Newly sequenced mitogenomes from 42 diverse fish species were used in evaluating the performance of the MitoAnnotator pipeline. The 42 species are as follows (the International Nucleotide Sequence Database Collaboration accession numbers are provided): Acanthocybium solandri (AP012945), Anchoviella sp. (AP012524), Aphanopus carbo (AP012944), Ariomma indica (AP012513), Ariomma lurida (AP012512), Assurger anzac (AP012508), Benthodesmus tenuis (AP012522), Dionda episcopa (AP012077), Diplospinus multistriatus (AP012523), Epinnula magistralis (AP012943), Eumegistus illustris (AP012497), Euthynnus affinis (AP012946), Evoxymetopon poeyi (AP012509), Gempylus serpens (AP012502), Gymnosarda unicolor (AP012510), Hemitremia flammea (AP012078), Icichthys lockingtoni (AP012511), Kali indica (AP012500), Luciocyprinus striolatus (AP012525), Luxilus chrysocephalus (AP012079), Macrhybopsis gelida (AP012080), Margariscus margarita (AP012081), Microphysogobio yaluensis (AP012073), Nesiarchus nasutus (AP012503), Nocomis biguttatus (AP012082), Notropis atherinoides (AP012083), Notropis baileyi (AP012084), Opsopoeodus emiliae (AP012085), Pampus punctatissimus (AP012516), Peprilus burti (AP012947), Promethichthys prometheus (AP012504), Pteraclis aesticola (AP012499), Rastrelliger kanagurta (AP012948), Ruvettus pretiosus (AP012506), Sarda orientalis (AP012949), Scombrolabrax heterolepis (AP012517), Sphyraena japonica (AP012501), Tanakia tanago (AP012526), Taractes asper (AP012498), Tetragonurus atlanticus (AP012515), Tetragonurus cuvieri (AP012514), and Thyrsitoides marleyi (AP012505). The extracted mitogenomes were amplified via the long PCR technique (Miya and Nishida 1999 ; Inoue et al. 2003a (link)) and sequenced with the Sanger sequencing technique.
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Affinis
Affinis
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Most cited protocols related to «Affinis»
To generate reference sequences for repetitive element families from the Fritillaria genomes, we performed graph‐based clustering of unique nuclear 454 reads using the repeatexplorer pipeline via galaxy (Novák et al., 2010 , 2013 ). Clustering was performed separately for F. affinis and F. imperialis to create a reference set of repeat families for each. Initial runs of repeatexplorer revealed that the number of reads from F. affinis that it is possible to cluster is limited by the presence of a relatively high‐abundance tandem repeat (corresponding to the FriSAT1 repeat identified by Ambrožová et al., 2011 ). The number of reads that can be analysed simultaneously by repeatexplorer is governed by the number of similarity hits produced, as all read overlaps are loaded into the computer memory during the graph‐based clustering step (Novák et al., 2013 ). Consequently, this limit does not differ greatly between, for example, 200 and 400 bp reads (it is recommended that reads of the same length are used), allowing coverage to be increased by analysing longer reads. Therefore, to maximize the genome coverage for F. affinis, clustering was performed on 400 bp reads; custom Perl scripts were used to trim reads of > 400 bp from the 3′ end and to remove any reads of < 400 bp. For F. affinis, all 400 bp reads were inputted into repeatexplorer , allowing it to randomly subsample the data set to the maximum number of reads that could be processed (830 674 of 1056 953 available 400 bp reads were used). A random sample of 400 bp reads (842 670) from F. imperialis was taken using the sequence sampling tool (v1.0.0) in repeatexplorer to create a data set providing the same level of genome coverage (0.74%) as for F. affinis. The clustering pipeline was run with ≥ 220 bp overlap for clustering and ≥ 160 bp overlap for assembly. All clusters containing ≥ 0.01% of the input reads were examined manually to identify clusters that required merging (i.e. where there was evidence that a single repeat family had been split over multiple clusters). Clusters were merged if they met the following criteria: they formed connected components with a significant number of similarity hits between the clusters (e.g. in a pair of clusters, 5% of the reads in the smaller cluster had Blast hits to reads in the larger cluster); they were of the same repeat type (e.g. Copia LTR retrotransposons); they would be merged in a logical position (e.g. for repetitive elements containing conserved domains, clusters were only merged if it would result in the conserved domains being joined in the correct order). The reclustering pipeline was run using ≥ 160 bp overlap for assembly and the merged clusters were examined manually to verify that all domains were in the correct orientation.
Clusters were annotated inrepeatexplorer according to hits from Blast searches to the repeatmasker Viridiplantae database and to a database of conserved domains; where a substantial number of reads matched the same repeat type (e.g. 20% of reads in the cluster matching a Gypsy LTR retrotransposon) these annotations were retained. For clusters not annotated in repeatexplorer (i.e. no significant Blast hits), or where only very few reads had a Blast hit or separate reads matched different repeat types (i.e. inconsistent Blast hits), contigs were searched against GenBank using Blastn and Blastx (Altschul et al., 1997 ) and submitted to Tandem Repeat Finder (Benson, 1999 ).
To calculate the proportion of the genome (genome proportion (GP)) comprised of each repeat family (i.e. cluster), we conducted Blast searches of all unique nuclear reads (Table S4) against databases of the contigs from the clustering analysis. GP was calculated for all clusters containing ≥ 0.05% of the reads inputted into repeatexplorer (Tables S5, S6; we refer to these as the ‘top’ repeat families); we used ≥ 0.05% reads as a cut‐off as these clusters contain > 165 kb of data, which is sufficient to provide several‐fold coverage for most known repetitive elements (e.g. see http://gydb.org ), and therefore can be expected to represent complete elements. Contigs from all clusters were used to create separate custom Blast databases for F. affinis and F. imperialis using the makeblastdb tool in Blast+ (v2.2.24+; Camacho et al., 2009 ). The unique nuclear read data sets from each of the 10 species sequenced (Table S4) were searched against each database using megablast in the Blastn tool in Blast+ (v2.2.24+). To capture the maximum number of hits, searches were conducted with a relaxed E‐value of 100 and no filter for low‐complexity sequence (further increases to the E‐value cut‐off did not result in additional hits); a single hit was recorded for each read. Blast results were then filtered using a custom Perl script to retain only those where ≥ 55% of the query read matched one of the contigs, with ≥ 90% similarity between the query and subject in the matching portion. We calculated the GP from the filtered Blast hits using a custom Perl script. For each contig, the number of bases of the query sequence participating in the top high‐scoring pair for each Blast hit was summed to give the total number of bp representing each contig in the data sets of unique nuclear reads. For each cluster, the number of bp for all of its contigs was summed and expressed as a percentage of the total data set size (i.e. total number of bp in the set of unique nuclear reads; Table S4) to give the value for GP. The genomic abundance of each cluster in Mb was calculated as follows: (total Mb of cluster in data set × genome size in Mb/data set size in Mb). GP and Mb estimates for the top clusters in F. affinis and F. imperialis are shown in Tables S5 and S6.
Clusters were annotated in
To calculate the proportion of the genome (genome proportion (GP)) comprised of each repeat family (i.e. cluster), we conducted B
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The Global Initiative on Sharing Avian Influenza Data (GISAID) was founded in 2006, and, since 2010, has been hosted by the German Federal Ministry of Food, Agriculture and Consumer Protection. GISAID has also become a coronavirus repository since December 2019. As of 4 March 2020, the cutoff point for our phylogenetic analysis, the GISAID database (https://www.gisaid.org/ ) had compiled 254 coronavirus genomes, isolated from 244 humans, nine Chinese pangolins, and one bat Rhinolophus affinis (BatCoVRaTG13 from Yunnan Province, China). The sequences have been deposited by 82 laboratories listed in Dataset S1, Supplementary Table 1 . Although SARS-CoV-2 is an RNA virus, the deposited sequences, by convention, are in DNA format. Our initial alignment confirmed an earlier report by Zhou et al. (7 (link)) that the pangolin coronavirus sequences are poorly conserved with respect to the human SARS-CoV-2 virus, while the bat coronavirus yielded a sequence similarity of 96.2% in our analysis, in agreement with the 96.2% published by Zhou et al. We discarded partial sequences, and used only the most complete genomes that we aligned to the full reference genome by Wu et al. (8 (link)) comprising 29,903 nucleotides. Finally, to ensure comparability, we truncated the flanks of all sequences to the consensus range 56 to 29,797, with nucleotide position numbering according to the Wuhan 1 reference sequence (8 (link)). The laboratory codes of the resulting 160 sequences and the bat coronavirus sequences are listed in Dataset S1, Supplementary Table 2 (Coronavirus Isolate Labels).
The 160 human coronavirus sequences comprised exactly 100 different types. We added to the data the bat coronavirus as an outgroup to determine the root within the phylogeny. Phylogenetic network analyses were performed with the Network 5011CS package, which includes, among other algorithms, the median joining network algorithm (3 (link)) and a Steiner tree algorithm to identify most-parsimonious trees within complex networks (9 ). We coded gaps of adjacent nucleotides as single deletion events (these deletions being rare, up to 24 nucleotides long, and mostly in the amino acid reading frame) and ran the data with the epsilon parameter set to zero, and performed an exploratory run by setting the epsilon parameter to 10. Both settings yielded a low-complexity network. The Steiner tree algorithm was then run on both networks and provided the identical result that the most-parsimonious trees within the network were of length 229 mutations. The structures of both networks were very similar, with the epsilon 10 setting providing an additional rectangle between the A and B clusters. The network output was annotated using the Network Publisher option to indicate geographic regions, sample collection times, and cluster nomenclature.
The 160 human coronavirus sequences comprised exactly 100 different types. We added to the data the bat coronavirus as an outgroup to determine the root within the phylogeny. Phylogenetic network analyses were performed with the Network 5011CS package, which includes, among other algorithms, the median joining network algorithm (3 (link)) and a Steiner tree algorithm to identify most-parsimonious trees within complex networks (9 ). We coded gaps of adjacent nucleotides as single deletion events (these deletions being rare, up to 24 nucleotides long, and mostly in the amino acid reading frame) and ran the data with the epsilon parameter set to zero, and performed an exploratory run by setting the epsilon parameter to 10. Both settings yielded a low-complexity network. The Steiner tree algorithm was then run on both networks and provided the identical result that the most-parsimonious trees within the network were of length 229 mutations. The structures of both networks were very similar, with the epsilon 10 setting providing an additional rectangle between the A and B clusters. The network output was annotated using the Network Publisher option to indicate geographic regions, sample collection times, and cluster nomenclature.
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This study was part of the Australian snakebite project (ASP) which prospectively recruits suspected and definite snake bite patients from more than one hundred hospitals across Australia and referrals from all major Australian poison centres. We reviewed all cases of definite brown snake envenoming. The recruitment, design and data collection have been described previously. [6] (link), [17] (link) Approval was obtained from several Human Research and Ethics Committees to cover all involved institutions.
Patient demographics, laboratory results, clinical effects, treatments and outcomes are all documented as part of ASP onto our case report forms that are faxed by the treating doctor to the study coordinating centre where the data is entered into a relational database. Where possible, patient serum is collected pre and post antivenom administration, centrifuged, and stored at −80°C for venom concentration quantification.
Patients were included in this study if the snake was identified by an expert or if brown snake venom was detected in the serum. All cases recruited to ASP between January 2004 and January 2012 were reviewed if they were identified as possible brown snake bites or envenoming cases based on expert snake identification, positive snake venom detection kit (sVDK) for brown snake venom, or clinical suspicion. Cases of VICC positive for tiger snake or taipan venom on sVDK on bite site or urine, but found to be negative in the serum for either venom were then tested with formal venom-specific enzyme immunoassay (EIA) for brown snake, and included if positive. The sVDK was not used as an inclusion criterion in the absence of expert snake identification or brown snake venom detected with venom-specific enzyme immunoassay.
Cases were classified into envenomation syndromes: VICC (complete or partial), myotoxicity, thrombotic microangiopathy and systemic symptoms, as previously described. [17] (link) Complete VICC is defined as undetectable fibrinogen and/or raised D-Dimer (at least 10 times the assay cut-off or >2.5 mg/L) and an international normalised ratio (INR) >3. Partial VICC is defined as low but detectable fibrinogen, elevated D-Dimer and a maximum INR <3. Other defined clinical effects were haemorrhage (type of haemorrhage; major haemorrhage was defined as an intracranial haemorrhage, large gastrointestinal haemorrhage with a drop in haemoglobin or any other life-threatening haemorrhage), early hypotensive collapse, cardiac arrest, seizure, electrocardiogram (ECG) changes and troponin concentrations. Treatment, complications and adverse events were analysed, including systemic hypersensitivity reactions to antivenom, which were defined as anaphylaxis if they met NIAID/FAAN consensus criteria for this diagnosis, [18] (link) and defined as severe according to the grading system developed by Brown. [19] (link).
Bite locations were converted into latitude and longitude coordinates usinghttp://www.csu.edu.au/australia/latlong/index.html , to plot a distribution map. In line with recent taxonomic revisions, [20] (link) cases were divided into Pseudonaja species groupings based on non-overlapping geographical regions: P. textilis (Eastern Australia); P. nuchalis (‘Top End’, Northern Territory) and ‘Western Australia’ including P. modesta, P. mengdeni and P. affinis. Locations outside these regions or where there was significant overlap were not included in this sub-group analysis.
All antivenom used in the study was equine F(ab’)2 and was manufactured by CSL Ltd. The dose of antivenom is defined as the amount administered before the first available post-antivenom blood sample for venom-specific enzyme immunoassay. Polyvalent antivenom contains on average the equivalent of eight vials of brown snake antivenom, based on a study of CSL terrestrial snake antivenoms. [21] (link) In patients given polyvalent antivenom the dose was converted to the equivalent number of brown snake antivenom vials using this 8 to 1 conversion. The total dose was also calculated for each patient receiving further antivenom.
Methods for the enzyme immunoassay have previously been described. [10] (link) Polyclonal antibodies (IgG) to brown snake venom raised in rabbits are used, with detection by biotinylated antibodies and streptavidin horseradish peroxidase. The limit of detection for brown snake venom was 0.15 ng/ml. The peak pre-antivenom venom concentration is reported where available. An enzyme immunoassay using labelled anti-Horse IgG was also used to detect antivenom in patient serum to confirm antivenom administration.
Medians, interquartile ranges (IQR) and ranges are used to report continuous data, and proportions were reported with 95% confidence intervals (CIs). For the enzyme immunoassay standard curves were fitted by linear and non-linear regression using both Excel and Prism 5.03 for Windows [GraphPad Software, San Diego California USA,www.graphpad.com ].
Patient demographics, laboratory results, clinical effects, treatments and outcomes are all documented as part of ASP onto our case report forms that are faxed by the treating doctor to the study coordinating centre where the data is entered into a relational database. Where possible, patient serum is collected pre and post antivenom administration, centrifuged, and stored at −80°C for venom concentration quantification.
Patients were included in this study if the snake was identified by an expert or if brown snake venom was detected in the serum. All cases recruited to ASP between January 2004 and January 2012 were reviewed if they were identified as possible brown snake bites or envenoming cases based on expert snake identification, positive snake venom detection kit (sVDK) for brown snake venom, or clinical suspicion. Cases of VICC positive for tiger snake or taipan venom on sVDK on bite site or urine, but found to be negative in the serum for either venom were then tested with formal venom-specific enzyme immunoassay (EIA) for brown snake, and included if positive. The sVDK was not used as an inclusion criterion in the absence of expert snake identification or brown snake venom detected with venom-specific enzyme immunoassay.
Cases were classified into envenomation syndromes: VICC (complete or partial), myotoxicity, thrombotic microangiopathy and systemic symptoms, as previously described. [17] (link) Complete VICC is defined as undetectable fibrinogen and/or raised D-Dimer (at least 10 times the assay cut-off or >2.5 mg/L) and an international normalised ratio (INR) >3. Partial VICC is defined as low but detectable fibrinogen, elevated D-Dimer and a maximum INR <3. Other defined clinical effects were haemorrhage (type of haemorrhage; major haemorrhage was defined as an intracranial haemorrhage, large gastrointestinal haemorrhage with a drop in haemoglobin or any other life-threatening haemorrhage), early hypotensive collapse, cardiac arrest, seizure, electrocardiogram (ECG) changes and troponin concentrations. Treatment, complications and adverse events were analysed, including systemic hypersensitivity reactions to antivenom, which were defined as anaphylaxis if they met NIAID/FAAN consensus criteria for this diagnosis, [18] (link) and defined as severe according to the grading system developed by Brown. [19] (link).
Bite locations were converted into latitude and longitude coordinates using
All antivenom used in the study was equine F(ab’)2 and was manufactured by CSL Ltd. The dose of antivenom is defined as the amount administered before the first available post-antivenom blood sample for venom-specific enzyme immunoassay. Polyvalent antivenom contains on average the equivalent of eight vials of brown snake antivenom, based on a study of CSL terrestrial snake antivenoms. [21] (link) In patients given polyvalent antivenom the dose was converted to the equivalent number of brown snake antivenom vials using this 8 to 1 conversion. The total dose was also calculated for each patient receiving further antivenom.
Methods for the enzyme immunoassay have previously been described. [10] (link) Polyclonal antibodies (IgG) to brown snake venom raised in rabbits are used, with detection by biotinylated antibodies and streptavidin horseradish peroxidase. The limit of detection for brown snake venom was 0.15 ng/ml. The peak pre-antivenom venom concentration is reported where available. An enzyme immunoassay using labelled anti-Horse IgG was also used to detect antivenom in patient serum to confirm antivenom administration.
Medians, interquartile ranges (IQR) and ranges are used to report continuous data, and proportions were reported with 95% confidence intervals (CIs). For the enzyme immunoassay standard curves were fitted by linear and non-linear regression using both Excel and Prism 5.03 for Windows [GraphPad Software, San Diego California USA,
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We sequenced libraries on multiple Illumina platforms in multiple core labs. We used the Illumina NextSeq 500 platform to generate PE75 data for the Rhodnius, Gambusia, Kinosternidae, and Wisteria projects and Illumina HiSeq 2500 or NextSeq 500 platforms to generate PE150 data for the Ixodidae, Sphyrna, and Eurycea projects. We planned all sequencing runs to produce approximately one million reads per sample, which facilitates comparison of the 3RAD results among species with varying genome sizes, with the exception of the Ixodidae project, where four million reads were targeted per sample.
We assembled data from each project independently using Stacks v1.42 (Catchen et al., 2013 (link); Catchen et al., 2011 (link); seeFile S6 ). For the Wisteria project, we used molecular ID tags to facilitate PCR duplicate removal with the module clone_filter in Stacks (Catchen et al., 2013 (link); Hoffberg et al., 2016 (link)). We describe detailed parameters and software specifications for each project in File S6 . Briefly, for most projects, we used the process_radtags program to demultiplex and/or clean and trim the sequence data. We parallel-merged the mates of paired-end reads. We used the denovo_map program to assemble reads de novo and to calculate coverage, number of loci, and number of SNPs recovered for each project; we compared these data to genome size and sequencing read length (PE75 or PE150). Finally, we used the populations program to export loci shared in at least in 60–75% of localities and individuals to VCF files. Because there exists a reference genome for Gambusia affinis (Hoffberg et al., 2018 (link); NCBI: NHOQ01000000 ; details in File S6 ), we also assembled data from this project against the reference. For population-level datasets, we calculated F-statistics and performed preliminary population clustering analyses in Structure v2.3.4 (Pritchard, Stephens & Donelly, 2000 (link); File S6 ). For the Kinosternidae project, we conducted a de novo locus assembly using pyRAD v1.0.4 (Eaton, 2014 (link); details in File S6 ).
Finally, we estimated the prevalence and impact of loci with third restriction enzyme cut-sites in our data. We estimated the proportion of these third restriction enzyme cut-sites relative to the first restriction enzyme cut-site (i.e., intended cut-site) for five of the projects, and we evaluated variation among adapters and projects using ANOVA in R v3.5.1 (R Core Team, 2018 ). To evaluate the effect of these loci in downstream analyses, we reanalyzed data from three of our projects (i.e., both Sphyrna and Amblyomma americanum) after removing third restriction enzyme loci from the datasets. To do this, we reassembled data in Stacks v1.44 (Catchen et al., 2011 (link); Catchen et al., 2013 (link)) using process_radtags two independent times: first, “rescuing barcodes”, cleaning, and trimming the raw sequence data as before, but disabling rad check (–disable_rad_check) to leave the cut-sites intact; and second, using the previous step’s output as input, checking only for exact, intended restriction enzyme cut-sites (i.e., XbaI and EcoRI). From this output, we assembled and analyzed data similar to above, as detailed inFile S6 .
We assembled data from each project independently using Stacks v1.42 (Catchen et al., 2013 (link); Catchen et al., 2011 (link); see
Finally, we estimated the prevalence and impact of loci with third restriction enzyme cut-sites in our data. We estimated the proportion of these third restriction enzyme cut-sites relative to the first restriction enzyme cut-site (i.e., intended cut-site) for five of the projects, and we evaluated variation among adapters and projects using ANOVA in R v3.5.1 (R Core Team, 2018 ). To evaluate the effect of these loci in downstream analyses, we reanalyzed data from three of our projects (i.e., both Sphyrna and Amblyomma americanum) after removing third restriction enzyme loci from the datasets. To do this, we reassembled data in Stacks v1.44 (Catchen et al., 2011 (link); Catchen et al., 2013 (link)) using process_radtags two independent times: first, “rescuing barcodes”, cleaning, and trimming the raw sequence data as before, but disabling rad check (–disable_rad_check) to leave the cut-sites intact; and second, using the previous step’s output as input, checking only for exact, intended restriction enzyme cut-sites (i.e., XbaI and EcoRI). From this output, we assembled and analyzed data similar to above, as detailed in
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Amblyomma americanum
Clone Cells
Deoxyribonuclease EcoRI
DNA Restriction Enzymes
Gambusia
Genome
Ixodidae
Mosquito Fish
neuro-oncological ventral antigen 2, human
Rhodnius
Single Nucleotide Polymorphism
Wisteria
Most recents protocols related to «Affinis»
A randomized complete block design consisting of five replications of four treatments was deployed on June 15 in an untreated rice field at the Rice Experiment Station in Biggs, CA, USA. Treatments consisted of mosquito fish (Gambusia affinis), a combination of predatory beetles (three adult Laccophilus maculosus Say and two adults Tropisternus lateralis (Fabricius)), an untreated control, and the industry-standard pesticide (lambda-cyhalothrin) at a rate of 75.7 mL per ring. Gambusia utilized in this study were laboratory-reared to adulthood from stream populations and averaged roughly 4 cm (measured using calipers). Beetles were collected from light traps deployed at the Rice Experiment Station in Biggs, CA, USA, during spring months. Aluminum rings, 1 m 2 in area and 61 cm high, acted as experimental plots within the field in accordance with previous rice invertebrate research methods [35] (link)[36] (link)[37] (link). Aluminum rings are installed in dry rice fields prior to flooding using wooden stakes secured into the clay soil to hold their cylindrical shape. Clay soil is packed around the bottom of each aluminum ring to ensure study species are unable to immigrate or emigrate from each ring (Supplementary Material Figures S1-S3). The entire experiment occupied a 7 × 9 m grid in the field. Aluminum rings effectively captured TPS, preventing them from moving in or out of the ring. No TPS were added or removed from rings during the experiment; thus, this study embraces the full, natural spatial heterogeneity in TPS densities. Both L. maculosus and T. lateralis beetles are naturally occurring in rice fields throughout the season and are capable of flying in and out of aluminum rings. Five beetles were consistently observed in designated beetle treatment rings throughout the study, suggesting that none emigrated from the ring during our study. Rings were deployed in a research field that had a high-density population of TPS the previous season. Each ring was seeded with rice variety M206 at a commercial rate of 10.8 g/ring one day after flooding (DAF). Treatments were applied 2 DAF, with the exception of lambda-cyhalothrin, which was applied at a commercial rate (0.139 L/ha) prior to flooding. The number of surviving TPS per ring was recorded as 3, 5, 7, and 9 DAF.
La avispa agalladora Andricus quercuslaurinus Melika & Pujade-Villar presenta dos etapas en su ciclo de vida: la sexual que produce agallas en las hojas y la asexual que causa agallas en las ramas y generan la muerte descendente de su principal hospedante Quercus affinis Scheidw. (Melika et al., 2009) (link). Desde diciembre del 2005, este insecto cinípido es el responsable de la muerte de al menos 80 % de la población natural de Q. affinis en Acaxochitlán, Hidalgo, México (Barrera-Ruiz et al., 2016) (link). La Comisión Nacional Forestal (CONAFOR) realizó aspersiones aéreas del insecticida Spirotetramat en 2012 y 2015 para disminuir la población de la avispa en la generación sexual (Barrera-Ruiz et al., 2016) (link). De abril a noviembre de 2018 se atendieron 1 812.86 ha afectadas por la avispa agalladora, por lo que se declaró contingencia fitosanitaria y se establecieron medidas de control integral de A. quercuslaurinus (Sistema Integral de Vigilancia y Control Fitosanitario Forestal [SIVICOFF], 2018).
La dimensión de afectación se evalúa con claves descriptivas o escalas de calificación. Estas claves tienen escalas con niveles que se traducen a porcentaje y grados de resistencia y niveles cualitativos como leve, moderado y alto (Alfenas et al., 2009) . Pujade-Villar et al. (2018) indican que el control de la avispa, a largo plazo, puede lograrse con el manejo por resistencia o tolerancia al ataque. Al respecto, Velasco-González (2019) determinó que 14 % de la población de Q. affinis del rancho La Victoria, Acaxochitlán, Hidalgo, es tolerante a la plaga.
La propagación vegetativa contribuye a generar individuos resistentes al ataque, ya que estos conservan las características genotípicas del árbol donante (Hartmann et al., 2014) . Además, los injertos acortan el periodo para la producción de semilla y el establecimiento de huertos semilleros de Q. affinis resistente a la avispa agalladora (Kita et al., 2018; (link)Loewe-Muñoz et al., 2022) (link). El objetivo del presente trabajo fue establecer las condiciones necesarias para la propagación mediante injerto de individuos de Q. affinis tolerantes al ataque de A. quercuslaurinus.
La dimensión de afectación se evalúa con claves descriptivas o escalas de calificación. Estas claves tienen escalas con niveles que se traducen a porcentaje y grados de resistencia y niveles cualitativos como leve, moderado y alto (Alfenas et al., 2009) . Pujade-Villar et al. (2018) indican que el control de la avispa, a largo plazo, puede lograrse con el manejo por resistencia o tolerancia al ataque. Al respecto, Velasco-González (2019) determinó que 14 % de la población de Q. affinis del rancho La Victoria, Acaxochitlán, Hidalgo, es tolerante a la plaga.
La propagación vegetativa contribuye a generar individuos resistentes al ataque, ya que estos conservan las características genotípicas del árbol donante (Hartmann et al., 2014) . Además, los injertos acortan el periodo para la producción de semilla y el establecimiento de huertos semilleros de Q. affinis resistente a la avispa agalladora (Kita et al., 2018; (link)Loewe-Muñoz et al., 2022) (link). El objetivo del presente trabajo fue establecer las condiciones necesarias para la propagación mediante injerto de individuos de Q. affinis tolerantes al ataque de A. quercuslaurinus.
En los primeros cuatro experimentos se usaron plantas de Q. affinis de ocho meses como portainjerto y en el quinto experimento se utilizaron patrones de Q. rugosa y Q. affinis (Cuadro 1). La semilla con la que se produjeron los portainjertos de Q. affinis se obtuvo en el vivero GUMAIR en la región de Acaxochitlán, Hidalgo.
El trasplante se hizo a los seis meses en bolsas de 4 L con sustrato a base de 60 % de enlame de encino y 40 % de corteza de pino composteada. Al momento del injertado, los portainjertos midieron 50 cm de altura y 1.5 cm de diámetro promedio. Los patrones de Q. rugosa tenían dos años, 50 cm de altura y 2 cm de diámetro promedio, y se encontraban en bolsas de polietileno negro de 2 L con una mezcla de sustrato de enlame de encino y composta en proporción 3:1. La planta se produjo en el vivero Finca M Y M SPR de RL en Zacatlán, Puebla, ubicada en 19° 59' 48.43" N y 97° 59' 26.56" O.
A cada portainjerto se le aplicó fertilizante de liberación lenta Yara® (DAP) 18-46-00 (N-P-K) más micronutrientes
El trasplante se hizo a los seis meses en bolsas de 4 L con sustrato a base de 60 % de enlame de encino y 40 % de corteza de pino composteada. Al momento del injertado, los portainjertos midieron 50 cm de altura y 1.5 cm de diámetro promedio. Los patrones de Q. rugosa tenían dos años, 50 cm de altura y 2 cm de diámetro promedio, y se encontraban en bolsas de polietileno negro de 2 L con una mezcla de sustrato de enlame de encino y composta en proporción 3:1. La planta se produjo en el vivero Finca M Y M SPR de RL en Zacatlán, Puebla, ubicada en 19° 59' 48.43" N y 97° 59' 26.56" O.
A cada portainjerto se le aplicó fertilizante de liberación lenta Yara® (DAP) 18-46-00 (N-P-K) más micronutrientes
Fresh samples of white shrimp (Metapenaeus affinis ) were procured from three distinct local markets and subsequently packed in plastic bags. The samples were then stored at a temperature of 4°C until utilized for further analysis. Local individuals proficient in shrimp identification were responsible for verifying the authenticity of the samples.
In the first four experiments, eight-month-old Q. affinis plants were used as rootstock and in the fifth experiment, Q. rugosa and Q. affinis rootstocks (Table 1).
The seed used to produce Q. affinis rootstocks was obtained from the GUMAIR nursery in the region of Acaxochitlán, Hidalgo. Transplanting was done after six months in 4 L bags with a substrate based on 60 % of oak bark and 40 % of composted pine bark. At the time of grafting, the rootstocks measured 50 cm in height and 1.5 cm in average diameter. The Q. rugosa rootstocks were two years old, 50 cm in height and 2 cm in average diameter and were in 2 L black polyethylene bags with a substrate mixture of oak bark and compost in a 3:1 ratio. The plant was produced at the Finca M Y M SPR de RL nursery in Zacatlán, Puebla, located at 19° 59' 48.43" N and 97° 59' 26. 56" W.
Yara® (DAP) 18-46-00 (N-P-K) slow-release fertilizer plus micronutrients (1 g•L -1 ) and Trichoderma harzianum strain ISF13 (2.5 x 10 4 conidia•mL -1 ) dissolved in water were applied to each rootstock. Subsequently, lateral branches were removed from the rootstocks and the apical shoot was left. Quaternary ammonium salts were applied as a disinfectant in the area where the cutting was performed.
injertos se hicieron con varetas herbáceas, semileñosas y leñosas de fenotipos tolerantes y susceptibles. La cantidad de injertos por árbol donante varió debido a que muchas púas eran delgadas y de yemas pequeñas; es decir, sin vigor y, además, lignificadas. Las varetas seleccionadas tenían vigor alto, consistencia semileñosa, entrenudos cortos y yemas grandes en el final de su latencia. En los árboles tolerantes y susceptibles se realizaron la misma cantidad de injertos.
Tres experimentos se realizaron en 2020 (verano: 8 de septiembre, 8 de octubre y 10 de noviembre) y dos en 2021 (invierno [4 de marzo] y otoño [28 de septiembre]).
The seed used to produce Q. affinis rootstocks was obtained from the GUMAIR nursery in the region of Acaxochitlán, Hidalgo. Transplanting was done after six months in 4 L bags with a substrate based on 60 % of oak bark and 40 % of composted pine bark. At the time of grafting, the rootstocks measured 50 cm in height and 1.5 cm in average diameter. The Q. rugosa rootstocks were two years old, 50 cm in height and 2 cm in average diameter and were in 2 L black polyethylene bags with a substrate mixture of oak bark and compost in a 3:1 ratio. The plant was produced at the Finca M Y M SPR de RL nursery in Zacatlán, Puebla, located at 19° 59' 48.43" N and 97° 59' 26. 56" W.
Yara® (DAP) 18-46-00 (N-P-K) slow-release fertilizer plus micronutrients (1 g•L -1 ) and Trichoderma harzianum strain ISF13 (2.5 x 10 4 conidia•mL -1 ) dissolved in water were applied to each rootstock. Subsequently, lateral branches were removed from the rootstocks and the apical shoot was left. Quaternary ammonium salts were applied as a disinfectant in the area where the cutting was performed.
injertos se hicieron con varetas herbáceas, semileñosas y leñosas de fenotipos tolerantes y susceptibles. La cantidad de injertos por árbol donante varió debido a que muchas púas eran delgadas y de yemas pequeñas; es decir, sin vigor y, además, lignificadas. Las varetas seleccionadas tenían vigor alto, consistencia semileñosa, entrenudos cortos y yemas grandes en el final de su latencia. En los árboles tolerantes y susceptibles se realizaron la misma cantidad de injertos.
Tres experimentos se realizaron en 2020 (verano: 8 de septiembre, 8 de octubre y 10 de noviembre) y dos en 2021 (invierno [4 de marzo] y otoño [28 de septiembre]).
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More about "Affinis"
Affinis, PubCompare.ai's cutting-edge AI platform, empowers researchers to optimize their scientific workflows and enhance the reproducibility of their findings.
This innovative solution streamlines the process of locating and comparing research protocols from various sources, including literature, preprints, and patents.
Utilizing advanced AI algorithms, Affinis enables users to easily identify the most suitable protocols and products for their specific research needs.
By drawing insights from a vast repository of scientific information, the platform helps researchers make informed decisions and elevate their scientific discoveries.
Affinis seamlessly integrates with commonly used tools and reagents, such as TRIzol reagent for RNA extraction, GraphPad Prism 7 for data analysis, and Silamat S5 shaker for sample preparation.
Additionally, it supports the use of NextSeq 550 for high-throughput sequencing, Maestro 11.5 for imaging analysis, and Apoptosis in situ detection kits for studying cell death processes.
The platform's powerful features also encompass the integration of Hyaluronic acid, a versatile biomaterial with numerous applications in tissue engineering and regenerative medicine.
Affinis provides researchers with the ability to navigate this extensive landscape of scientific tools and resources, empowering them to make data-driven decisions and streamline their research workflows.
By leveraging the insights gained from Affinis, researchers can optimize their experimental protocols, enhance the reproducibility of their findings, and ultimately accelerate the pace of scientific discovery.
The platform's user-friendly interface and intuitive design make it accessible to researchers of all levels, fostering collaboration and knowledge-sharing within the scientific community.
Embracing the power of Affinis, researchers can expect to experience a seamless and efficient research process, leading to more impactful and groundbreaking scientific advancements.
This innovative solution streamlines the process of locating and comparing research protocols from various sources, including literature, preprints, and patents.
Utilizing advanced AI algorithms, Affinis enables users to easily identify the most suitable protocols and products for their specific research needs.
By drawing insights from a vast repository of scientific information, the platform helps researchers make informed decisions and elevate their scientific discoveries.
Affinis seamlessly integrates with commonly used tools and reagents, such as TRIzol reagent for RNA extraction, GraphPad Prism 7 for data analysis, and Silamat S5 shaker for sample preparation.
Additionally, it supports the use of NextSeq 550 for high-throughput sequencing, Maestro 11.5 for imaging analysis, and Apoptosis in situ detection kits for studying cell death processes.
The platform's powerful features also encompass the integration of Hyaluronic acid, a versatile biomaterial with numerous applications in tissue engineering and regenerative medicine.
Affinis provides researchers with the ability to navigate this extensive landscape of scientific tools and resources, empowering them to make data-driven decisions and streamline their research workflows.
By leveraging the insights gained from Affinis, researchers can optimize their experimental protocols, enhance the reproducibility of their findings, and ultimately accelerate the pace of scientific discovery.
The platform's user-friendly interface and intuitive design make it accessible to researchers of all levels, fostering collaboration and knowledge-sharing within the scientific community.
Embracing the power of Affinis, researchers can expect to experience a seamless and efficient research process, leading to more impactful and groundbreaking scientific advancements.