This work was funded by Genome BC, Genome Canada, and Coastal Genomics. The authors thank Kirby Cronin and Michael Chan for their help in sample collection and processing. We also would like to acknowledge Thea Van Rossum and Dr. Fiona Brinkman for bioinformatics assistance.

1. Raccolta Acqua e Filtrazione <ol><li> Raccogliere campioni di acqua dolce provenienti da vari siti (Figura 1). Passare campioni attraverso una serie di filtri: 1 micron filtro, filtro 0,2 micron, e 30 kDa taglio del filtro a flusso tangenziale sistematicamente eucariotica separata, particelle di dimensioni batteriche e virali, rispettivamente. Nota: Solo la purificazione e analisi del materiale recuperato sui 0,2 micron filtri (batteri a vita libera) è descritta in questa relazione, ma approcci simili possono essere utilizzati per le altre particelle recuperate dai filtri. </li></ol> 2. Concentrazione batterica, estrazione e purificazione del DNA <ol><li> Rimuovere il filtro a membrana 0,2 micron (s) dal sistema di filtrazione dell&#39;acqua (diagramma schematico, Figura 2). Piegare il filtro 0,2 micron disco a metà e posizionarlo in un tubo da 50 ml con il lato aperto in alto. Aggiungere 5 ml di soluzione tampone fosfato 1x (PBS) e 0,01% Tween, pH 7.4 inil tubo. Se più di un filtro viene utilizzato durante il processo di impiegare un tubo diverso per filtro. Tubo negozio (s) con filtro a 4 ° C fino elaborato. In caso contrario, passare al punto 2.2. </li><li> Rimuovere il filtro 0,2 micron membrana dal tubo 50 ml con una pinza sterile. Filtro Place (s) su una piastra di Petri (lasciare il tampone PBS nel tubo). <ol><li> Con pinze sterili e forbici sterili, tagliate il filtro in piccole strisce (1 cm x 1 cm). Disinfettare pinze e forbici immergendo nel 70% isopropanolo, asciugandosi con un DNA di superficie decontaminante e risciacquo con acqua ultrapura di tipo 1 tra i diversi campioni. </li></ol></li><li> Posizionare il filtro tagliato a striscioline di nuovo nello stesso tubo da 50 ml. Aggiungere 10 ml di PBS 1x e 0,01% Tween, pH 7.4 al filtro quindi c&#39;è un totale di 15 ml di tampone nella provetta 50 ml. </li><li> Aggiungere 6 perle di tungsteno pulite (3 mm di diametro) in ciascun tubo 50 ml, coprire il tubo con Parafilm, e vortex energicamente per 20 minuti (utilizzare 50 ml tubi adattatore vortex). Se multiple filtri vengono elaborati da un campione, trasferimento e piscina tutto l&#39;omogeneizzato in una provetta pulita 50 ml. Centrifugare le provette a 3.300 xg per 15 min a 4 ° C. </li><li> Risospendere il pellet e aliquote cellule batteriche (~ 1 ml Aliquote) in 1,7 ml microprovette. Si noti che ci saranno 5 provette da microcentrifuga per campione. </li><li> Centrifugare le provette da microcentrifuga a 10.000 xg per 10 min, e rimuovere la maggior parte del surnatante fino a ~ 200 microlitri mark. </li><li> Conservare i campioni a -80 ° C, o procedi per estrarre DNA batterico utilizzando un kit di isolamento di DNA disponibile in commercio come da istruzioni del produttore. Durante l&#39;uso batterica estrazione del DNA sia PBS o acqua come controllo di estrazione negativo e E. coli come controllo di estrazione positivo. </li><li> Poiché DNA da più tubi vengono estratti, piscina sub-aliquote parallele dello stesso campione in una provetta 2 ml. Poi condurre / N precipitazione O utilizzando una soluzione composta da 0,1volumi di 3 M acetato di sodio, 2 volumi di etanolo al 100%, e 5 ml di 5 mg / mL acrilammide lineare. Mescolare bene e conservare i campioni a -80 ° C. </li><li> Centrifugare alla massima velocità (17.000 xg) per 30 minuti a 4 ° C. Lavare pellet con 1 ml di ghiacciata etanolo al 70%, aria secca in un armadio biosicurezza per non più di 5 min e risospendere pellet di DNA in 34 ml di 10 mM Tris-Cl, pH 8,5. Nota: acrilamide lineare aiuterà a visualizzare pellet di DNA dopo la O / N precipitazione. </li><li> Determinare la quantità di DNA e di qualità utilizzando una sensibilità elevata fluorescenza nucleico test acido quantificazione e uno spettrofotometro microvolumi, rispettivamente, seguendo le istruzioni del fabbricante (vedi tabella dei Materiali). Nota: Se più campioni vengono preparati al momento, una fluorescenza test acido nucleico ultrasensibile per quantificare dsDNA e basata su piastra fluorimetro / spettrofotometro può essere usato al posto. </li></ol> 3. DNA Biblioteca Preparazione <ol><li&gt; Normalizza DNA batterico genomico estratto da campioni di acqua ad una concentrazione di ~ 0,2 ng / ml. </li><li> Enzimaticamente frammento uno nanogrammi di DNA batterico utilizzando un metodo basato trasposone-(tagmentation). Aggiungere adattatore e index sequenze sul DNA frammentato seguendo le istruzioni del produttore. Soggetto tagmented campioni a 12 cicli di PCR, come indicato nelle istruzioni del produttore, a quel punto gli indici di sequenziamento sono incorporati. </li></ol> 4. Automated Gel Selezione Size <ol><li> Salta standard di post-PCR clean-up step descritto nelle istruzioni del produttore (Vedi Tabella dei Materiali). Formato selezionare campioni post-PCR direttamente utilizzando una piattaforma automatizzata di selezione del formato a base di gel. <ol><li> Aggiungere 3,5 ml di tampone di caricamento per ogni campione. </li><li> Dopo il protocollo del produttore, caricare i campioni alla workstation elettroforesi, specificando un target formato-selezione di 500-800 bp, in un estratto di 300 mlvolume di ioni, con un 1,5% di agarosio cassette pre-cast. </li><li> Concentrare il materiale in uscita prima (300 ml), fino a 25 ml di etanolo tramite precipitazione. Nota: In alternativa, utilizzare la workstation elettroforesi per automatizzare la concentrazione per un maggior numero di campioni tramite piastra di filtraggio e del collettore di aspirazione. <ol><li> Precipitare il volume di eluizione grezzo utilizzando 0,1 volumi di 3 M acetato di sodio, 2 volumi di etanolo 100% e 5 ml di 5 mg / mL acrilammide lineare. Mescolare bene, posto i campioni a -80 ° CO / N. Centrifugare i campioni a 17.000 xg per 30 min. </li><li> Eliminare surnatanti e procedere a lavare pellet di DNA con 1 ml di ghiacciata etanolo al 70%. </li><li> Centrifugare i campioni di nuovo a 17.000 xg per 30 min, scartano surnatanti, aria secca, e infine risospendere pellet di DNA in 25 ml di 10 mM Tris-Cl, pH 8,5. </li></ol></li></ol></li><li> (Opzionale) Utilizzare 1 ml di dimensioni librerie DNA selezionato con la piattaforma di selezione formato gel automatico per fare un cinquediluizione -fold con soluzione tampone Tris-EDTA, pH 8.0. Analizzare le librerie con uno strumento elettroforesi capillare basato su chip per analizzare dsDNA qualità secondo le istruzioni del produttore. </li></ol> 5. Biblioteca Normalizzazione e Sequencing <ol><li> Procedere per normalizzare i campioni utilizzando perline di normalizzazione della biblioteca (inclusi nel kit di preparazione biblioteca basato transposon-) come descritto nella guida di preparazione del produttore. <ol><li> In alternativa, misura librerie dsDNA usando un&#39;alta sensibilità fluorescente nucleico dosaggio acido quantificazione, seguita riunendo a rapporti equimolari per raggiungere una concentrazione finale di dsDNA 2 nM. Procedere a denaturare librerie utilizzando 10 ml di biblioteche in pool e 10 ml di 0,2 N NaOH, incubare per 5 minuti a temperatura ambiente. Diluire librerie denaturati mediante tampone di ibridazione (incluso con il kit di preparazione a base transposon-) per un volume finale di 1 ml e la concentrazione di 11:05. </li></ol></li><li> Caricare il campiones in una piattaforma di sequenziamento di nuova generazione seguendo i protocolli standard di sequenziamento del produttore. </li></ol>

<ol>
	<li>Siuda, W., Chrost, R. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Concentration+and+susceptibility+of+dissolved+DNA+for+enzyme+degradation+in+lake+water+-+some+methodological+remarks.">Concentration and susceptibility of dissolved DNA for enzyme degradation in lake water - some methodological remarks.</a> Aquatic Microbial Ecology. 21, 195-201 (2000).</li><li>Ficetola, G. F., Miaud, C., Pompanon, F., Taberlet, P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Species+detection+using+environmental+DNA+from+water+samples.">Species detection using environmental DNA from water samples.</a> Biology letters. 4, 423-425 (2008).</li><li>Liles, M. R., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Recovery,+purification,+and+cloning+of+high-molecular-weight+DNA+from+soil+microorganisms.">Recovery, purification, and cloning of high-molecular-weight DNA from soil microorganisms.</a> Applied and environmental microbiology. 74, 3302-3305 (2008).</li><li>Bey, B. S., Fichot, E. B., Dayama, G., Decho, A. W., Norman, R. S. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Extraction+of+high+molecular+weight+DNA+from+microbial+mats.">Extraction of high molecular weight DNA from microbial mats.</a> BioTechniques. 49, 631-640 (2010).</li><li>Tebbe, C. C., Vahjen, W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Interference+of+humic+acids+and+DNA+extracted+directly+from+soil+in+detection+and+transformation+of+recombinant+DNA+from+bacteria+and+a+yeast.">Interference of humic acids and DNA extracted directly from soil in detection and transformation of recombinant DNA from bacteria and a yeast.</a> Applied and environmental microbiology. 59, 2657-2665 (1993).</li><li>Solonenko, S. A., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Sequencing+platform+and+library+preparation+choices+impact+viral+metagenomes.">Sequencing platform and library preparation choices impact viral metagenomes.</a> BMC genomics. 14, 320 (2013).</li><li>Aird, D., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Analyzing+and+minimizing+PCR+amplification+bias+in+Illumina+sequencing+libraries.">Analyzing and minimizing PCR amplification bias in Illumina sequencing libraries.</a> Genome biology. 12, R18 (2011).</li><li>Quail, M. A., Swerdlow, H., Turner, D. J., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Improved+protocols+for+the+illumina+genome+analyzer+sequencing+system.">Improved protocols for the illumina genome analyzer sequencing system.</a> Current protocols in human genetics / editorial board, Jonathan L. Haines .. [et al.]. 18, 18 (2009).</li><li>Head, S. R., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Library+construction+for+next-generation+sequencing:+overviews+and+challenges.">Library construction for next-generation sequencing: overviews and challenges.</a> BioTechniques. 56, 61-64, 66, 68 (2014).</li><li>Dijk, E. L., Jaszczyszyn, Y., Thermes, C. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Library+preparation+methods+for+next-generation+sequencing:+tone+down+the+bias.">Library preparation methods for next-generation sequencing: tone down the bias.</a> Experimental cell research. 322, 12-20 (2014).</li><li>Grunenwald, H., Baas, B., Caruccio, N., Syed, F. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Rapid,+high-throughput+library+preparation+for+next-generation+sequencing.">Rapid, high-throughput library preparation for next-generation sequencing.</a> Nature Methods. 7, (2010).</li><li>Sambrook, J., Russell, D. W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Molecular cloning : a laboratory manual. , (2001).</li><li>Lee, P. Y., Costumbrado, J., Hsu, C. Y., Kim, Y. H. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Agarose+gel+electrophoresis+for+the+separation+of+DNA+fragments.">Agarose gel electrophoresis for the separation of DNA fragments.</a> Journal of visualized experiments. , (2012).</li><li>Quail, M. A., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+large+genome+center's+improvements+to+the+Illumina+sequencing+system.">A large genome center's improvements to the Illumina sequencing system.</a> Nature methods. 5, 1005-1010 (2008).</li><li>Marine, R., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Evaluation+of+a+transposase+protocol+for+rapid+generation+of+shotgun+high-throughput+sequencing+libraries+from+nanogram+quantities+of+DNA.">Evaluation of a transposase protocol for rapid generation of shotgun high-throughput sequencing libraries from nanogram quantities of DNA.</a> Applied and environmental microbiology. 77, 8071-8079 (2011).</li><li>Rohland, N., Reich, D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Cost-effective+high-throughput+DNA+sequencing+libraries+for+multiplexed+target+capture.">Cost-effective high-throughput DNA sequencing libraries for multiplexed target capture.</a> Genome research. 22, 939-946 (2012).</li><li>Lamble, S., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Improved+workflows+for+high+throughput+library+preparation+using+the+transposome-based+nextera+system.">Improved workflows for high throughput library preparation using the transposome-based nextera system.</a> Bmc Biotechnology. 13, (2013).</li><li>Picelli, S., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Tn5+transposase+and+tagmentation+procedures+for+massively+scaled+sequencing+projects.">Tn5 transposase and tagmentation procedures for massively scaled sequencing projects.</a> Genome research. , (2014).</li><li>Rhodes, J., Beale, M. A., Fisher, M. C. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Illuminating+Choices+for+Library+Prep:+A+Comparison+of+Library+Preparation+Methods+for+Whole+Genome+Sequencing+of+Cryptococcus+neoformans+Using+Illumina+HiSeq.">Illuminating Choices for Library Prep: A Comparison of Library Preparation Methods for Whole Genome Sequencing of Cryptococcus neoformans Using Illumina HiSeq.</a> PloS One. 9, e113501 (2014).</li></ol>

Jared R. Slobodan e Matthew J. Nesbitt entrambi titolari di azioni di Coastal Genomics, una società di proprietà privata British Columbia offre la tecnologia Ranger.

La presenza di dimeri adattatori e raggruppamento di piccole dimensioni inserto preferenzialmente essere sequenziati in piattaforme attuali rappresentano una diminuzione delle rese utilizzabili e sotto-utilizzo della capacità di 15 dell&#39;apparecchiatura. L&#39;uso di metodi branello battitori combinati con un approccio basato trasposone-per preparare librerie può comportare più di taglio DNA rispetto ad altri metodi di estrazione 4,5. Tuttavia, tutti i metodi di estrazione e biblioteca prepar...

Metagenomics involves the sequencing of all the genetic material in a sample to characterize the microbial communities present. It is a complex and expensive process which involves the conversion of extracted nucleic acids into DNA libraries followed by next-generation sequencing. High quality libraries are essential for maximal data output and accurate metagenomics analysis. Environmental samples, such as water samples, often pose significant challenges to generating high quality libraries, due to low amounts of DNA that may also be degraded1-3 and the presence of inhibitors of PCR4-6. 
High quality libraries ideally consist of longer segments of DNA within a narrow range of lengths. In order to maximize the amount of useful data generated per sequencing run, the length of the DNA in the library should be at least as long as the maximum read length of the sequencing method being used. When using a sequencing-by-synthesis technology such as the Illumina MiSeq, the size of the DNA fragments affects the efficiency at which clusters are generated on the flow cell. For instance, when a library contains both shorter and longer DNA fragments, the shorter ones will be over-represented in the sequencing data7,8. In contrast, a library with similarly sized DNA fragments will be proportionally represented in the sequencing data. Many library preparation kits use ligation-based methods to add adapters to the DNA fragments and size selection is necessary to remove adapter dimers that do not contain an insert9,10. There are numerous methods11,12 to achieve this but the one technique that gives the most consistent results is the electrophoretic separation of DNA followed by the recovery of the desired lengths of DNA13,14. This process can be performed manually for a small number of samples, but when faced with processing hundreds of samples, automated solutions are required. The currently available platforms for automated gel size selection are low throughput and new platforms are needed to process large numbers of samples for sequencing. The Ranger Technology can be integrated with existing liquid handling workstations to enable the use of agarose gel electrophoresis for size selection and analytical purposes on a scale that satisfies today&#8217;s high throughput environment.

<table border="0" cellpadding="0" cellspacing="0">
	<tbody>
		<tr>
			<td>Peristaltic pump Masterflex P/S 1400 Series</td>
			<td>Thermo Scientific&#160;</td>
			<td>1400-1620</td>
			<td></td>
		</tr>
		<tr>
			<td>0.2 &#181;m Supor Membrane</td>
			<td>VWR</td>
			<td>CA28143-969</td>
			<td>Pall Corporation, Ann Harbor, MI</td>
		</tr>
		<tr>
			<td>Tungsten carbide beads 3 mm (200)</td>
			<td>Qiagen</td>
			<td>69997</td>
			<td></td>
		</tr>
		<tr>
			<td>Isopropyl alcohol 70%</td>
			<td>Jedmon Products</td>
			<td>825751</td>
			<td>Healthcare Plus</td>
		</tr>
		<tr>
			<td>DNA away</td>
			<td>VWR</td>
			<td>7010</td>
			<td>Molecular BioProducts, Inc. San Diego, CA</td>
		</tr>
		<tr>
			<td>Milli-Q water purification system</td>
			<td>Fisher Scientific</td>
			<td>ZMQS6VF0Y</td>
			<td>Merck Millipore. This system has been discontinued.</td>
		</tr>
		<tr>
			<td>20 X PBS pH 7.5</td>
			<td>VWR</td>
			<td>E703-1L</td>
			<td>Amresco, Inc., Solon, OH</td>
		</tr>
		<tr>
			<td>Tween 20</td>
			<td>Fisher Scientific</td>
			<td>BP337-100</td>
			<td>Fisher chemicals</td>
		</tr>
		<tr>
			<td>Vortex adapter for 2 (50 ml) tubes</td>
			<td>VWR</td>
			<td>13000-V1-50</td>
			<td>MoBio, Carlsbad, CA</td>
		</tr>
		<tr>
			<td>Vortex-Genie 2, 120V (Model G560)</td>
			<td>VWR</td>
			<td>SI-0236</td>
			<td>Scientific Industries, Inc.</td>
		</tr>
		<tr>
			<td>Beckman Centrifuge</td>
			<td>Raeyco Lab Equipment Systems Management Ltd</td>
			<td>Model J-6B</td>
			<td></td>
		</tr>
		<tr>
			<td>PowerLyzer Powersoil DNA isolation kit</td>
			<td>VWR</td>
			<td>12855-100</td>
			<td>MoBio, Carlsbad, CA</td>
		</tr>
		<tr>
			<td>Vortex adapter for 24 (1.5-2 ml) tubes</td>
			<td>VWR</td>
			<td>13000-V1-24</td>
			<td>MoBio, Carlsbad, CA</td>
		</tr>
		<tr>
			<td>Microfuge 18 centrifuge</td>
			<td>Beckman Coulter</td>
			<td>367160</td>
			<td></td>
		</tr>
		<tr>
			<td>Nimbus Select workstation with Ranger Technology</td>
			<td>Hamilton Robotics</td>
			<td>92720-01</td>
			<td>Includes the liquid handling workstation and integrated Ranger Tech (electrophoresis hardware)</td>
		</tr>
		<tr>
			<td>Ranger reagent kit</td>
			<td>Coastal Genomics</td>
			<td>CG-10600-150-12-21</td>
			<td>Includes loading buffer and cassettes</td>
		</tr>
		<tr>
			<td>Ethyl alcohol (anhydrous)</td>
			<td>Commercial Alcohols</td>
			<td>P016EAAN</td>
			<td>Greenfield Ethanol</td>
		</tr>
		<tr>
			<td>Sodium acetate</td>
			<td>Sigma-Aldrich</td>
			<td>S2889-250G</td>
			<td></td>
		</tr>
		<tr>
			<td>Linear acrylamide (5 mg/ml)</td>
			<td>Life Technologies</td>
			<td>AM9520</td>
			<td>Ambion</td>
		</tr>
		<tr>
			<td>Eppendorf refrigerated centrifuge</td>
			<td>Raeyco Lab Equipment Systems Management Ltd.</td>
			<td>5417R</td>
			<td></td>
		</tr>
		<tr>
			<td>Buffer EB (250 ml)</td>
			<td>Qiagen</td>
			<td>19086</td>
			<td></td>
		</tr>
		<tr>
			<td>NanoDrop 1000 Spectrophotometer</td>
			<td>Thermo Scientific</td>
			<td>ND-1000</td>
			<td></td>
		</tr>
		<tr>
			<td>Qubit fluorometer</td>
			<td>Life Technologies</td>
			<td>Q32857</td>
			<td>Invitrogen. This product has been discontinued.</td>
		</tr>
		<tr>
			<td>Qubit dsDNA HS assay kit</td>
			<td>Life Technologies</td>
			<td>Q32854</td>
			<td>Invitrogen</td>
		</tr>
		<tr>
			<td>High sensitivity DNA reagent</td>
			<td>Agilent Technologies</td>
			<td>5067-4626</td>
			<td></td>
		</tr>
		<tr>
			<td>High sensitivity DNA chips</td>
			<td>Agilent Technologies</td>
			<td>5067-4626</td>
			<td></td>
		</tr>
		<tr>
			<td>Agilent 2011 Bioanalyzer</td>
			<td>Agilent Technologies</td>
			<td>G2938B</td>
			<td></td>
		</tr>
		<tr>
			<td>Nextera XT DNA sample preparation kit</td>
			<td>Illumina</td>
			<td>FC-131-1024</td>
			<td></td>
		</tr>
		<tr>
			<td>Nextera XT index kit</td>
			<td>Illumina</td>
			<td>FC-131-1001</td>
			<td></td>
		</tr>
		<tr>
			<td>MiSeq reagent kit v2 (500-cycles)</td>
			<td>Illumina</td>
			<td>MS-102-2003</td>
			<td></td>
		</tr>
		<tr>
			<td>Miseq system</td>
			<td>Illumina</td>
			<td>SY-410-1003</td>
			<td></td>
		</tr>
	</tbody>
</table>

automated gel size selection to improve the quality of next-generation sequencing libraries prepared from environmental water samples

Next-generation sequencing of environmental samples can be challenging because of the variable DNA quantity and quality in these samples. High quality DNA libraries are needed for optimal results from next-generation sequencing. Environmental samples such as water may have low quality and quantities of DNA as well as contaminants that co-precipitate with DNA. The mechanical and enzymatic processes involved in extraction and library preparation may further damage the DNA. Gel size selection enables purification and recovery of DNA fragments of a defined size for sequencing applications. Nevertheless, this task is one of the most time-consuming steps in the DNA library preparation workflow. The protocol described here enables complete automation of agarose gel loading, electrophoretic analysis, and recovery of targeted DNA fragments. 
In this study, we describe a high-throughput approach to prepare high quality DNA libraries from freshwater samples that can be applied also to other environmental samples. We used an indirect approach to concentrate bacterial cells from environmental freshwater samples; DNA was extracted using a commercially available DNA extraction kit, and DNA libraries were prepared using a commercial transposon-based protocol. DNA fragments of 500 to 800 bp were gel size selected using Ranger Technology, an automated electrophoresis workstation. Sequencing of the size-selected DNA libraries demonstrated significant improvements to read length and quality of the sequencing reads.

Concentrazione DNA, e valutazione della qualità Concentrazioni DNA batterico variava ,01-0,11 ng ​​/ ml per campione dei vari siti di bacino (Tabella 1). DNA isolato da frazione batterica aveva A 260/280 e 260/230 A rapporti di 1,4-1,8 e 0,3-1,6 rispettivamente. Mentre alcuni dei coefficienti A 260/230 erano relativamente bassa, nessuna inibizione apparente è stata osservata nella biblioteca preparato e altre applicazio...

Watch this Scientific Journal Video about Automated Gel Size Selection to Improve the Quality of Next-generation Sequencing Libraries Prepared from Environmental Water Samples at JoVE.com

Automated Gel Size Selection to Improve the Quality of Next-generation Sequencing Libraries Prepared from Environmental Water Samples

This manuscript describes an automated gel size selection approach for purifying DNA fragments for next-generation sequencing. The Ranger Technology provides complete automation of the entire process of agarose gel loading, electrophoretic analysis, and recovery of targeted DNA fragments allowing for high-throughput and high quality next-generation sequencing libraries.

Automated Gel Selection Size per migliorare la qualità delle Biblioteche di sequenziamento di nuova generazione Preparato da campioni di acqua ambientale

Next-generation sequencing of environmental samples can be challenging because of the variable DNA quantity and quality in these samples. High quality DNA ...

automated-gel-size-selection-to-improve-quality-next-generation

Research

JoVE Journal

Environment

10.4K Views.  The University of British Columbia. This manuscript describes an automated gel size selection approach for purifying DNA fragments for next-generation sequencing. The Ranger Technology provides complete automation of the entire process of agarose gel loading, electrophoretic analysis, and recovery of targeted DNA fragments allowing for high-throughput and high quality next-generation sequencing libraries. 

Video: Automated Gel Size Selection to Improve the Quality of Next-generation Sequencing Libraries Prepared from Environmental Water Samples

EPA Method 1615. Measurement of Enterovirus and Norovirus Occurrence in Water by Culture and RT-qPCR. I. Collection of Virus Samples

EPA Method 1615 was developed with a goal of providing a standard method for measuring enteroviruses and noroviruses in environmental and drinking waters. The standardized sampling component of the method concentrates viruses that may be present in water by passage of a minimum specified volume of water through an electropositive cartridge filter. The minimum specified volumes for surface and finished/ground water are 300 L and 1,500 L, respectively. A major method limitation is the tendency for the filters to clog before meeting the sample volume requirement. Studies using two different, but equivalent, cartridge filter options showed that filter clogging was a problem with 10% of the samples with one of the filter types compared to 6% with the other filter type. Clogging tends to increase with turbidity, but cannot be predicted based on turbidity measurements only. From a cost standpoint one of the filter options is preferable over the other, but the water quality and experience with the water system to be sampled should be taken into consideration in making filter selections.

EPA Method 1615 uses an electropositive filter to concentrate enteroviruses and noroviruses in environmental and drinking waters. This manuscript describes the procedure for collecting samples for Method 1615 analyses.

Metodo EPA 1615. Misura di Enterovirus e Norovirus Evento in acqua per la cultura e RT-qPCR. I. Raccolta di campioni di virus

EPA Method 1615 was developed with a goal of providing a standard method for measuring enteroviruses and noroviruses in environmental and drinking waters. ...

Ricerca

Ambiente

Physical Isolation of Endospores from Environmental Samples by Targeted Lysis of Vegetative Cells

Endospore formation is a survival strategy found among some bacteria from the phylum Firmicutes. During endospore formation, these bacteria enter a morpho-physiological resting state that enhances survival under adverse environmental conditions. Even though endospore-forming Firmicutes are one of the most frequently enriched and isolated bacterial groups in culturing studies, they are often absent from diversity studies based on molecular methods. The resistance of the spore core is considered one of the factors limiting the recovery of DNA from endospores. We developed a method that takes advantage of the higher resistance of endospores to separate them from other cells in a complex microbial community using physical, enzymatic and chemical lysis methods. The endospore-only preparation thus obtained can be used for re-culturing or to perform downstream analysis such as tailored DNA extraction optimized for endospores and subsequent DNA sequencing. This method, applied to sediment samples, has allowed the enrichment of endospores and after sequencing, has revealed a large diversity of endospore-formers in freshwater lake sediments. We expect that the application of this method to other samples will yield a similar outcome.

A method to single out bacterial endospores from complex microbial communities was developed to perform tailored culture or molecular studies of this group of bacteria.

Isolamento fisico di Endospore da campioni ambientali da mirata Lisi di cellule vegetative

Endospore formation is a survival strategy found among some bacteria from the phylum Firmicutes. During endospore formation, these bacteria enter a ...

A Simple Method for Automated Solid Phase Extraction of Water Samples for Immunological Analysis of Small Pollutants

A new method for solid phase extraction (SPE) of environmental water samples is proposed. The developed prototype is cost-efficient and user friendly, and enables to perform rapid, automated and simple SPE. The pre-concentrated solution is compatible with analysis by immunoassay, with a low organic solvent content. A method is described for the extraction and pre-concentration of natural hormone 17&#946;-estradiol in 100 ml water samples. Reverse phase SPE is performed with octadecyl-silica sorbent and elution is done with 200 &#181;l of methanol 50% v/v. Eluent is diluted by adding di-water to lower the amount of methanol. After preparing manually the SPE column, the overall procedure is performed automatically within 1 hr. At the end of the process, estradiol concentration is measured by using a commercial enzyme-linked immune-sorbent assay (ELISA). 100-fold pre-concentration is achieved and the methanol content in only 10% v/v. Full recoveries of the molecule are achieved with 1 ng/L spiked de-ionized and synthetic sea water samples.

A protocol for the extraction and pre-concentration of estradiol from water samples by using an automated and miniaturized system is presented.

Un metodo semplice per Automated fase solida estrazione di campioni di acqua per l&#39;analisi immunologiche di piccole inquinanti

A new method for solid phase extraction (SPE) of environmental water samples is proposed. The developed prototype is cost-efficient and user friendly, and ...

Use of a Filter Cartridge for Filtration of Water Samples and Extraction of Environmental DNA

Recent studies demonstrated the use of environmental DNA (eDNA) from fishes to be appropriate as a non-invasive monitoring tool. Most of these studies employed disk fiber filters to collect eDNA from water samples, although a number of microbial studies in aquatic environments have employed filter cartridges, because the cartridge has the advantage of accommodating large water volumes and of overall ease of use. Here we provide a protocol for filtration of water samples using the filter cartridge and extraction of eDNA from the filter without having to cut open the housing. The main portions of this protocol consists of 1) filtration of water samples (water volumes &#8804;4 L or &gt;4 L); (2) extraction of DNA on the filter using a roller shaker placed in a preheated incubator; and (3) purification of DNA using a commercial kit. With the use of this and previously-used protocols, we perform metabarcoding analysis of eDNA taken from a huge aquarium tank (7,500 m3) with known species composition, and show the number of detected species per library from the two protocols as the representative results. This protocol has been developed for metabarcoding eDNA from fishes, but is also applicable to eDNA from other organisms.

We describe a protocol for filtration of water samples with a filter cartridge and extraction of environmental DNA (eDNA) without having to cut open the housing to remove the filter. This protocol is developed for metabarcoding eDNA from fishes, but is also applicable to eDNA from other organisms.

L&#39;utilizzo di una cartuccia filtrante per filtrazione di acqua campioni ed estrazione di DNA ambientale

Recent studies demonstrated the use of environmental DNA (eDNA) from fishes to be appropriate as a non-invasive monitoring tool. Most of these studies ...

Controlled-release of Chlorine Dioxide in a Perforated Packaging System to Extend the Storage Life and Improve the Safety of Grape Tomatoes

A controlled-release chlorine dioxide (ClO2) pouch was developed by sealing a slurry form of ClO2 into semipermeable polymer film; the release properties of the pouch were monitored in containers with or without fruit. The pouch was affixed to the inside of a perforated clamshell containing grape tomatoes, and the effect on microbial population, firmness, and weight loss was evaluated during a 14 day storage period at 20 &#176;C. Within 3 days, the ClO2 concentration in the clamshells reached 3.5 ppm and remained constant until day 10. Thereafter, it decreased to 2 ppm by day 14. The ClO2 pouch exhibited strong antimicrobial activity, reducing Escherichia coli populations by 3.08 log CFU/g and Alternaria alternata populations by 2.85 log CFU/g after 14 days of storage. The ClO2 treatment also reduced softening and weight loss and extended the overall shelf life of the tomatoes. Our results suggest that ClO2 treatment is useful for extending the shelf life and improving the microbial safety of tomatoes during storage without impairing their quality.

Here, we describe a protocol for the application of a novel, slow-release ClO2 product that reduces spoilage and extends the shelf life of fresh fruit. The slow-release ClO2 product was added to standard commercial grape tomato packaging and tested against Escherichia coli and Alternaria alternata.

A rilascio di biossido di cloro in un sistema di imballaggio forato per prolungare la durata di conservazione e migliorare la sicurezza dei Pomodori

A controlled-release chlorine dioxide (ClO2) pouch was developed by sealing a slurry form of ClO2 into semipermeable polymer film; the release properties ...

Extraction of Organochlorine Pesticides from Plastic Pellets and Plastic Type Analysis

Plastic resin pellets, categorized as microplastics (&#8804;5 mm in diameter), are small granules that can be unintentionally released to the environment during manufacturing and transport. Because of their environmental persistence, they are widely distributed in the oceans and on beaches all over the world. They can act as a vector of potentially toxic organic compounds (e.g., polychlorinated biphenyls) and might consequently negatively affect marine organisms. Their possible impacts along the food chain are not yet well understood. In order to assess the hazards associated with the occurrence of plastic pellets in the marine environment, it is necessary to develop methodologies that allow for rapid determination of associated organic contaminant levels. The present protocol describes the different steps required for sampling resin pellets, analyzing adsorbed organochlorine pesticides (OCPs) and identifying the plastic type. The focus is on the extraction of OCPs from plastic pellets by means of a pressurized fluid extractor (PFE) and on the polymer chemical analysis applying Fourier Transform-InfraRed (FT-IR) spectroscopy. The developed methodology focuses on 11 OCPs and related compounds, including dichlorodiphenyltrichloroethane (DDT) and its two main metabolites, lindane and two production isomers, as well as the two biologically active isomers of technical endosulfan. This protocol constitutes a simple and rapid alternative to existing methodology for evaluating the concentration of organic contaminants adsorbed on plastic pieces.

Microplastics act as vector of potentially toxic organic contaminants with unpredictable effects. This protocol describes an alternative methodology for assessing the levels of organochlorine pesticides adsorbed on plastic pellets and identifying the polymer chemical structure. The focus is on pressurized fluid extraction and attenuated total reflectance Fourier transform infrared spectroscopy.

Estrazione di pesticidi di organochlorato da pellicole di plastica e analisi di tipo plastico

Plastic resin pellets, categorized as microplastics (&#8804;5 mm in diameter), are small granules that can be unintentionally released to the environment ...

Experimental Column Setup for Studying Anaerobic Biogeochemical Interactions Between Iron (Oxy)Hydroxides, Trace Elements, and Bacteria

Fate and speciation of trace elements (TEs), such as arsenic (As) and mercury (Hg), in aquifers are closely related to physio-chemical conditions, such as redox potential (Eh) and pH, but also to microbial activities that can play a direct or indirect role on speciation and/or mobility. Indeed, some bacteria can directly oxidize As(III) to As(V) or reduce As(V) to As(III). Likewise, bacteria are strongly involved in Hg cycling, either through its methylation, forming the neurotoxin monomethyl mercury, or through its reduction to elemental Hg&#176;. The fates of both As and Hg are also strongly linked to soil or aquifer composition; indeed, As and Hg can bind to organic compounds or (oxy)hydroxides, which will influence their mobility. In turn, bacterial activities such as iron (oxy)hydroxide reduction or organic matter mineralization can indirectly influence As and Hg sequestration. The presence of sulfate/sulfide can also strongly impact these particular elements through the formation of complexes such as thio-arsenates with As or metacinnabar with Hg.
Consequently, many important questions have been raised on the fate and speciation of As and Hg in the environment and how to limit their toxicity. However, due to their reactivity towards aquifer components, it is difficult to clearly dissociate the biogeochemical processes that occur and their different impacts on the fate of these TE.
To do so, we developed an original, experimental, column setup that mimics an aquifer with As- or Hg-iron-oxide rich areas versus iron depleted areas, enabling a better understanding of TE biogeochemistry in anoxic conditions. The following protocol gives step by step instructions for the column set-up either for As or Hg, as well as an example with As under iron and sulfate reducing conditions.

Experimental Column Setup for Studying Anaerobic Biogeochemical Interactions Between Iron OxyHydroxides, Trace Elements, and Bacteria

Fate and speciation of arsenic and mercury in aquifers are closely related to physio-chemical conditions and microbial activity. Here, we present an original experimental column setup that mimics an aquifer and enables a better understanding of trace element biogeochemistry in anoxic conditions. Two examples are presented, combining geochemical and microbiological approaches.

Installazione colonna sperimentale per lo studio anaerobici biogeochimici interazioni tra batteri, oligoelementi e idrossidi di ferro (ossi)

Fate and speciation of trace elements (TEs), such as arsenic (As) and mercury (Hg), in aquifers are closely related to physio-chemical conditions, such as ...

Continuous Hydrologic and Water Quality Monitoring of Vernal Ponds

Vernal ponds, also referred to as vernal pools, provide critical ecosystem services and habitat for a variety of threatened and endangered species. However, they are vulnerable parts of the landscapes that are often poorly understood and understudied. Land use and management practices, as well as climate change are thought to be a contribution to the global amphibian decline. However, more research is needed to understand the extent of these impacts. Here, we present methodology for characterizing a vernal pond's morphology and detail a monitoring station that can be used to collect water quantity and quality data over the duration of a vernal pond's hydroperiod. We provide methodology for how to conduct field surveys to characterize the morphology and develop stage-storage curves for a vernal pond. Additionally, we provide methodology for monitoring the water level, temperature, pH, oxidation-reduction potential, dissolved oxygen, and electrical conductivity of water in a vernal pond, as well as monitoring rainfall data. This information can be used to better quantify the ecosystem services that vernal ponds provide and the impacts of anthropogenic activities on their ability to provide these services.

Understanding the ecosystem services and processes provided by vernal ponds and the impacts of anthropogenic activities on their ability to provide these services requires intensive hydrologic monitoring. This sampling protocol using in-situ monitoring equipment was developed to understand the impact of anthropogenic activities on water levels and quality.

Continuo idrologici e monitoraggio della qualità di Vernal stagni di acqua

Vernal ponds, also referred to as vernal pools, provide critical ecosystem services and habitat for a variety of threatened and endangered species. ...

Optimized Procedure for Determining the Adsorption of Phosphonates onto Granular Ferric Hydroxide using a Miniaturized Phosphorus Determination Method

This paper introduces a procedure to investigate the adsorption of phosphonates onto iron-containing filter materials, particularly granular ferric hydroxide (GFH), with little effort and high reliability. The phosphonate, e.g., nitrilotrimethylphosphonic acid (NTMP), is brought into contact with the GFH in a rotator in a solution buffered by an organic acid (e.g., acetic acid) or Good buffer (e.g., 2-(N-morpholino)ethanesulfonic acid) [MES] and N-cyclohexyl-2-hydroxyl-3-aminopropanesulfonic acid [CAPSO]) in a concentration of 10 mM for a specific time in 50 mL centrifuge tubes. Subsequently, after membrane filtration (0.45 &#181;m pore size), the total phosphorus (total P) concentration is measured using a specifically developed determination method (ISOmini). This method is a modification and simplification of the ISO 6878 method: a 4 mL sample is mixed with H2SO4 and K2S2O8 in a screw cap vial, heated to 148-150 &#176;C for 1 h and then mixed with NaOH, ascorbic acid and acidified molybdate with antimony(III) (final volume of 10 mL) to produce a blue complex. The color intensity, which is linearly proportional to the phosphorus concentration, is measured spectrophotometrically (880 nm). It is demonstrated that the buffer concentration used has no significant effect on the adsorption of phosphonate between pH 4 and 12. The buffers, therefore, do not compete with the phosphonate for adsorption sites. Furthermore, the relatively high concentration of the buffer requires a higher dosage concentration of oxidizing agent (K2S2O8) for digestion than that specified in ISO 6878, which, together with the NaOH dosage, is matched to each buffer. Despite the simplification, the ISOmini method does not lose any of its accuracy compared to the standardized method.

This paper introduces a procedure to investigate the adsorption of phosphonates onto iron-containing filter materials, particularly granular ferric hydroxide, with little effort and high reliability. In a buffered solution, the phosphonate is brought into contact with the adsorbent using a rotator and then analyzed via a miniaturized phosphorus determination method.

Procedura ottimizzata per determinare l'adsorbimento di fosfonati su idrossido ferrico granulare utilizzando un metodo di determinazione del fosforo miniaturizzato

This paper introduces a procedure to investigate the adsorption of phosphonates onto iron-containing filter materials, particularly granular ferric ...

Composition and Distribution Analysis of Bioaerosols Under Different Environmental Conditions

Variable microorganisms in particulate matter (PM) under different environmental conditions may have significant impacts on human health. In this study, we described a protocol for multiple analyses of the biological compositions in environmental PM. Five experiments are presented: (1) PM number monitoring by using a laser particle counter; (2) PM collection by using a cyclonic aerosol sampler; (3) PM collection by using a high-volume air sampler with filters; (4) culturable microbes collection by the Andersen six-stage sampler; and (5) detection of biological composition of environmental PM by bacterial 16SrDNA and fungal ITS region sequencing. We selected hazy days and a livestock farm as two typical examples of the application in this protocol. In this study, these two sampling methods, cyclonic aerosol sampler and filter sampler, showed different sampling efficiency. The cyclonic aerosol sampler performed much better in terms of collecting bacteria, while these two methods showed the same efficiency in collecting fungi. Filter samplers can work under low temperature conditions while cyclonic aerosol samplers have a sampling limitation for temperature. A solid impacting sampler, such as an Andersen six-stage sampler, can be used to sample bioaerosols directly into the culture medium, which increases the survival rate of culturable microorganisms. However, this method mainly relies on culture while more than 99% of microbes cannot be cultured. DNA extracted from the culturable bacteria collected by the Andersen six-stage sampler and samples collected by cyclonic aerosol sampler and filter sampler were detected by bacterial 16S rDNA and fungal ITS region sequencing.All the methods above may have wide application in many fields of study, such as environmental monitoring and airborne pathogen detection. From these results, we can conclude that these methods can be used under different conditions and may help other researchers further explore the health impacts of environmental bioaerosols.

Understanding the biological composition of environmental particulate matter is important for the study of its significant impacts on human health and disease spread. Here, we used three types of bioaerosol sampling methods and a biological analysis of airborne microbes to better explore airborne microbial communities under different environmental conditions.

Composizione e analisi della distribuzione di Bioaerosols in diverse condizioni ambientali

Variable microorganisms in particulate matter (PM) under different environmental conditions may have significant impacts on human health. In this study, ...