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Method Article

A Small Volume Procedure for Viral Concentration from Water

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DOI:

10.3791/51744

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February 3rd, 2015

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In This Article

Summary

An approach was developed for identifying optimal viral concentration conditions for small volume water samples using spikes of human adenovirus. The techniques described here are used to identify concentration parameters for other viral targets, and applied to large-scale viral concentration experimentation.

Abstract

Small-scale concentration of viruses (sample volumes 1-10 L, here simulated with spiked 100 ml water samples) is an efficient, cost-effective way to identify optimal parameters for virus concentration. Viruses can be concentrated from water using filtration (electropositive, electronegative, glass wool or size exclusion), followed by secondary concentration with beef extract to release viruses from filter surfaces, and finally tertiary concentration resulting in a 5-30 ml volume virus concentrate. In order to identify optimal concentration procedures, two different electropositive filters were evaluated (a glass/cellulose filter [1MDS] and a nano-alumina/glass filter [NanoCeram]), as well as different secondary concentration techniques; the celite technique where three different celite particle sizes were evaluated (fine, medium and large) followed by comparing this technique with that of the established organic flocculation method. Various elution additives were also evaluated for their ability to enhance the release of adenovirus (AdV) particles from filter surfaces. Fine particle celite recovered similar levels of AdV40 and 41 to that of the established organic flocculation method when viral spikes were added during secondary concentration. The glass/cellulose filter recovered higher levels of both, AdV40 and 41, compared to that of a nano-alumina/glass fiber filter. Although not statistically significant, the addition of 0.1% sodium polyphosphate amended beef extract eluant recovered 10% more AdV particles compared to unamended beef extract.

Introduction

Human enteric viruses are important causative agents of waterborne diseases 1-3, but are generally present in low numbers in contaminated environmental waters, making their detection difficult without concentration. Procedures used to concentrate viruses typically include a filtration step, followed by filter elution, and secondary concentration of the filter eluate. A common filtration procedure relies on use of charged membranes such as electropositive filters (recently reviewed in 4,5). These filters rely on capturing viruses suspended in water using electrostatic interactions between the filter surface (positively charged) and targeted virus ....

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Protocol

1. Preparation of Glassware and Filter Housings

  1. Unless otherwise noted, sterilize all glassware, filter housings and solutions at 121 °C for 15 min. To ensure sterility, cover all openings or exposed surfaces with either aluminum foil or tape-secured paper prior to sterilization.
  2. Assemble filtration apparatus by attaching filter housing (47 mm diameter) to 1 L side arm Erlenmeyer flask. Collect filters required: 47 mm diameter electropositive/electronegative disc filters.
  3. Prepare 1 L of 1.5% beef extract (flocculating; produces floc particles when pH of solution is lowered to 3.5, or non-flocculating; whi....

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Results

Celite selection

Three different types of celite were tested prior to the selection of the best performing variant. Celites with fine to medium sized particles produced the highest adenovirus recoveries. Use of larger celites resulted in lower recoveries for both AdV40 and 41 (range 32%-100%) (Figure 1). Average recoveries of adenovirus 40 were 144% ± 52% (fine), 115% ± 28% (medium) and 82% ± 53% (large) particle celites and for AdV41, 132% ± 39% (fine), 83% ± 25% (medium) and.......

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Discussion

Electropositive filters are useful in concentrating viruses from water; however these filters can differ in their structure and composition which could in turn alter their effectiveness. Compounding this problem, capsid structures and charges vary between virus strains requiring concentration techniques be tailored to ensure optimal recovery 15. Through simple modifications of the existing concentration techniques (e.g., electropositive filters, beef extract elution), more effective concentration of t.......

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Disclosures

No competing financial interests.

The views expressed in this article are those of the authors and do not necessarily reflect the views or policies of the U.S. Environmental Protection Agency. Mention of trade names or commercial products does not constitute endorsement or recommendation for use.

Acknowledgements

We would like to thank Dr. Nicholas J. Ashbolt and Dr. G. Shay Fout for their review of the manuscript.

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Materials

List of materials used in this article
NameCompanyCatalog NumberComments
Adenovirus 40 stockATCCVR-931
Adenovirus 41 stockATCCVR-930
Sodium ThiosulfateFluka Chemical Co.72051
Celites #577Fluka Chemical Co.22142
NanoCeram 47 mmArgonideN/A
1MDS 47 mm3M6408502
AP-20 Prefilter 47 mmMillipore Corp.AP2004700
Glycine Sigma50046-1KG
Sodium PolyphosphateAcros Organics390930010
TrypsinGibco25200
PBSSigmaP5368
Hydrochloric AcidFisherA481-212
BBL Beef ExtractBD Biosciences212303
Difco Beef ExtractBD Biosciences211520
ABI 7900 Real-time PCR systemABIN/A
Stainless Steel Filter HousingMillipore Corp.XX2004720
Blood DNA Extraction KitQiagen 51104
EPA MPN Calculatorhttp://www.epa.gov/nerlcwww/online.html

References

  1. Sinclair, R. G., Jones, E. L., Gerba, C. P. Viruses in recreational water-borne disease outbreaks: a review. Journal of Applied Microbiology. 107, 1769-1780 (2009).
  2. WHO. Guidelines for Safe Recreational Water Environments. , World Health Organization. Geneva. (2003).
  3. Westrell, T., et al.

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