We thank Mauricio Aguirre Morales for his contribution to the development of this system. &#160;Financial support came from the Swiss National Science Foundation to T.J.B.

1. Setup of the Positioning Device
<ol>
	<li>Wire the positioning device to a microcontroller board, following the instruction in https://github.com/grbl/grbl/wiki/Connecting-Grbl.</li>
	<li>Connect the microcontroller to a single-board computer with internet connection via a USB cable and install the GRBL server as described in https://gitlab.com/FlumeAutomation/GRBL_Server.git. Now the positioning device should be navigable from a webpage hosted at http://IP:5020/. Alternatively, the positioning device can be navigated with a Python script, as demonstrated in the first part of the worked example ImagesAcquisition.ipynb (Supplementary File 2).</li>
</ol>
2. OCT Setup
<ol>
	<li>Mount the OCT probe to the positioning device using a compatible dove-tail holder. If required, install an immersion adapter on the objective lens.</li>
	<li>Position the computer and OCT base unit on a bench next to the experiment (e.g., microfluidic devices, flow chambers, flumes, filtration systems). Make sure that the optical cord (maximum length of approx. 1.8 m) is freely moving, long enough to reach all intended locations and not interfering with the experimental setup.</li>
	<li>Install the OCT system together with the available software as described by the manufacturer.</li>
	<li>Install the software packages for automated OCT scan acquisition as described in https://gitlab.com/FlumeAutomation/automated-oct-scans-acquisition.git.</li>
</ol>
3. Image Acquisition
<ol>
	<li>Power on the OCT system and the positioning device. Make sure the device can move freely.</li>
	<li>Open the file config.json in a text editor. Edit the config.json file to adjust default image acquisition parameter (Table 2), such as the refractive index&#160;(1.33 for water at 20 &#176;C, 1.00 for air) and the destination folder for acquired data and metadata.&#160;</li>
	<li>Define the size of the field-of-view (FOV) and the number of A-scans per B-scan in config.json. 
	NOTE: These two parameters determine the size of the voxels of the final dataset and the size of the output file and should match the optical resolution of the probe (x-y voxel size should not be smaller than half of the optical resolution). The number of A- and B-scans affects the spatial extent to be covered which trades-off against available disk space and processing power.</li>
	<li>Define the signal boundaries of the output OCT scan in config.json. These depend on the type of sample. It is thus recommended to determine these parameters based on intensity histograms of a set of preliminary scans. Save the changes in config.json.</li>
	<li>Navigate the OCT probe to a site of interest. Focus the sample and adjust the reference arm and light source intensity for optimal image quality. Repeat this procedure for a number of positions and note the coordinates. 
	NOTE: This will allow the subsequent automatic OCT scan acquisition around these reference points. Note that the reference arm length and intensity cannot be changed during automated image acquisition.</li>
	<li>Open the ImageAcquisition.ipynb file (Supplementary File 2) in Juypter Notebook. Each cell contains code to perform specific tasks and can be run separately via pressing Cell | Run, or Ctrl + Enter or Shift + Enter.
	<ol>
		<li>Set the path to the required libraries and the default configuration parameters. Alternatively, define a new set of temporary parameters.</li>
		<li>Connect to the positioning device and initialize the OCT.</li>
		<li>Calibrate the positioning device (i.e., perform a &#8220;homing&#8221;).</li>
		<li>Acquire the datasets covering the positions of interests in single-scan or mosaic pattern, specifying the number and the overlap (e.g., 30%) of neighboring tiles. 
		NOTE: The memory is allocated prior to the scan, which optimizes computer resource use. Data is saved in 8 bits *.raw format to save storage space, into the destination folder defined in config.json, using the time stamp and the position as naming convention (i.e., %Y%m%d_%H%M%S_&#60;position&#62;). Metadata including the OCT settings and coordinates are saved in the same folder in a *.srm file with the same naming convention. Depending on settings such as FOV and resolution, file size may reach up to 1.5 GB per OCT scan.</li>
	</ol>
	</li>
	<li>To avoid abortion of data acquisition, make sure that there is sufficient free disk space or continuously move OCT datasets to an external hard drive.</li>
</ol>
4. Image Correction and Display
<ol>
	<li>Open the Jupyter notebook ImageProcessing.ipynb (Supplementary File 1) for a worked example of OCT image processing (correction of distortion, background subtraction, calculation of elevation maps, elevation map stitching).</li>
	<li>If required, crop OCT scans in order to exclude spurious signals and reoriented the dataset (biofilm should appear above the substratum).</li>
	<li>Correct for spherical aberration. This is accomplished by a correction algorithm that utilizes a highly reflective reference surface known to be flat (e.g., bottom of the flume, substratum). First, the algorithm defines a grid of 20&#215;20 vertical lines regularly spaced across the xy-plane of the OCT scan. Then, it selects a circular area around each point and averages signal intensities along the vertical profile (Figure 2B). The vertical profiles are processed with a modified Gaussian filter: 
	<img alt="Equation 1" src="/files/ftp_upload/59356/59356eq1.jpg" style="opacity: 0.9;" /> 
	where x is the input signal, and &#963; its standard deviation, while C is determined such as: 
	<img alt="Equation 2" src="/files/ftp_upload/59356/59356eq2.jpg" style="opacity: 0.9;" /> 
	The reference surface is localized as local maxima in each of these profiles. Misidentified points are filtered based on the positions&#160;of their neighbors in three dimensions (Figure 2C). Finally, a 2nd order polynomial surface reflecting the distortion introduced by the scan lens is fitted across these points (Figure 2C). The fitted surface is then used to shift each pixel in z-direction, thus obtaining a flattened image.&#160;The parameters of this algorithm should be adjusted to the characteristics of the OCT&#160;scan.</li>
	<li>Correct for background noise. Identify an empty area of the image (typically above the biofilm) and use the correction algorithm to subtract the average background intensity from the intensity values of the image to produce a final corrected OCT image (Figure 2D).</li>
	<li>Compute an elevation map from the 3D OCT dataset. In this step, define a reference surface of interest for the specific experiment (e.g., the substratum) and an appropriate threshold intensity. Then, use the elevation map calculation algorithm to calculate the thickness of the biofilm for each coordinate (x,y) of the binary mask and assign it to a new 2D matrix&#160; (Figure 3A). Thickness values are then assigned to a 2D matrix of the size of the original image in x and y directions. An image is rendered in which the elevation of the surface is reported as grayscale value (Figure 3B).</li>
	<li>In case several OCT scans are taken in a mosaic pattern, define the number of rows and columns and stitch the respective elevation maps. Figure 5 presents examples of stitched elevation maps, covering the broad range of spatial scales and resolutions achievable with the described setup.</li>
</ol>

<ol>
	<li>Flemming, H. C., Wingender, J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+biofilm+matrix.">The biofilm matrix.</a> Nature reviews. Microbiology. 8, 623-633 (2010).</li><li>Flemming, H. -. 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=Biofilms:+an+emergent+form+of+bacterial+life.">Biofilms: an emergent form of bacterial life.</a> Nature reviews. Microbiology. 14, 563 (2016).</li><li>Stoodley, P., Lewandowski, Z., Boyle, J. D., Lappin-Scott, H. M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Oscillation+characteristics+of+biofilm+streamers+in+turbulent+flowing+water+as+related+to+drag+and+pressure+drop.">Oscillation characteristics of biofilm streamers in turbulent flowing water as related to drag and pressure drop.</a> Biotechnology and Bioengineering. 57, 536-544 (1998).</li><li>Stoodley, P., Lewandowski, Z., Boyle, J. D., Lappin-Scott, H. M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+formation+of+migratory+ripples+in+a+mixed+species+bacterial+biofilm+growing+in+turbulent+flow.">The formation of migratory ripples in a mixed species bacterial biofilm growing in turbulent flow.</a> Environmental microbiology. 1, 447-455 (1999).</li><li>Banin, E., Vasil, M. L., Greenberg, E. P. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Iron+and+Pseudomonas+aeruginosa+biofilm+formation.">Iron and Pseudomonas aeruginosa biofilm formation.</a> Proceedings of the Natural Academy of Sciences U.S.A. 102, 11076-11081 (2005).</li><li>Battin, T. J., Besemer, K., Bengtsson, M. M., Romani, A. M., Packmann, A. I. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+ecology+and+biogeochemistry+of+stream+biofilms.">The ecology and biogeochemistry of stream biofilms.</a> Microbiology. 14, 251-263 (2016).</li><li>Battin, T. 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=Microbial+landscapes:+new+paths+to+biofilm+research.">Microbial landscapes: new paths to biofilm research.</a> Nature Reviews. Microbiology. 5, 76-81 (2007).</li><li>Neu, T. R., Lawrence, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Innovative+techniques,+sensors,+and+approaches+for+imaging+biofilms+at+different+scales.">Innovative techniques, sensors, and approaches for imaging biofilms at different scales.</a> Trends in Microbiology. 23, 233-242 (2015).</li><li>Meleppat, R. K., Shearwood, C., Seah, L. K., Matham, M. V. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Quantitative+optical+coherence+microscopy+for+the+in+situ+investigation+of+the+biofilm.">Quantitative optical coherence microscopy for the in situ investigation of the biofilm.</a> J. of Biomedical Optics. 21 (12), 127002 (2016).</li><li>Wagner, M., Horn, H. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Optical+coherence+tomography+in+biofilm+research:+A+comprehensive+review.">Optical coherence tomography in biofilm research: A comprehensive review.</a> Biotechnology and Bioengineering. 114, 1386-1402 (2017).</li><li>Huang, D., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Optical+coherence+tomography.">Optical coherence tomography.</a> Science. 254, 1178-1181 (1991).</li><li>Haisch, C., Niessner, R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Visualisation+of+transient+processes+in+biofilms+by+optical+coherence+tomography.">Visualisation of transient processes in biofilms by optical coherence tomography.</a> Water Resources. 41, 2467-2472 (2007).</li><li>Drexler, W., Fujimoto, J. G. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Optical Coherence Tomography: Technology and Applications. , (2008).</li><li>Fercher, A. F. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Optical+coherence+tomography+&#8211;+development,+principles,+applications.">Optical coherence tomography &#8211; development, principles, applications.</a> Zeitschrift f&#252;r Medizinische Physik. 20, 251-276 (2010).</li><li>Lee, H. -. C., Liu, J. J., Sheikine, Y., Aguirre, A. D., Connolly, J. L., Fujimoto, J. G. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Ultrahigh+speed+spectral-domain+optical+coherence+microscopy.">Ultrahigh speed spectral-domain optical coherence microscopy.</a> Biomedical Optics Express. , 41236-41254 (2013).</li><li>Fortunato, L., Leiknes, T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=In-situ+biofouling+assessment+in+spacer+filled+channels+using+optical+coherence+tomography+(OCT):+3D+biofilm+thickness+mapping.">In-situ biofouling assessment in spacer filled channels using optical coherence tomography (OCT): 3D biofilm thickness mapping.</a> Bioresource Technology. 229, 231-235 (2017).</li><li>Niederdorfer, R., Peter, H., Battin, T. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Attached+biofilms+and+suspended+aggregates+are+distinct+microbial+lifestyles+emanating+from+differing+hydraulics.">Attached biofilms and suspended aggregates are distinct microbial lifestyles emanating from differing hydraulics.</a> Nature Microbiology. 1, 16178 (2016).</li><li>Roche, K. 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=Benthic+biofilm+controls+on+fine+particle+dynamics+in+streams.">Benthic biofilm controls on fine particle dynamics in streams.</a> Water Resources. 53, 222-236 (2016).</li><li>Fortunato, L., Jeong, S., Wang, Y., Behzad, A. R., Leiknes, T. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Integrated+approach+to+characterize+fouling+on+a+flat+sheet+membrane+gravity+driven+submerged+membrane+bioreactor.">Integrated approach to characterize fouling on a flat sheet membrane gravity driven submerged membrane bioreactor.</a> Bioresource Technology. 222, 335-343 (2016).</li><li>Morgenroth, E., Milferstedt, K. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Biofilm+engineering:+linking+biofilm+development+at+different+length+and+time+scales.">Biofilm engineering: linking biofilm development at different length and time scales.</a> Reviews in Environmental Science and Bio/Technology. 8, 203-208 (2009).</li></ol>

Sebastian Sch&#228;fer is employed at Thorlabs Inc.

OCT imaging is well suited to resolve structures in the micrometer range with a FOV of several square millimeters. It is thus a powerful tool for biofilm research10,18. However, OCT is currently limited to a maximum scan area of 100 - 256 mm2, while biofilm structural patterns often exceed this spatial scale19, especially when morphological differentiation is driven by large scale environmental gradients20</sup...

Biofilms are a highly successful microbial lifestyle adaptation and these interphase-associated and matrix-enclosed communities of microorganisms dominate microbial life in natural and industrial settings1,2. There, biofilms form complex architectures, such as elongated streamers3, ripples4 or mushroom-like caps5 with important consequences for biofilm growth, structural stability and resistance to stress6. While much about biofilm structural differentiation has been learned from work on mono-species cultures grown in miniature flow chambers, most biofilms are highly complex communities often including members of all domains of life6. Appreciating these complex biofilms as microbial landscapes7 and understanding how biofilm structure and function interact in complex communities is thus at the forefront of biofilm research.
A mechanistic understanding of the morphogenesis of complex biofilms in response to environmental cues requires carefully designed experiments in conjunction with spatially and temporally resolved observations of biofilm physical structure across relevant scales8. However, the non-destructive observation of biofilm growth in experimental systems has been severely limited by logistic constraints such as the need to move samples (e.g., to a microscope) often damaging the delicate biofilm structure.
The protocol presented here introduces a fully automated system based on optical coherence tomography (OCT), which allows the in situ, non-invasive monitoring of biofilm morphogenesis at the mesoscale (mm range). OCT is an emerging imaging technique in biofilm research with applications in water treatment and biofouling research, medicine9 and stream ecology10. In OCT, a low coherence light source is split into a sample and reference arm; the interference of the light reflected and scattered by the biofilm (sample arm) and the light of the reference arm is analyzed. A series of axial intensity profiles (A-scans) which contains depth-resolved structural information is acquired and merged into a B-scan (a cross section). A series of adjacent B-scans composes the final 3D volume scan10. OCT provides a lateral optical resolution in the range of approximately 10 &#181;m and is therefore well suited to study mesoscopic structural differentiation of biofilms10,12. For a more detailed description of OCT, refer to Drexler and Fujimoto13and Fercher and colleagues14. Although the field-of-view of a single OCT xy-scan reaches up to hundreds of square micrometers, larger-scale patterns cannot be quantified by means of OCT in a single scan. With respect to biofilms in natural habitats such as streams and rivers, this currently limits our ability to assess biofilm morphogenesis at scales matching the physical and hydraulic template of the habitat.
In order to surpass these spatial limits and to acquire OCT scans automatically, a spectral-domain OCT imaging probe was mounted on a 3-axis positioning system. The installation permits the acquisition of several OCT scans in an overlapping mosaic pattern (tile scan), effectively achieving the tomographic imaging of surface areas up to 100 cm2. Furthermore, the high positioning precision of this system enables to reliably monitor the growth and development of biofilm features in specific sites during long-term experiments. The system is modular and individual components (i.e., positioning device and OCT) of the installation can be used as standalone solutions or flexibly combined. Figure 1 provides an overview of the hard- and software components of the installation.
The system was tested with a commercially available GRBL-controlled CNC positioning device (Table of Materials). The operating distances of this specific positioning platform are 600&#215;840&#215;140 mm, with a manufacturer-indicated accuracy of +/- 0.05 mm and a programmable resolution of 0.005 mm. GRBL is an open-source (GPLv3 License), high-performance motion control for CNC devices. Therefore, every GRBL-based (version &#62; 1.1) positioning device should be compatible with the guidelines and software packages presented here. Moreover, the software could be adapted to other stepmotor controllers with STEP-DIR input type with few modifications.
The OCT device used to assess the performance of the system (Table of Materials) features a low coherence light source with a center wavelength of 930 nm (bandwidth = 160 nm) and adjustable reference arm length and intensity. In the example presented here, an immersion adapter for dipping the OCT probe into flowing water was also used (Table of Materials). The software package developed here for automated OCT scan acquisition critically depends on the SDK provided together with the specific OCT system, however, OCT systems from the same manufacturer with different scan lenses and central wavelengths should be readily compatible.
The GRBL device is controlled by a web server installed on a single-board computer (Figure 1). This grants remote control of the device from any computer with local network or internet access. The OCT device is controlled by a separate computer, allowing the operation of the OCT system aside the automated experimental setup. Finally, the software packages include libraries to synchronize OCT probe positioning and OCT scan acquisition (i.e., to automatically acquire 3D imaging datasets in a mosaic pattern or in a set of defined positions). Defining the position of the OCT probe in 3D effectively allows to adjust the focal plane specifically for (regional) sets of scans. Specifically, on uneven surfaces, different focal planes (i.e., different positions in z direction) can be specified for each OCT scan.
A set of software packages was developed to process raw OCT scans (Table 1). Navigation of the positioning device, OCT scan acquisition and dataset processing are performed with Python-coded Jupyter notebooks, which allow remarkable flexibility in the development and optimization of the software. Two worked and annotated examples of such notebooks (for image acquisition and processing, respectively) are available from https://gitlab.com/FlumeAutomation/automated-oct-scans-acquisition.git They are intended as starting points for customization of the method. A Jupyter notebook is a web browser based application which contain cells with annotated Python code. Each step is contained in a cell of the notebook, which can be executed separately. Due to the different length of the light path through the scan lens (spherical aberration)15, the raw OCT scans appear distorted (Figure 2A). We developed an algorithm to automatically correct for this distortion in acquired OCT scans (contained in ImageProcessing.ipynb, Supplementary File 1). Furthermore, biofilm morphology can be visualized as a 2D elevation map, as was previously used in membrane systems16, and we illustrate how elevation maps obtained from scans taken in a tiling array can be stitched.
Finally, the functionality of the described laboratory installation is illustrated using a flume experiment in which phototrophic stream biofilm is exposed to a gradient of flow velocity.

<table border="0" cellpadding="0" cellspacing="0" style="width:631px;" width="631">
	<tbody>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">OCT Probe</td>
			<td style="width:129px;">Thorlabs</td>
			<td style="width:119px;">GAN210C1</td>
			<td style="width:167px;">OCT imaging device</td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">OCT scan lens</td>
			<td style="width:129px;">Thorlabs&#160;</td>
			<td style="width:119px;">OCT-LK3-BB</td>
			<td></td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">Immersion adapter</td>
			<td style="width:129px;">Thorlabs&#160;</td>
			<td style="width:119px;">OCT-IMM3-SP1</td>
			<td></td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">Stepcraft 840 CK</td>
			<td style="width:129px;">STEPCRAFT</td>
			<td style="width:119px;">NA</td>
			<td>positioning device</td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">microcontroller</td>
			<td style="width:129px;">Arduino Uno R3</td>
			<td style="width:119px;">NA</td>
			<td></td>
		</tr>
		<tr height="21">
			<td height="21" style="height:21px;width:216px;">Single-board computer</td>
			<td style="width:129px;">Raspberry PI</td>
			<td style="width:119px;">NA</td>
			<td></td>
		</tr>
		<tr height="42">
			<td height="42" style="height:42px;width:216px;">camera</td>
			<td style="width:129px;">Canon EOS 7D Mark II</td>
			<td style="width:119px;">NA</td>
			<td></td>
		</tr>
		<tr height="42">
			<td height="42" style="height:42px;width:216px;">camera lens</td>
			<td style="width:129px;">Canon MACRO EFS 35 mm</td>
			<td style="width:119px;">NA</td>
			<td></td>
		</tr>
	</tbody>
</table>

automated 3d optical coherence tomography to elucidate biofilm morphogenesis over large spatial scales

Biofilms are a most successful microbial lifestyle and prevail in a multitude of environmental and engineered settings. Understanding biofilm morphogenesis, that is the structural diversification of biofilms during community assembly, represents a remarkable challenge across spatial and temporal scales. Here, we present an automated biofilm imaging system based on optical coherence tomography (OCT). OCT is an emerging imaging technique in biofilm research. However, the amount of data that currently can be acquired and processed hampers the statistical inference of large scale patterns in biofilm morphology. The automated OCT imaging system allows covering large spatial and extended temporal scales of biofilm growth. It combines a commercially available OCT system with a robotic positioning platform and a suite of software solutions to control the positioning of the OCT scanning probe, as well as the acquisition and processing of 3D biofilm imaging datasets. This setup allows the in situ and non-invasive automated&#160;monitoring of biofilm development and may be further developed to couple OCT imaging with macrophotography and microsensor profiling.

We demonstrate the functionality of the automated OCT imaging system using a flume experiment designed to study the spatio-temporal morphogenesis of phototrophic stream biofilms. A gradually narrowing geometry of the flumes induced gradients in flow velocity along the center of the flume (see reference17).&#160; The temporal development and structural differentiation of biofilm was monitored over 18 days&#160;with the aim to better understand the effects&#160;of hydrodynamic conditions on biofilm mo...

Watch this Scientific Journal Video about Automated 3D Optical Coherence Tomography to Elucidate Biofilm Morphogenesis Over Large Spatial Scales at JoVE.com

Automated 3D Optical Coherence Tomography to Elucidate Biofilm Morphogenesis Over Large Spatial Scales

自动 3D 光学相干断层扫描，以在大型空间尺度上阐明生物膜变形

Microbial biofilms form complex architectures at interphases and develop into highly scale-dependent spatial patterns. Here, we introduce an experimental system (hard- and software) for the automated acquisition of 3D optical coherence tomography (OCT) datasets. This toolset allows the non-invasive and multi-scale characterization of biofilm morphogenesis in space and time.

Biofilms are a most successful microbial lifestyle and prevail in a multitude of environmental and engineered settings. Understanding biofilm ...

automated-3d-optical-coherence-tomography-to-elucidate-biofilm

Research

JoVE Journal

Environment

6.8K 次观看.  Ecole Polytechnique Fédérale de Lausanne. 在这里，我们提出了一个基于光学相干断层扫描或 OCT 的自动化系统。这使我们能够监测生物膜的结构在较大的空间尺度或很长一段时间。OCT 成像非常适合解决微米范围内的结构，但目前其最大面积限制在 250 平方毫米左右。生物膜通常超过这一规模，特别是当分化是由大规模的环境梯度驱动的。实验装置使我们能够监测生物膜在大空间尺度和长时间内三维形态。该系?...

视频: Automated 3D Optical Coherence Tomography to Elucidate Biofilm Morphogenesis Over Large Spatial Scales

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

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

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

自动凝胶尺寸选择，以提高下一代测序文库的质量，从环境水样准备

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

科研

环境科学

Using Pharmacological Manipulation and High-precision Radio Telemetry to Study the Spatial Cognition in Free-ranging Animals

An animal&#39;s ability to perceive and learn about its environment plays a key role in many behavioral processes, including navigation, migration, dispersal and foraging. However, the understanding of the role of cognition in the development of navigation strategies and the mechanisms underlying these strategies is limited by the methodological difficulties involved in monitoring, manipulating the cognition of, and tracking wild animals. This study describes a protocol for addressing the role of cognition in navigation that combines pharmacological manipulation of behavior with high-precision radio telemetry. The approach uses scopolamine, a muscarinic acetylcholine receptor antagonist, to manipulate cognitive spatial abilities. Treated animals are then monitored with high frequency and high spatial resolution via remote triangulation. This protocol was applied within a population of Eastern painted turtles (Chrysemys picta) that has inhabited seasonally ephemeral water sources for ~100 years, moving between far-off sources using precise (&#177; 3.5 m), complex (i.e., non-linear with high tortuosity that traverse multiple habitats), and predictable routes learned before 4 years of age. This study showed that the processes used by these turtles are consistent with spatial memory formation and recall. Together, these results are consistent with a role of spatial cognition in complex navigation and highlight the integration of ecological and pharmacological techniques in the study of cognition and navigation.

This paper describes a novel protocol that combines the pharmacological manipulation of memory and radio telemetry to document and quantify the role of cognition in navigation.

使用药理操纵和高精度无线电遥测研究空间认知中自由放养的动物

An animal&#39;s ability to perceive and learn about its environment plays a key role in many behavioral processes, including navigation, migration, ...

Biofilm Removal Using Carbon Dioxide Aerosols without Nitrogen Purge

Biofilms can cause serious concerns in many applications. Not only can they cause economic losses, but they can also present a public health hazard. Therefore, it is highly desirable to remove biofilms from surfaces. Many studies on CO2 aerosol cleaning have employed nitrogen purges to increase biofilm removal efficiency by reducing the moisture condensation generated during the cleaning. However, in this study, periodic jets of CO2 aerosols without nitrogen purges were used to remove Pseudomonas putida biofilms from polished stainless steel surfaces. CO2 aerosols are mixtures of solid and gaseous CO2 and are generated when high-pressure CO2 gas is adiabatically expanded through a nozzle. These high-speed aerosols were applied to a biofilm that had been grown for 24 hr. The removal efficiency ranged from 90.36% to 98.29% and was evaluated by measuring the fluorescence intensity of the biofilm as the treatment time was varied from 16 sec to 88 sec. We also performed experiments to compare the removal efficiencies with and without nitrogen purges; the measured biofilm removal efficiencies were not significantly different from each other (t-test, p &gt; 0.55). Therefore, this technique can be used to clean various bio-contaminated surfaces within one minute.

Biofilms on surfaces can be effectively and rapidly removed by using a periodic jet of carbon dioxide aerosols without a nitrogen purge.

去除生物膜使用二氧化碳气溶胶没有氮气吹扫

Biofilms can cause serious concerns in many applications. Not only can they cause economic losses, but they can also present a public health hazard. ...

Tracking Infiltration Front Depth Using Time-lapse Multi-offset Gathers Collected with Array Antenna Ground Penetrating Radar

A Ground Penetrating Radar (GPR) system based on a ground-coupled, densely populated antenna array was used to collect data during an infiltration experiment conducted at a test site near the Tottori Sand Dune, Japan. The antenna array used in this study consists of 10 transmitting antennas (Tx) and 11 receiving antennas (Rx). For this experiment, the system was configured to use all possible Tx-Rx pairings, resulting in a Multi-Offset Gather (MOG) consisting of 110 Tx-Rx combinations. The array was left stationary at a position directly above the infiltration area and data were collected every 1.5 seconds using a time-based trigger. Common-Offset Gather (COG) and Common Mid-Point (CMP) data cubes were reconstructed from the MOG data during post-processing. There have been few studies that used time-lapse CMP data to estimate changes in velocity of propagation. In this study, electromagnetic (EM) wave velocity was estimated heuristically at 1-minute intervals from the reconstructed CMP data through curve fitting, using the hyperbola equation. We then proceeded to calculate the depth of the wetting front. The evolution of the wetting front over time obtain through this method is consistent with the observations from a soil moisture sensor which was placed at a depth below 20 cm. The results obtained in this study demonstrate the ability of such array GPR system to monitor a subsurface dynamic process like water infiltration accurately and quantitatively.

Here we present a Ground Penetrating Radar (GPR) system based on a ground-coupled, densely populated antenna array for monitoring the dynamic process of subsurface water infiltration. A time-lapse radar image of the infiltration process allowed estimating the depth of the wetting front during the course of the infiltration process.

利用阵列天线探地雷达采集的时移多偏移收集跟踪入渗前深度

A Ground Penetrating Radar (GPR) system based on a ground-coupled, densely populated antenna array was used to collect data during an infiltration ...

Composition and Distribution Analysis of Bioaerosols Under Different Environmental Conditions

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

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

不同环境条件下生物气溶胶的组成及分布分析

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

Atom Probe Tomography Analysis of Exsolved Mineral Phases

Element diffusion rates and temperature/pressure control a range of fundamental volcanic and metamorphic processes. Such processes are often recorded in lamellae exsolved from host mineral phases. Thus, the analysis of the orientation, size, morphology, composition and spacing of exsolution lamellae is an area of active research in the geosciences. The conventional study of these lamellae has been conducted by scanning electron microscopy (SEM) and transmission electron microscopy (TEM), and more recently with focused ion beam (FIB)-based nanotomography, yet with limited chemical information. Here, we explore the use of atom probe tomography (APT) for the nanoscale analysis of ilmenite exsolution lamellae in igneous titanomagnetite from ash deposits erupted from the active Soufri&#232;re Hills Volcano (Montserrat, British West Indies). APT allows the precise calculation of interlamellar spacings (14&#8211;29 &#177; 2 nm) and reveals smooth diffusion profiles with no sharp phase boundaries during the exchange of Fe and Ti/O between the exsolved lamellae and the host crystal. Our results suggest that this novel approach permits nanoscale measurements of lamellae composition and interlamellar spacing that may provide a means to estimate the lava dome temperatures necessary to model extrusion rates and lava dome failure, both of which play a key role in volcanic hazard mitigation efforts.

Analysis of the morphology, composition, and spacing of exsolution lamellae can provide essential information to understand geological processes related to volcanism and metamorphism. We present a novel application of APT for the characterization of such lamellae and compare this approach to the conventional use of electron microscopy and FIB-based nanotomography.

原子探针断层扫描分析的解脱矿物相

Element diffusion rates and temperature/pressure control a range of fundamental volcanic and metamorphic processes. Such processes are often recorded in ...

Combining Fluidic Devices with Microscopy and Flow Cytometry to Study Microbial Transport in Porous Media Across Spatial Scales

Understanding the transport, dispersion and deposition of microorganisms in porous media is a complex scientific task comprising topics as diverse as hydrodynamics, ecology and environmental engineering. Modeling bacterial transport in porous environments at different spatial scales is critical to better predict the consequences of bacterial transport, yet current models often fail to up-scale from laboratory to field conditions. Here, we introduce experimental tools to study bacterial transport in porous media at two spatial scales. The aim of these tools is to obtain macroscopic observables (such as breakthrough curves or deposition profiles) of bacteria injected into transparent porous matrices. At the small scale (10-1000 &#181;m), microfluidic devices are combined with optical video-microscopy and image processing to obtain breakthrough curves and, at the same time, to track individual bacterial cells at the pore scale. At larger scale, flow cytometry is combined with a self-made robotic dispenser to obtain breakthrough curves. We illustrate the utility of these tools to better understand how bacteria are transported in complex porous media such as the hyporheic zone of streams. As these tools provide simultaneous measurements across scales, they pave the way for mechanism-based models, critically important for upscaling. Application of these tools may not only contribute to the development of novel bioremediation applications but also shed new light on the ecological strategies of microorganisms colonizing porous substrates.

Breakthrough curves (BTCs) are efficient tools to study the transport of bacteria in porous media. Here we introduce tools based on fluidic devices in combination with microscopy and flow cytometric counting to obtain BTCs.

将流体设备与显微镜和流式细胞学相结合，研究跨空间尺度的多孔介质中的微生物传输

Understanding the transport, dispersion and deposition of microorganisms in porous media is a complex scientific task comprising topics as diverse as ...

Ecotoxicological Methodologies to Evaluate Biomarkers at Different Scales in Neotropical Anurans

The new questions in ecotoxicology highlight the importance of applying a battery of biomarkers, as this results in ecotoxicological predictions that improve not only the interpretation of the effects of environmental stressors on organisms but also the determination of their possible impact. It is well known that the use of ecotoxicological biomarkers at different levels of organization allows for the prediction of the biological responses of organisms to environmental stressors, which is useful in environmental risk assessment. 
Nevertheless, it is necessary to consider the optimization of basic procedures, to generate historical data in control groups, and to employ specific bioassays to evaluate responses in organs and tissues in order to elucidate the nature and variation of the effects observed. Therefore, the present work aims to describe several ecotoxicological methodologies employed in all stages of neotropical anurans at different ecological levels and to validate them as useful biomarkers to be used both in wildlife and in laboratory conditions. In this work, these biomarkers were applied at the individual/organismic level (body condition index), histological/physiological level (histopathology, histometric, and pigmentary analyses), biochemical level (oxidative stress enzymes), and genetic level (direct and oxidative damage in DNA by comet assay). 
Although these methodologies have small variations or modifications depending on the species, these techniques provide effective biomarkers for evaluating the effect of xenobiotics on anurans, which possess certain characteristics that make them useful indicator species of aquatic and terrestrial ecosystems. In conclusion, the battery of biomarkers employed in the present study has proven to be adequate for estimating toxic responses in Neotropical anurans and can be further recommended as bioindicators for identifying the impact of pollutants on the aquatic ecosystems of the region. Finally, it is recommended to achieve the standardization of these important biomarkers for anurans in specific regions as well as to possibly include them in risk assessments and decision-making.

<meta charset="utf8"></head><body>评估新热带 Anurans 不同尺度生物标志物的生态毒理学方法

In this paper, standardized ecotoxicological methods for the evaluation of biomarkers in neotropical anuran species are presented. Specifically, this paper details several methodologies at different scales of ecotoxicological evaluation, such as the genetic, cellular-histological, biochemical, morphological, and individual levels.

评估新热带 Anurans 不同尺度生物标志物的生态毒理学方法

The new questions in ecotoxicology highlight the importance of applying a battery of biomarkers, as this results in ecotoxicological predictions that ...

高通量树木年轮分析和密度估计

Tree Core Analysis with X-ray Computed Tomography

An X-ray computed tomography (CT) toolchain is presented to obtain tree-ring width (TRW), maximum latewood density (MXD), other density parameters, and quantitative wood anatomy (QWA) data without the need for labor-intensive surface treatment or any physical sample preparation. The focus here is on increment cores and scanning procedures at resolutions ranging from 60 &#181;m down to 4 &#181;m. Three scales are defined at which wood should be looked at: (i) inter-ring scale, (ii) ring scale, i.e., tree-ring analysis and densitometry scale, as well as (iii) anatomical scale, the latter approaching the conventional thin-section quality. Custom-designed sample holders for each of these scales enable high-throughput scanning of multiple increment cores. A series of software routines were specifically developed to efficiently treat three-dimensional X-ray CT images of the tree cores for TRW and densitometry. This work briefly explains the basic principles of CT, which are needed for a proper understanding of the protocol. The protocol is presented for some known species that are commonly used in dendrochronology. The combination of rough density estimates, TRW and MXD data, as well as quantitative anatomy data, allows us to broaden and deepen current analyses for climate reconstructions or tree response, as well as further develop the field of dendroecology/climatology and archeology.

作者聚焦：用于树芯分析的 X 射线 CT 工具链的进步

Here we show how to process tree cores with an X-ray computed tomography toolchain. Except for chemical extraction for some purposes, no further physical lab treatment is needed. The toolchain can be used for biomass estimations, for obtaining MXD/tree-ring width data as well as for obtaining quantitative wood anatomy data.

使用 X 射线计算机断层扫描进行树芯分析

An X-ray computed tomography (CT) toolchain is presented to obtain tree-ring width (TRW), maximum latewood density (MXD), other density parameters, and ...