This work was supported by Laboratory Directed Research and Development (LDRD) program of Lawrence Berkeley National Laboratory supported by the Office of Science, of the U.S. Department of Energy under Contract No. DE-AC02-05CH11231 and an award DE-SC0014079 from the U.S. Department of Energy Office of Science to UC Berkeley. Work at the Molecular Foundry was supported under U.S. Department of Energy Contract No. DE-AC02-05CH11231. We also thank Suzanne M. Kosina, Katherine Louie, Benjamin P. Bowen, and Benjamin J. Cole at Lawrence Berkeley National Laboratory for all their help.

Caution: This protocol includes the use of hazardous chemicals, sharp objects, electrical devices, hot objects, and other hazards that may result in injury. Appropriate personal protective equipment (PPE, e.g., chemically resistant gloves, safety glasses, lab coat, long clothes, closed-toed shoes, etc.) should be worn, and the appropriate safety procedures (safety training, use of a fume hood, etc.) should be followed.
1. EcoFAB Device Fabrication: Casting PDMS Layers (Figure 2 &#38; Figure 3)
<ol>
	<li>Construct the EcoFAB molds using 3D printing techniques (the design files are available at . Each mold includes three parts: a casting frame, a featured mold base, and an insert, as shown in Figure 2. Print the mold base and insert out of rigid opaque photopolymers using a 3D plastic printer. Utilize a minimum of 100 &#181;m resolution, and print the casting frame with acrylonitrile butadiene styrene (ABS).</li>
	<li>Mix 40 mL of siloxane elastomer base with curing agent in a disposable 1 L container. Depending on the desired experiment (steps 2.1 and 2.2), use different ratios (v/v) of elastomer base/curing agent (5:1, 15:1, or 30:1). Proceed to steps 1.3 to 1.8 for all kinds of mixtures. 
	Caution: Wear chemically resistant gloves, safety glasses, and other PPEs.</li>
	<li>Place the container in a vacuum chamber for at least 30 min to remove air bubbles from the elastomer mixture.</li>
	<li>Pour the mixture into the assembled 3D printed plastic mold (Figure 3A) and keep the mold on a heating block at 85 &#176;C for 4 h (Figure 3B). 
	Caution: Wear PPE to avoid burns.</li>
	<li>Let the mold cool down for 5 min. Then pull out the insert from the mold gently (Figure 3C), and then slowly insert a utility knife between the casting frame and PDMS (the solidified elastomer mixture) to separate them (Figure 2D).</li>
	<li>Press the mold base with PDMS up out of the casting frame (Figure 3E). Use a knife or other tools to gently separate the PDMS layer from the mold base at the edges (Figure 3F), and then slowly peel it off from the mold surface (Figure 3G).</li>
	<li>Create inlet and outlet channels on the PDMS layers by making ~1.6 mm holes for the inlet and outlet ports with a 15 gauge blunt needle (Figure 3H, I). 
	NOTE: The standard mold has an inlet and outlet port, while the wide-outlet mold only needs the inlet port (Figure 3H, I).</li>
	<li>Use scissors to trim the edges of PDMS layers. 
	NOTE: The trimmed PDMS layers should be &#8805;76 mm x 51 mm rectangles for small EcoFAB devices and &#8805;102 mm x 83 mm rectangles for large EcoFAB devices.</li>
</ol>
2. EcoFAB Device Fabrication: Chemically Attaching PDMS Layers onto Microscope Slides (Figure 3 &#38; Figure 4)
<ol>
	<li>Permanently bonding the PDMS layers to microscope slides
	<ol>
		<li>Rinse the bonding side of the PDMS layer (made of a 15:1 elastomer base to curing agent mixture) and 7.6 &#215; 5 cm microscope slide with methanol and then blow dry with compressed air or an ultra-pure nitrogen gun. 
		Caution: Methanol is toxic. Work in a fume hood and wear protective eye covering, gloves and other PPEs.</li>
		<li>Place the microscope slide and PDMS layer into a plasma cleaner with their bonding sides facing up (Figure 3J). If a plasma cleaner is not available, skip to step 2.2.</li>
		<li>Close the chamber and the gas vent valve of the plasma cleaner, and turn on the vacuum and pump down the chamber for 1 min.</li>
		<li>Turn on the power of the plasma generator, and switch the radio frequency (RF) level to &#34;HI&#34; for 1 min.</li>
		<li>Turn off both the vacuum pump and the plasma power, and vent the chamber to atmosphere.</li>
		<li>Take out the microscope slide and PDMS layer from the plasma chamber, and quickly press all four edges of the PDMS layer onto the slide with even pressure (Figure 3L). Make sure the center oval region of the PDMS layer (the root chamber) does not touch the slide.</li>
		<li>Place the sealed EcoFAB device on a 120 &#176;C heating block for 20 min to further secure the permanent bonding between the PDMS layer and the microscope slide.</li>
		<li>Let the device cool down for 5 min. Trim off the extra edges of the PDMS layer with a knife.</li>
	</ol>
	</li>
	<li>Reversible physical sealing of the PDMS layers to microscope slides
	<ol>
		<li>The reversible sealing technique utilizes a set of custom clamps (either printed by a 3D plastic printer or machined in metal, the drawings are shown in Figure 4).
		<ol>
			<li>Place the microscope slide into the cutout on the bottom clamp plate, and then align the PDMS layer (made of a 5:1 elastomer base to curing agent mixture) on top of the slide.</li>
			<li>Place the top clamp plate over the PDMS layer. Secure the top and bottom plates together using four hex cap screws, orienting the screws so that the nuts are threaded on from the top of the clamp.</li>
		</ol>
		</li>
		<li>Adhering PDMS directly to microscope slides
		<ol>
			<li>Position the PDMS layer (made of a 30:1 elastomer base to curing agent mixture) on top of a microscope slide.</li>
			<li>Press the PDMS layer to the slide. The soft, very adhesive PDMS layer (30:1) should stick to the slide creating a waterproof seal without the permanent chemical bonding or physical press from a clamp (Figure 3L).</li>
		</ol>
		</li>
	</ol>
	</li>
</ol>
3. EcoFABs Sterilization
<ol>
	<li>Rinse EcoFAB devices with ultrapure water.</li>
	<li>Place one EcoFAB device in an EcoFAB container, and add 70% ethanol until the device is submerged. Close the container lid and shake gently to wet all surfaces inside with ethanol. Make sure the root growth chamber of the EcoFAB device is filled with ethanol, with very few or no air bubbles.</li>
	<li>After 30 min incubation at room temperature, pour off 70% ethanol, and repeat the incubation with 100% ethanol for 5 min.</li>
	<li>Drain out ethanol, and incubate the sterilized EcoFAB for 16 h in a laminar flow hood to dry it completely. If available, sterilize the system by turning on the UV light within hood for 1 h. 
	Caution: Wear appropriate PPE when working with UV lights.</li>
	<li>Store the sterilized EcoFABs in a sterile hood or autoclaved bags for future use.</li>
</ol>
4. EcoFABs with LED Grow Lights (Figure 5)
<ol>
	<li>Attaching LED strips onto EcoFAB containers
	<ol>
		<li>Mark out the locations on the EcoFAB container for 9 LED clips. Start with the first clip 120 mm up from the bottom of the container along an edge (Figure 5A), and proceed to mark out clip locations in a spiral around the container, with each next clip dropping 10 mm. A spiral of 9 clips that allows a 1 m LED strip to wrap around the container twice.</li>
		<li>Hot glue an LED clip to each marked position by adding two dabs of hot glue onto the container, aligned with the position of the clips&#39; mounting holes. Press the clip holes into these two dabs of glue, then add another dab of glue on top of the holes. Repeat the procedure for all clips until 9 clips form a spiral (Figure 5B). 
		Caution: Wear gloves and other PPE when working with hot glue to avoid burns.</li>
		<li>Thread the LED strip through the clips in a spiral shape, with LEDs facing into the container. The strip should circle around twice (Figure 5C).</li>
	</ol>
	</li>
	<li>Connecting LED strips to the power supply with a controller (Figure 5D displays an EcoFAB chamber with illuminated lights, the programming of the controller is described in step 4.3). 
	Caution: Electrical shock hazard: make sure the power supply is unplugged when connecting wires.
	<ol>
		<li>Connect the positive and negative terminals of the power supply to the &#34;INPUT: V+&#34; and &#34;INPUT: V-&#34; terminals of the controller using 2-wire cable (Figure 5E displays a schematic drawing of the controller setup).</li>
		<li>Connect the negative lead from the bare end of a female-to-bare cable to one &#34;OUTPUT&#34; channel on the controller. 
		NOTE: There are five channels on the controller that is utilized in this protocol, so it can support up to five 1 m LED strips.</li>
		<li>Connect all positive leads of the cables to a compact splicing connector (if more than one channels are needed), and then link this connector to the &#34;OUTPUT V+&#34; terminal of the controller.</li>
		<li>Plug each LED strip into the female end of the cables, so each LED has its own channel to be controlled. If desired, use female-to-male cables to extend the reach.</li>
	</ol>
	</li>
	<li>Program the controller for a desired light cycle according to manufacturer&#39;s instructions,</li>
</ol>
5. Growing Plants in EcoFABs
<ol>
	<li>Seed sterilization and germination 
	NOTE: The seed sterilization and all following steps with seedlings must be performed in sterile conditions. The sterilization process discussed below is suitable to the seeds of Arabidopsis thaliana, Avena barbata, Brachypodium distachyon, and Panicum virgatum. Panicum virgatum seeds should be suspended in 60% sulfuric acid for 1 h before the sterilization process. It is advised to prepare 1 - 2 seeds per EcoFAB device, considering the germination rate and the homogeneity of germination.
	<ol>
		<li>Soak the seeds in 70% ethanol for 2 min.</li>
		<li>Remove ethanol with a pipette, and rinse the seeds with sterile water three times.</li>
		<li>Leave the seeds in 10% bleach solution for 5 min.</li>
		<li>Remove the bleach solution, and thoroughly wash the seeds using sterile water three times.</li>
		<li>Add sterile water to the seeds, and incubate the microcentrifuge tube in a 4 &#176;C refrigerator for 7 days.</li>
		<li>Evenly spread the seeds on 0.5 Murashige &#38; Skoog (MS) medium with 0.6% phytagel and seal the plates with micropore tape.</li>
		<li>Grow the plants to a root length of about 5 mm for transfer to EcoFABs (Figure 6A). For the experiments presented here, apply a 16 h light/8 h dark illumination regime in a 22 &#176;C growth chamber, and incubate the plants 2 - 7 d before transfer to EcoFAB (2 days for Avena barbata and Brachypodium distachyon, 7 days for Arabidopsis thaliana and Panicum virgatum).</li>
	</ol>
	</li>
	<li>Transferring seedlings into EcoFABs with liquid medium (Figure 6)
	<ol>
		<li>Using a sterile syringe or micropipette, flush the root chamber of an EcoFAB device with sterile water for three times, and then fill the root chamber with the growth medium of interest, for example 0.5 MS medium (Figure 6B, step 5.1.6).</li>
		<li>Carefully insert a single seedling into the plant reservoir of the EcoFAB device (Figure 6C). 
		NOTE: The root should be fully submerged inside the root chamber, with the shoot sticking out of the reservoir.</li>
		<li>Add 3 mL of sterile water into the container, avoiding the EcoFAB device. This will increase the humidity and reduce the evaporation of the medium from the root chamber.</li>
		<li>Close the container, and seal the lid with micropore tape (Figure 6D).</li>
		<li>Place the EcoFAB into a plant incubator, or utilize the EcoFAB illumination system in a controlled temperature environment suitable for the growth of the respective plant (step 4). For this study, set the chamber to 24 &#176;C.</li>
		<li>Periodically check the EcoFAB to refill growth media inside the root growth chamber and add water to the container. Perform all steps in sterile conditions. 
		NOTE: For early plant growth stages, refilling of the root growth chamber is necessary every 5 to 7 days. For later growth stages, a refilling is necessary every 2 to 3 days. If desired, use a syringe or pipette to collect root exudate solution from the root growth chambers into an microcentrifuge tube and store it in a -80 &#176;C freezer; also, image the root morphology with a gel imager or microscope.</li>
	</ol>
	</li>
	<li>Transferring seedlings into EcoFABs with solid substrates
	<ol>
		<li>Use the root chambers fabricated with a 5:1 mixture of elastomer base to curing agent if using a set of custom clamps to attach it to a microscope slide (Figure 3K, Figure 4); or choose a PDMS layer made of 30:1 base to curing agent mixture if adhering PDMS layers to slides directly (as described in step 2.2).</li>
		<li>Sterilize the EcoFAB chambers, as described in step 3.</li>
		<li>Carefully add sterilized soil/sand into the root chamber, turn the PDMS layer upside down, and add the substrate to the root chamber. Avoid any particulate fall on the area that will be in contact with the microscope slide, since this will reduce adhesion.</li>
		<li>Place the microscope slide on top of the PDMS layer, and press all the edges firmly. Carefully flip the EcoFAB device so that no soil/sand falls out of the reservoir opening. 
		NOTE: For EcoFAB devices made of a 5:1 base to curing agent mixture, use a custom clamp to secure the seal.</li>
		<li>Flow liquid medium or water through the inlet or outlet channel of the EcoFAB device, and transfer a seedling into its plant reservoir, as described in step 3.3.</li>
	</ol>
	</li>
	<li>Adding microbes into EcoFABs
	<ol>
		<li>Transfer a microbial colony to an incubation tube with 8 mL of LB broth, and grow it to OD 0.5 (approximately 12 h).</li>
		<li>Transfer the culture solution into a 15 mL centrifuge tube, and centrifuge it at room temperature for 5 min at 3000 x g to pellet microbes.</li>
		<li>Remove the supernatant, and add 8 mL of plant growth medium used in the target EcoFAB. Suspend the pellet of microbes, and centrifuge the tube at room temperature for 5 min at 3000 x g.</li>
		<li>Repeat step 5.4.3. twice to completely remove any LB nutrient traces.</li>
		<li>Add plant growth medium to the washed microbe pellet until its optical density is about 0.5 at 600 nm.</li>
		<li>Add 20 &#181;L of the microbe solution into the root chamber through the EcoFAB outlet. The strains used in this publication traveled to plant roots within 2 - 3 days, and started colonizing root surfaces.</li>
		<li>For engineered chemiluminescent, make sure to include the inducer (1 mM IPTG) in plant growth medium to induce luciferase expression.</li>
	</ol>
	</li>
</ol>
6. Metabolite Profiling of Root Exudates from EcoFABs
<ol>
	<li>Sample preparation for LC/MS based metabolomics analysis
	<ol>
		<li>Put the microcentrifuge tubes with root exudates collected from EcoFABs in a lyophilizer, and turn on the lyophilizer to remove all the water from the tubes.</li>
		<li>Add 300 &#181;L of LC-MS grade methanol into each tube, and sonicate for 30 min. 
		Caution: Wear PPE when working with methanol.</li>
		<li>Place the tubes in a centrifuge, and centrifuge them at 3000 x g for 5 min.</li>
		<li>Transfer the supernatant solutions into new microcentrifuge tubes, and evaporate methanol in a vacuum concentrator.</li>
		<li>Add 150 &#181;L of methanol with 1 mM LC-MS internal standards into each tube, and incubate the tubes in a 4 &#176;C refrigerator for 12 h.</li>
		<li>Centrifuge the tubes at 3000 x g for 5 min, and transfer the supernatant into 0.22 &#181;m filter tubes.</li>
		<li>Centrifuge the filter tubes, and transfer the filtered solutions into 2.0 mL LC/MS vials with 200 &#181;L of inserts.</li>
		<li>Place the vials inside a LC/MS rack, and load the rack inside the LC/MS auto-sampler.</li>
	</ol>
	</li>
	<li>Data analysis
	<ol>
		<li>Get an access of Metabolite Atlas and custom Python scripts26 or use other data analysis software.</li>
		<li>Identify metabolites based on m/z values, retention time and compound fragmentation patterns using a library of metabolite standards.27</li>
	</ol>
	</li>
</ol>
7. Mass Spectroscopic Imaging of Plant Roots in EcoFABs (Figure 7)
NOTE: EcoFAB devices made of a 5:1 elastomer base to curing agent mixture with custom clamps (Figure 7A) are used for root stamping onto nanostructure-initiator mass spectrometry (NIMS) chips,28,29,30 since PDMS layers can be reversely bonded to the surfaces of NIMS chips.
<ol>
	<li>Sterilize a NIMS chip surface with UV light for 1 h.</li>
	<li>Pick an EcoFAB with a growing plant from the incubator, and place it in a sterile hood.</li>
	<li>Open the EcoFAB container, and remove the top plate of the clamp.</li>
	<li>Lift up the PDMS layer together with the plant inside, and carefully attach the PDMS layer with the plant onto a NIMS chip (Figure 7B, D, E). 
	NOTE: Once the root touches the NIMS chip surface, it should not be moved. This prevents &#34;smearing&#34; of the root metabolites.</li>
	<li>Gently press down on the roots through the PDMS layer until the roots fully contact the NIMS surface. Leave the roots on the NIMS surface for 20 min.</li>
	<li>Lift off the PDMS layer including the plant from the NIMS chip, again avoiding moving the root across the NIMS surface. Return the plant to the clamp if desired.</li>
	<li>Attach the NIMS chip onto a custom MALDI plate and load the plate into a MALDI spectrometer for mass imaging (Figure 7C).</li>
	<li>Use OpenMSI program to generate the NIMS image of root metabolites (Figure 7D-G)31.</li>
</ol>

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T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Imaging+the+Root+Hair+Morphology+of+Arabidopsis+Seedlings+in+a+Two-layer+Microfluidic+Platform.">Imaging the Root Hair Morphology of Arabidopsis Seedlings in a Two-layer Microfluidic Platform.</a> J. Vis. Exp. (126), (2017).</li><li>Garvin, D. F., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Development+of+Genetic+and+Genomic+Research+Resources+for+Brachypodium+distachyon,+a+New+Model+System+for+Grass+Crop+Research.">Development of Genetic and Genomic Research Resources for Brachypodium distachyon, a New Model System for Grass Crop Research.</a> Crop Sci. 48 (Supplement_1), S69-S84 (2008).</li><li>Lisensky, G. C., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Replication+and+Compression+of+Surface+Structures+with+Polydimethylsiloxane+Elastomer.">Replication and Compression of Surface Structures with Polydimethylsiloxane Elastomer.</a> J. Chem. Educ. 76 (4), 537 (1999).</li><li>Friend, J., Yeo, L. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Fabrication+of+microfluidic+devices+using+polydimethylsiloxane.">Fabrication of microfluidic devices using polydimethylsiloxane.</a> Biomicrofluidics. 4 (2), 026502 (2010).</li><li>Yao, Y., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Analysis+of+Metabolomics+Datasets+with+High-Performance+Computing+and+Metabolite+Atlases.">Analysis of Metabolomics Datasets with High-Performance Computing and Metabolite Atlases.</a> Metabolites. 5 (3), 431-442 (2015).</li><li>Sumner, L. W., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Proposed+minimum+reporting+standards+for+chemical+analysis+Chemical+Analysis+Working+Group+(CAWG)+Metabolomics+Standards+Initiative+(MSI).">Proposed minimum reporting standards for chemical analysis Chemical Analysis Working Group (CAWG) Metabolomics Standards Initiative (MSI).</a> Metabolomics. 3 (3), 211-221 (2007).</li><li>Gao, J., de Raad, M., Bowen, B. P., Zuckermann, R. N., Northen, T. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Application+of+Black+Silicon+for+Nanostructure-Initiator+Mass+Spectrometry.">Application of Black Silicon for Nanostructure-Initiator Mass Spectrometry.</a> Anal. Chem. 88 (3), 1625-1630 (2016).</li><li>Gao, J., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Morphology-Driven+Control+of+Metabolite+Selectivity+Using+Nanostructure-Initiator+Mass+Spectrometry.">Morphology-Driven Control of Metabolite Selectivity Using Nanostructure-Initiator Mass Spectrometry.</a> Anal. Chem. 89 (12), 6521-6526 (2017).</li><li>Woo, H. -. K., Northen, T. R., Yanes, O., Siuzdak, G. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Nanostructure-initiator+mass+spectrometry:+a+protocol+for+preparing+and+applying+NIMS+surfaces+for+high-sensitivity+mass+analysis.">Nanostructure-initiator mass spectrometry: a protocol for preparing and applying NIMS surfaces for high-sensitivity mass analysis.</a> Nat. Protoc. 3 (8), 1341-1349 (2008).</li><li>R&#252;bel, O., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=OpenMSI:+A+High-Performance+Web-Based+Platform+for+Mass+Spectrometry+Imaging.">OpenMSI: A High-Performance Web-Based Platform for Mass Spectrometry Imaging.</a> Anal. Chem. 85 (21), 10354-10361 (2013).</li><li>L&#243;pez-Bucio, J., Cruz-Ram&#305;&#769;rez, A., Herrera-Estrella, L. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+role+of+nutrient+availability+in+regulating+root+architecture.">The role of nutrient availability in regulating root architecture.</a> Curr Opin Plant Biol. 6 (3), 280-287 (2003).</li><li>Lynch, J. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Steep,+cheap+and+deep:+an+ideotype+to+optimize+water+and+N+acquisition+by+maize+root+systems.">Steep, cheap and deep: an ideotype to optimize water and N acquisition by maize root systems.</a> Ann. Bot. 112 (2), 347-357 (2013).</li><li>Rell&#225;n-&#193;lvarez, R., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=GLO-Roots:+an+imaging+platform+enabling+multidimensional+characterization+of+soil-grown+root+systems.">GLO-Roots: an imaging platform enabling multidimensional characterization of soil-grown root systems.</a> eLife. 4, e07597 (2015).</li><li>Kamilova, F., Validov, S., Azarova, T., Mulders, I., Lugtenberg, B. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Enrichment+for+enhanced+competitive+plant+root+tip+colonizers+selects+for+a+new+class+of+biocontrol+bacteria.">Enrichment for enhanced competitive plant root tip colonizers selects for a new class of biocontrol bacteria.</a> Environ. Microbiol. 7 (11), 1809-1817 (2005).</li><li>Klitgaard, A., Nielsen, J. B., Frandsen, R. J. N., Andersen, M. R., Nielsen, K. F. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Combining+Stable+Isotope+Labeling+and+Molecular+Networking+for+Biosynthetic+Pathway+Characterization.">Combining Stable Isotope Labeling and Molecular Networking for Biosynthetic Pathway Characterization.</a> Anal. Chem. 87 (13), 6520-6526 (2015).</li></ol>

The authors have nothing to disclose.

The protocols reported here for using ecosystem fabrication to create EcoFABs provides community resources for systematic plant biology studies in highly controlled laboratory conditions. Advances in 3D printing provide widely accessible technologies for constructing and iteratively refining EcoFAB designs. The root chamber presented here is found to be well suited for imaging microscopy and maintaining sterility, enabling controlled addition of microbes to investigate plant-microbe interactions.The EcoFAB platform is compatible with various plant species. It is important to recognize physiological effects of growing the plants within the narrow root chamber such that additional experiments will be required to generalize findings to plants growing in natural environments.
The use of sterile chambers and LED grow light enables the investigation of the effects of various light conditions, including wavelength, intensity, and duration, on plant growth and related physiological parameters in parallel. Reversible bonding root chambers allow the use of solid substrates as well as to spatially collect solid samples for biochemical and genetic analysis. The applications of solid substrates, such as soils, sand, and quartz beads, offer the possibilities of using EcoFABs to construct more ecologically relevant laboratory ecosystems. However, all the systems presented here use saturated liquid (hydroponic cultures) which are not an accurate reflection of most soils and it will be important to further refine these designs to maintain air pockets within the soil such that they better represent natural soils.
The use of both simple cameras and microscopes is described to image root system morphology development at both bulk to cellular levels. This suitability for monitoring root morphology imaging and quantification will likely be helpful for understanding the regulatory mechanisms of plant physiological and molecular signals triggered by plant genotypic adaptions to growth conditions. However, a limitation for studying physiological root development is the current horizontal placement of the EcoFAB device. In natural environments, the roots gravitropic response leads to a predominantly vertical development of the root system. Thus, the horizontal system presented here likely differs in some factors from a natural environment, and the fabrication of EcoFAB systems with vertical placement of the root chamber is a desirable goal for future EcoFAB versions. Although the current EcoFAB devices are placed horizontally, the analysis of root morphology parameters in various conditions, or in response to microbes, is possible. High resolution imaging can be applied to capture root colonization dynamics of single isolates or communities, providing information about which plant parts are colonized in various nutrient sufficient and deficient conditions. It is anticipated that such studies will provide important new insights into how plant microbiomes are assembled, and how these dynamics change over time, for example as the roots develop.
Microfluidic devices enable imaging of very young plants, and usually the amount of metabolites collected is not sufficient for LCMS analysis. Soil-based systems, such as rhizotrons, allow the imaging of root morphology when either the plants are transformed with chemiluminescent construct (Glo-root) or with NMR-based methods33,34. Metabolite extractions from these systems are time consuming because of large volume of samples. EcoFABs are a combination of both: the fabrication is similar to microfluidic devices. EcoFABs were designed to be simple and inexpensive to reproduce, but the size of the chamber can be adjusted to grow plants with small or large root systems, up to their reproductive stages. Simultaneous observations of root morphology changes and root exudation are possible. The system is sterile, enabling controlled addition of specific microbes.
EcoFABs are designed to enable controlled introduction and sampling of microbes and metabolites. Specifically, samples collected from root growth chambers are found to be sufficient for mass spectroscopic metabolite profiling. The integration of mass spectrometry imaging (e.g., NIMS technique presented here) provides a non-destructive approach of studying metabolite spatial distributions of root systems. This technique will likely be helpful in future stable isotope tracing experiments and mapping microbial localization to specific metabolites36. While this protocol has focused on single isolates, the same design can certainly be used for more complex communities. The sample volumes and biomass within the EcoFABs are likely more than sufficient for further integration with DNA sequencing technologies, which will be important to characterizing and monitoring microbial community structure and gene expression.
In conclusion, this protocol details the fabrication of laboratory ecosystems designed for the investigation of plant-microbe interactions, with emphasis on simple and accessible methods that can easily be implemented and extended by researchers around the world. Current efforts are aimed at demonstrating the reproducibility between labs and the integration of a temperature control system such that each EcoFAB will have independently controlled light and temperature. A further advancement of the system will be the integration of automated sampling and refilling of the EcoFAB root chambers and the development of reproducible protocols for establishing relevant plant microbiomes within EcoFABs.

The application of beneficial plant microbes in agriculture offers great potential to increase sustainable food and biofuel production to provide for a growing population1,2,3,4. A significant amount of work supports the importance of plant microbiomes in plant nutrient uptake, tolerance to stresses, and resistance to disease5,6,7,8. However, it is difficult to investigate these mechanisms of plant-microbe interactions in field ecosystems due to the complexity and associated irreproducibility and inability to precisely control microbiome composition and genetics (e.g., using microbial mutants)4,9,10.
One strategy is to construct simplified model ecosystems to enable controlled, replicated laboratory experiments investigating plant-microbe interactions to generate insights that can be further tested in the field10,11,12. This concept builds on traditional approaches using plants grown in soil-filled pots or on agar slabs within greenhouses or incubators13. Although these will likely remain the most widely used approaches, they lack the ability to precisely monitor and manipulate plant growth environments. To these ends, rhizoboxes and rhizotrons represent a major improvement in the ability to study below-ground processes14,15, and, first protocols were published for analyzing rhizosphere metabolites in soil16. More recently, to enable high throughput analysis, advanced microfluidic devices13,17&#160;such as Plant Chip18,19, RootArray20, and RootChip21, have been developed as efficient tools for plant phenotyping with micrometer-scale spatial resolution to monitor the early growth stages of the small model plant Arabidopsis thaliana in liquid flow medium. Recently, a two-layer imaging platform was described that enables root hair imaging of Arabidopsis thaliana at seedling stage with a microfluidic platform22.
Here, detailed protocols for constructing controlled laboratory devices (EcoFABs) are provided, for studying plant microbe interactions and show that they can be used to study diverse plants including Arabidopsis thaliana, Brachypodium distachyon23, the ecologically important wild oat Avena barbata, and the bioenergy crop Panicum virgatum (switchgrass). EcoFAB is a sterile plant growth platform that includes two primary components: the EcoFAB device and sterile plant-sized transparent container. The EcoFAB device is made from a polydimethylsiloxane (PDMS) manufacturing process that involves casting PDMS layers from a 3D printed plastic mold and bonding PDMS layers onto microscope slides using methods previously reported24,25. The detailed procedures of EcoFAB workflow, such as device fabrication, sterilization, seed germination, seedling transplantation, microbe inoculation/cocultivation, sample preparation, and analysis, are described in this protocol (Figure 1). Further modifications of the basic workflow are described, including the installation of computer controlled LED grow lights and the utilization of solid substrates. The utilization of imaging techniques to investigate root morphology changes, microbial colonization of roots, and mass spectroscopic imaging of root exudates are described. We anticipate that the simple, inexpensive design based on readily available materials, as well as the detailed protocols presented here, will turn the EcoFAB platform into a community resource, standardizing laboratory plant-microbiome studies.

<table>
	<tbody>
		<tr>
			<td>3D printed custom mold</td>
			<td>LBNL</td>
			<td></td>
			<td>STL files available here www.eco-fab.org; The EcoFABs molds described here were printed by FATHOM: http://studiofathom.com</td>
		</tr>
		<tr>
			<td>Dow sylgard 184 silicone elastomer clear kit</td>
			<td>Ellsworth Adhesives</td>
			<td>184 SIL ELAST KIT 0.5KG</td>
			<td></td>
		</tr>
		<tr>
			<td>Air duster spray</td>
			<td>VWR</td>
			<td>75780-350</td>
			<td>any compressed gas duster should work</td>
		</tr>
		<tr>
			<td>15 gauge blunt needle</td>
			<td>VWR</td>
			<td>89166-240</td>
			<td></td>
		</tr>
		<tr>
			<td>5 mL syringe with Luer-Lok Tip</td>
			<td>VWR</td>
			<td>BD309646</td>
			<td></td>
		</tr>
		<tr>
			<td>3&#8221;x2&#8221; microscope glass slide</td>
			<td>VWR</td>
			<td>48382-179</td>
			<td></td>
		</tr>
		<tr>
			<td>1.75&#34; x 2.56&#34; x 3.56&#34; EcoFAB box</td>
			<td>Amazon</td>
			<td>B005GAQ25Q</td>
			<td></td>
		</tr>
		<tr>
			<td>4&#8221; x 3 &#188;&#8221; microscope glass slide</td>
			<td>Ted Pella</td>
			<td>260231</td>
			<td></td>
		</tr>
		<tr>
			<td>4.87&#34; x 4.87&#34; x 5.50&#34; EcoFAB box</td>
			<td>Amazon</td>
			<td>B00P9QVOS2</td>
			<td></td>
		</tr>
		<tr>
			<td>Plasma Cleaner</td>
			<td>Harrick Plasma</td>
			<td>PDC-001</td>
			<td></td>
		</tr>
		<tr>
			<td>3D printed custom clamp</td>
			<td>LBNL</td>
			<td></td>
			<td>STL files available from Trent Northen&#39;s lab</td>
		</tr>
		<tr>
			<td>Sterile hood</td>
			<td>AirClean&#160;Systems</td>
			<td>AC600 Series PCR Workstations</td>
			<td></td>
		</tr>
		<tr>
			<td>PTFE syringe tubing</td>
			<td>Sigma-Aldrich</td>
			<td>Z117315-1EA</td>
			<td></td>
		</tr>
		<tr>
			<td>Ethanol</td>
			<td>VWR</td>
			<td>89125-172</td>
			<td></td>
		</tr>
		<tr>
			<td>Bleach</td>
			<td></td>
			<td></td>
			<td></td>
		</tr>
		<tr>
			<td>Murashige and Skoog (MS) Macronutrient Salt Base</td>
			<td>Phytotechnologies Laboratories</td>
			<td>M502</td>
			<td></td>
		</tr>
		<tr>
			<td>Murashige and Skoog (MS) Micronutrient Salt Base</td>
			<td>Phytotechnologies Laboratories</td>
			<td>M554</td>
			<td></td>
		</tr>
		<tr>
			<td>Soil</td>
			<td>Hummert International</td>
			<td>Pro-Mix PGX</td>
			<td></td>
		</tr>
		<tr>
			<td>Phytagel</td>
			<td>Sigma-Aldrich</td>
			<td>71010-52-1</td>
			<td></td>
		</tr>
		<tr>
			<td>Arabidopsis thaliana</td>
			<td>Lehle Seeds</td>
			<td>WT-24 Col-4 Columbia wild type</td>
			<td></td>
		</tr>
		<tr>
			<td>Brachypodium distachyon</td>
			<td>LBNL</td>
			<td>Standard Bd-21 line</td>
			<td>Available from John Vogel&#39;s lab</td>
		</tr>
		<tr>
			<td>Panicum virgatum</td>
			<td>The Samuel Roberts Noble Foundation</td>
			<td>Alamo switchgrass</td>
			<td></td>
		</tr>
		<tr>
			<td>Micropore tape</td>
			<td>VWR</td>
			<td>56222-182</td>
			<td></td>
		</tr>
		<tr>
			<td>LC-MS grade methanol</td>
			<td>VWR</td>
			<td>JT9830-3</td>
			<td></td>
		</tr>
		<tr>
			<td>Lyophilizer</td>
			<td>LABCONCO</td>
			<td>FreeZone 2.5 Plus</td>
			<td></td>
		</tr>
		<tr>
			<td>SpeedVAC concentrator</td>
			<td>Thermo Scientific</td>
			<td>Savant&#8482; SPD111 SpeedVac</td>
			<td></td>
		</tr>
		<tr>
			<td>Ultrafree-MC GV Centrifugal Filter-0.22 &#181;m</td>
			<td>Millipore</td>
			<td>UFC30GV00</td>
			<td></td>
		</tr>
		<tr>
			<td>Liquid chromotography system</td>
			<td>Agilent</td>
			<td>Agilent 1290 LC system</td>
			<td></td>
		</tr>
		<tr>
			<td>Q Exactive mass spectrometer</td>
			<td>Thermo Scientific</td>
			<td>Q Exactive&#8482; Hybrid Quadrupole-Orbitrap MS</td>
			<td></td>
		</tr>
		<tr>
			<td>NIMS chip and custom MALDI plate</td>
			<td>LBNL</td>
			<td></td>
			<td>For detailed protocol see: doi:10.1038/nprot.2008.110</td>
		</tr>
		<tr>
			<td>MALDI mass spectrometer</td>
			<td>AB Sciex</td>
			<td>TOF/TOF 5800 MALDI MS</td>
			<td></td>
		</tr>
		<tr>
			<td>Nano-coated LED grow light strip</td>
			<td>LED World Lighting</td>
			<td>HH-SRB60F010-2835</td>
			<td></td>
		</tr>
		<tr>
			<td>Power supply</td>
			<td>LED World Lighting</td>
			<td>MD45W24VA, LV100-24N-UNV-J</td>
			<td></td>
		</tr>
		<tr>
			<td>TC420 controller</td>
			<td>Amazon</td>
			<td>B0197U7R8Q</td>
			<td></td>
		</tr>
		<tr>
			<td>Silicone LED clips</td>
			<td>Amazon</td>
			<td>B00N9X1GI0</td>
			<td></td>
		</tr>
		<tr>
			<td>Hot glue gun</td>
			<td>Amazon</td>
			<td>B006IY359K</td>
			<td></td>
		</tr>
		<tr>
			<td>Female-to-bare LED connector cable</td>
			<td>LED World Lighting</td>
			<td>HH-F05</td>
			<td></td>
		</tr>
		<tr>
			<td>Female-to-male LED connector extension cable</td>
			<td>LED World Lighting</td>
			<td>HH-MF1</td>
			<td></td>
		</tr>
		<tr>
			<td>20AWG 2-wire cable</td>
			<td>LED World Lighting</td>
			<td>6102051TFT4</td>
			<td></td>
		</tr>
		<tr>
			<td>WAGO 221-415 Splicing Connector</td>
			<td>LED World Lighting</td>
			<td>221-415</td>
			<td></td>
		</tr>
	</tbody>
</table>

ecosystem fabrication (ecofab) protocols for the construction of laboratory ecosystems designed to study plant-microbe interactions

Beneficial plant-microbe interactions offer a sustainable biological solution with the potential to boost low-input food and bioenergy production. A better mechanistic understanding of these complex plant-microbe interactions will be crucial to improving plant production as well as performing basic ecological studies investigating plant-soil-microbe interactions. Here, a detailed description for ecosystem fabrication is presented, using widely available 3D printing technologies, to create controlled laboratory habitats (EcoFABs) for mechanistic studies of plant-microbe interactions within specific environmental conditions. Two sizes of EcoFABs are described that are suited for the investigation of microbial interactions with various plant species, including Arabidopsis thaliana, Brachypodium distachyon, and Panicum virgatum. These flow-through devices allow for controlled manipulation and sampling of root microbiomes, root chemistry as well as imaging of root morphology and microbial localization. This protocol includes the details for maintaining sterile conditions inside EcoFABs and mounting independent LED light systems onto EcoFABs. Detailed methods for addition of different forms of media, including soils, sand, and liquid growth media coupled to the characterization of these systems using imaging and metabolomics are described. Together, these systems enable dynamic and detailed investigation of plant and plant-microbial consortia including the manipulation of microbiome composition (including mutants), the monitoring of plant growth, root morphology, exudate composition, and microbial localization under controlled environmental conditions. We anticipate that these detailed protocols will serve as an important starting point for other researchers, ideally helping create standardized experimental systems for investigating plant-microbe interactions.

Each EcoFAB system includes an EcoFAB device and a plant sized transparent plastic container. One EcoFAB device has a plant reservoir, a root growth chamber, a 1.6 mm flow inlet, and a 1.6 mm outlet for standard EcoFAB device (Figure 2D &#38; Figure 3H) or a 10 mm outlet for wide-outlet EcoFAB device (Figure 2F &#38; Figure 3I). The plant reservoir is designed in a trapezoid shape that has a 6 mm top opening and 3 mm bottom opening, and this design reduces the chance of flow leakage during liquid injection and also ensures enough space for plant growth. The root growth chamber adopts an oval shape with 2 mm depth to fit many model plants&#39; root systems, as shown in Figure 2C and E. Both inlet and outlet channels of a standard EcoFAB device can be connected with PTFE tubing so nutrient solutions can flow into the root growth chamber without opening the EcoFAB container. The wide-outlet EcoFAB device greatly reduces the flow resistance of the outlet, and is preferably used when growing plants with thick root systems or periodically collecting root exudates after complex root systems are derived from plants.
The casting molds for fabricating PDMS layers of EcoFAB devices are created in a design software, and then 3D printed in rigid opaque photopolymers, as shown in Figure 2 and Figure 3. Plants inside EcoFABs can be directly observed with a microscope using a long work distance, ensuring the sterile grow environment (Figure 8A, Supplementary File 1). EcoFAB devices with plants can also fit onto a high-resolution microscope stage, which enables higher resolution imaging of plant-microbe interactions (Figure 8B, Supplementary File 2). Sterility is not maintained in this environment, and high-resolution imaging is therefore only suitable for endpoint measurements.
EcoFABs are designed to enable systematic studies of plants, such as their morphology, metabolisms, and microbial communities at their different growth stages across their life cycles. Here, EcoFABs were examined as a general platform to study a variety of plant species. Figure 8C-E show 7-day old Arabidopsis thaliana, Brachypodium distachyon, and Panicum virgatum growing in EcoFABs. All three plants were found to grow well in the EcoFAB for over one month. Both the dicot, Arabidopsis thaliana and the monocot, Brachypodium distachyon were found to live up to their reproduction stages in the EcoFABs.
The reversible sealing system allows the use of solid substrates (e.g., soil) within the EcoFABs (step 2.2). This reversible sealing approach enables loading of solid substrates into root growth chambers, and also enables sample collection from specific regions of root rhizospheres. Figure 8F-H show a group of 14-day old Brachypodium distachyon growing in hydroponic medium, as well as sand and soil supplemented with hydroponic medium (sand) and water (soil). The thin solid substrate layer in root growth chambers allows light to penetrate through for microscopic imaging of root systems.
Root morphology is defined as spatial configuration and distribution of a plant root system and has been approved as an essential physiology response to diverse growth environments, such as nutrient or water availability32,33,34. EcoFABs provide a convenient approach of studying plant morphology over time or under different nutrient conditions. Figure 9A-F show an example of using EcoFABs to track root morphologies of Brachypodium distachyon in the first three weeks. A Brachypodium distachyon seedling was transferred into the EcoFAB device, and its root structure was recorded by a camera inside a BIO-RAD gel imager. Image processing program, such as Image J, python and matlab, can be further applied to quantify the changes of root morphologies over time or at different medium environments. The quantification of total root area over the course of three weeks showed a gradual increase at the early stage (&#60;1 week) followed by a linear growth trend to the end of three weeks, as shown in Figure 9G.
A primary motivation for constructing the EcoFAB is to investigate plant-microbe interactions. As described in step 5.4, microorganisms are transferred into root growth chambers of EcoFAB devices through the inlet channel. Figure 10 shows, an EcoFAB containing Pseudomonas simea (formerly, fluorescens) WCS417 (WCS417), a plant growth promoting rhizobacteria with chemiluminescent labels, was added into the plant root systems with a concentration of 106 cells per plant. The WCS417 signal was detected with a gel imager, which indicated a distinct spatial distribution of WCS417 microbes in root growth chambers. In both MS liquid medium with and without the sand solid substrate, WCS417 microbes colonized the surfaces of the entire root systems with microbes concentrated around the root tip areas, possibly due to the active nutrient production of root tips (Figure 10G&#38;H)35. On the other hand, the WCS417 microbes in soil substrate accumulated around the plant reservoir region instead of root tips (Figure 10I). As the microbes were added through the outlet channel, the microbes were also able to move in the soil substrate, but did not accumulate on the root, as observed in liquid medium with or without sand. This could indicate that the soil is a sufficient nutrient source, and the microbes migrated to the plant reservoir for optimal respiration conditions.
To study metabolite profiling of plant root exudates as well as metabolite uptake and release from plant-microbe interactions, the exudate solutions from the root growth chambers was collected across various growth stages of plants in EcoFABs. As described in step 6, exudate samples are then extracted for LC-MS analysis. Using this method, a range of metabolites exuded by the plant and consumed by the microbes was detected, and the related metabolite profiling of root exudates with and without microbes colonization is currently under investigation.
<img alt="Figure 1" class="xfigimg" src="/files/ftp_upload/57170/57170fig1.jpg" /> 
Figure 1: The EcoFAB workflow. Plants are germinated on plate, and transferred to the sterilized EcoFAB, microbes can be added. Nondestructive sampling: root exudates can be sampled and imaged, and root morphology can be visualized. Destructive sampling allows analysis of microbe, root, and shoot parameters in detail.
<img alt="Figure 2" class="xfigimg" src="/files/ftp_upload/57170/57170fig2.jpg" /> 
Figure 2: The components of 3D printed molds for EcoFAB device fabrication. (A) Top and tilted views of a casting frame. (B) Top and tilted views of an insert. (C) Top and tilted views of a standard mold base. (E) Top and tilted views of a wide-outlet mold base. (D, F) Assembled molds for fabricating standard and wide-outlet EcoFAB devices, respectively. The oval dimensions are 51 mm x 34 mm for small EcoFAB mold and 76 mm x 62 mm for large EcoFAB mold. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig2large.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/57170/57170fig3.jpg" /> 
Figure 3: EcoFAB device fabrication. (A) Pouring the mixture of elastomer base and curing agent into the mold. (B) Heating the mold with mixture at 85 &#176;C for 4 h. (C) Removing the insert from the mold. (D) Separating the PDMS from the casting frame. (E) Pushing the mold base out of the casting frame. (F) Using a knife to separate the PDMS from the mold along the edges. (G) Peeling the PDMS layer slowly off the mold base. (H) Poking holes for both inlet and outlet channels of the standard PDMS layer. (I) Poking a hole for the inlet channel of the wide-outlet PDMS layer. (J) The PDMS layer (made of a 15:1 elastomer base to curing agent mixture) and a microscope slide are rinsed, and transferred into a plasma cleaner for bonding. (K) Using clamps to hold the PDMS layer (made of a 5:1 elastomer base to curing agent mixture) onto a microscope slide. (L) Pressing the PDMS layer (made of a 30:1 elastomer base to curing agent mixture) directly onto a microscope slide. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig3large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 4" class="xfigimg" src="/files/ftp_upload/57170/57170fig4.jpg" /> 
Figure 4: The design of custom clamps. (A) Top and tilted views of a top clamp plate. (B) Top and tilted views of a bottom clamp plate. (C) Top and tilted views of assembled clamp with four sets of hex cap screws. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig4large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 5" class="xfigimg" src="/files/ftp_upload/57170/57170fig5.jpg" /> 
Figure 5: Installing LED grow lights. (A) Marking out the locations for 9 LED clips in a spiral around the EcoFAB container. (B) LED clips attached to the EcoFAB container. (C) Threading a LED strip through these clips. (D) Connecting the LED strip to a controller wired with a 24V power supply. (E) The schematic of wire connections to the controller. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig5large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 6" class="xfigimg" src="/files/ftp_upload/57170/57170fig6.jpg" /> 
Figure 6: Transferring seedlings into EcoFABs. (A) Brachypodium distachyon plants grown for 2 days on a 0.5 MS plate. (B) Filling the root chamber with plant growth medium. (C) Using a tweezer to carefully insert the root into the plant reservoir. (D) Sealing the EcoFAB container with micropore tape, after adding 3 mL of water to the bottom of the container. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig6large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 7" class="xfigimg" src="/files/ftp_upload/57170/57170fig7.jpg" /> 
Figure 7: NIMS imaging of plant roots in EcoFABs. (A) A Brachypodium distachyon growing in a sterile EcoFAB. (B) Attaching the PDMS layer with the plant onto a NIMS chip for 20 min. (C) Using copper tape to attach the NIMS chip onto a custom MALDI plate, and loading it into a MALDI mass spectrometer. (D-G) one 7-day old and one 20-day old Brachypodium distachyon plant used for NIMS imaging (D, E) and the corresponding NIMS images (F, G). The predominant ions were highlighted in red, green, and blue. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig7large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 8" class="xfigimg" src="/files/ftp_upload/57170/57170fig8.jpg" /> 
Figure 8: The general applications of EcoFABs. (A) Directly capturing root growth of Brachypodium distachyon in an EcoFAB with a long work distance microscope setup. (B) Directly observing root-microbe interactions with a high-resolution microscope setup. (C-E) 7-day old Arabidopsis thaliana (C), Brachypodium distachyon (D), and Panicum virgatum (E) in 0.5 MS hydroponic medium, (F-H) 14-day old Brachypodium distachyon grown in 0.5 MS hydroponics (F), in sand (G) and soil (H) substrate supplied with 0.5 MS medium and water, respectively. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig8large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 9" class="xfigimg" src="/files/ftp_upload/57170/57170fig9.jpg" /> 
Figure 9: Using EcoFABs to study root morphology. (A-F) Root development of Brachypodium distachyon growing in EcoFABs filled with 0.5 MS medium during first three weeks: (A) 2 days, (B) 4 days, (C) 7 days, (D) 11 days, (E) 14 days, (F) 21 days of growth. (G) Averaged root surface areas were estimated by ImageJ software. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig9large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 10" class="xfigimg" src="/files/ftp_upload/57170/57170fig10.jpg" /> 
Figure 10: Using EcoFABs to study root-microbe interactions. (A, B, C) A group of 15-day old Brachypodium distachyon colonizing with Pseudomonas fluorescens WCS417 in different forms of media-MS liquid solution, sand and soil substrates. (D, E, F) Bright field pictures of their root systems. (G, H, I) The corresponding chemiluminescent images of these root systems after 14 days co-cultivation. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/57170fig10large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
Supplementary File 1. Using EcoFAB to capture root growth. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/video1_capture_growing_roots_(2).mp4">Please click here to download this file.</a>
Supplementary File 2. Using EcoFAB to capture root-microbes interactions. <a href="https://cloudflare-jove-com.remotexs.ntu.edu.sg/files/ftp_upload/57170/video2_capture_root_microbes_interaction.avi">Please click here to download this file.</a>

Watch this Scientific Journal Video about Ecosystem Fabrication EcoFAB Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions at JoVE.com

Ecosystem Fabrication EcoFAB Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions

This article describes detailed protocols for ecosystem fabrication of devices (EcoFABs) that enable the studies of plants and plant-microbe interactions in highly controlled laboratory conditions.

Ecosystem Fabrication (EcoFAB) Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions

Beneficial plant-microbe interactions offer a sustainable biological solution with the potential to boost low-input food and bioenergy production. A ...

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JoVE Journal

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18.3K Views.  Lawrence Berkeley National Laboratory. This article describes detailed protocols for ecosystem fabrication of devices (EcoFABs) that enable the studies of plants and plant-microbe interactions in highly controlled laboratory conditions.

Video: Ecosystem Fabrication EcoFAB Protocols for The Construction of Laboratory Ecosystems Designed to Study Plant-microbe Interactions

A Fish-feeding Laboratory Bioassay to Assess the Antipredatory Activity of Secondary Metabolites from the Tissues of Marine Organisms

Marine chemical ecology is a young discipline, having emerged from the collaboration of natural products chemists and marine ecologists in the 1980s with the goal of examining the ecological functions of secondary metabolites from the tissues of marine organisms. The result has been a progression of protocols that have increasingly refined the ecological relevance of the experimental approach. Here we present the most up-to-date version of a fish-feeding laboratory bioassay that enables investigators to assess the antipredatory activity of secondary metabolites from the tissues of marine organisms. Organic metabolites of all polarities are exhaustively extracted from the tissue of the target organism and reconstituted at natural concentrations in a nutritionally appropriate food matrix. Experimental food pellets are presented to a generalist predator in laboratory feeding assays to assess the antipredatory activity of the extract. The procedure described herein uses the bluehead, Thalassoma bifasciatum, to test the palatability of Caribbean marine invertebrates; however, the design may be readily adapted to other systems. Results obtained using this laboratory assay are an important prelude to field experiments that rely on the feeding responses of a full complement of potential predators. Additionally, this bioassay can be used to direct the isolation of feeding-deterrent metabolites through bioassay-guided fractionation. This feeding bioassay has advanced our understanding of the factors that control the distribution and abundance of marine invertebrates on Caribbean coral reefs and may inform investigations in diverse fields of inquiry, including pharmacology, biotechnology, and evolutionary ecology.

This bioassay employs a model predatory fish to assess the presence of feeding-deterrent metabolites from organic extracts of the tissues of marine organisms at natural concentrations using a nutritionally comparable food matrix.

Marine chemical ecology is a young discipline, having emerged from the collaboration of natural products chemists and marine ecologists in the 1980s with ...

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 ...

Understanding Dissolved Organic Matter Biogeochemistry Through In Situ Nutrient Manipulations in Stream Ecosystems

Dissolved organic matter (DOM) is a highly diverse mixture of molecules providing one of the largest sources of energy and nutrients to stream ecosystems. Yet the in situ study of DOM is difficult as the molecular complexity of the DOM pool cannot be easily reproduced for experimental purposes. Nutrient additions to streams however, have been shown to repeatedly alter the in situ and ambient DOM pool. Here we demonstrate an easily replicable field-based method for manipulating the ambient pool of DOM at the ecosystem scale. During nutrient pulse experiments changes in the concentration of both dissolved organic carbon and dissolved organic nitrogen can be examined across a wide-range of nutrient concentrations. This method allows researchers to examine the controls on the DOM pool and make inferences regarding the role and function that certain fractions of the DOM pool play within ecosystems. We advocate the use of this method as a technique to help develop a deeper understanding of DOM biogeochemistry and how it interacts with nutrients. With further development this method may help elucidate the dynamics of DOM in other ecosystems.

Understanding Dissolved Organic Matter Biogeochemistry Through In Situ Nutrient Manipulations in Stream Ecosystems

Dissolved organic matter provides an important source of energy and nutrients to stream ecosystems. Here we demonstrate a field-based method to manipulate the ambient pool of dissolved organic matter in situ through easily replicable nutrient pulses.

Dissolved organic matter (DOM) is a highly diverse mixture of molecules providing one of the largest sources of energy and nutrients to stream ecosystems. ...

Procedures of Laboratory Fumigation for Pest Control with Nitric Oxide Gas

Nitric oxide (NO) is a newly discovered fumigant for postharvest pest control. This paper provides detailed protocols for conducting NO fumigation on fresh products and procedures for residue analysis and product quality evaluation. An airtight fumigation chamber containing fresh fruit and vegetables is first flushed with nitrogen (N2) to establish an ultralow oxygen (ULO) environment followed by injection of NO. The fumigation chamber is then kept at a low temperature of 2 - 5 &#176;C for a specified time period necessary to kill a target pest to complete a fumigation treatment. At the end of a fumigation treatment, the fumigation chamber is flushed with N2 to dilute NO prior to opening the chamber to ambient air to prevent the reaction between NO and O2, which produces NO2 and may damage delicate fresh products. At different times after NO fumigation, NO2 in headspace and nitrate and nitrite in liquid samples were measured as residues. Product quality was evaluated after 2 weeks of post-treatment cold storage to determine effects of NO fumigation on product quality. Keeping&#160;O2 from reacting with NO is critical to NO fumigation and is an important part of the protocols. Measuring NO levels is challenging and a practical solution is provided. Possible protocol modifications are also suggested for measuring NO levels in the fumigation chambers as well as residues. NO fumigation has the potential to be a practical alternative to methyl bromide fumigation for postharvest pest control on fresh and stored products. This publication is intended to assist other researchers in conducting NO fumigation research for postharvest pest control and accelerating the development of NO fumigation for practical applications.

This paper describes nitric oxide (NO) fumigation protocols for postharvest pest control. Fumigation chambers are flushed with nitrogen (N2) to establish ultralow oxygen conditions before NO is injected. At the end, chambers are flushed with N2 to dilute NO before exposing products to ambient air to prevent exposure to NO2.

Nitric oxide (NO) is a newly discovered fumigant for postharvest pest control. This paper provides detailed protocols for conducting NO fumigation on ...

Adherence of Bacteria to Plant Surfaces Measured in the Laboratory

This manuscript describes a method to measure bacterial binding to axenic plant surfaces in the light microscope and through the use of viable cell counts. Plant materials used include roots, sprouts, leaves, and cut fruits. The methods described are inexpensive, easy, and suitable for small sample sizes. Binding is measured in the laboratory and a variety of incubation media and conditions can be used. The effect of inhibitors can be determined. Situations that promote and inhibit binding can also be assessed. In some cases it is possible to distinguish whether various conditions alter binding primarily due to their effects on the plant or on the bacteria.

An easy method for measuring and characterizing bacterial adhesion to plants, particularly roots and sprouts, is described in this article.

This manuscript describes a method to measure bacterial binding to axenic plant surfaces in the light microscope and through the use of viable cell ...

Wastewater Irrigation Impacts on Soil Hydraulic Conductivity: Coupled Field Sampling and Laboratory Determination of Saturated Hydraulic Conductivity

Since the early 1960s, an alternative wastewater discharge practice at The Pennsylvania State University has been researched and its impacts monitored. Rather than discharging treated wastewater to a stream, and thereby directly impacting the stream quality, the effluent is applied to forested and cropped land managed by the University. Concerns related to reductions in soil hydraulic conductivity occur when considering wastewater reuse. The methodology described in this manuscript, matching soil sample size with the size of the laboratory-based hydraulic conductivity measurement apparatus, provides the benefits of a relatively rapid collection of samples with the benefits of controlled laboratory boundary conditions. The results suggest that there may have been some impact of wastewater reuse on the soil&#39;s ability to transmit water at deeper depths in the depressional areas of the site. Most of the reductions in the soil hydraulic conductivity in the depressions appear to be related to the depth from which the sample was collected, and by inference, associated with the soil structural and textural differences.

Here we present a methodology which matches a soil sample size and a hydraulic conductivity measurement device to prevent the so-called wall flow along the inside of the soil container from being erroneously included in water flow measurements. Its use is demonstrated with samples collected from a wastewater irrigation site.

Since the early 1960s, an alternative wastewater discharge practice at The Pennsylvania State University has been researched and its impacts monitored. ...

Evaluating Dryocosmus Kuriphilus-induced Damage on Castanea Sativa

Dryocosmus kuriphilus Yasumatsu has become a major pest for Castaneasativa since its arrival in Europe. Its galling activity results in the formation of different gall types and prevents the development of normal shoots. Repeated and uncontrolled attacks cause, besides the production of galls and the attendant gall-related reduction in leaf area, progressive corruption of the branch architecture, including the death of branch parts, and an increase in dormant bud activation. Thus far, there have been few attempts to quantify branch architecture damage. Further, the different methods for assessing infestation degree (MAID) that have been developed focus only on the galls' presence and abundance.
Using the leaf area to sapwood area relationship as a green biomass indicator, we developed in a previous study a damage composite index (DCI) that takes into account the most important branch architectural features, allowing for realistic damage assessment during the entire epidemic process. 
The aim of this study is to present this novel method and highlight differences in the damage description with respect to other broadly used indices. Results show how the DCI depicts branch damage better, especially during the epidemic peak, compared to MAID, which tend to underestimate it. We conclude by suggesting how to properly evaluate the overall impact of the pest by means of our composite damage index, the infestation degree using classic methods, and crown transparency evaluations.

Evaluating Dryocosmus Kuriphilus-induced Damage on Castanea Sativa

It is common practice to assess the damage caused by Dryocosmus kuriphilus by considering the abundance of galls alone rather than by also taking related branch corruption into consideration. We propose a composite damage index that takes into account the most important branch features, thus enabling more realistic damage assessment.

Dryocosmus kuriphilus Yasumatsu has become a major pest for Castaneasativa since its arrival in Europe. Its galling activity results in the formation of ...

Construction of a Low-cost Mobile Incubator for Field and Laboratory Use

Incubators are essential for a range of culture-based microbial methods, such as membrane filtration followed by cultivation for assessing drinking water quality. However, commercially available incubators are often costly, difficult to transport, not flexible in terms of volume, and/or poorly adapted to local field conditions where access to electricity is unreliable. The purpose of this study was to develop an adaptable, low-cost and transportable incubator that can be constructed using readily available components. The electronic core of the incubator was first developed. These components were then tested under a range of ambient temperature conditions (3.5 &#176;C - 39 &#176;C) using three types of incubator shells (polystyrene foam box, hard cooler box, and cardboard box covered with a survival blanket). The electronic core showed comparable performance to a standard laboratory incubator in terms of the time required to reach the set temperature, inner temperature stability and spatial dispersion, power consumption, and microbial growth. The incubator set-ups were also effective at moderate and low ambient temperatures (between 3.5 &#176;C and 27 &#176;C), and at high temperatures (39 &#176;C) when the incubator set temperature was higher. This incubator prototype is low-cost (&lt; 300 USD) and adaptable to a variety of materials and volumes. Its demountable structure makes it easy to transport. It can be used in both established laboratories with grid power or in remote settings powered by solar energy or a car battery. It is particularly useful as an equipment option for field laboratories in areas with limited access to resources for water quality monitoring.

This paper describes a method for building an adaptable, low-cost and transportable incubator for microbial testing of drinking water. Our design is based on widely available materials and can operate under a range of field conditions, while still offering the advantages of higher-end laboratory-based models.

Incubators are essential for a range of culture-based microbial methods, such as membrane filtration followed by cultivation for assessing drinking water ...

Measuring the Shape and Size of Activated Sludge Particles Immobilized in Agar with an Open Source Software Pipeline

Experimental bioreactors, such as those treating wastewater, contain particles whose size and shape are important parameters. For example, the size and shape of activated sludge flocs can indicate the conditions at the microscale, and also directly affect how well the sludge settles in a clarifier.
Particle size and shape are both misleadingly &#39;simple&#39; measurements. Many subtle issues, often unaddressed in informal protocols, can arise when sampling, imaging, and analyzing particles. Sampling methods may be biased or not provide enough statistical power. The samples themselves may be poorly preserved or undergo alteration during immobilization. Images may not be of sufficient quality; overlapping particles, depth of field, magnification level, and various noise can all produce poor results. Poorly specified analysis can introduce bias, such as that produced by manual image thresholding and segmentation.
Affordability and throughput are desirable alongside reproducibility. An affordable, high throughput method can enable more frequent particle measurement, producing many images containing thousands of particles. A method that uses inexpensive reagents, a common dissecting microscope, and freely-available open source analysis software allows repeatable, accessible, reproducible, and partially-automated experimental results. Further, the product of such a method can be well-formatted, well-defined, and easily understood by data analysis software, easing both within-lab analyses and data sharing between labs.
We present a protocol that details the steps needed to produce such a product, including: sampling, sample preparation and immobilization in agar, digital image acquisition, digital image analysis, and examples of experiment-specific figure generation from the analysis results. We have also included an open-source data analysis pipeline to support this protocol.

The size and shape of particles in activated sludge are important parameters that are measured using varying methods. Inaccuracies arise from non-representative sampling, suboptimal images, and subjective analysis parameters. To minimize these errors and ease measurement, we present a protocol specifying every step, including an open source software pipeline.

Experimental bioreactors, such as those treating wastewater, contain particles whose size and shape are important parameters. For example, the size and ...

Modeling the Size Spectrum for Macroinvertebrates and Fishes in Stream Ecosystems

The size spectrum is an inverse, allometric scaling relationship between average body mass (M) and the density (D) of individuals within an ecological community or food web. Importantly, the size spectrum assumes that individual size, rather than species&#8217; behavioral or life history characteristics, is the primary determinant of abundance within an ecosystem. Thus, unlike traditional allometric relationships that focus on species-level data (e.g., mean species&#8217; body size vs. population density), size spectra analyses are &#8216;ataxic&#8217; &#8211; individual specimens are identified only by their size, without consideration of taxonomic identity. Size spectra models are efficient representations of traditional, complex food webs and can be used in descriptive as well as predictive contexts (e.g., predicting responses of large consumers to changes in basal resources). Empirical studies from diverse aquatic ecosystems have also reported moderate to high levels of similarity in size spectra slopes, suggesting that common processes may regulate the abundances of small and large organisms in very different settings. This is a protocol to model the community-level size spectrum in wadable streams. The protocol consists of three main steps. First, collect quantitative benthic fish and invertebrate samples that can be used to estimate local densities. Second, standardize the fish and invertebrate data by converting all individuals to ataxic units (i.e., individuals identified by size, irrespective of taxonomic identity), and summing individuals within log2 size bins. Third, use linear regression to model the relationship between ataxic M and D estimates. Detailed instructions are provided herein to complete each of these steps, including custom software to facilitate D estimation and size spectra modeling.

This is a protocol to model the size spectrum (scaling relationship between individual mass and population density) for combined fish and invertebrate data from wadable streams and rivers. Methods include: field techniques to collect quantitative fish and invertebrate samples; lab methods to standardize the field data; and statistical data analysis.

The size spectrum is an inverse, allometric scaling relationship between average body mass (M) and the density (D) of individuals within an ecological ...