The development of these methods, especially shed skin lipid extraction, occurred during cooperative agreements (14-7412-1061-CA, 15-7412-1155-CA, and 16-7412-1269-CA) between James Madison University (JMU) and the U.S. Department of Agriculture&#39;s Animal and Plant Health Inspection Service (APHIS). M.R.P. acknowledges the contributions of the following students to the development of the shed skin methods: S. Patel (Washington and Lee University [WLU]), J. Zachry (WLU), R. Flores (JMU), J. Noll (JMU), and S. Ashton (JMU).

All procedures involving the use of vertebrates were approved by the Institutional Animal Care and Use Committee of James Madison University.
1. Extraction
<ol>
	<li>Shed skin extraction 
	<ol>
		<li>Gather approximately 30 cm2 of shed from a single reptile, removing the head and cloacal sections that can contaminate the samples. Wear chloroprene gloves and clean the shed of debris.</li>
		<li>Tare the balance with a bag or weigh boat and weigh the shed (&#177; 0.01 g). 
		NOTE: The mass precision is determined by the precision of the balance. Shed skin mass is the standardization factor for extracted skin lipid mass (see below) and significantly covaries with extracted lipid mass.</li>
		<li>Separate the shed into smaller (5 cm2) pieces and add them to a sealable glass container with a hexane-compatible lid (e.g., a glass mason jar with a metal lid or a lab flask with a PTFE lid). Decant enough hexane into the container to fully submerge the shed skin pieces. Seal the container. 
		CAUTION: Hexane is flammable, a respiratory irritant, and is associated with several short- and long-term health hazards. Procedures involving hexane are performed in a fume hood (laboratory) or outdoors (field) while wearing appropriate personal protective equipment (PPE) (e.g., splash goggles, chloroprene gloves, long sleeves, close-toed shoes).</li>
		<li>Label the container(s) with a pencil or solvent-resistant pen. Leave the container(s) in the fume hood at room temperature overnight or up to 24 h.</li>
		<li>Remove the shed pieces using clean metal forceps or tongs. Shake the pieces to retain any remaining hexane in the container. Allow the skin pieces to dry on paper towels; then, discard them. If multiple extractions are being performed, clean the tongs/forceps between each sample. To clean the tongs/forceps, rinse them in ~50 mL of hexane in a beaker.</li>
		<li>If the extract is not to be used immediately, decant or pipette the extract into a glass vial of appropriate volume, seal it with a PTFE-lined cap, label it, and store it at -20 &#176;C. 
		CAUTION: Because the extract contains hexane, store the vials in an explosion-proof freezer.</li>
	</ol>
	</li>
	<li>Dead whole animal extraction
	<ol>
		<li>Record the snout-vent length (SVL; in centimeters) and mass (in grams) of the animal. If the total lipid or pheromone production per unit of skin surface area is to be determined, use a tailor&#8217;s tape measure to obtain the maximum body circumference (in centimeters).</li>
		<li>For the extraction, choose a container that has a diameter that is 1/3 of the length of the animal. Position the carcass securely at the bottom of the container with the head and cloaca on top. Decant sufficient hexane into the container to maximize the submerged surface area of the body. 
		NOTE: If the head or cloaca become submerged for any amount of time in extraction, take note.</li>
		<li>Secure the lid, label the container, and soak it in a fume hood at room temperature overnight or up to 24 h.</li>
		<li>When removing the carcass, use clean metal forceps or tongs. Retain the residual hexane on the carcass in the container by allowing it to drip from the body, not from the head or tail. Seal the container.</li>
		<li>If the extract is not to be used immediately, decant the extract or pipette it into a glass vial of appropriate volume, seal it with a PTFE-lined cap, label it, and store it at -20 &#176;C.</li>
	</ol>
	</li>
</ol>
2. Lipid Mass Determination
NOTE: The extracted lipid mass can be determined in one of two ways: with a glass vial or with a round-bottom flask, using a rotary evaporator.
<ol>
	<li>Determine the extracted lipid mass via the glass vial method.
	<ol>
		<li>Use a preweighed vial of sufficient size (7 mL, 22 mL, 50 mL, etc.). Include the cap and the label in the total mass, or always weigh the vial without cap and label (markings on the label also add mass). Place the label on the neck of the flask to avoid water contact. 
		NOTE: Evaporation in glass vials is efficient if the researcher has access to a gas manifold system where multiple vials can be evaporated simultaneously under an N2 stream.</li>
		<li>Transfer the extract to the vial, using a glass pipette with a rubber bulb or, for large-volume extracts, an electronic pipette controller with a disposable 10 mL glass pipette. Rinse the container with ~3 mL of hexane and transfer to the vial as well.</li>
		<li>Evaporate the sample under a gentle N2 stream. Tilt the vial at an angle to enable a maximum solvent surface area. Condensate will form on the outside of the vial as the hexane evaporates. 
		NOTE: Rings of lipid will form in the vial as the hexane evaporates, so periodically swirl the extract.</li>
		<li>Evaporate the sample to dryness; then, reweigh. Record the total lipid yield. 
		NOTE: For analysis across different groups, standardize the lipid mass either to shed mass (lipid mass [in grams] divided by shed mass [in grams] x 100 yields the percent lipid mass of the shed) or to the animal&#8217;s SVL (lipid mass [in milligrams] divided by SVL [in centimeters]; yields the lipid mass per unit length). Larger animals produce more lipid, and many species are strongly sexually dimorphic, which imposes significant bias in the data.</li>
	</ol>
	</li>
	<li>Determine the extracted lipid mass via the rotary evaporator.
	<ol>
		<li>For a faster evaporation per individual sample, transfer the extract to a preweighed round-bottom flask and evaporate it using a rotary evaporator.
		<ol>
			<li>If particulates are noticeable in the extract, filter the sample by placing a filter paper cone in the neck of the flask; then, transfer the extract to the flask and allow it to gravity filter. Dispose of the filter paper after the full extract is transferred. 
			NOTE: Transfer the sample volume (up to ~80% flask volume) before rotary evaporation. Any bubbling of the extract into the condenser of the rotary evaporator causes contamination and requires the condenser to be cleaned. A bump trap can be placed between the flask and the neck of the condenser if bubbles or &#8220;bumping&#8221; occur in most samples.</li>
		</ol>
		</li>
		<li>Turn on the power to the rotary evaporator and water bath (50 &#176;C; lower than the solvent boiling point). Turn on the cold-water flow to the condenser. 
		NOTE: The condenser of the rotary evaporator is connected to either a circulating chiller or a cold-water spigot venting to the drain. The flow rate can be slow if the water is cooler than ambient, to condense the solvent vapor leaving the flask and entering the condenser.</li>
		<li>Turn on the vacuum source (water vacuum or pump). Ensure the vacuum pressure is sufficient to hold the flask to the neck of the condenser. Open the vent at the end of the condenser before connecting the flask. Slide the flask onto the neck of the condenser, close the vent to seal, and ensure the flask cannot disconnect from the condenser when the flask is released.</li>
		<li>Lower the flask until ~50% is submerged in the bath. Start the rotation of the flask at medium speed. If the vacuum, speed, condenser flow, and bath temperature are optimal, the solvent vapor leaving the flask will condense on the coil and drip into the recovery flask.
		<ol>
			<li>If the sample boils (e.g., large bubbles, rapid gassing), immediately reduce the vacuum and/or speed of the rotary evaporator. If the boiling continues, turn off the flask rotation, turn off the vacuum, raise the flask from the bath, and release the vacuum seal. Repeat steps 2.2.3 and 2.2.4. 
			NOTE: If no solvent is collecting in the recovery flask but the extract is obviously evaporating, the vacuum is most likely nonoptimal and must be readjusted.</li>
		</ol>
		</li>
		<li>Evaporate the sample under the vacuum until ~2 mL of solvent remains in the flask (large-volume extracts), or, if a preweighed flask is being used, evaporate until a bead of liquid with a &#60;1 cm diameter is visible in the bottom of the flask. Turn off the rotation and vacuum; then, raise the flask out of the bath.</li>
		<li>Hold the flask neck as the vacuum seal is released; then, twist the neck to slide it from the condenser. If a large volume flask is being used, swirl the condensed extract in the flask to dissolve visible lipids; then, transfer the solution via pipette to a smaller-volume, preweighed flask. Add 3 mL of hexane to rinse the large flask, swirl it, pipette it to the smaller flask, and evaporate again (steps 2.2.3 - 2.2.5).</li>
		<li>The bead of liquid in the extract will solidify as the hexane evaporates. Once dry, allow it to reach room temperature. Lipids will form a translucent, white to yellow wax in the flask (~5 min). Weigh the flask to obtain the final mass. 
		NOTE: Depending on the nature of the lipids extracted, they will have either solid (e.g., wax) or semisolid (e.g., crude oil) properties, especially when fractionated lipids are evaporated (see below).</li>
	</ol>
	</li>
	<li>Solubilize the lipids in the recorded volume of hexane to yield &#8805;1 mg of lipid per 1 mL of hexane. The working volume for progressing to chromatography is ~5 mL. If transferring from flask to vial, retain 2 mL of the total volume to rinse the flask after transferring the majority of the extract to the vial.</li>
	<li>Label the vials, seal them with PTFE-lined caps, and store them at -20 &#176;C.</li>
</ol>
3. Column Chromatography
NOTE: To separate unknown compounds based on polarity into specific fractions, extracted lipid mass can be added to prepared liquid chromatography columns and fractionated using standard elution.
<ol>
	<li>Preparation of the column
	<ol>
		<li>Depending on the lipid mass in the extract, use either a large- or a small-volume glass chromatography column with a Teflon stopcock. The column is either fitted with or fused to a fixed-volume reservoir (500 mL for a large column; 250 mL for a small column). Henceforth, this protocol only refers to a large-volume chromatography column fused to a reservoir. Thoroughly clean any new glassware and parts to be used in chromatography as described in section 4; then, rinse them with hexane or another nonpolar solvent.</li>
		<li>Fold a piece of fiberglass wool (~14 cm in length [L] x 4 cm in width [W]) repeatedly until a square of ~4 cm x 4 cm is formed. Use a wooden dowel rod longer than the column to position the fiberglass at the bottom of the column.</li>
		<li>Secure the column in a hood to a standard ring stand with two clamps (e.g., swivel or modular), one above the stopcock and one beneath the neck of the reservoir. Level the column. Position the column at a height to allow sufficient working distance for the 500 mL beaker to fit easily under the column. Open the stopcock.</li>
		<li>Pour washed and dried sand into the column, until a ~3 cm of sand rests above the fiberglass. Place black or dark paper under the column and tap it gently. If sand falls from the column with every tap, the fiberglass barrier is insufficient. Repeat steps 3.1.2 - 3.1.4. 
		NOTE: Use an unfolded paperclip taped to the end of a dowel rod to fetch the fiberglass from the bottom.</li>
		<li>Place the 500 mL beaker under the column. Slowly decant ~25 mL of hexane from a 100 mL beaker or graduated cylinder into the column reservoir to wet the sand. Close the stopcock when there is ~0.5 cm of hexane above the sand.</li>
		<li>Weigh out neutral alumina. For each small column, use ~50 g; ~175 g for each large column. Pour the alumina into a 1 L Erlenmeyer flask. Limit 400 g of alumina per 1 L flask.</li>
		<li>To activate the alumina (activity III), pipette deionized water of a volume equal to 6% of the alumina mass (i.e., for 100 g of alumina, add 6 mL of water). Add the water as drops throughout the alumina.</li>
		<li>Cover the flask with aluminum foil or a cork. Vigorously swirl (do not shake) to evenly disperse the charge. Continue until no visible clumps remain. 
		NOTE: The flask will warm as the water reacts with the alumina, which is to be expected.</li>
		<li>Add hexane until the alumina is completely covered, with ~0.5 cm of hexane above the alumina. Swirl the flask to form a slurry.</li>
		<li>Place a vented funnel in the reservoir of the column and a 500 mL glass beaker beneath the column. Open the stopcock. Swirl the alumina and steadily pour it into the column. Ensure the alumina is settling evenly in the column and no large bubbles or cracks are forming in the alumina column. Gently tap the side of the column to evenly settle the alumina. 
		NOTE: Additional hexane must be added for additional pours, to maintain the slurry. The hexane collecting in the beaker under the column can be reused if the glass beaker was clean at the start.</li>
		<li>The column is formed when the top of the alumina is stable and ~4 cm beneath the neck of the column at the base of the reservoir. Use a pipette to rinse the inside of the reservoir with hexane for residual alumina. Using a funnel, gently add a second layer of sand on top of the alumina, to ~1 cm beneath the reservoir. 
		NOTE: Hexane will flow from the column as the stopcock remains open. Do not let the column dry out. If the column dries out, the process must begin again, starting at step 3.1.2. The protocol can be stopped here if the columns are prepared a day before fractionation. Firmly place a cork in the top of the reservoir or cover it tightly with foil. Fill the reservoir with ~100 mL of hexane. Tighten the stopcock.</li>
	</ol>
	</li>
	<li>Fractionation of the lipid extract 
	NOTE: Regardless of column size, fractions of lipid extract can be collected individually and pooled based on their fraction polarity or discarded completely if they do not contain any known/identified target compounds. Rounds of replicate elution (n = 3 volumes) are passed through the column to ensure the sufficient elution of the lipids. Follow Table 1 for large-column elution (with an extract mass &#62;30 mg) or small-column elution (with an extract mass &#60;30 mg). A tailored elution protocol for isolating only methyl ketones is in Table 2.
	<ol>
		<li>Either remove the remaining hexane at the top of the column, using a large-volume pipette, or allow the hexane to drip out into a clean beaker. Leave ~3 mL of hexane above the sand at the top of the column. 
		NOTE: The collected hexane is pure if it only contacted clean glassware and can be recycled in the first fraction.</li>
		<li>Transfer the lipid extract to the column, using a long glass pipette. Slowly pipette the extract to avoid disturbing the sand layer. Rinse the extract vial or flask with ~5 mL of hexane and transfer it to the column. 
		NOTE: If the extract was stored at -20 &#176;C, the lipids will be precipitated. Warm the vial until no more precipitate is visible.</li>
		<li>Open the stopcock and allow the sample to load into the column. If the extract has a large mass (&#62;30 mg), a yellowish band may be visible in the alumina, just below the sand at the top. Collect the flow through in a waste beaker as this hexane is no longer clean. Close the stopcock when ~3 mL remains on top of the sand. 
		CAUTION: The lipid in the extract, now bound to the alumina and column, cannot dry out or the sample will be lost.</li>
		<li>Place a preweighed and labeled round-bottom flask (100 mL, 250 mL, or 500 mL) beneath the column before pouring the first fraction. Fractions to be discarded can be collected in a common glass container.</li>
		<li>Prepare the first fraction (100% hexane:0% diethyl ether [heretofore, &#8220;ether&#8221;]) in a graduated cylinder. If preparing fractions in advance, cover with foil or stopper with cork. 
		NOTE: Fractions progress in polarity; therefore, the cylinder does not need to be rinsed between fractions.</li>
		<li>Add the first fraction to the reservoir by pouring via a vented glass funnel directed to a side of the reservoir to avoid disturbing the sand layer. Open the stopcock to start the elution. Close the stopcock when ~3 mL of hexane remains above the sand at the top of the column. 
		NOTE: Never stop an elution within an individual fraction by closing the stopcock before the majority of the eluate has been collected. Between fractions, do not leave the stopcock closed for longer than ~1 h because delays can alter the quality and repeatability of the elution.</li>
		<li>Repeat steps 3.2.4 - 3.2.6 for fractions 2 and 3. Collect the fractions in appropriately sized flasks that allow headspace for rotary evaporation, especially if the fractions are being pooled.</li>
		<li>Prepare a fourth fraction (2% ether) and add it to the reservoir. Place the next flask under the column, open the stopcock, and collect the fourth fraction. Prepare a fifth fraction; then, continue as needed. 
		NOTE: It is possible to evaporate the first fraction(s) via rotary evaporation while collecting successive fractions.</li>
		<li>For preparing fractions to be used in GC-MS analyses, obtain a fraction mass using a 0.01 or 0.1 mg precision balance. Solubilize the lipid fractions to yield 1 mg of lipid per 1 mL of hexane.</li>
	</ol>
	</li>
</ol>
4. Cleaning
<ol>
	<li>Leave the stopcock open and invert the column in the waste beaker. The alumina and sand will run out of the column; alternatively, shake to expedite the process. Use a dowel rod to fetch the fiberglass wool if it is stuck (avoid scratching glass) or blow it out with an N2 stream.</li>
	<li>Dissemble and clean all glassware, using laboratory-grade detergent in hot water in a plastic tub with a glassware brush (with hair or plastic bristles). Wash 3x. Rinse well with plenty of warm water until the glass is no longer slick to the touch.</li>
	<li>Rinse&#160;the glassware and tools 3x with deionized water. Place them on a rack to air-dry. To accelerate the drying, add a small volume of acetone (3 mL) to the glassware, swirl, and allow it to air-dry or run it under an N2 stream.</li>
</ol>

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The authors have nothing to disclose.

The extraction of skin lipids in reptiles can be applied to living or dead skin, in addition to shed skin, which offers versatility in the experimental application of this technique. Further, extractions of skin lipids can be done in the field, to enable a dynamic application of the method to a wide range of biologists2,13. Extraction of skin lipids is simple; therefore, it is easy to scale up extractions as needed per experiment or design, and practitioners need not have significant expertise to execute the methods. The only limiting factors for scaling up are the availability of fume hood space, an abundance of clean, sealable glassware, and solvent storage space.
Skin lipid extract fractionation can be tailored to a researcher&#39;s needs and, therefore, has similar flexibility to lipid extraction. For example, neutral lipids can be eluted and then discarded, to result in target fractions that may purify compounds of interest or simplify bioassays. Fractionation can be performed at multiple scales within and across lipid samples. For example, multiple columns can be run simultaneously to make the process more efficient. Or, only a portion of a total lipid extract can be fractionated on a small column to, thus, spare reagents and time. Fractionation is primarily limited by the mass of the total lipid extract and the precision of the equipment available to the researcher. For example, if the researcher has a balance with a 10.0 mg precision, the determination of the fraction mass and, therefore, the accuracy of the sample preparation for the GC-MS analysis is significantly, if not completely, impeded. The same is true for the glassware. If the researcher has a large-volume column for fractionation but has a small total lipid mass to separate, the elution or separation of the compounds will progress but will require a significant wastage of solvents, reagents, time, and potentially, the target compounds themselves.
It is advised to perform a quality control check before determining the elution scheme, as seen in Table 2, and decide what fractions may be discarded. To confirm the elution of the desired lipids, a column can be run where each fraction, 1 - 15, is collected individually and then analyzed using GC-MS. In Figure 3, representative gas chromatograph traces show that methyl ketones from garter snakes only elute from the column in a specific fraction. By performing this quality control step, a modified elution scheme can be developed for a given species to ensure the maximum yield of the compounds of interest. Changes in the materials, such as the supplier or lot of the alumina or the age of the diethyl ether, will absolutely result in differences in elution that should be controlled for by performing a quality control test.
The techniques described are limited chiefly by the chemical nature of the cues that can be obtained. Primarily, these methods only allow researchers to isolate and separate long-chain lipids from the skin of reptiles. Many species of reptiles use airborne and/or proteinaceous cues as chemical signals, and the described methods are incompatible with isolating said cues. Further, nonpolar solvents will not extract aqueous cues from the surfaces of reptiles or sources of cue deposition (e.g., cage water, fecal matter, aquatic substrate) that may indeed contain abundant chemical signals. Appropriate methods for capturing these types of cues are available to researchers (e.g., solid-phase microextraction [SPME] for volatile cues and high-performance liquid chromatography [HPLC] for aqueous cues), although, like the methods described above, there is a technical learning curve.
Most importantly, the utility of the final chemical mixture to the researcher should guide the methods used. For example, if a researcher wants to know if a male focal animal can distinguish between the cues produced by male vs. female conspecifics in a targeted bioassay, extraction is the only method needed2,3. If the identification of sexually dimorphic compounds is the goal, however, the extract ought to be purified, to enable greater confidence in assigning identifications to specific molecules or groups of molecules via chemical analysis1,6,9,11. However, to even conduct chromatography with a lipid source, a significant mass of starting extract is required so that measurable fraction masses can be obtained; otherwise, the pooling of samples can be pursued but is not optimal14.
Future developments of this protocol include measures to utilize and adapt the procedure for more reptilian species. Additional noninvasive methods of extracting skin lipids are also being developed.

Reptiles produce lipids in the epidermis, either directly from skin cells or from discrete glands that are used in social communication, such as mate assessment and tracking, territoriality, and intra- and interspecific recognition1,2,3,4. The isolation of these skin lipids has utility in research focused on evolutionary patterns and mechanisms of chemical communication, in addition to understanding the waterproofing role of lipids in the evolution of terrestrial life2,3,4. Further, many reptiles, especially squamates (lizards, snakes), are invasive species of concern in sensitive ecosystems, and the development of pheromone-based lures to improve trapping and removal is ongoing5,6. The impermeability of reptile skin facilitates the extraction of the lipids present to obtain relatively pure extractions of a potentially robust source of chemical signals. The principle steps for quantifying reptile skin lipids in the described protocol include extraction, total lipid determination, and fractionation via column chromatography1,6,7. The methods have been used routinely as they yield bioactive isolates that explain much about mate choice and selection, especially in snakes2.
Skin lipids can be extracted from either living skin, shed skin, or dead whole reptiles, using nonpolar or polar organic solvents1,7,8,9. It should be noted that museum specimens stored in solvents such as ethanol are not optimal for the extraction of skin lipids, and only fresh or freshly frozen carcasses should be considered as possible sources for extraction. Skin lipids are inert, which makes them stable on the surface of the skin and easy to extract7. In their signaling roles in reptile ecology, skin lipid cues are often deposited in harsh environments, but because of their robust chemical properties, such cues can retain their information value over long periods of time10,11,12. The extraction process solubilizes the lipids, using a nonpolar solvent (e.g., hexane, benzene, toluene) over an hours-long soak, followed by the evaporation of the solvent, to leave a measurable mass of lipid extract7,8. Skin lipids are highly miscible in nonpolar solvents, and a wide range of hydrocarbons can be extracted from a similarly diverse array of sources.
Fractionation is more laborious than extraction but serves to separate the total lipid extract into specific fractions via column chromatography, to aid in the purification and possible identification of the compounds therein1,6,7,8. The total lipid extract is bound to a substrate-based column, and then, individual eluates (&#34;fractions&#34;) of solvent at specific volumes are passed sequentially through the column to elute sets of compounds from the lipid mixture that have a common polarity6,7,8. In lipid chromatography, the fractions progress in polarity at some standardized sequence by increasing the relative amount of polar solvent (e.g., diethyl ether) in nonpolar solvent (typically expressed as a percentage: 0%, 2%, 4% ether, etc.)6,7,8. Though methods like thin-layer chromatography (TLC) can be used to separate lipids in a mixture and are simpler, column chromatography is preferred because it uses a closed system, is easy to control, can separate more concentrated mixtures, and is compatible with multiplexing for efficiency. In this manuscript, we describe several methods for extracting skin lipids of reptiles and, then, provide a standard protocol for isolating different sets of compounds based on polarity, using traditional column chromatography. In many research projects involving the isolation of chemical cues, the ultimate goal is to effect change in the receivers exposed to those cues. Whole lipid extracts or specific fractions can, then, be used in bioassays to determine any biological activity elicited by the compounds therein1,2,6,7. In basic biological research, for example, bioassays using specific fractions can reveal to researchers that a purified source of pheromones has been isolated, and then, methods for the identification of the target compounds can be pursued. From a wildlife management perspective, identification may not be the goal, and instead, the active fraction could be used in the field to attract conspecifics to traps or inhibit mate tracking in the nonnative habitat13,14.

<table>
	<tbody>
		<tr>
			<td>Powder-free Chloroprene Gloves</td>
			<td>Microflex</td>
			<td>NEC-288</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.2 &#34;gloves&#34;)</td>
		</tr>
		<tr>
			<td>Ohaus Adventurer Precision Balance</td>
			<td>Ohaus</td>
			<td>AX622</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.3 &#34;balance&#34;)</td>
		</tr>
		<tr>
			<td>Freund Container Ball 16oz Mason Jar &#38; Lid</td>
			<td>Ball</td>
			<td>NC9661590</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.5 &#34;mason jar&#34;)</td>
		</tr>
		<tr>
			<td>Hexane, Mixtures of Isomers</td>
			<td>Sigma-Aldrich</td>
			<td>650544</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.6 &#34;hexane&#34;)</td>
		</tr>
		<tr>
			<td>Hi/Lo Write-On Temperature Tape</td>
			<td>Electron Microscopy Sciences</td>
			<td>5029927</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.8 &#34;tape&#34;)</td>
		</tr>
		<tr>
			<td>Single-Neck Round-Bottom Flask, capacity 500 mL</td>
			<td>Sigma-Aldrich</td>
			<td>Z414514</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.2.4 &#34;500 mL&#34;)</td>
		</tr>
		<tr>
			<td>Single-Neck Round-Bottom Flask, capacity 100 mL</td>
			<td>Sigma-Aldrich</td>
			<td>Z414492</td>
			<td>See &#34;3.2 Fractionating&#34; (step 3.2.4 &#34;100 mL&#34;)</td>
		</tr>
		<tr>
			<td>Cork Flask Support Ring</td>
			<td>Sigma-Aldrich</td>
			<td>Z512419</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.2.1 &#34;cork support ring&#34;)</td>
		</tr>
		<tr>
			<td>Accu-jet Pro Pipette Controller</td>
			<td>Sigma-Aldrich</td>
			<td>Z671533</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.1.3 &#34;electric pipette controller&#34;)</td>
		</tr>
		<tr>
			<td>Disposable Individually Wrapped Glass Serological Pipets, 10 mL</td>
			<td>Pyrex</td>
			<td>13-666-7E</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.1.3 &#34;10 mL pipette&#34;)</td>
		</tr>
		<tr>
			<td>Rotavapor R II</td>
			<td>Buchi</td>
			<td>2422A0</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.2.1 &#34;rotary evaporator&#34;)</td>
		</tr>
		<tr>
			<td>Elliptical Bump Trap</td>
			<td>Chemglass Life Science</td>
			<td>501215241</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.2.1 &#34;bump trap&#34;)</td>
		</tr>
		<tr>
			<td>7 mL Vials, Screw Top, Clear Glass</td>
			<td>Supelco</td>
			<td>27151</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.11 &#34;7 mL vial&#34;)</td>
		</tr>
		<tr>
			<td>7 mL Vial Screw Cap, Solid Top with PTFE Liner</td>
			<td>Supelco</td>
			<td>27152</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.11 &#34;cap&#34;)</td>
		</tr>
		<tr>
			<td>22 mL Vials, Screw Top, Clear Glass</td>
			<td>Supelco</td>
			<td>27173</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.11 &#34;22 mL vial&#34;)</td>
		</tr>
		<tr>
			<td>22 mL Vial Screw Cap, Solid Top with PTFE Liner</td>
			<td>Supelco</td>
			<td>27174-U</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.11 &#34;cap&#34;)</td>
		</tr>
		<tr>
			<td>Excellence XS Analytical Balance</td>
			<td>Mettler-Toledo</td>
			<td>XS205DU</td>
			<td>See &#34;2. Extraction&#34; (step 2.1.2.1 &#34;balance&#34;)</td>
		</tr>
		<tr>
			<td>5 3/4&#34; Disposable Glass Pipette</td>
			<td>Fisherbrand</td>
			<td>NC0418555</td>
			<td>See &#34;1.1 Shed Extraction set-up&#34; (step 1.1.11 &#34;pipette&#34;)</td>
		</tr>
		<tr>
			<td>Chromatography column with PTFE Stopcock Assembly</td>
			<td>Kimble-Chase</td>
			<td>17810-19300</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.1 &#34;small glass column&#34;)</td>
		</tr>
		<tr>
			<td>Cast-Iron L-Shaped Base Support Stands</td>
			<td>Fischerbrand</td>
			<td>11474207</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.1 &#34;support stand&#34;)</td>
		</tr>
		<tr>
			<td>3-Prong Dual Adjust Nickel-Plated Zinc Clamp</td>
			<td>Troemner</td>
			<td>2300203</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.1 &#34;clamps&#34;)</td>
		</tr>
		<tr>
			<td>Clamp Regular Holder</td>
			<td>Fischerbrand</td>
			<td>05754Q</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.1 &#34;clamp holder&#34;)</td>
		</tr>
		<tr>
			<td>Sand,Washed and Dried</td>
			<td>Macron Fine Chemical</td>
			<td>MK-7062-212</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.5 &#34;sand&#34;)</td>
		</tr>
		<tr>
			<td>Alumina, Neutral</td>
			<td>Sorbtech</td>
			<td>15740-5</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.7 &#34;alumina&#34;); only known manufacturer in the US</td>
		</tr>
		<tr>
			<td>Narrow-Neck Heavy-Duty Glass Erlenmeyer Flask, 1000mL</td>
			<td>Pyrex</td>
			<td>4980-1L</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.1.6 &#34;Erlenmeyer flask&#34;)</td>
		</tr>
		<tr>
			<td>Single-Neck Round-Bottom Flask, capacity 250 mL</td>
			<td>Sigma-Aldrich</td>
			<td>Z100684</td>
			<td>See &#34;3.1 Preparing the column&#34; (step 3.2.4 &#34;250 mL round bottom flask&#34;)</td>
		</tr>
		<tr>
			<td>Calibrated Chromatography Column with Solvent Reservoir</td>
			<td>Sigma-Aldrich</td>
			<td>Z560553</td>
			<td>See &#34;3.2 Preparing the column&#34; (step 3.2.1 &#34;large glass column&#34;)</td>
		</tr>
		<tr>
			<td>Ethyl Ether Anhydrous</td>
			<td>Fisher Chemical</td>
			<td>E138500</td>
			<td>See &#34;3.2 Fractionating&#34; (step 3.2.5 &#34;ether&#34;)</td>
		</tr>
		<tr>
			<td>Alconox Detergnet</td>
			<td>Sigma-Aldrich</td>
			<td>242985</td>
			<td>See &#34;4. Cleaning&#34; (step 4.2 &#34;Alconox&#34;)</td>
		</tr>
		<tr>
			<td>Acetone (Certified ACS)</td>
			<td>Fisher Chemical</td>
			<td>A18P-4</td>
			<td>See &#34;4. Cleaning&#34; (step 4.4 &#34;acetone&#34;)</td>
		</tr>
	</tbody>
</table>

chemical isolation, quantification, and separation of skin lipids from reptiles

Reptiles signal to conspecifics using lipids in their skin, primarily to enable mate tracking and assessment. The isolation of these lipids has utility in research focused on evolutionary patterns and mechanisms of chemical communication, in addition to understanding the waterproofing role of lipids in the evolution of terrestrial life. In an applied approach, such skin-based cues have potential use for wildlife managers dealing with invasive species. The main steps for quantifying reptile skin lipids in the protocol presented here include extraction, total lipid determination, and fractionation via column chromatography, the latter process resulting in purified eluates of compounds which can then either be analyzed to assign compound identifications (e.g., gas chromatography-mass spectrometry [GC-MS]) and/or used directly in more refined bioassays. Skin lipids can be extracted from living skin, shed skin, or dead whole animals, using nonpolar organic solvents (e.g., hexane, benzene, toluene). Extraction solubilizes the lipids and, then, the solvent can be evaporated to yield a measurable lipid-only extract. Fractionation involves the separation of the total lipid extract into specific eluates via traditional column chromatography. The total lipid extract is first bound to a substrate-based column (e.g., alumina) and, then, individual eluates (&#34;fractions&#34;) of solvent at specific volumes are passed sequentially through the column to elute sets of compounds from the lipid mixture based on common polarity. The fractions progress in polarity at a standardized sequence by increasing the relative amount of polar solvent (e.g., diethyl ether) in nonpolar solvent. In this manuscript, we describe several methods for extracting skin lipids of reptiles and, then, provide a standard protocol for isolating different sets of compounds based on polarity, using traditional column chromatography. Whole lipid extracts or specific fractions can, then, be used in bioassays to determine any biological activity elicited by the compounds therein.

Following extraction, the total lipid mass is the first type of data that can be acquired through the protocol presented here. However, total lipid mass values should never be analyzed without some attempt to standardize the obtained values. Several approaches can be used, but we recommend either standardizing the extracted lipid mass to the animal&#39;s SVL (in centimeters) or to the mass of the shed skin that was extracted. The former results in a lipid-mass-per-length value and the latter will be a proportion of source mass. The reason for the standardization is that larger animals naturally produce more skin lipids because they have a greater total skin surface area. Figure 1A exemplifies this association, where the extracted skin lipid mass scales linearly with the mass of shed skin extracted. Once standardized to the total shed skin mass, this linear relationship is completely removed (Figure 1B).
Following fractionation, the same standardization approach can be used with the masses of the individual fractions (Figure 2). In this sample data set, each fraction is not contributing equally to the total extracted lipid mass: neutral lipids (fractions 1 - 3) are the dominant set of compounds by mass proportion compared to each set of more polar lipids (fractions 4 - 6, 7 - 9, and 10 - 12).
<img alt="Figure 1" class="xfigimg" src="/files/ftp_upload/59018/59018fig1.jpg" /> 
Figure 1: Relationships between extracted lipid mass and input material. (A) In reptiles, the relationship between the total shed skin mass and the extracted skin lipid mass is positively correlated (P &#60; 0.001). (B) When the extracted skin lipid mass is standardized to the total shed mass (the lipid mass divided by the shed mass), this relationship is no longer present (P = 0.46). <a href="https://www.jove.com/files/ftp_upload/59018/59018fig1large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 2" class="xfigimg" src="/files/ftp_upload/59018/59018fig2.jpg" /> 
Figure 2: Standardized fraction masses following elution. Using column chromatography, skin lipid extracts can be eluted into fractions, based on compound polarity. The fraction mass is, then, expressed as a proportion of the total lipid extract (fraction mass [in milligrams] divided by total lipid extract mass [in milligrams) to determine differences between fractions or experimental groups8. The bars represent the means. The top error is SEM; the bottom error is 95% CI. Individual data points are provided for clarity. <a href="https://www.jove.com/files/ftp_upload/59018/59018fig2large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 3" class="xfigimg" src="/files/ftp_upload/59018/59018fig3.jpg" /> 
Figure 3: Representative gas chromatographs of methyl ketone fractions. (A) With the proper elution, methyl ketones are the most abundant compounds in fraction 7 from Table 2 and can be seen as couplets of peaks (retention time = 24 - 34 min). (B) Fraction 6 from Table 2, however, only yields nontarget compounds. This same result can occur when the polar solvent used in the mobile phase is expired or if the column is stopped for long periods of time (&#62;1 h) between fractions. Note the difference in molecular abundance between the two traces. <a href="https://www.jove.com/files/ftp_upload/59018/59018fig3large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<table border="1" fo:keep-together.within-page="1" fo:keep-with-next.within-page="always">
	<tbody>
		<tr>
			<td>Fraction</td>
			<td>Hexane (mL)</td>
			<td>Diethyl ether (mL)</td>
		</tr>
		<tr>
			<td>1,2,3</td>
			<td>100 [30]</td>
			<td>0 [0]</td>
		</tr>
		<tr>
			<td>4,5,6</td>
			<td>98 [29.4]</td>
			<td>2 [0.6]</td>
		</tr>
		<tr>
			<td>7,8,9</td>
			<td>96 [28.8]</td>
			<td>4 [1.2]</td>
		</tr>
		<tr>
			<td>10,11,12</td>
			<td>92 [27.6]</td>
			<td>8 [2.4]</td>
		</tr>
		<tr>
			<td>13,14,15</td>
			<td>84 [25.2]</td>
			<td>16 [4.8]</td>
		</tr>
	</tbody>
</table>
Table 1: Standard elution volumes for skin lipid fractionation. Solvent volumes and percentages are given for both large-volume (e.g., 250 mL) and [small-volume] (e.g., 100 mL) chromatography columns using alumina (activity III). Hexane is the carrier solvent; diethyl ether is the mobile phase.
<table border="1" fo:keep-together.within-page="1" fo:keep-with-next.within-page="always">
	<tbody>
		<tr>
			<td>Fraction&#160;</td>
			<td>Hexane (mL)</td>
			<td>Diethyl ether (mL)</td>
			<td>Notes</td>
		</tr>
		<tr>
			<td>1, 2, 3</td>
			<td>30</td>
			<td>0</td>
			<td>elute; do not collect&#160;</td>
		</tr>
		<tr>
			<td>4, 5</td>
			<td>28.8</td>
			<td>1.2</td>
			<td>elute; do not collect</td>
		</tr>
		<tr>
			<td>6, 7, 8</td>
			<td>28.8</td>
			<td>1.2</td>
			<td>collect individually; majority of methyl ketone mass will be in fraction 7; GC-MS quality control checks should be run on 6 and 8 to ensure proper elution of the ketones &#160;</td>
		</tr>
	</tbody>
</table>
Table 2: Modified elution scheme for garter snake methyl ketones. These volumes are for use with a small-volume chromatography column and with the brand of alumina currently available. The eluted fraction positive for methyl ketones has a strong bioactivity in field assays with wild, courting male garter snakes1,7. To confirm the presence of methyl ketones in the target fractions, samples can be diluted to 1 mg/mL and analyzed via GC-MS. Figure 3 provides representative chromatograms for both positive and negative results following elution.

Watch this Scientific Journal Video about Chemical Isolation, Quantification, and Separation of Skin Lipids from Reptiles at JoVE.com

Chemical Isolation, Quantification, and Separation of Skin Lipids from Reptiles

Aislamiento químico, cuantificación y separación de los lípidos de la piel de los Reptiles

In reptiles, skin lipids from conspecifics are crucial for sexual signaling, with potential use in invasive species management. Here, we describe protocols for extracting skin lipids from shed skin or whole animals, determining and analyzing the total lipid mass, and separating the lipids using fractionation via column chromatography.

Reptiles signal to conspecifics using lipids in their skin, primarily to enable mate tracking and assessment. The isolation of these lipids has utility in ...

chemical-isolation-quantification-separation-skin-lipids-from

Research

JoVE Journal

Environment

10.8K vistas.  James Madison University. Nuestro protocolo permite a los investigadores aislar las moléculas de señalización bioactiva utilizadas por los reptiles en la comunicación química. Así como la separación y purificación de estos compuestos para pruebas adicionales, o incluso la identificación. Usando este método, los investigadores pueden obtener una fuente de señales químicas y luego extraerlas para su cuantificación o uso de bioensayo de forma aislada.Demostrando el procedimiento hoy estará Holly Ruck...

Video: Chemical Isolation, Quantification, and Separation of Skin Lipids from Reptiles

Integrated Field Lysimetry and Porewater Sampling for Evaluation of Chemical Mobility in Soils and Established Vegetation

Potentially toxic chemicals are routinely applied to land to meet growing demands on waste management and food production, but the fate of these chemicals is often not well understood. Here we demonstrate an integrated field lysimetry and porewater sampling method for evaluating the mobility of chemicals applied to soils and established vegetation. Lysimeters, open columns made of metal or plastic, are driven into bareground or vegetated soils. Porewater samplers, which are commercially available and use vacuum to collect percolating soil water, are installed at predetermined depths within the lysimeters. At prearranged times following chemical application to experimental plots, porewater is collected, and lysimeters, containing soil and vegetation, are exhumed. By analyzing chemical concentrations in the lysimeter soil, vegetation, and porewater, downward leaching rates, soil retention capacities, and plant uptake for the chemical of interest may be quantified. Because field lysimetry and porewater sampling are conducted under natural environmental conditions and with minimal soil disturbance, derived results project real-case scenarios and provide valuable information for chemical management. As chemicals are increasingly applied to land worldwide, the described techniques may be utilized to determine whether applied chemicals pose adverse effects to human health or the environment.

Field lysimetry and porewater sampling allow researchers to evaluate the fate of chemicals applied to soils and established vegetation. The goal of this protocol is to demonstrate how to install required instrumentation and collect samples for chemical analysis during integrated field lysimetry and porewater sampling experiments.

Lysimetry Integrado de campo y toma de muestras de agua intersticial para la Evaluación de la Movilidad de Química en Suelos y Vegetación Establecido

Potentially toxic chemicals are routinely applied to land to meet growing demands on waste management and food production, but the fate of these chemicals ...

Investigación

Medio ambiente

Physical, Chemical and Biological Characterization of Six Biochars Produced for the Remediation of Contaminated Sites

The physical and chemical properties of biochar vary based on feedstock sources and production conditions, making it possible to engineer biochars with specific functions (e.g. carbon sequestration, soil quality improvements, or contaminant sorption). In 2013, the International Biochar Initiative (IBI) made publically available their Standardized Product Definition and Product Testing Guidelines (Version 1.1) which set standards for physical and chemical characteristics for biochar. Six biochars made from three different feedstocks and at two temperatures were analyzed for characteristics related to their use as a soil amendment. The protocol describes analyses of the feedstocks and biochars and includes: cation exchange capacity (CEC), specific surface area (SSA), organic carbon (OC) and moisture percentage, pH, particle size distribution, and proximate and ultimate analysis. Also described in the protocol are the analyses of the feedstocks and biochars for contaminants including polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), metals and mercury as well as nutrients (phosphorous, nitrite and nitrate and ammonium as nitrogen). The protocol also includes the biological testing procedures, earthworm avoidance and germination assays. Based on the quality assurance / quality control (QA/QC) results of blanks, duplicates, standards and reference materials, all methods were determined adequate for use with biochar and feedstock materials. All biochars and feedstocks were well within the criterion set by the IBI and there were little differences among biochars, except in the case of the biochar produced from construction waste materials. This biochar (referred to as Old biochar) was determined to have elevated levels of arsenic, chromium, copper, and lead, and failed the earthworm avoidance and germination assays. Based on these results, Old biochar would not be appropriate for use as a soil amendment for carbon sequestration, substrate quality improvements or remediation.

Biochar is a carbon-rich material used as a soil amendment with the ability to sustainably sequester carbon, improve substrate quality and sorb contaminants. This protocol describes the 17 analytical methods used for the characterization of biochar, which is required prior to large scale implementation of these amendments in the environment.

Física, química y caracterización biológica de seis biochars Producido para la Remediación de Sitios Contaminados

The physical and chemical properties of biochar vary based on feedstock sources and production conditions, making it possible to engineer biochars with ...

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.

El aislamiento físico de endosporas de muestras ambientales por Targeted lisis de las células vegetativas

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

Simultaneous DNA-RNA Extraction from Coastal Sediments and Quantification of 16S rRNA Genes and Transcripts by Real-time PCR

Real Time Polymerase Chain Reaction also known as quantitative PCR (q-PCR) is a widely used tool in microbial ecology to quantify gene abundances of taxonomic and functional groups in environmental samples. Used in combination with a reverse transcriptase reaction (RT-q-PCR), it can also be employed to quantify gene transcripts. q-PCR makes use of highly sensitive fluorescent detection chemistries that allow quantification of PCR amplicons during the exponential phase of the reaction. Therefore, the biases associated with &#39;end-point&#39; PCR detected in the plateau phase of the PCR reaction are avoided. A protocol to quantify bacterial 16S rRNA genes and transcripts from coastal sediments via real-time PCR is provided. First, a method for the co-extraction of DNA and RNA from coastal sediments, including the additional steps required for the preparation of DNA-free RNA, is outlined. Second, a step-by-step guide for the quantification of 16S rRNA genes and transcripts from the extracted nucleic acids via q-PCR and RT-q-PCR is outlined. This includes details for the construction of DNA and RNA standard curves. Key considerations for the use of RT-q-PCR assays in microbial ecology are included.

A protocol to quantify bacterial 16S rRNA genes and transcripts from coastal sediments via real-time PCR is provided. The methodology includes the co-extraction of DNA and RNA; preparation of DNA-free RNA; and 16S rRNA gene and transcript quantification via RT-q-PCR, including standard curve construction.

ADN-ARN simultánea extracción de los sedimentos costeros y cuantificación de 16S rRNA genes y las transcripciones de PCR en tiempo real

Real Time Polymerase Chain Reaction also known as quantitative PCR (q-PCR) is a widely used tool in microbial ecology to quantify gene abundances of ...

Methods of Soil Resampling to Monitor Changes in the Chemical Concentrations of Forest Soils

Recent soils research has shown that important chemical soil characteristics can change in less than a decade, often the result of broad environmental changes. Repeated sampling to monitor these changes in forest soils is a relatively new practice that is not well documented in the literature and has only recently been broadly embraced by the scientific community. The objective of this protocol is therefore to synthesize the latest information on methods of soil resampling in a format that can be used to design and implement a soil monitoring program. Successful monitoring of forest soils requires that a study unit be defined within an area of forested land that can be characterized with replicate sampling locations. A resampling interval of 5 years is recommended, but if monitoring is done to evaluate a specific environmental driver, the rate of change expected in that driver should be taken into consideration. Here, we show that the sampling of the profile can be done by horizon where boundaries can be clearly identified and horizons are sufficiently thick to remove soil without contamination from horizons above or below. Otherwise, sampling can be done by depth interval. Archiving of sample for future reanalysis is a key step in avoiding analytical bias and providing the opportunity for additional analyses as new questions arise.

Repeated soil sampling has recently been shown to be an effective way to monitor forest soil change over years and decades. To support its use, a protocol is presented that synthesizes the latest information on soil resampling methods to aid in the design and implementation of successful soil monitoring programs.

Los métodos de remuestreo del suelo para controlar los cambios en las concentraciones químicas de los suelos forestales

Recent soils research has shown that important chemical soil characteristics can change in less than a decade, often the result of broad environmental ...

Development of Metarhizium anisopliae as a Mycoinsecticide: From Isolation to Field Performance

A major concern when developing commercial mycoinsecticides is the kill speed compared to that of chemical insecticides. Therefore, isolation and screening for the selection of a fast-acting, highly virulent entomopathogenic fungus are important steps. Entomopathogenic fungi, such as Metarhizium, Beauveria, and Nomurea, which act by contact, are better suited than Bacillus thuringiensis or nucleopolyhedrosis virus (NPV), which must be ingested by the insect pest. In the present work, we isolated 68 Metarhizium strains from infected insects using a soil dilution and bait method. The isolates were identified by the amplification and sequencing of the ITS1-5.8S-ITS2 and 26S rDNA region. The most virulent strain of Metarhizium anisopliae was selected based on the median lethal concentration (LC50) and time (LT50) obtained in insect bioassays against III-instar larvae of Helicoverpa armigera. The mass production of spores by the selected strain was carried out with solid-state fermentation (SSF) using rice as a substrate for 14 days. Spores were extracted from the sporulated biomass using 0.1% tween-80, and different formulations of the spores were prepared. Field trials of the formulations for the control of an H. armigera infestation in pigeon peas were carried out by randomized block design. The infestation control levels obtained with oil and aqueous formulations (78.0% and 70.9%, respectively) were better than the 63.4% obtained with chemical pesticide.

Development of Metarhizium anisopliae as a Mycoinsecticide: From Isolation to Field Performance

Here, we report the different stages involved in the knowledge-based development of an effective mycoinsecticide, including the isolation, identification, screening, and selection of the "best-fit" entomopathogenic fungus, Metarhizium anisopliae, for the control of insect pests in agriculture.

Desarrollo de<em&gt; Metarhizium anisopliae</em&gt; Como Mycoinsecticide: Del aislamiento al funcionamiento del campo

A major concern when developing commercial mycoinsecticides is the kill speed compared to that of chemical insecticides. Therefore, isolation and ...

Quantification of Endogenous Auxin and Cytokinin During Internode Culture of Ipecac

Adventitious shoot formation is an important technique for the propagation of economically important crops and for the regeneration of transgenic plants. Phytohormone treatment is required for the induction of adventitious shoots in most species. Whether adventitious shoots can be induced is determined by the balance between auxin and cytokinin (CK) levels. Much effort goes into determining optimum concentrations and combinations of phytohormones in each tissue used as explants and in each plant species. In ipecac, however, adventitious shoots can be induced on internodal segments in culture medium without phytohormone treatment. This allows the inherent plasticity of ipecac for cell differentiation to be evaluated. To induce adventitious shoots in ipecac, we cultured internodal segments at 24 &#176;C under 15 &#181;mol m&#8722;2 s&#8722;1 of light in a 14-h light/10-h dark cycle on phytohormone-free B5 medium solidified with 0.2% gellan gum for 5 weeks. To investigate phytohormone dynamics during adventitious shoot formation, we measured endogenous indole-3-acetic acid and CKs in the segments by liquid chromatography-tandem mass spectrometry LC-MS/MS. This method allows analysis of endogenous indole-3-acetic acid and CKs levels in a simple manner. It can be applied to investigate the dynamics of endogenous auxin and CK during organogenesis in other plant species.

Adventitious shoots can be induced on internodal segments of ipecac without phytohormone treatment. To evaluate phytohormone dynamics during adventitious shoot formation, we measured endogenous auxin and cytokinin in internodal segments by LC-MS/MS.

Cuantificación de endógeno auxina y citoquinina durante cultura de entrenudo de Ipecacuana

Adventitious shoot formation is an important technique for the propagation of economically important crops and for the regeneration of transgenic plants. ...

Isolation of Mandibular Gland Reservoir Contents from Bornean 'Exploding Ants' (Formicidae) for Volatilome Analysis by GC-MS and MetaboliteDetector

The aim of this manuscript is to present a protocol describing the metabolomic analysis of Bornean &#39;exploding ants&#39; belonging to the Colobopsis cylindrica (COCY) group. For this purpose, the model species C. explodens is used. Ants belonging to the minor worker caste possess distinctive hypertrophied mandibular glands (MGs). In territorial combat, they use the viscous contents of their enlarged mandibular gland reservoirs (MGRs) to kill rival arthropods in characteristic suicidal &#39;explosions&#39; by voluntary rupture of the gastral integument (autothysis). We show the dissection of worker ants of this species for the isolation of the gastral portion of the wax-like MGR contents as well as listing the necessary steps required for solvent-extraction of the therein contained volatile compounds with subsequent gas chromatography-mass spectrometry (GC-MS) analysis and putative identification of metabolites contained in the extract. The dissection procedure is performed under cooled conditions and without the use of any dissection buffer solution to minimize the changes in the chemical composition of the MGR contents. After solvent-based extraction of volatile metabolites contained therein, the necessary steps for analyzing the samples via liquid-injection-GC-MS are presented. Lastly, data processing and putative metabolite identification with the use of the open-source software MetaboliteDetector is shown. With this approach, the profiling and identification of volatile metabolites in MGRs of ants belonging to the COCY group via GC-MS and the MetaboliteDetector software become possible.

Isolation of Mandibular Gland Reservoir Contents from Bornean &#039;Exploding Ants&#039; Formicidae for Volatilome Analysis by GC-MS and MetaboliteDetector

Minor workers of the ant species Colobopsis explodens are dissected to isolate the wax-like content stored in their hypertrophied mandibular gland reservoirs for subsequent solvent-extraction and analysis by gas chromatography-mass spectrometry. The&#160;annotation and identification of volatile constituents using the open-source software MetaboliteDetector is also described.

Aislamiento de glándula Mandibular depósito contenidos de Borneo ' explosión de hormigas (Formicidae) para análisis por GC-MS y MetaboliteDetector de Volatilome

The aim of this manuscript is to present a protocol describing the metabolomic analysis of Bornean &#39;exploding ants&#39; belonging to the Colobopsis ...

Cultivation of Green Microalgae in Bubble Column Photobioreactors and an Assay for Neutral Lipids

There is significant interest in the study of microalgae for engineering applications such as the production of biofuels, high value products, and for the treatment of wastes. As most new research efforts begin at laboratory scale, there is a need for cost-effective methods for culturing microalgae in a reproducible manner. Here, we communicate an effective approach to culture microalgae in laboratory-scale photobioreactors, and to measure the growth and neutral lipid content of that algae. Instructions are also included on how to set up the photobioreactor system. Although the example organisms are species of Chlorella and Auxenochlorella, this system can be adapted to cultivate a wide range of microalgae, including co-cultures of algae with non-algae species. Stock cultures are first grown in bottles to produce inoculum for the photobioreactor system. Algae inoculum is concentrated and transferred to photobioreactors for cultivation in batch mode. Samples are collected daily for the optical density readings. At the end of the batch culture, cells are harvested by centrifuge, washed, and freeze dried to obtain a final dry weight concentration. The final dry weight concentration is used to create a correlation between the optical density and the dry weight concentration. A modified Folch method is subsequently used to extract total lipids from the freeze-dried biomass and the extract is assayed for its neutral lipid content using a microplate assay. This assay has been published previously but protocol steps were included here to highlight critical steps in the procedure where errors frequently occur. The bioreactor system described here fills a niche between simple flask cultivation and fully-controlled commercial bioreactors. Even with only 3-4 biological replicates per treatment, our approach to culturing algae leads to tight standard deviations in the growth and lipid assays.

Here, we present a protocol to construct lab-scale bubble column photobioreactors and use them to culture microalgae. It also provides a method for the determination of the culture growth rate and neutral lipid content.

Cultivo de microalgas verdes en fotobiorreactores de columna de burbuja y un análisis de lípidos neutros

There is significant interest in the study of microalgae for engineering applications such as the production of biofuels, high value products, and for the ...

Coupling Carbon Capture from a Power Plant with Semi-automated Open Raceway Ponds for Microalgae Cultivation

In the United States, 35% of the total carbon dioxide (CO2) emissions come from the electrical power industry, of which 30% represent natural gas electricity generation. Microalgae can biofix CO2 10 to 15 times faster than plants and convert algal biomass to products of interest, such as biofuels. Thus, this study presents a protocol that demonstrates the potential synergies of microalgae cultivation with a natural gas power plant situated in the southwestern United States in a hot semi-arid climate. State-of-the-art technologies are used to enhance carbon capture and utilization via the green algal species Chlorella sorokiniana, which can be further processed into biofuel. We describe a protocol involving a semi-automated open raceway pond and discuss the results of its performance when it was tested at the Tucson Electric Power plant, in Tucson, Arizona. Flue gas was used as the main carbon source to control pH, and Chlorella sorokiniana was cultivated. An optimized medium was used to grow the algae. The amount of CO2 added to the system as a function of time was closely monitored. Additionally, other physicochemical factors affecting algal growth rate, biomass productivity, and carbon fixation were monitored, including optical density, dissolved oxygen (DO), electroconductivity (EC), and air and pond temperatures. The results indicate that a microalgae yield of up to 0.385 g/L ash-free dry weight is attainable, with a lipid content of 24%. Leveraging synergistic opportunities between CO2 emitters and algal farmers can provide the resources required to increase carbon capture while supporting the sustainable production of algal biofuels and bioproducts.

A protocol is described to utilize the carbon dioxide in natural gas power plant flue gas to cultivate microalgae in open raceway ponds. Flue gas injection is controlled with a pH sensor, and microalgae growth is monitored with real time measurements of optical density.