexpressed after organophosphate insecticide selection and also was found to be over-expressed in organophosphate resistant B. germanica strains from different global origins <ref type="bibr">(Scharf et al., 1997b</ref><ref type="bibr">(Scharf et al., , 1999))</ref>. While the molecular identity of P450MA remains unknown, it may be among the P450s identified in the present study, of which Cyp6 members were the most abundant.</p><p>Lastly, the identification of decreased P450 O-demethylation activity in the F6-selected strain does not appear to be an erroneous or trivial result. This is because there is good agreement between reduced O-demethylation activity in our F6selected indoxacarb-resistant strain and transcriptome results showing downregulation of several P450 contigs in the same genetic lineage. This latter finding also suggests that increased O-demethylation activity may not be a useful biomarker for indoxacarb resistance.</p><p>With regard to hydrolytic activity, it is considered more important for indoxacarb activation in B. germanica than detoxification <ref type="bibr">(Gondhalekar et al., 2016)</ref>. Esterases and associated hydrolases are overall not as well studied as the P450s discussed above, but several DE hydrolase and esterase homologs were identified through the current study. Several of these DE esterase contigs had significant matches to FE4 esterases from other insects with well-established roles in insecticide metabolism <ref type="bibr">(Field and Foster, 2002;</ref><ref type="bibr">Srigiriraju et al., 2009)</ref>. Esterase activity toward model substrates was also elevated in the F6-selected strain, which is consistent with the several upregulated esterase/hydrolase contigs that were identified through transcriptome sequencing. It is also possible that, despite being important for indoxacarb activation, increased hydrolytic activation could still enable greater detoxification by P450 and other detox enzymes and subsequent clearance from the body <ref type="bibr">(Gondhalekar et al., 2016)</ref> by Glutathione-S-transferases, some of which were also upregulated.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>Microbial Disappearance</head><p>Invertebrates were the first hosts of apicomplexan parasites like Plasmodium and Toxoplasma which later switched to vertebrate hosts during their evolution <ref type="bibr">(Kopecn&#225; et al., 2006)</ref>. Biotic associations of cockroaches with microbes have been known for over 100 years and include bacteria, archaea, viruses, protists, fungi, gregarines, and nematodes <ref type="bibr">(Roth and Willis, 1960;</ref><ref type="bibr">Kakumanu et al., 2018)</ref>. In the present study, transcript contigs from representatives of all of these groups were greatly reduced with indoxacarb selection. Omics approaches similar to those used here have previously identified gregarines and other eukaryotic microbes in insects and thus it should not be surprising that similar eukaryotic microbe transcripts were identified in the present study through the use of poly-A RNA tagging <ref type="bibr">(McCarthy et al., 2011;</ref><ref type="bibr">Scharf, 2015;</ref><ref type="bibr">Scharf et al., 2017)</ref>. Many of the microbial genera that were reduced by the selection process are potential pathogens to humans and companion animals (e.g., Cryptosporidium, Toxoplasma, Vitrella, Plasmodium, Neospora, etc.) and thus our findings on their disappearance may be highlighting a previously unknown/unacknowledged benefit of cockroach baits.</p><p>Gregarine protist contigs were the dominant downregulated contigs in the F6-indoxacarb selected line. One common parasitic gregarine, Gregarine blattarum, can infect multiple cockroach species including B. germanica, as well as other invertebrates <ref type="bibr">(Yahaya et al., 2017)</ref>. Gregarine infection has been shown to cause pathological effects in B. germanica as well as increase susceptibility to the fungal pathogen Metarhizium anisopliae and the growth regulator insecticide triflumuron <ref type="bibr">(Lopes and Alves, 2005)</ref>, which compels us to ask the question: is insecticide susceptibility caused in part by microbial pathogens or parasite stress? Cockroaches in culture are particularly susceptible to gregarine infections and such infections can be reduced by antimicrobial drugs <ref type="bibr">(Clopton and Smith, 2002;</ref><ref type="bibr">Smith and Clopton, 2003)</ref>. However, it does not appear that many of the sampled microbial groups are exclusively associated with laboratory rearing <ref type="bibr">(Kakumanu et al., 2018)</ref>. Gregarines are further known to accelerate larval development in cat fleas, Ctenocephalides felis <ref type="bibr">(Alarc&#243;n et al., 2017)</ref> and have recently been identified in cucumber beetles, Acalymma vittatum, with no apparent impacts on fitness <ref type="bibr">(Coco et al., 2020)</ref>. To our knowledge no prior reports are available describing the effects of insecticides on gregarines, but a prior report does document impacts on related termite gut protists by the nicotinoid insecticide imidacloprid <ref type="bibr">(Sen et al., 2015)</ref>. While it is not clear if the disappearance of these internal microbes enhances host fitness to enable a rapid buildup of xenobiotic resistance, or vice-versa (i.e., if resistance happens first), our findings provide important new insights into the potential stepwise basis of resistance evolution and the complex physiological interactions involved.</p></div>
<div xmlns="http://www.tei-c.org/ns/1.0"><head>CONCLUSION</head><p>This study provides new insights into cockroach insecticide resistance evolution from multiple physiological perspectives ranging from xenobiotic metabolism and excretion to pathogen and parasite resistance. The identities of dozens of candidate bioactivation and detoxification enzymes were revealed, namely cytochrome P450s and esterases/hydrolases, which agrees strongly with outcomes of preceding indoxacarb metabolomics work in B. germanica <ref type="bibr">(Gondhalekar et al., 2016)</ref>. Many of the genes studied here also had strong matches to the B. germanica genome <ref type="bibr">(Harrison et al., 2018a,b)</ref> and thus our findings provide important annotations that have been lacking in many cases. Because we used a selection-based approach with temporally parallel non-selected controls that originated from the same genetic stock, and compared strains from both common and distinct genetic origins in a stepwise fashion, the insights provided have limited caveats. Thus, the correlated expression for a subset of candidate genes between independently-selected resistant strains suggests there are common, predictable patterns to resistance evolution across populations.</p><p>An unanticipated outcome was that numerous microbial transcripts were reduced with insecticide selection. In terms of the causative agents behind microbial disappearance, three possibilities exist: (i) direct antimicrobial effects by indoxacarb, (ii) indirect effects of antimicrobial preservatives in the bait matrix, or (iii) co-selection for dual detoxification and immune pathways. While the potentially direct effects of the selecting insecticide or bait matrix preservatives on eukaryotic microbes are logical, the causative factors underlying virus and bacterial declines are less clear and should be further investigated. Findings also revealed a potential added benefit of cockroach baits for curing cockroaches of potentially deleterious pathogens and associated allergens that can affect both humans and companion animals. A priori goals of this study did not include identification of effects on cockroach parasites and pathogens, and thus our experimental design was not optimized for gaining insights into host-microbial interactions. Future work thus needs to examine for similarities in genes, microbes and processes revealed here, with the ultimate goal of reducing impacts of insecticide resistance and concurrently creating healthier indoor urban environments.</p></div><note xmlns="http://www.tei-c.org/ns/1.0" place="foot" xml:id="foot_0"><p>Frontiers in Physiology | www.frontiersin.org</p></note>
			<note xmlns="http://www.tei-c.org/ns/1.0" place="foot" xml:id="foot_1"><p>February 2022 | Volume 12 | Article 816675</p></note>
			<note xmlns="http://www.tei-c.org/ns/1.0" place="foot" n="1" xml:id="foot_2"><p>http://bioinfogp.cnb.csic.es/tools/venny/index.html Frontiers in Physiology | www.frontiersin.org</p></note>
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