http://lod.bco-dmo.org/id/dataset/784927
eng; USA
utf8
dataset
Highest level of data collection, from a common set of sensors or instrumentation, usually within the same research project
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
2019-12-20
ISO 19115-2 Geographic Information - Metadata - Part 2: Extensions for Imagery and Gridded Data
ISO 19115-2:2009(E)
Collections of fish and invertebrates settled in artificial seagrass landscapes
2019-12-23
publication
2019-12-23
revision
Marine Biological Laboratory/Woods Hole Oceanographic Institution Library (MBLWHOI DLA)
2020-02-24
publication
https://doi.org/10.1575/1912/bco-dmo.784927.1
Lauren Yeager
University of Texas - Marine Science Institute
principalInvestigator
F. Joel Fodrie
University of North Carolina at Chapel Hill
principalInvestigator
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
publisher
Cite this dataset as: Yeager, L., Fodrie, F. (2019) Collections of fish and invertebrates settled in artificial seagrass landscapes. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2019-12-23 [if applicable, indicate subset used]. doi:10.1575/1912/bco-dmo.784927.1 [access date]
Dataset Description: <p>Collections of fish and invertebrates settles in artificial seagrass landscapes collected between June and August 2018.</p> Methods and Sampling: <p>We measured recruitment of fishes and crabs to artificial and natural seagrass beds in Back Sound, North Carolina from June to August 2018.&nbsp; We sampled 26 artificial seagrass landscapes defined by 18m x 13m landscape extents (234 m<sup>2</sup>). Within each landscape, we varied habitat amount and fragmentation independently in a crossed design. We created a custom algorithm to generate random landscapes using the randomHabitat function in the secr package in R (Efford 2018, R Core Team 2018). Landscapes were generated along two orthogonal axes of habitat cover (10-60%) and fragmentation using a random modified clusters method (percolation probability = 0.10-0.59 which determines patch number; higher percolation coefficients correspond to less patchiness)(Saura and Martinez-Millan 2000). Landscapes were constrained to fall within 2% of the area input parameter, while holding patch number similar within fragmentation levels (1, 2-3, 4-5, 6-7, or 8-10 patches for each level). Using this approach, we constructed landscapes in which seagrass area and number of patches were uncorrelated (R = -0.02), allowing us to independently assess the effects of seagrass area and habitat configuration on fish communities across experimental study sites. Artificial seagrass units (ASUs) were used to create artificial seagrass landscapes.&nbsp; ASUs were made by tying green plastic ribbon to polyethylene mesh cut into 1.2m x 0.86m rectangles, with ~450, 15 cm tall shoots (with 2 blades each) attached each unit. ASUs were deployed by affixing ASUs in designated configurations to bare sediment using metal lawn staples. These artificial landscapes were deployed between May 23 to May 31, 2018.&nbsp; We compared the artificial seagrass landscapes to natural landscapes in the same area.&nbsp; We sampled 18 haphazardly selected natural seagrass patches that were at least 100 m away from the artificial seagrass landscapes.</p>
<p>We used Standardized Monitoring Units for Reef Fishes (SMURFs, Ammann 2004) to measure recruitment of fishes and invertebrates into each landscape.&nbsp; SMURFs used in this study were 60 x 15 x 20 cm in size with an outer shell made from 5 cm x 7.6 cm polyethylene mesh.&nbsp; Each SMURF was filled with crumpled 2.5 x 2.5 cm polyethylene mesh and plastic mesh produce bags (<a href="https://www.amazon.com/dp/B01LWL1YFT/ref=cm_sw_r_cp_api_i_J9TzCbZZ5GKR6">https://www.amazon.com/dp/B01LWL1YFT/ref=cm_sw_r_cp_api_i_J9TzCbZZ5GKR6</a>). For deployment, SMURFs were deployed attached to the bottom at one end, but floated vertically in the water column.&nbsp; SMURFs were deployed for ~24hrs, including overnight, and collected before noon on the following day (pick-up times are included in the data).&nbsp; Upon retrieval, the SMURF was enclosed in a custom made BINKE net (Anderson and Carr 1998) made out of 1.5 mm square nylon netting.&nbsp; The SMURF was brought to the boat within the enclosed BINKE net and placed into a large plastic tub.&nbsp; It was shaken vigorously while being rinsed with buckets of seawater and then the rinse water in the tub was visually inspected for organisms which we collected, placed in a resealable plastic bag, and quickly froze in an ice and seawater slurry. This process was repeated until three successive rinses yielded no new organisms.&nbsp; The water in the tub was passed through a 1 mm mesh sieve to ensure no organisms remained in the tub. All organisms were returned to the lab for processing. Each landscape was sampled on 9 different dates between June and August, representing the major recruitment period for most fishes in this system.</p>
Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1635950 Award URL: http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1635950
Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1661683 Award URL: https://www.nsf.gov/awardsearch/showAward?AWD_ID=1661683
completed
Lauren Yeager
University of Texas - Marine Science Institute
750 Channel View Dr
Port Aransas
TX
78373
US
laurenayeager@gmail.com
pointOfContact
F. Joel Fodrie
University of North Carolina at Chapel Hill
252-726-6841
Institute of Marine Sciences & Department of Marine Sciences 3431 Arendell Street
Morehead City
NC
28557
USA
jfodrie@unc.edu
pointOfContact
asNeeded
Dataset Version: 1
Unknown
Sample_ID
Landscape_type
Percent_cover_treatment
Fragmentation_treatment
Site
Pick_up_date
Pick_up_time
Gear
Latitude
Longitude
Processed_by
Taxa
Size
Larvae_settler
N
Notes
PickUp_DateTime_UTC_ISO
theme
None, User defined
sample identification
sample type
percent coverage
treatment
site
date
time of day
sampling_method
latitude
longitude
investigator
taxon
length
flag
count
comments
ISO_DateTime_UTC
featureType
BCO-DMO Standard Parameters
otherRestrictions
otherRestrictions
Access Constraints: none. Use Constraints: Please follow guidelines at: http://www.bco-dmo.org/terms-use Distribution liability: Under no circumstances shall BCO-DMO be liable for any direct, incidental, special, consequential, indirect, or punitive damages that result from the use of, or the inability to use, the materials in this data submission. If you are dissatisfied with any materials in this data submission your sole and exclusive remedy is to discontinue use.
Collaborative Research: Habitat fragmentation effects on fish diversity at landscape scales: experimental tests of multiple mechanisms
https://www.bco-dmo.org/project/714026
Collaborative Research: Habitat fragmentation effects on fish diversity at landscape scales: experimental tests of multiple mechanisms
<p>Amount and quality of habitat is thought to be of fundamental importance to maintaining coastal marine ecosystems. This research will use large-scale field experiments to help understand how and why fish populations respond to fragmentation of seagrass habitats. The question is complex because increased fragmentation in seagrass beds decreases the amount and also the configuration of the habitat (one patch splits into many, patches become further apart, the amount of edge increases, etc). Previous work by the investigators in natural seagrass meadows provided evidence that fragmentation interacts with amount of habitat to influence the community dynamics of fishes in coastal marine landscapes. Specifically, fragmentation had no effect when the habitat was large, but had a negative effect when habitat was smaller. In this study, the investigators will build artificial seagrass habitat to use in a series of manipulative field experiments at an ambitious scale. The results will provide new, more specific information about how coastal fish community dynamics are affected by changes in overall amount and fragmentation of seagrass habitat, in concert with factors such as disturbance, larval dispersal, and wave energy. The project will support two early-career investigators, inform habitat conservation strategies for coastal management, and provide training opportunities for graduate and undergraduate students. The investigators plan to target students from underrepresented groups for the research opportunities.</p>
<p>Building on previous research in seagrass environments, this research will conduct a series of field experiments approach at novel, yet relevant scales, to test how habitat area and fragmentation affect fish diversity and productivity. Specifically, 15 by 15-m seagrass beds will be created using artificial seagrass units (ASUs) that control for within-patch-level (~1-10 m2) factors such as shoot density and length. The investigators will employ ASUs to manipulate total habitat area and the degree of fragmentation within seagrass beds in a temperate estuary in North Carolina. In year one, response of the fishes that colonize these landscapes will be measured as abundance, biomass, community structure, as well as taxonomic and functional diversity. Targeted ASU removals will then follow to determine species-specific responses to habitat disturbance. In year two, the landscape array and sampling regime will be doubled, and half of the landscapes will be seeded with post-larval fish of low dispersal ability to test whether pre- or post-recruitment processes drive landscape-scale patterns. In year three, the role of wave exposure (a natural driver of seagrass fragmentation) in mediating fish community response to landscape configuration will be tested by deploying ASU meadows across low and high energy environments.</p>
Habitat Fragmentation
largerWorkCitation
project
eng; USA
oceans
-76.602848
-76.588016
34.70033333
34.7067
2018-06-07
2018-08-17
North Carolina
0
BCO-DMO catalogue of parameters from Collections of fish and invertebrates settled in artificial seagrass landscapes
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
http://lod.bco-dmo.org/id/dataset-parameter/784947.rdf
Name: Sample_ID
Units: unitless
Description: Unique sample identifier: site + date
http://lod.bco-dmo.org/id/dataset-parameter/784948.rdf
Name: Landscape_type
Units: unitless
Description: Was the SMURF placed in a natural seagrass bed (natural) or one made of artifical seagrass units (ASU)
http://lod.bco-dmo.org/id/dataset-parameter/784949.rdf
Name: Percent_cover_treatment
Units: percentage (%)
Description: Percent cover treatment- area of the landscape covered in artificial seagrass
http://lod.bco-dmo.org/id/dataset-parameter/784950.rdf
Name: Fragmentation_treatment
Units: unitless
Description: Fragmentation treatment - percolation coefficient from random landscape generation"
http://lod.bco-dmo.org/id/dataset-parameter/784951.rdf
Name: Site
Units: unitless
Description: Site name
http://lod.bco-dmo.org/id/dataset-parameter/784952.rdf
Name: Pick_up_date
Units: unitless
Description: Date retrieved
http://lod.bco-dmo.org/id/dataset-parameter/784953.rdf
Name: Pick_up_time
Units: unitless
Description: Time retrieved on 24-hour clock in local time (EST)
http://lod.bco-dmo.org/id/dataset-parameter/784954.rdf
Name: Gear
Units: unitless
Description: Collection gear
http://lod.bco-dmo.org/id/dataset-parameter/784955.rdf
Name: Latitude
Units: decimal degrees
Description: Latitude (South is negative)
http://lod.bco-dmo.org/id/dataset-parameter/784956.rdf
Name: Longitude
Units: decimal degrees
Description: Longitude (West is negative)
http://lod.bco-dmo.org/id/dataset-parameter/784957.rdf
Name: Processed_by
Units: unitless
Description: Intials of person who processed the sample
http://lod.bco-dmo.org/id/dataset-parameter/784958.rdf
Name: Taxa
Units: unitless
Description: Taxa name
http://lod.bco-dmo.org/id/dataset-parameter/784959.rdf
Name: Size
Units: millimeter (mm)
Description: Standard length (fish), carapace length (shrimp), or carapace width (crabs)
http://lod.bco-dmo.org/id/dataset-parameter/784960.rdf
Name: Larvae_settler
Units: unitless
Description: Was the organism in the larval stage or recently settled? Y = yes, N = no
http://lod.bco-dmo.org/id/dataset-parameter/784961.rdf
Name: N
Units: unitless
Description: Count, number of individuals
http://lod.bco-dmo.org/id/dataset-parameter/784962.rdf
Name: Notes
Units: unitless
Description: Notes
http://lod.bco-dmo.org/id/dataset-parameter/784963.rdf
Name: PickUp_DateTime_UTC_ISO
Units: yyyy-MM-dd'T'HH:mm
Description: Pick up date and time in UTC and ISO formatted. The column shows up as nd when there was no local time defined for that specific row.
GB/NERC/BODC > British Oceanographic Data Centre, Natural Environment Research Council, United Kingdom
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
63681
https://darchive.mblwhoilibrary.org/bitstream/1912/25431/1/dataset-784927_smurf-faunal-settlement__v1.tsv
download
https://doi.org/10.1575/1912/bco-dmo.784927.1
download
onLine
dataset
<p>We measured recruitment of fishes and crabs to artificial and natural seagrass beds in Back Sound, North Carolina from June to August 2018.&nbsp; We sampled 26 artificial seagrass landscapes defined by 18m x 13m landscape extents (234 m<sup>2</sup>). Within each landscape, we varied habitat amount and fragmentation independently in a crossed design. We created a custom algorithm to generate random landscapes using the randomHabitat function in the secr package in R (Efford 2018, R Core Team 2018). Landscapes were generated along two orthogonal axes of habitat cover (10-60%) and fragmentation using a random modified clusters method (percolation probability = 0.10-0.59 which determines patch number; higher percolation coefficients correspond to less patchiness)(Saura and Martinez-Millan 2000). Landscapes were constrained to fall within 2% of the area input parameter, while holding patch number similar within fragmentation levels (1, 2-3, 4-5, 6-7, or 8-10 patches for each level). Using this approach, we constructed landscapes in which seagrass area and number of patches were uncorrelated (R = -0.02), allowing us to independently assess the effects of seagrass area and habitat configuration on fish communities across experimental study sites. Artificial seagrass units (ASUs) were used to create artificial seagrass landscapes.&nbsp; ASUs were made by tying green plastic ribbon to polyethylene mesh cut into 1.2m x 0.86m rectangles, with ~450, 15 cm tall shoots (with 2 blades each) attached each unit. ASUs were deployed by affixing ASUs in designated configurations to bare sediment using metal lawn staples. These artificial landscapes were deployed between May 23 to May 31, 2018.&nbsp; We compared the artificial seagrass landscapes to natural landscapes in the same area.&nbsp; We sampled 18 haphazardly selected natural seagrass patches that were at least 100 m away from the artificial seagrass landscapes.</p>
<p>We used Standardized Monitoring Units for Reef Fishes (SMURFs, Ammann 2004) to measure recruitment of fishes and invertebrates into each landscape.&nbsp; SMURFs used in this study were 60 x 15 x 20 cm in size with an outer shell made from 5 cm x 7.6 cm polyethylene mesh.&nbsp; Each SMURF was filled with crumpled 2.5 x 2.5 cm polyethylene mesh and plastic mesh produce bags (<a href="https://www.amazon.com/dp/B01LWL1YFT/ref=cm_sw_r_cp_api_i_J9TzCbZZ5GKR6">https://www.amazon.com/dp/B01LWL1YFT/ref=cm_sw_r_cp_api_i_J9TzCbZZ5GKR6</a>). For deployment, SMURFs were deployed attached to the bottom at one end, but floated vertically in the water column.&nbsp; SMURFs were deployed for ~24hrs, including overnight, and collected before noon on the following day (pick-up times are included in the data).&nbsp; Upon retrieval, the SMURF was enclosed in a custom made BINKE net (Anderson and Carr 1998) made out of 1.5 mm square nylon netting.&nbsp; The SMURF was brought to the boat within the enclosed BINKE net and placed into a large plastic tub.&nbsp; It was shaken vigorously while being rinsed with buckets of seawater and then the rinse water in the tub was visually inspected for organisms which we collected, placed in a resealable plastic bag, and quickly froze in an ice and seawater slurry. This process was repeated until three successive rinses yielded no new organisms.&nbsp; The water in the tub was passed through a 1 mm mesh sieve to ensure no organisms remained in the tub. All organisms were returned to the lab for processing. Each landscape was sampled on 9 different dates between June and August, representing the major recruitment period for most fishes in this system.</p>
Specified by the Principal Investigator(s)
<p>Samples were processed in the lab to identify and measure all organisms collected.&nbsp; Each sample was examined with the aid of a dissecting microscope and organisms were identified to the lowest reasonable taxonomic levels and the size each fish and crab was measured to the nearest mm.&nbsp; The purpose of these collections was to sample fish recruitment, but the SMURFs also attracted other post-settlement organisms including many shrimps and some larger juvenile fishes and crabs.&nbsp; We identified all organisms collected, including shrimp to higher level taxonomic groupings (family or infraorder), even if they were not recently recruited from the plankton. We then indicated whether organisms were likely larvae/new recruits vs. other post-settlement organisms (via the “Larvae.settler” column in the dataset).&nbsp; We considered fish &lt;20 mm SL as new recruits and larval crabs in Megalopa stage or newly metamorphosed (&lt;3 mm carapace width) as larvae/settlers.</p>
<p>BCO-DMO processing notes:</p>
<ul>
<li>Adjusted titles to comply with database set-up</li>
<li>Replaced comma by semicolon in "Notes" column</li>
<li>Added PickUp_DateTime_UTC_ISO column</li>
</ul>
<p>&nbsp;</p>
Specified by the Principal Investigator(s)
asNeeded
7.x-1.1
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact