Funding for the development of this protocol was provided by the Southeastern Pennsylvania Consortium for Higher Education and the Cabrini College Science Department. Additional funding and support came from Arcadia University and Immaculata University. We especially thank Dr. Karen Snetselaar at St. Joseph University for kindly taking the electron microscopic images of our isolated phages.&#160;Additional support was provided by the Howard Hughes Medical Institute Science Education Alliance Phage Hunters Advancing Genomics and Evolutionary Science (SEA-PHAGES) program.

1. Preparation of Arthobacter Cells for Phage Isolation
<ul>
	<li>Culture Arthrobactersp. KY3901 colonies streaked on an Luria Bertaini (LB) agar plate incubated at 30 &#176;C for 2-3 days. Pick a colony and use a sterile loop to add it to 250 ml of LB broth in a baffled culture flask and incubate in a shaking incubator at 225 rpm at 30 &#176;C.</li>
	<li>Allow approximately 24 hr of growth to obtain late exponential/early stationary phase cells for phage infection experiments. Monitor the state of bacterial growth closely to prevent cells from entering the middle to late stationary growth state. 
	NOTE: Cell growth should consist of an optical density OD600 between 0.5-.0.7 for the phage isolation and purification procedures/steps described below.</li>
</ul>
2. Collection of Phage from Soil Samples
<ol>
	<li>Gather 200-400 g of soil from desired location. Note: Since bacteria in the Arthrobacter genus are common soil bacteria they and the phages that infect them can be found in and are pervasive in most types of soil.</li>
	<li>Add at least 400 ml of Phage Buffer (PB) [68 mM NaCl, 10 mM MgSO4,10 mM Tris-CL (pH 7.5)] to the soil and mix in a large enough flask so that at least 200 ml of PB is in the supernatant and is able to be extracted.</li>
	<li>Mix by gently stirring or swirling until the soil is suspended and allow the soil sediment to settle, typically 30 min.</li>
	<li>Pass the &#8220;soil extract&#8221; through filter paper by gravity filtration to remove soil sediment debris.</li>
	<li>Add LB powder and mix to make a 2% solution (4 g LB powder in 200 ml soil extract).</li>
	<li>Pass the solution through a 0.22 &#181;m filter by vacuum filtration to obtain a sterile filtrate. If possible, continue on to step 2.7 immediately. If need be, store filtered samples at 4 &#176;C for up to a week before proceeding, however, the number of viable phage particles will be reduced.</li>
	<li>Aliquot multiple 50 ml portions of the filter-sterilized LB/soil extract mixture into individual 250 ml sterilized shaking baffled culture flasks using aseptic techniques. Add sterile 2.0 M CaCl2 solution to the final desired concentrations (0-50 mM) since different Arthrobacter phages grow optimally under different CaCl2 conditions. 
	NOTE: We find that the majority of the Arthrobacter phages&#160;identified by us are within the range of 1 mM-2.5 mM CaCl2. However, several of the isolated phages grew by us exclusively at 0 mM CaCl2.or at very high CaCl2 concentrations. Proceed immediately to step 3.1.</li>
</ol>
3. Phage Isolation
<ol>
	<li>Add 1 to 2.5 ml of late exponential/early stationary phase bacteria culture to each of the flasks. For an OD600 from 0.5-0.7, use 1 ml of cells. For an OD600 higher than an OD of 0.7 use 2.5 ml of cells. 
	NOTE: Cells in exponential phase growth typically yield more phages and higher titers than cells in stationary phase growth.</li>
	<li>Shake flasks at 250 rpm at 30 &#176;C for approximately 24 hr in a shaking incubator.</li>
	<li>After a 24 hr incubation period remove enrichment flasks from the shaking incubator and dilute the enrichment samples ten-fold in phage buffer.</li>
	<li>Set up culture tubes with 0.5 ml of late exponential/early stationary phase bacteria culture and add various amounts of the enrichment culture (5 &#181;l to 500 &#181;l of a 10-1 dilution in PB) to the culture tubes. 
	NOTE: It is advisable to test a wide range of concentrations since each soil sample generates different phage titers after enrichment.</li>
	<li>Add CaCl2 to culture tubes to make a final concentration equal to the concentration present in the original enrichment flask. Use a range of different CaCl2 concentrations to select for many phages with varying CaCl2 dependencies. 
	NOTE: Most phages will be isolated within the CaCl2 range of 1-2.5 mM but there are phages isolated most optimally anywhere from 0-50 mM CaCl2 concentrations. Because of this it is best to check a range of CaCl2 concentrations to maximize the number of unique isolated Arthrobacter phages.</li>
	<li>Mix 4.5 ml&#160;of LB top agar in the culture tube and pour the mixture onto an LB agar plate. Swirl gently to distribute across the plate evenly and allow for top agar to solidify for approximately 15 min. 
	NOTE: Top agar can be prepared in larger batches (250 ml) and extra top agar can be stored at RT and reused for subsequent experiments for at least two weeks. Although there are different formulas used to make top agar, we make top agar using 7g/L of agar mixed with LB. Place top agar in a 60 &#176;C water bath to retain the liquid state during the course of an experiment.</li>
	<li>Invert the plate and incubate at desired temperature (temperature to 30 &#176;C) O/N to 48 hr. Vary these conditions to optimize for the phages present. Most isolated phages come from plates incubated at 30 &#176;C at 1-2.5 mM CaCl2 concentration after a 24 hr incubation period.</li>
</ol>
4. Phage Purification
<ol>
	<li>After a 24 hr incubation check for plaque formation on plates. Continue incubation for up to 72 hr if no plaques are evident or to determine if additional plaques will appear. If needed, store plates with putative plaques for up to a week at 4 &#176;C prior to proceeding. 
	&#8203;NOTE: It is not uncommon to find a variety of different plaque morphologies on one plate. Finding plaques after 3 days of incubation is possible but rare.</li>
	<li>Purify desired phages from clearly isolated plaques using the streak plaque method. Touch a plaque with a sterile wooden stick. Streak the plaque by running a wooden stick through a flame, allowing the stick to cool briefly, and then rubbing the stick on the agar plate in the gentle motion as shown in Figure 1. Repeat this using a clean stick for each pass.</li>
	<li>Alternatively, use the traditional plaque titer assay to isolate individual phage plaques. The plaque titer assay does require the use of more reagents such as LB agar and LB top agar and materials such as petri plates for phage plaque isolation. We have been highly successful using the streak plaque method but it is technically easier to isolate individual plaques using the plaque titer assay.</li>
	<li>Once the LB agar plate is streaked at least three times, mark the area with the lowest concentration of putative phage particles and GENTLY apply 0.5 ml of Arthrobacter and 4.5 ml of molten LB top agar (containing the same concentration of calcium chloride as the parent plate) and allow it to spread evenly across the plate.</li>
	<li>Invert and incubate plate O/N. Repeat the streak plaque technique for at least three iterations to ensure a pure phage species is isolated. Store plates at 4 &#176;C for up to a week as needed between streaks without significant loss of phage viability.</li>
	<li>Once desired plaques have been grown and isolated on the final streak plate, touch one well isolated plaque with a micropipette tip and re-suspend in 100 &#181;l PB. Serially dilute this 100 solution out to the 10-8 dilution by passing 20 &#181;l of the sample into 180 &#181;l of fresh PB.</li>
	<li>Add 10 &#181;l of each dilution to 0.5 ml of grown Arthrobacter in a culture tube for 5 to 10 min at RT and plate by mixing the infected bacteria with 4.5 ml of molten LB top agar containing the same concentration of CaCl2 used to isolate the phage from the original soil sample. Save all dilutions made at 4 &#176;C until the next day.</li>
	<li>Determine the phage serial dilution needed to make a web pattern using the traditional plaque titer assay. The purpose of the plaque titer assay is to determine the phage titer needed to obtain a web pattern plate. Identify a web pattern plate as mostly devoid of bacteria but containing remnants of bacteria that have not yet been lysed by phages. Add 5 ml of late exponential/ early stationary Arthrobacter culture to a sterile 50 ml culture flask.
	<ol>
		<li>Add 100 &#181;l of the dilution (that gave a web pattern to the Arthrobacter culture) in the culture flask and allow the phages to infect the bacteria cells for 5 to 10 min at RT. Mix with molten LB top agar containing the same concentration of CaCl2 as used to initially identify the phage and plate 5 ml of this mixture onto 10 fresh LB plates. Allow to solidify and incubate inverted plates at 30 &#176;C.</li>
	</ol>
	</li>
	<li>The next day, flood the web pattern plates with 5 ml of PB and store O/N&#160;at 4 &#176;C or 4 hr at RT.</li>
	<li>Filter the phage lysate through a 0.22 &#181;m syringe filter and store at 4 &#176;C. Use this final phage stock for additional experiments such as electron microscopy images of phage particles, phage genomic DNA isolation for DNA restriction enzyme analysis and genomic sequencing using standard procedures. For long term storage of the phage stock, add an equal amount of the phage lysate to sterile glycerol in small vials for stock archiving at -80 &#176;C. 
	NOTE: For those not experienced with these phage techniques,&#160;a great resource is the online accessible www.phagesdb.org website.</li>
</ol>

<ol>
	<li>Shapir, N., Mongodin, E. F., Sadowsky, M. J., Daugherty, S. C., Nelson, K. E., Wackett, L. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Evolution+of+Catabolic+Pathways:+Genomic+Insights+into+Microbial+s-Triazine+Metabolism.">Evolution of Catabolic Pathways: Genomic Insights into Microbial s-Triazine Metabolism.</a> J Bacteriol. 189 (3), 674-682 (2007).</li><li>Qingyan, L., Ying, L., Xikun, Z., Baoli, C. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Isolation+and+Characterization+of+Atrazine+Degrading+Arthrobacter+sp.+AD26+and+Use+of+this+Strain+in+Bioremediation+of+Contaminated+Soil.">Isolation and Characterization of Atrazine Degrading Arthrobacter sp. AD26 and Use of this Strain in Bioremediation of Contaminated Soil.</a> J Environ Sci. 20, 1226-1230 (2008).</li><li>Wang, J., Zhu, L., Liu, A., Ma, T., Wang, Q., Xie, H., Wang, J., Jiang, T., Zhao, T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Isolation+and+characterization+of+an+Arthrobacter+sp.+Strain+HB-5+that+Transforms+Atrazine.">Isolation and characterization of an Arthrobacter sp. Strain HB-5 that Transforms Atrazine.</a> Environ Geochem Hlth. 33, 259-266 (2011).</li><li>Mages, I. S., Frodl, R., Bernard, K. A., Funke, G. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Identities+of+Arthrobacter+spp.+And+Arthrobacter-Like+Bacteria+Encountered+in+Human+Clinical+Specimens.">Identities of Arthrobacter spp. And Arthrobacter-Like Bacteria Encountered in Human Clinical Specimens.</a> J Clin Microbiol. 46 (9), 2980-2986 (2008).</li><li>Brown, D. R., Holt, J. G., Pattee, P. A. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Isolation+and+Characterization+of+Arthrobacter+Bacteriophages+and+Their+Application+to+Phage+Typing+of+Soil+Arthrobacters.">Isolation and Characterization of Arthrobacter Bacteriophages and Their Application to Phage Typing of Soil Arthrobacters.</a> Appl Environ Microbiol. 35 (1), 185-191 (1978).</li><li>Petrovski, S., Seviour, R. J., Tillett, D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Prevention+of+Gordonia+and+Nocardia+Stabilized+Foam+Formation+by+Using+Bacteriophage+GTE7.">Prevention of Gordonia and Nocardia Stabilized Foam Formation by Using Bacteriophage GTE7.</a> Appl Environ Microbiol. 77 (21), 7864-7867 (2011).</li><li>Le Marrec, C., Moreau, S., Loury, S., Blanco, C., Trautwetter, a. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Genetic+Characterization+of+Site-specific+Integration+Functions+of+phi+AAU2+infecting+&#8220;Arthrobacter+aureus&#8221;+C70.">Genetic Characterization of Site-specific Integration Functions of phi AAU2 infecting &#8220;Arthrobacter aureus&#8221; C70.</a> J Bacteriology. 178 (7), 1996-2004 (1996).</li><li>Casida, L. E., Liu, K. C. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Arthrobacter+globiformis+and+Its+Bacteriophage+in+Soil.">Arthrobacter globiformis and Its Bacteriophage in Soil.</a> J Appl Microbiol. 28 (6), 951-959 (1974).</li><li>Einck, K. H., Pattee, P. A., Holt, J. G., Hagedorn, C., Miller, J. A., Berryhill, D. L. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Isolation+and+Characterization+of+a+Bacteriophage+of+Arthrobacter+globiformis.">Isolation and Characterization of a Bacteriophage of Arthrobacter globiformis.</a> J Virol. 12 (5), 1031-1033 (1973).</li><li>Twest, R., Kropinski, A. M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Bacteriophage+Enrichment+from+Soil+and+Water.">Bacteriophage Enrichment from Soil and Water.</a> Methods Mol Bio. 501, 15-21 (2009).</li><li>Fullner, K. J., Hatfull, G. F. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Mycobacteriophage+L5+Infection+of+Mycobacterium+bovis+BCG:+Implications+for+Phage+Genetics+in+the+Slow-growing+Mycobacteria.">Mycobacteriophage L5 Infection of Mycobacterium bovis BCG: Implications for Phage Genetics in the Slow-growing Mycobacteria.</a> Mol Microbiol. 26 (4), 755-766 (1997).</li><li>Robb, S. M., Woods, D. R., Robb, F. T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Phage+Growth+Characteristics+on+Stationary+Phase+Achromobacter+cells.">Phage Growth Characteristics on Stationary Phase Achromobacter cells.</a> J Gen Virol. 41 (2), 265-272 (1978).</li><li>Bolger-Munro, M., Cheung, K., Fang, A., Wang, L. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=T4+Bacteriophage+Average+Burst+Size+Varies+with+Escherichia+coli+B23+Cell+Culture+Age.">T4 Bacteriophage Average Burst Size Varies with Escherichia coli B23 Cell Culture Age.</a> Journal of Experimental Microbiology and Immunology. 17, 115-119 (2013).</li></ol>

Authors declare no competing financial interests.

Despite many previous attempts to isolate phages capable of infecting Arthrobacter hosts, we had little success using standard enrichment procedures. The generalized method of bacterial enrichment developed and adapted by van Twest and Kropinski10 to enrich phages from environmental samples remains the basis for the majority of enrichment procedures. Evidence from previous studies suggests that methods of direct plating have produced detectable plaques on strains of Arthrobacter albeit with v...

The ubiquity of Arthrobacter species in soil environments offers a vast number and diversity of phages capable of being isolated from this species of host bacteria. Bacterial members of the Acintobacteriaceae family are most notable for their catabolic pathways of degrading recalcitrant compounds like atrazine and various other pesticides and herbicides1,2,3. Though most research has been done using environmental strains of Arthrobacter, clinical isolates of this genus is found in blood, urine, eyes, and many other human sources all displaying phylogenetic heterogeneity4.
While there is a rather extensive body of research on Arthrobacter bacteria, only a few studies report on the phages capable of infecting members of this diverse genus. Interestingly though, work done previously on Arthrobacter phages touches on several key distinct topics such as the typing of soil Arthrobacter species5, industrial uses with the purpose of reducing deleterious foam in activated sludge treatment plants 6, and work highlighting site specific recombination and integrase genes7.
Various enrichment technique protocols have been employed to generate pure phage isolates in Arthrobacter species. Early procedures include incubations of soil with added toxic agents like nicotine salts for periods of over one year8 giving rise to phages capable of only infecting A. globiformis. Studies done using soil percolated with labile organics appeared to produce detectable phages via plaque assay techniques, omitting lengthy incubation periods8. Interestingly though, a technique resembling direct plating was used in the past giving rise to several phages while still having a notably low success rate by the investigators5, citing past studies with low success rates8.
Overall, the isolation techniques used in the past were notable for having little efficacy in practice despite the Arthrobacter genus representing the most common aerobic soil isolate in nature4,9,,Van Twest and Kropinski10 present enrichment methods for isolating phages from water and soil adapted from earlier techniques used to enrich environmental bacterial isolates but these enrichment techniques proved inefficient in isolating Arthrobacter phages. The purpose of the method described here is to show &#8220;proof of concept&#8221; that the early enrichment methods can be adapted to consistently and effectively isolate Arthrobacter phages, overcoming previous technical challenges associated with isolating phages from this bacterial genus.

<table border="0" cellpadding="0" cellspacing="0">
	<tbody>
		<tr>
			<td>LB Broth powder</td>
			<td>Fisher</td>
			<td>BP9722-2</td>
			<td>It&#39;s best to order these in bulk.</td>
		</tr>
		<tr>
			<td>Granulated Agar</td>
			<td>Fisher</td>
			<td>BP1423-2</td>
			<td>It&#39;s best to order these in bulk.</td>
		</tr>
		<tr>
			<td>0.22 um syringe filters</td>
			<td>Fisher</td>
			<td>09-719A</td>
			<td></td>
		</tr>
		<tr>
			<td>.22 um buchner filters</td>
			<td>Fisher</td>
			<td align="right">430320</td>
			<td>More than 50 mL of liquid can be obtained by carefully swapping the receiving tube.</td>
		</tr>
		<tr>
			<td>Eppendorf Tubes</td>
			<td>Fisher</td>
			<td>05-408-129</td>
			<td></td>
		</tr>
		<tr>
			<td>5 mL pipets individual</td>
			<td>Fisher</td>
			<td>13-678-11D</td>
			<td></td>
		</tr>
		<tr>
			<td>50 mL conical tubes</td>
			<td>Fisher</td>
			<td align="right">76002844</td>
			<td></td>
		</tr>
		<tr>
			<td>15 mL conical tubes</td>
			<td>Fisher</td>
			<td align="right">76002845</td>
			<td></td>
		</tr>
		<tr>
			<td>10 mL pipets individual</td>
			<td>Fisher</td>
			<td>13-676-10J</td>
			<td></td>
		</tr>
		<tr>
			<td>25 mL pipets individual</td>
			<td>Fisher</td>
			<td>13-676-10K</td>
			<td></td>
		</tr>
		<tr>
			<td>Whatman qualitative filter paper</td>
			<td>Fisher</td>
			<td>1001-824</td>
			<td></td>
		</tr>
	</tbody>
</table>

an optimized enrichment technique for the isolation of arthrobacter bacteriophage species from soil sample isolates

Bacteriophage isolation from environmental samples has been performed for decades using principles set forth by pioneers in microbiology. The isolation of phages infecting Arthrobacter hosts has been limited, perhaps due to the low success rate of many previous isolation techniques, resulting in an underrepresented group of Arthrobacter phages available for study. The enrichment technique described here, unlike many others, uses a filtered extract free of contaminating bacteria as the base for indicator bacteria growth, Arthrobactersp. KY3901, specifically. By first removing soil bacteria the target phages are not hindered by competition with native soil bacteria present in initial soil samples. This enrichment method has resulted in dozens of unique phages from several different soil types and even produced different types of phages from the same enriched soil sample isolate. The use of this procedure can be expanded to most nutrient rich aerobic media for the isolation of phages in a vast diversity of interesting host bacteria.

To demonstrate reproducibility of the improved enrichment technique for Arthrobacter phages,&#160;30 different soil samples were used at different times and locations during the spring and summer of 2014. Of these 30 soil samples unique Arthrobacter phages were obtained from 22 of collected soil samples using this enrichment procedure. The standard enrichment procedure yielded unique phages from 3 of the same soil samples. The enrichment samples can have a very high phage titer needing initial dilution ...

Watch this Scientific Journal Video about An Optimized Enrichment Technique for the Isolation of Arthrobacter Bacteriophage Species from Soil Sample Isolates at JoVE.com

An Optimized Enrichment Technique for the Isolation of Arthrobacter Bacteriophage Species from Soil Sample Isolates

We present an enrichment protocol for the isolation of bacteriophages infecting bacteria in the Arthrobacter genus. This enrichment protocol produces fast and reproducible results for the isolation and amplification of Arthrobacter phages from soil isolates.

An Optimized Enrichment Technique for the Isolation of Arthrobacter Bacteriophage Species from Soil Sample Isolates

Bacteriophage isolation from environmental samples has been performed for decades using principles set forth by pioneers in microbiology. The isolation of ...

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19.4K vistas.  University of the Sciences. We present an enrichment protocol for the isolation of bacteriophages infecting bacteria in the Arthrobacter genus. This enrichment protocol produces fast and reproducible results for the isolation and amplification of Arthrobacter phages from soil isolates.

Video: An Optimized Enrichment Technique for the Isolation of Arthrobacter Bacteriophage Species from Soil Sample Isolates

Design and Operation of a Continuous 13C and 15N Labeling Chamber for Uniform or Differential, Metabolic and Structural, Plant Isotope Labeling

Tracing rare stable isotopes from plant material through the ecosystem provides the most sensitive information about ecosystem processes; from CO2 fluxes and soil organic matter formation to small-scale stable-isotope biomarker probing. Coupling multiple stable isotopes such as 13C with 15N, 18O or&#160;2H has the potential to reveal even more information about complex stoichiometric relationships during biogeochemical transformations. Isotope labeled plant material has been used in various studies of litter decomposition and soil organic matter formation1-4. From these and other studies, however, it has become apparent that structural components of plant material behave differently than metabolic components (i.e. leachable low molecular weight compounds) in terms of microbial utilization and long-term carbon storage5-7. The ability to study structural and metabolic components separately provides a powerful new tool for advancing the forefront of ecosystem biogeochemical studies. Here we describe a method for producing 13C and 15N labeled plant material that is either uniformly labeled throughout the plant or differentially labeled in structural and metabolic plant components.
Here, we present the construction and operation of a continuous 13C and 15N labeling chamber that can be modified to meet various research needs. Uniformly labeled plant material is produced by continuous labeling from seedling to harvest, while differential labeling is achieved by removing the growing plants from the chamber weeks prior to harvest. Representative results from growing Andropogon gerardii Kaw demonstrate the system&#39;s ability to efficiently label plant material at the targeted levels. Through this method we have produced plant material with a 4.4 atom%13C and 6.7 atom%15N uniform plant label, or material that is differentially labeled by up to 1.29 atom%13C and 0.56 atom%15N in its metabolic and structural components (hot water extractable and hot water residual components, respectively). Challenges lie in maintaining proper temperature, humidity, CO2 concentration,&#160;and light levels in an airtight 13C-CO2 atmosphere for successful plant production. This chamber description represents a useful research tool to effectively produce uniformly or differentially multi-isotope labeled plant material for use in experiments on ecosystem biogeochemical cycling.

Design and Operation of a Continuous 13C and 15N Labeling Chamber for Uniform or Differential, Metabolic and Structural, Plant Isotope Labeling

This method explains how to build and operate a continuous 13C and 15N isotope labeling chamber for uniform or differential plant tissue labeling. Representative results from metabolic and structural labeling of Andropogon gerardii are discussed.

Tracing rare stable isotopes from plant material through the ecosystem provides the most sensitive information about ecosystem processes; from CO2 fluxes ...

Design and Construction of an Urban Runoff Research Facility

As the urban population increases, so does the area of irrigated urban landscape. Summer water use in urban areas can be 2-3x winter base line water use due to increased demand for landscape irrigation. Improper irrigation practices and large rainfall events can result in runoff from urban landscapes which has potential to carry nutrients and sediments into local streams and lakes where they may contribute to eutrophication. A 1,000 m2 facility was constructed which consists of 24 individual 33.6 m2 field plots, each equipped for measuring total runoff volumes with time and collection of runoff subsamples at selected intervals for quantification of chemical constituents in the runoff water from simulated urban landscapes. Runoff volumes from the first and second trials had coefficient of variability (CV) values of 38.2 and 28.7%, respectively. CV values for runoff pH, EC, and Na concentration for both trials were all under 10%. Concentrations of DOC, TDN, DON, PO4-P, K+, Mg2+, and Ca2+ had CV values less than 50% in both trials. Overall, the results of testing performed after sod installation at the facility indicated good uniformity between plots for runoff volumes and chemical constituents. The large plot size is sufficient to include much of the natural variability and therefore provides better simulation of urban landscape ecosystems.

This paper describes the design, construction, and function of a 1,000 m2 facility containing 24 individual 33.6 m2 field plots equipped for measuring total runoff volumes with time and collection of runoff subsamples at selected intervals for quantification of chemical constituents in the runoff water from simulated home lawns.

As the urban population increases, so does the area of irrigated urban landscape. Summer water use in urban areas can be 2-3x winter base line water use ...

Soil Sampling and Isolation of Entomopathogenic Nematodes (Steinernematidae, Heterorhabditidae)

Entomopathogenic nematodes (a.k.a. EPN) represent a group of soil-inhabiting nematodes that parasitize a wide range of insects. These nematodes belong to two families: Steinernematidae and Heterorhabditidae. Until now, more than 70 species have been described in the Steinernematidae and there are about 20 species in the Heterorhabditidae. The nematodes have a mutualistic partnership with Enterobacteriaceae bacteria and together they act as a potent insecticidal complex that kills a wide range of insect species.
Herein, we focus on the most common techniques considered for collecting EPN from soil. The second part of this presentation focuses on the insect-baiting technique, a widely used approach for the isolation of EPN from soil samples, and the modified White trap technique which is used for the recovery of these nematodes from infected insects. These methods and techniques are key steps for the successful establishment of EPN cultures in the laboratory and also form the basis for other bioassays that consider these nematodes as model organisms for research in other biological disciplines. The techniques shown in this presentation correspond to those performed and/or designed by members of S. P. Stock laboratory as well as those described by various authors.

Soil Sampling and Isolation of Entomopathogenic Nematodes Steinernematidae, Heterorhabditidae

Entomopathogenic nematodes are soil-inhabiting roundworms that parasitize a wide range of insects. We demonstrate sampling methods used for the isolation of these nematodes from the soil using two techniques: the insect baiting and the modified White trap, for the recovery of nematodes from soil samples and infected insect cadavers, respectively.

Entomopathogenic nematodes (a.k.a. EPN) represent a group of soil-inhabiting nematodes that parasitize a wide range of insects. These nematodes belong to ...

A CO2 Concentration Gradient Facility for Testing CO2 Enrichment and Soil Effects on Grassland Ecosystem Function

Continuing increases in atmospheric carbon dioxide concentrations (CA) mandate techniques for examining impacts on terrestrial ecosystems. Most experiments examine only two or a few levels of CA concentration and a single soil type, but if CA can be varied as a gradient from subambient to superambient concentrations on multiple soils, we can discern whether past ecosystem responses may continue linearly in the future and whether responses may vary across the landscape. The Lysimeter Carbon Dioxide Gradient Facility applies a 250 to 500 &#181;l L-1 CA gradient to Blackland prairie plant communities established on lysimeters containing clay, silty clay, and sandy soils. The gradient is created as photosynthesis by vegetation enclosed in in temperature-controlled chambers progressively depletes carbon dioxide from air flowing directionally through the chambers. Maintaining proper air flow rate, adequate photosynthetic capacity, and temperature control are critical to overcome the main limitations of the system, which are declining photosynthetic rates and increased water stress during summer. The facility is an economical alternative to other techniques of CA enrichment, successfully discerns the shape of ecosystem responses to subambient to superambient CA enrichment, and can be adapted to test for interactions of carbon dioxide with other greenhouse gases such as methane or ozone.

A CO2 Concentration Gradient Facility for Testing CO2 Enrichment and Soil Effects on Grassland Ecosystem Function

The Lysimeter Carbon Dioxide Gradient Facility creates a 250 to 500 &#181;l L-1 linear carbon dioxide gradient in temperature-controlled chambers housing grassland plant communities on clay, silty clay, and sandy soil monoliths. The facility is used to determine how past and future carbon dioxide levels affect grassland carbon cycling.

Continuing increases in atmospheric carbon dioxide concentrations (CA) mandate techniques for examining impacts on terrestrial ecosystems. Most ...

Spotting Cheetahs: Identifying Individuals by Their Footprints

The cheetah (Acinonyx jubatus) is Africa's most endangered large felid and listed as Vulnerable with a declining population trend by the IUCN1. It ranges widely over sub-Saharan Africa and in parts of the Middle East. Cheetah conservationists face two major challenges, conflict with landowners over the killing of domestic livestock, and concern over range contraction. Understanding of the latter remains particularly poor2. Namibia is believed to support the largest number of cheetahs of any range country, around 30%, but estimates range from 2,9053 to 13,5204. The disparity is likely a result of the different techniques used in monitoring.
Current techniques, including invasive tagging with VHF or satellite/GPS collars, can be costly and unreliable. The footprint identification technique5 is a new tool accessible to both field scientists and also citizens with smartphones, who could potentially augment data collection. The footprint identification technique analyzes digital images of footprints captured according to a standardized protocol. Images are optimized and measured in data visualization software. Measurements of distances, angles, and areas of the footprint images are analyzed using a robust cross-validated pairwise discriminant analysis based on a customized model. The final output is in the form of a Ward's cluster dendrogram. A user-friendly graphic user interface (GUI) allows the user immediate access and clear interpretation of classification results.
The footprint identification technique algorithms are species specific because each species has a unique anatomy. The technique runs in a data visualization software, using its own scripting language (jsl) that can be customized for the footprint anatomy of any species. An initial classification algorithm is built from a training database of footprints from that species, collected from individuals of known identity. An algorithm derived from a cheetah of known identity is then able to classify free-ranging cheetahs of unknown identity. The footprint identification technique predicts individual cheetah identity with an accuracy of &gt;90%.

The cheetah (Acinonyx jubatus) is an iconic, endangered species, but conservation efforts are challenged by habitat shrinkage and conflict with commercial farmers. The footprint identification technique, a robust, accurate and cost-effective image classification system, is a new approach to monitoring cheetahs.

The cheetah (Acinonyx jubatus) is Africa's most endangered large felid and listed as Vulnerable with a declining population trend by the IUCN1. It ranges ...

Protocol for Microplastics Sampling on the Sea Surface and Sample Analysis

Microplastic pollution in the marine environment is a scientific topic that has received increasing attention over the last decade. The majority of scientific publications address microplastic pollution of the sea surface. The protocol below describes the methodology for sampling, sample preparation, separation and chemical identification of microplastic particles. A manta net fixed on an &#187;A frame&#171; attached to the side of the vessel was used for sampling. Microplastic particles caught in the cod end of the net were separated from samples by visual identification and use of stereomicroscopes. Particles were analyzed for their size using an image analysis program and for their chemical structure using ATR-FTIR and micro FTIR spectroscopy. The described protocol is in line with recommendations for microplastics monitoring published by the Marine Strategy Framework Directive (MSFD) Technical Subgroup on Marine Litter. This written protocol with video guide will support the work of researchers that deal with microplastics monitoring all over the world.

The protocol below describes the methodology for: microplastics sampling on the sea surface, separation of microplastic and chemical identification of particles. This protocol is in line with the recommendations for microplastics monitoring published by the MSFD Technical Subgroup on Marine Litter.

Microplastic pollution in the marine environment is a scientific topic that has received increasing attention over the last decade. The majority of ...

Isolation and Analysis of Microbial Communities in Soil, Rhizosphere, and Roots in Perennial Grass Experiments

Plant and soil microbiome studies are becoming increasingly important for understanding the roles microorganisms play in agricultural productivity. The purpose of this manuscript is to provide detail on how to rapidly sample soil, rhizosphere, and endosphere of replicated field trials and analyze changes that may occur in the microbial communities due to sample type, treatment, and plant genotype. The experiment used to demonstrate these methods consists of replicated field plots containing two, pure, warm-season grasses (Panicum virgatum and Andropogon gerardii) and a low-diversity grass mixture (A. gerardii, Sorghastrum nutans, and Bouteloua curtipendula). Briefly, plants are excavated, a variety of roots are cut and placed in phosphate buffer, and then shaken to collect the rhizosphere. Roots are brought to the laboratory on ice and surface sterilized with bleach and ethanol (EtOH). The rhizosphere is filtered and concentrated by centrifugation. Excavated soil from around the root ball is placed into plastic bags and brought to the lab where a small amount of soil is taken for DNA extractions. DNA is extracted from roots, soil, and rhizosphere and then amplified with primers for the V4 region of the 16S rRNA gene. Amplicons are sequenced, then analyzed with open access bioinformatics tools. These methods allow researchers to test how the microbial community diversity and composition varies due to sample type, treatment, and plant genotype. Using these methods along with statistical models, the representative results demonstrate there are significant differences in microbial communities of roots, rhizosphere, and soil. Methods presented here provide a complete set of steps for how to collect field samples, isolate, extract, quantify, amplify, and sequence DNA, and analyze microbial community diversity and composition in replicated field trials.

Excavation of plant roots from the field as well as processing of samples into endosphere, rhizosphere, and soil are described in detail, including DNA extraction and data analysis methods. This paper is designed to enable other laboratories to use these techniques for the study of soil, endosphere, and rhizosphere microbiomes.

Plant and soil microbiome studies are becoming increasingly important for understanding the roles microorganisms play in agricultural productivity. The ...

Use of Principal Components for Scaling Up Topographic Models to Map Soil Redistribution and Soil Organic Carbon

Landscape topography is a critical factor affecting soil formation and plays an important role in determining soil properties on the earth surface, as it regulates the gravity-driven soil movement induced by runoff and tillage activities. The recent application of Light Detection and Ranging (LiDAR) data holds promise for generating high spatial resolution topographic metrics that can be used to investigate soil property variability. In this study, fifteen topographic metrics derived from LiDAR data were used to investigate topographic impacts on redistribution of soil and spatial distribution of soil organic carbon (SOC). Specifically, we explored the use of topographic principal components (TPCs) for characterizing topography metrics and stepwise principal component regression (SPCR) to develop topography-based soil erosion and SOC models at site and watershed scales. Performance of SPCR models was evaluated against stepwise ordinary least square regression (SOLSR) models. Results showed that SPCR models outperformed SOLSR models in predicting soil redistribution rates and SOC density at different spatial scales. Use of TPCs removes potential collinearity between individual input variables, and dimensionality reduction by principal component analysis (PCA) diminishes the risk of overfitting the prediction models. This study proposes a new approach for modeling soil redistribution across various spatial scales. For one application, access to private lands is often limited, and the need to extrapolate findings from representative study sites to larger settings that include private lands can be important.

Landscape processes are critical components of soil formation and play important roles in determining soil properties and spatial structure in landscapes. We propose a new approach using stepwise principal component regression to predict soil redistribution and soil organic carbon across various spatial scales.

Landscape topography is a critical factor affecting soil formation and plays an important role in determining soil properties on the earth surface, as it ...

An Optimized Rhizobox Protocol to Visualize Root Growth and Responsiveness to Localized Nutrients

Roots are notoriously difficult to study. Soil is both a visual and mechanical barrier, making it difficult to track roots in situ without destructive harvest or expensive equipment. We present a customizable and affordable rhizobox method that allows the non-destructive visualization of root growth over time and is particularly well-suited to studying root plasticity in response to localized resource patches. The method was validated by assessing maize genotypic variation in plasticity responses to patches containing 15N-labeled legume residue. Methods are described to obtain representative developmental measurements over time, measure root length density in resource-containing and control patches, calculate root growth rates, and determine 15N recovery by plant roots and shoots. Advantages, caveats, and potential future applications of the method are also discussed. Although care must be taken to ensure that experimental conditions do not bias root growth data, the rhizobox protocol presented here yields reliable results if carried out with sufficient attention to detail.

Visualizing and measuring root growth in situ is extremely challenging. We present a customizable rhizobox method to track root development and proliferation over time in response to nutrient enrichment. This method is used to analyze maize genotypic differences in root plasticity in response to an organic nitrogen source.

Roots are notoriously difficult to study. Soil is both a visual and mechanical barrier, making it difficult to track roots in situ without destructive ...

Using Caenorhabditis elegans for Studying Trans- and Multi-Generational Effects of Toxicants

Information about toxicities of chemicals are essential in their application and waste management. For chemicals at low concentrations, the long-term effects are very important in judging their consequences in the environment and on human health. In demonstrating long-term influences, effects of chemicals over generations in recent studies provide new insight. Here, we describe protocols for studying effects of chemicals over multiple generations using free-living nematode Caenorhabditis elegans. Two aspects are presented: (1) trans-generational (TG) and (2) multi-generational effect studies, the latter of which is separated to multi-generational exposure (MGE) and multi-generational residual (MGR) effect studies. The TG effect study is robust with a simple purpose to determine whether chemical exposure to parents can result in any residual consequences on offspring. After the effects are measured on parents, sodium hypochlorite solutions are used to kill the parents and keep the offspring so as to facilitate effect measurement on the offspring. The TG effect study is used to determine whether the offspring are affected when their parent is exposed to the pollutants. The MGE and MGR effect study is systematical used to determine whether continuous generational exposure can result in adaptive responses in offspring over generations. Careful pick-up and transfer are used to distinguish generations to facilitate effect measurement on each generation. We also combined protocols to measure locomotion behavior, reproduction, lifespan, biochemical and gene expression changes. Some example experiments are also presented to illustrate the trans- and multi-generational effect studies.

Using Caenorhabditis elegans for Studying Trans- and Multi-Generational Effects of Toxicants

Trans- and multi-generational effects of persistent chemicals are essential in judging their long-term consequences in the environment and on the human health. We provide novel detailed methods for studying trans- and multi-generational effects using free-living nematode Caenorhabditis elegans.

Information about toxicities of chemicals are essential in their application and waste management. For chemicals at low concentrations, the long-term ...