Contributors | Affiliation | Role |
---|---|---|
Maas, Amy | Bermuda Institute of Ocean Sciences (BIOS) | Principal Investigator |
Blanco-Bercial, Leocadio | Bermuda Institute of Ocean Sciences (BIOS) | Co-Principal Investigator |
Gossner, Hannah | Bermuda Institute of Ocean Sciences (BIOS) | Technician |
York, Amber D. | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
One pair of 1m2 MOCNESS (Multiple Open Closing Nets with Environmental Sensor System) tows were performed during each cruise- one during the day, and one at night (MOCNESS, Wiebe et al, 1985). Nets with 150um mesh were used to better capture the smaller midwater zooplankton community in the region. Eight nets were fired in sequence along the upcast to capture spatially discrete zooplankton samples between 600m and the surface. While nets one, two, and three consistently targeted depths of 600-500m, 500m-400m, and 400-300m, depths for nets four through eight varied based on hydrographic features including the thermocline, deep chlorophyll maximum, and oxygen minimum zone (Maas et al, 2014, Steinberg et al, 2008). Once onboard, samples were split in two using a Motoda splitter (Motoda, 1959) with half preserved with sodium tetraborate buffered 4% formalin in seawater to be scanned with a ZooSCAN (Gorsky et al, 2010) and half placed in 95% undenatured ethanol for metabarcoding.
A representative subsample of the formalin-preserved zooplankton community from each net were imaged using a ZooSCAN ver. 4 at either 4,800 dpi or 2,400 dpi (following the methods in: Gorsky et al., 2010, Vandromme et al., 2012 as detailed in Maas et al. 2021). The change in resolution partway through the project was a result of recommendations from Hydroptic and loss of software support for 4800dpi imaging. In order to better represent all size classes in the images, the original sample was divided into three size categories. All individuals larger than 2 cm were selected by eye and scanned separately from all the others (fraction "d1"). The remainder of the sample was sieved through a 1-mm mesh sieve, and both size fractions were individually scanned ("d2" >1000um, "d3" 153-1000um). From these smaller size fractions, at least 1500 particles were scanned after subsampling using a Motoda splitter (Motoda, 1959), requiring generation of two separate scans for both size classes. This resulted in a total of five images per net.
ZooSCAN Image names:
Image names include: cruise#_mocnessID_net#_sizefraction_ and _a|b if a replicate and end in _raw_1.tif
Multiple images of the same size fraction were sometimes taken to obtain a sufficient number of particles. These replicates are named a or b. If there is no replicate they don’t have a letter in the image name. An a and b scan were always done for size classes d2 and d3. This was important because the split size is for the sum of a+b (e.g. if a is ¼ and b is ¼, the acq_sub_part will be 0.5).
Example of image names:
ae2112_m22_n4_d3_a_raw_1.tif [a replicate]
ae2112_m22_n4_d3_b_raw_1.tif [b replicate]
ae2204_m27_n5_d1_raw_1.tif [no replicate]
This dataset contains the "object_id" (the particle identifier) which is constructed the same way as the image name except it as an additional _# at the end. This additional number in the object_id is added by the ZooProcess software (Hydroptic, 2016).
e.g.
object_id: ae1614_m3_n1_d2_a_1_100
image_name: ae1614_m3_n1_d2_a_1.tif
Particle names:
Names for particles follow the pattern "CruiseID_MocnessID_NetNumber_ScanFraction" followed by "_1_XXX", with "1" being automatically added by the software to indicate no duplicates of that scan and "XXX" being the unique particle number within that scan.
Parameter (column name) nomenclature and data origin:
* (see the "Parameters" section which contains all column information for the ecotaxa output table)
Parameters (column names) beginning with "object" include basic identifying metadata input by the user as well as all particle measurement data generated by ZooProcess. Any parameters beginning with "object_annotation" parameters are added by Ecotaxa. Parameters that begin with "sample" are sampling metadata input by the user during the scanning process. "Process" parameters describe the software and assumptions or corrections input during the data processing. "Acq" describes the portion of the sample scanned (input by user) and provides some summary data about the scanned image.
Interpreting acq_sub_part
For this project, the acq sub part is the fraction of the individual scan only. "A" and "B" scans of the same fraction can be statistically combined for analysis (e.g. d2_a and d2_b from the same net can be combined by adding the sub parts to create just a "d2" group).
Instruments:
The Multiple Opening/Closing Net and Environmental Sensing System or MOCNESS is a family of net systems based on the Tucker Trawl principle. There are currently 8 different sizes of MOCNESS in existence which are designed for capture of different size ranges of zooplankton and micro-nekton. Each system is designated according to the size of the net mouth opening and in two cases, the number of nets it carries. The original MOCNESS (Wiebe et al, 1976) was a redesigned and improved version of a system described by Frost and McCrone (1974)(from MOCNESS manual). The MOCNESS used in this experiment is a 1m2 (mouth size) rigged with nine 150um mesh nets. One is flown open on the downcast to balance the net (Net 0- contents preserved but not analyzed), and the other eight (Net 1-8) are triggered on the upcast at desired depths. This particular MOCNESS was originally manufactured by Biological Environmental Sensor Systems (BESS), but was refit with new electronics from SIO/STS in 2017 (Net Interface Unit, Net Angle Sensor) to allow it to interface with Seabird instruments (SBE9Plus CTD, SBE3S Temperature, SBE4C Conductivity, SBE11 Deck Box).
The ZooSCAN (CNRS patent) system makes use of scanner technology with custom lighting and a watertight scanning chamber into which liquid zooplankton samples can be placed. The scanner recovers a high-resolution, digital image and the sample can be recovered without damage. These digital images can then be investigated by computer processing. While the resolution of the digitized zooplankton images is lower than the image obtained using a binocular microscope, this technique has proven to be more than adequate for large sample sets. Identification of species is done by automatic comparison of the image (vignette) of each individual animal in the scanned image with a library data set which may be built by the investigator for each individual survey or imported from a previous survey. The latest machine learning algorithm allows high recognition levels even if we recommend complementary manual sorting to achieve a high number of taxonomic groups. Scans for this dataset performed with a ZooSCAN (Hydroptic, HYDROPTIC_V4) running with Vuescan (version 9.5.24) and ZooProcess (version 8.22, ImageJ macro suite).
Scans were processed using ZooProcess (version 8.22, ImageJ macro suite). The "Convert and process from RAW" function was used to separate particles into individual vignettes and generate a suite of measurements for each particle. "Doubles" (vignettes containing more than one particle) were manually separated in the software and reprocessed.
Example vignettes (see Supplemental files for example image download):
Processed scans and their corresponding metadata were then uploaded to Ecotaxa (Picheral et al, https://ecotaxa.obs-vlfr.fr/), where a training set was created using manually classified images from this project as well as existing validated images from other projects in the Sargasso Sea. Classification categories were chosen based on taxon of interest, identification level in previous projects, and known limitations of the software. Generally, broader level taxonomic groups are used. Identification of all particles was predicted, then manually validated.
Data versioning
The ecotaxa data included in this dataset version are "Ecotaxa Export version 1.0."
The ecotaxa export file will be updated in a versioned manner as validation of identification is completed. Ecotaxa output versions are as follows:
Version 1: No identifications, predicted or validated
Version 2: All identifications predicted
Version 3: All identifications validated
Version 1:
* Data from source file ecotaxa_export_5446_20240606_1831 v1.0.tsv were imported into the BCO-DMO data system as the primary table for this dataset with "nan" values interpreted as missing data identifiers.
* After import, select columns designated to have the missing data identifier 99999 had a find and replace operation performed to turn 99999 values into system missing data identifiers. This was not done on import since only some columns were described as using this identifier by the data providers. 99999 is within the valid numeric range for columns such as object_intden and object_area_exec so it is possible that if there were any real 99999 values, they were instead interpreted as missing data.
** In the BCO-DMO data system missing data identifiers are displayed according to the format of data you access. For example, in csv files it will be blank (null) values. In Matlab .mat files it will be NaN values. When viewing data online at BCO-DMO, the missing value will be shown as blank (null) values.
* Parameters (column names) renamed to comply with BCO-DMO naming conventions. See https://www.bco-dmo.org/page/bco-dmo-data-processing-conventions
* object_ISO_DateTime_UTC added from local date and time columns.
* extra trailing slash removed in object_link (all values were "http://www.zooscan.obs-vlfr.fr//"). This link may not be persistent for long term curation, a citation for the site was added as a related publication along with the date it was accessed.
* lat lon column names changed for consistency with another dataset of the same data type https://www.bco-dmo.org/dataset/932252. object_lat -> object_lat_start and object_lon -> object_lon_start to correspond to _end columns.
* lat and lons rounded to 5 decimal places.
* References in metadata to Ecotaxa "annotation" columns were removed as those columns were not provided with this version of the data table. They will be included in future updates to this dataset (see Methodolgy and Data Procesing sections).
* format in acq_scan_time updated to newer ecotaxa convention (e.g. times 112023 -> 12:20:23).
File |
---|
931883_v1_zoo-med-agg_ecotaxa-and-zooprocess.csv (Comma Separated Values (.csv), 298.83 MB) MD5:799e487dc69e69f786a045ee46db68dd Primary data file for dataset ID 931883, version 1. |
File |
---|
Example copepod vignette filename: copepod_6994.jpg (JPEG Image (.jpg), 289.71 KB) MD5:48a2abf039b09fd29dd60d2c8b5e6c41 Example vignette of one object. See methodology for more details about how these are used in Ecotaxa and how the vignettes are extracted from raw ZooScan images (see "Related Datasets" section for ZooScan images). |
Example ostracod vignette filename: ostracod_female.jpg (JPEG Image (.jpg), 282.64 KB) MD5:d184d0302369c3e457dfdd328a46d5bc Example vignette of one object. See methodology for more details about how these are used in Ecotaxa and how the vignettes are extracted from raw ZooScan images (see "Related Datasets" section for ZooScan images). |
Example pteropod vignette filename: thecosome1.jpg (JPEG Image (.jpg), 196.87 KB) MD5:30de45c826833e537998cc589e142ca7 Example vignette of one object. See methodology for more details about how these are used in Ecotaxa and how the vignettes are extracted from raw ZooScan images (see "Related Datasets" section for ZooScan images). |
Parameter | Description | Units |
object_id | Particle identification number. Typically cruiseID_mocnessID_net#_taxonomy_image#. [Source: User] | unitless |
object_lat_start | Starting latitude of sample collection. [Source: User] | Decimal degrees |
object_lon_start | Starting longitude of sample collection. [Source: User] | Decimal degrees |
object_date | Date of sample collection. Local time zone (ADT/AST). Source: User] | unitless |
object_time | Start time of sample collection. Local time zone (ADT/AST). [Source: User] | unitless |
object_ISO_DateTime_UTC | Datetime with timezone (start time of sample collection). Format ISO 8601, Time Zone UTC. [Source: User] | unitless |
object_link | URL to Villefranche sur mer Quantitative Imaging Platform which hosts manuals summarizing image capture and upload. Autogenerated by software. [Source: Zooprocess] | unitless |
object_depth_min | Minimum depth of sample collection (Zmin, shallowest net depth). [Source: User] | Meters |
object_depth_max | Maximum depth of sample collection (Zmax, deepest net depth). [Source: User] | Meters |
object_lat_end | Ending latitude of sample collection. [Source: User] | Decimal degrees |
object_lon_end | Ending longitude of sample collection. [Source: User] | Decimal degrees |
object_area | Surface area of the object. [Source: Zooprocess] | Square pixels |
object_mean | Average grey value within the object. Pixel intensity value 0-255 (8 bit greyscale image). | pixel intensity |
object_stddev | Standard deviation of the grey value used to generate the mean grey value. Pixel intensity value 0-255 (8 bit greyscale image). | pixel intensity |
object_mode | Modal grey value within the object. Pixel intensity value 0-255 (8 bit greyscale image). | pixel intensity |
object_min | Minimum grey value within the object (0=black). Pixel intensity value 0-255 (8 bit greyscale image). | pixel intensity |
object_max | Maximum grey value within the object (255=white). Pixel intensity value 0-255 (8 bit greyscale image). | pixel intensity |
object_x | X position of the center of gravity of the object within the vignette. [Source: Zooprocess] | Pixels |
object_y | Y position of the center of gravity of the object within the vignette. [Source: Zooprocess] | Pixels |
object_xm | X position of the center of gravity of the object's grey levels within the vignette. [Source: Zooprocess] | Pixels |
object_ym | Y position of the center of gravity of the object's grey levels within the vignette. [Source: Zooprocess] | Pixels |
object_perim | Length of the outside boundary (perimeter) of the object. [Source: Zooprocess] | Pixels |
object_bx | X coordinate of the top left point of the smallest rectangle enclosing the object within the whole scan image. [Source: Zooprocess] | Pixels |
object_by | Y coordinate of the top left point of the smallest rectangle enclosing the object within the whole scan image. [Source: Zooprocess] | Pixels |
object_width | Width of the smallest rectangle enclosing the object. [Source: Zooprocess] | Pixels |
object_height | Height of the smallest rectangle enclosing the object. [Source: Zooprocess] | Pixels |
object_major | Primary axis of the best fitting ellipse for the object. [Source: Zooprocess] | Pixels |
object_minor | Secondary axis of the best fitting ellipse for the object. [Source: Zooprocess] | Pixels |
object_angle | Angle between the primary axis and a line parallel to the x-axis of the image. [Source: Zooprocess] | Decimal degrees |
object_circ | Circularity. (4*pi*Area)/Perim^2. A value of 1 indicates a perfect circle, a value approaching 0 indicates an increasingly elongated polygon. . [Source: Zooprocess] | unitless |
object_feret | Maximum ferret diameter, i.e. the longest distance between any two points along the object boundary. [Source: Zooprocess] | Pixels |
object_intden | Integrated density. The sum of the grey values of the pixels in the object (i.e. = Area*Mean). . [Source: Zooprocess] | unitless |
object_median | Median grey value within the object. Pixel intensity value 0-255 (8 bit greyscale image). [Source: Zooprocess] | pixel intensity |
object_skew | Skewness (third order moment about the mean) of the histogram of the grey level values. [Source: Zooprocess] | unitless |
object_kurt | Kurtosis (fourth order moment about the mean) of the histogram of grey level values. [Source: Zooprocess] | unitless |
object_perc_area | Percentage of object's surface area that is comprised of holes, defined as the background grey level. [Source: Zooprocess] | Percentage |
object_xstart | X coordinate of the top left point of the image within the scan. [Source: Zooprocess] | Pixels |
object_ystart | Y coordinate of the top left point of the image within the scan. [Source: Zooprocess] | Pixels |
object_area_exc | Surface area of the object excluding holes (=Area*(1-(%area/100)). [Source: Zooprocess] | Square pixels |
object_fractal | Fractal dimension of the object boundary (Berube and Jebrak, 1999). [Source: Zooprocess] | unitless |
object_skelarea | Surface area of skeleton in pixels. In a binary image, the skeleton is obtained by repeatedly removing pixels from the edges of objects until they are reduced to the width of a single pixel. (Berube and Jebrak, 1999). [Source: Zooprocess] | Pixels |
object_slope | Slope of the grey level normalized cumulative histogram. [Source: Zooprocess] | unitless |
object_histcum1 | Grey level at 25% of the normalized cumulative histogram of grey levels. [Source: Zooprocess] | pixel intensity |
object_histcum2 | Grey level at 50% of the normalized cumulative histogram of grey levels. [Source: Zooprocess] | pixel intensity |
object_histcum3 | Grey level at 75% of the normalized cumulative histogram of grey levels. [Source: Zooprocess] | pixel intensity |
object_xmg5 | X position of the center of gravity of the object using a gamma value of 5. [Source: Zooprocess] | Pixels |
object_ymg5 | Y position of the center of gravity of the object using a gamma value of 5. [Source: Zooprocess] | Pixels |
object_nb1 | Number of remaining objects in the image after thresholding on level Histcum 1. [Source: Zooprocess] | unitless |
object_nb2 | Number of remaining objects in the image after thresholding on level Histcum 2. [Source: Zooprocess] | unitless |
object_nb3 | Number of remaining objects in the image after thresholding on level Histcum 3. [Source: Zooprocess] | unitless |
object_compentropy | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_compmean | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_compslope | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_compm1 | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_compm2 | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_compm3 | always set to 0, measurement no longer perfomed in Zooprocess. [Source: Zooprocess] | unitless |
object_symetrieh | Bilateral horizonal symmetry index (Romagnan et al 2016). [Source: Zooprocess] | unitless |
object_symetriev | Bilateral vertical symmetry index (Romagnan et al 2016). [Source: Zooprocess] | unitless |
object_symetriehc | Symmetry of the object in relation to the horizontal axis after thresholding the grey level at Histcum 1 value. [Source: Zooprocess] | unitless |
object_symetrievc | Symmetry of the object in relation to the vertical axis after thresholding at grey level Histcum 1 value. [Source: Zooprocess] | unitless |
object_convperim | The perimeter of the smallest polygon within which all points of the object fit. [Source: Zooprocess] | Pixels |
object_convarea | The area of the smallest polygon within which all points of the object fit. [Source: Zooprocess] | Pixels |
object_fcons | Measure of contrast based on the texture feature descriptor (Amadasun and King, 1989). [Source: Zooprocess] | unitless |
object_thickr | Thickness ratio; relationship between the maximum thickness of an object and the average thickness of the object excluding the maximum. . [Source: Zooprocess] | unitless |
object_tag | Old variable which is no longer used (0 or 1; 1 if duplicate "tagged" object). [Source: Zooprocess] | unitless |
object_esd | Equivalent spherical diameter. Sqrt(area/?). [Source: Zooprocess] | Pixels |
object_elongation | Elongation index. Major axis/minor axis. [Source: Zooprocess] | unitless |
object_range | Range of grey values (0-255). [Source: Zooprocess] | pixel intensity |
object_meanpos | Relative position of the mean grey. (Mean grey- Max grey)/(Mean grey-Min grey). [Source: Zooprocess] | unitless |
object_centroids | Difference between the mass and the grey-level object's centroids. Square root ((objGreyX - objX)^2 + (objGreyY - objY)^2). [Source: Zooprocess] | Pixels |
object_cv | Coefficient of variation of grey values. 100*(stddev/mean). [Source: Zooprocess] | unitless |
object_sr | Index of variation of grey values. 100*(stddev/max-min)). [Source: Zooprocess] | unitless |
object_perimareaexc | Index of relative complexity of the perimeter. perimeter/area_exc. [Source: Zooprocess] | unitless |
object_feretareaexc | Alternate elongation index. feret/area_exc. [Source: Zooprocess] | unitless |
object_perimferet | Index of relative complexity of the perimeter. perim/feret. [Source: Zooprocess] | unitless |
object_perimmajor | Alternate index of relative complexity of the perimeter. perim/major. [Source: Zooprocess] | unitless |
object_circex | Circularity of the object excluding white pixels. (4*pi(?)*area_exc)/perimeter^2. [Source: Zooprocess] | unitless |
object_cdexc | Distance between the mass and the grey-level object's centroids. (centroid^2)/area_exc. [Source: Zooprocess] | Pixels |
sample_id | Name of sample (scan) from which the object originates (image_name without .tif extension). [Source: User] | unitless |
sample_dataportal_descriptor | Optional descriptor. [Source: User] | unitless |
sample_scan_operator | Initials of the individual who performed the scan. [Source: User] | unitless |
sample_ship | Research vessel (if applicable) where sample was taken. [Source: User] | unitless |
sample_program | Research program (if applicable) under which sample was taken. [Source: User] | unitless |
sample_stationid | Station identifier (if applicable) at which sample was taken. [Source: User] | unitless |
sample_bottomdepth | Recorded depth of the seafloor at the start of the tow. [Source: User] | Meters |
sample_ctdrosettefilename | Associated CTD file name (if applicable). [Source: User] | unitless |
sample_other_ref | Optional other reference notes. [Source: User] | unitless |
sample_tow_nb | Number of tows, if more than one, combined to create sample. [Source: User] | Count |
sample_tow_type | Type of tow profile used to collect sample. 1= oblique, 2 = horizontal, 3=vertical, 0= Other sampling method. [Source: User] | unitless |
sample_net_type | Type of net used to collect the sample (e.g. MOCNESS, Reeve, Tucker, etc). [Source: User] | unitless |
sample_net_mesh | Mesh size of the net used to collect the sample. [Source: User] | Microns |
sample_net_surf | Area of net mouth. [Source: User] | Meters squared |
sample_zmax | Maximum depth of tow or net for this sample. [Source: User] | Meters |
sample_zmin | Minimum depth of tow or net for this sample. [Source: User] | Meters |
sample_tot_vol | Total volume of water filtered while capturing this sample. [Source: User] | Meters cubed |
sample_comment | Optional comment on this sample. [Source: User] | unitless |
sample_tot_vol_qc | Quality flag for how volume of this tow or net was acquired. 1= RECORDED volume (flowmeter), 2= Calculated volume (using the mean volumne of other nets, 3= Estimated volume (net area * tow distance) . [Source: User] | unitless |
sample_depth_qc | Quality flag for how the depth of this tow or net was acquired. 1= Measured by a depth sensor, 2= Calculated from cable length and angle, 3= Estimated from cable length. [Source: User] | unitless |
sample_sample_qc | Quality flag for condition of the sample at time of scanning. Set of four digits defined below.; First digit is sample airtightness. 1=OK, 2=NOK (not ok); Second digit is sample richness. 1= Normal richness, 2=Very rich sample, 3=No plankton (almost) in sample; Third digit is sample condition. 1= Good condition , 2 = Dryed (no remaining liquid), 3= Rotton (loss of fixative); Fourth digit is disturbing elements. 1=No disturbing elements, 2=One of few large objects present in jar, 3=SOUP (phytoplankton, organic matter, clay/mud/mineral); . [Source: User] | unitless |
sample_barcode | Barcode number assigned to sample if applicable. [Source: User] | unitless |
sample_duration | Duration of the sampling tow. [Source: User] | Minutes |
sample_ship_speed | Average ship speed during tow. [Source: User] | Knots |
sample_cable_length | Maximum cable out during tow (m). [Source: User] | Meters |
sample_cable_angle | Angle of the net cable during the tow (degrees from vertical). [Source: User] | Degrees |
sample_cable_speed | Speed of the winch payout/retrival during the tow. [Source: User] | Meters per minute |
sample_nb_jar | Number of the jar containing the sample. [Source: User] | unitless |
sample_open | Undefined. [Source: User] | unitless |
process_id | Process identifier. "zooprocess" and then the sample ID. [Source: Zooprocess] | unitless |
process_date | Date the scan was performed. Local time zone (ADT/AST). [Source: Zooprocess] | unitless |
process_time | Time the scan was performed. Local time zone (ADT/AST). [Source: Zooprocess]. | unitless |
process_img_software_version | Version of zooprocess software utilized. [Source: Zooprocess] | unitless |
process_img_resolution | Resolution of the scan. [Source: Zooprocess] | Dpi |
process_img_od_grey | Parameter not used- always nan. [Source: Zooprocess] | unitless |
process_img_od_std | Parameter not used- always 0. [Source: Zooprocess] | unitless |
process_img_background_img | Image name of background scan used. [Source: Zooprocess] | unitless |
process_particle_version | Version of zooprocess software used to process particles. [Source: Zooprocess] | unitless |
process_particle_threshold | 8 bit coded grey level value to separate the objects from the background. [Source: Zooprocess] | pixel intensity |
process_particle_pixel_size_mm | The number of pixels per millimeter with this dpi. [Source: Zooprocess] | Pixels per millimeter |
process_particle_min_size_mm | Minimum size particle included in vignette extraction. [Source: Zooprocess] | Millimeters |
process_particle_max_size_mm | Maximum size particle included in vignette extraction. [Source: Zooprocess] | Millimeters |
process_particle_sep_mask | Whether or not to include a separation mask created during separation of touching vignettes. [Source: Zooprocess] | unitless |
process_particle_bw_ratio | ratio of pixels from the image that are above the threshold value (i.e; objects of image noise). [Source: Zooprocess] | unitless |
process_software | Software name, version, and date used to process this sample. [Source: Zooprocess] | unitless |
acq_id | Name of the fraction or replicate being imaged (format fraction_cruise_mocness_net). [Source: Zooprocess] | unitless |
acq_instrument | Type of instrument used to take original image (e.g. Zooscan, UVP, etc). [Source: User] | unitless |
acq_min_mesh | The minimum mesh size/minimum hypothetical particle size of the fraction being imaged. [Source: User] | Microns |
acq_max_mesh | The maximum mesh size/maximum hypothetical particle size of the fraction being imaged. [Source: User] | Microns |
acq_sub_part | Portion of the sample in this image- denominator of the ratio (e.g. 1/64 will read "64"). [Source: User] | Integer |
acq_sub_method | Method or splitter type used to subsample (e.g. Motoda, folsom). [Source: User] | unitless |
acq_hardware | Hardware used to image the sample including version number (Zooscan model). [Source: Zooprocess] | unitless |
acq_software | Software used to take the image- Vuescan version number. [Source: Zooprocess] | unitless |
acq_author | Initials of individual who took the image. [Source: Zooprocess] | unitless |
acq_imgtype | Type of image (e.g. zooscan, UVP). . [Source: Zooprocess] | unitless |
acq_scan_date | Date that the scan was performed. Local time zone (ADT/AST). [Source: Zooprocess] | unitless |
acq_scan_time | Time the scan was performed. Local time zone (ADT/AST). [Source: Zooprocess] | unitless |
acq_quality | Parameter not used- always nan. [Source: Zooprocess] | unitless |
acq_bitpixel | Flag- Vuescan coding of the grey resolution for the raw image. [Source: Zooprocess] | unitless |
acq_greyfrom | Flag- The green channel of image from the scanner sensor is converted in grey by Vuescan for the image saving and processing. [Source: Zooprocess] | unitless |
acq_scan_resolution | Flag- Vuescan coding of the resolution, utilized by Zooprocess to compute the pixel size and image resolution in dpi. [Source: Zooprocess] | unitless |
acq_rotation | Flag- The raw image from the scanner is rotated before being saved. [Source: Zooprocess] | unitless |
acq_miror | Flag- The raw image from the scanner is mirrored before being saved. [Source: Zooprocess] | unitless |
acq_xsize | Horizontal size of the scan. [Source: Zooprocess] | Pixels |
acq_ysize | Vertical size of the scan. [Source: Zooprocess] | Pixels |
acq_xoffset | Scan frame X offset, from scanner factory calibration. [Source: Zooprocess] | Pixels |
acq_yoffset | Scan frame Y offset, from scanner factory calibration. [Source: Zooprocess] | Pixels |
acq_lut_color_balance | Indicates that the raw image normalisation will be done by Zooprocess. [Source: Zooprocess] | unitless |
acq_lut_filter | If there is a filter in the acquisition LUT (all should be "no"). [Source: Zooprocess] | unitless |
acq_lut_min | Minimum 16 bit coded grey level utilized for the 16 to 8 bit raw image conversion/normalisation by Zooprocess. [Source: Zooprocess] | pixel intensity |
acq_lut_max | Maximum 16 bit coded grey level utilized for the 16 to 8 bit raw image conversion/normalisation by Zooprocess. [Source: Zooprocess] | pixel intensity |
acq_lut_odrange | Optical Density range for the 16 to 8 bit raw image conversion/normalisation by Zooprocess (always 1.8). [Source: Zooprocess] | unitless |
acq_lut_ratio | ratio applied to the acq_lut_max value for the 16 to 8 bit raw image conversion/normalisation by Zooprocess (always 1.15). [Source: Zooprocess] | unitless |
acq_lut_16b_median | Measured median grey level of the raw image. [Source: Zooprocess] | pixel intensity |
Dataset-specific Instrument Name | 1m MOCNESS |
Generic Instrument Name | MOCNESS1 |
Generic Instrument Description | The Multiple Opening/Closing Net and Environmental Sensing System or MOCNESS is a family of net systems based on the Tucker Trawl principle. The MOCNESS-1 carries nine 1-m2 nets usually of 335 micrometer mesh and is intended for use with the macrozooplankton. All nets are black to reduce contrast with the background. A motor/toggle release assembly is mounted on the top portion of the frame and stainless steel cables with swaged fittings are used to attach the net bar to the toggle release. A stepping motor in a pressure compensated case filled with oil turns the escapement crankshaft of the toggle release which sequentially releases the nets to an open then closed position on command from the surface. -- from the MOCNESS Operations Manual (1999 + 2003). |
Dataset-specific Instrument Name | ZooSCAN ver. 4 |
Generic Instrument Name | ZooSCAN |
Dataset-specific Description | http://www.hydroptic.com/index.php/public/Page/product_item/ZOOSCAN
A representative subsample of the formalin-preserved zooplankton community from each net were imaged using a ZooSCAN ver. 4 at either 4,800 dpi or 2,400 dpi (following the methods in: Gorsky et al., 2010, Vandromme et al., 2012 as detailed in Maas et al. 2021).
Scans for this dataset performed with a ZooSCAN (Hydroptic, HYDROPTIC_V4) running with Vuescan (version 9.5.24) and ZooProcess (version 8.22, ImageJ macro suite). |
Generic Instrument Description | Description excerpt from Hydroptic website
http://www.hydroptic.com/index.php/public/Page/product_item/ZOOSCAN
The ZooSCAN (CNRS patent) system makes use of scanner technology with custom lighting and a watertight scanning chamber into which liquid zooplankton samples can be placed. The scanner recovers a high-resolution, digitial image and the sample can be recovered without damage. These digital images can then be investigated by computer processing. While the resolution of the digitized zooplankton images is lower than the image obtained using a binocular microscope this technique has proved to be more than adequate for large sample sets. Identification of species is done by automatic comparison of the image (vignette) of each individual animal in the scanned image with a library data set which may be built by the investigator for each individual survey or imported from a previous survey. The latest machine learning algorithm allows high recognition levels even if we recommend complementary manual sorting to achieve a high number of taxonomic groups. |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2021-07-08 |
End Date | 2021-07-16 |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2021-11-16 |
End Date | 2021-11-19 |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2022-03-28 |
End Date | 2022-04-04 |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2022-07-13 |
End Date | 2022-07-18 |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2022-11-23 |
End Date | 2022-11-30 |
Website | |
Platform | R/V Atlantic Explorer |
Start Date | 2023-03-18 |
End Date | 2023-03-26 |
NSF Award Abstract:
The purpose of this collaborative project is to advance understanding of the role of marine planktonic animals (or zooplankton) in the biological pump, or transport of carbon from surface to deeper ocean waters. This movement of carbon from surface to deep ocean water can ultimately affect carbon dioxide in the atmosphere, with implications for global climate. Many marine zooplankton, including species of copepods and krill, play a direct role in the biological pump both because they are abundant and because they can migrate from surface waters at night, where they feed, to depths of more than 500 m at night. At the same time, some organisms called flux feeders will remain at depth and do not migrate. Instead, they rely on particles produced by other zooplankton feeding in surface waters. In this project, the investigators are focusing on populations of flux feeders in the deeper ocean waters of the Sargasso Sea. They are leveraging an ongoing long-term research program, conducting field collections using specialized nets and particle traps, as well lab experiments, as a way to understand how these organisms modify the particles around them. This project is supporting a postdoctoral scientist and providing research experiences for undergraduates at two institutions. An education specialist is creating lesson plans for an award-winning Ask-A-Biologist website, designed for public and K-12 audiences. Images of zooplankton will be disseminated to the public and scientific community via EcoTaxa (a web platform devoted to plankton biodiversity, with images and taxonomic annotation) and physical samples will be archived as part of a teaching library.
The oceanic biological carbon pump refers to the export of dissolved and particulate organic carbon to the deep ocean, and it is a significant driver of atmospheric carbon uptake by the oceans. Evidence from long-term research carried out at the Bermuda Atlantic Time-series Study (BATS) site suggests that the spectrum of particles collected by gel-traps below the euphotic zone changes drastically below 150 m, which is attributed to resident populations of zooplankton that feed on vertically migrating zooplankton as well as sinking particles. The goals of this study are to investigate the role of different zooplankton taxa on both particle aggregate formation and in particle transformation, and to compare and characterize the particles generated by the zooplankton communities with those collected by particle traps. The investigators are combining field collections with experiments onboard ship and in environmental chambers. They are collecting samples over two years, with three cruises a year to capture distinct seasons. They are assessing high-resolution vertical distribution of zooplankton in the upper 600 m using Multiple Opening-Closing Net and Environmental Sensing System (MOCNESS) tows during day- and night-time, to distinguish diel vertical migrators from resident populations and to quantify contributions to particulate organic carbon flux via fecal pellet production. On each cruise, sinking particles are being collected using gel trap tubes attached to the particle traps deployed monthly at BATS. In addition, roller tank experiments are determining how individual zooplankton mediate aggregate formation. Particle types and fecal pellets are being characterized using image analysis and DNA-based analysis of microbial communities. Finally, ongoing data collection from the long-term BATS program is providing invaluable environmental context and will ensure results from this study contribute to ongoing community efforts to observe and predict the fate of carbon in our global system.
This award reflects NSF's statutory mission and has been deemed worthy of support through evaluation using the Foundation's intellectual merit and broader impacts review criteria.
Funding Source | Award |
---|---|
NSF Division of Ocean Sciences (NSF OCE) | |
NSF Division of Ocean Sciences (NSF OCE) |