Abstract:
Multiple arrays with heated panels (1 degree Celsius and 2 degrees Celsius above ambient temperature and non-heated) were deployed subtidally in the Menai Strait for a period of 13 months from the summer of 2015 to the summer of 2016. The effect of temperature on species composition of the assemblage, seasonal effects and on the growth rates of one of the main colonisers, the polychaete Spirobranchus triqueter was assessed. Underwater photographs of the panels were taken regularly over the course of 13 months. The images were merged into a single image using Photoshop CS5. The growth rate of the main coloniser Spirobranchus triqueter and species diversity and percentage of the panel community were measured using Fiji(ImageJ) and Rstudio.
This project was funded by NERC: reference NE/J007501/1 "Effects of warming on recruitment and marine benthic community development in Antarctica".
Keywords:
Heated settlement panel, Menai Strait, community analysis, short-term, temperate ecosystem
Villota Nieva, L., Clark, M.S., Davies, A., & Peck, L.S. (2024). Species community analysis of heated panels deployed in the Menai Strait between summers 2015 and 2016 (Version 1.0) [Data set]. NERC EDS UK Polar Data Centre. https://doi.org/10.5285/b6d32e40-3c71-4bc5-83bf-e3a8c2b050dc
| Access Constraints: | Data are under embargo until publication of the associated manuscript. |
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| Use Constraints: | This data is governed by the NERC data policy http://www.nerc.ac.uk/research/sites/data/policy/ and supplied under Open Government Licence v.3 http://www.nationalarchives.gov.uk/doc/open-government-licence/version/3/. |
| Creation Date: | 2024-03-12 |
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| Dataset Progress: | Complete |
| Dataset Language: | English |
| ISO Topic Categories: |
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| Parameters: |
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| Personnel: | |
| Name | UK PDC |
| Role(s) | Metadata Author |
| Organisation | British Antarctic Survey |
| Name | Dr Leyre Villota Nieva |
| Role(s) | Investigator |
| Organisation | British Antarctic Survey |
| Name | Prof Melody S Clark |
| Role(s) | Investigator |
| Organisation | British Antarctic Survey |
| Name | Dr Andrew Davies |
| Role(s) | Investigator |
| Organisation | University of Rhode Island |
| Name | Prof Lloyd S Peck |
| Role(s) | Investigator |
| Organisation | British Antarctic Survey |
| Parent Dataset: | N/A |
| Reference: | Villota Nieva L, Clark MS, Davies AJ, Peck LS. Field simulated climate change has little effect on temperate marine encrusting communities. In prep. | |
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| Quality: | Panel instrumentation was regularly checked. | |
| Lineage: | Panel deployment: The panels were deployed in the Menai Strait, Wales, UK (53.2307 N, 4.1537 W). This is a special area of conservation (SAC) where the diversity of habitats and the strong tides have promoted high benthic diversity. The area is typified by muddy sand substrates with some boulders and rocky outcrops, creating islands for settlement and development of hard substratum communities. The dynamics of the water flow in the strait are dominated by strong tides, causing the water column to remain vertically mixed throughout the year, with little difference between surface and bottom water temperatures. Sea surface water temperature (SST) in the Menai Strait can vary annually between 5°C - 18°C, with SST temperatures recorded during the period of this study of 6°C - 16.3°C (https://seatemperature.info/menai-bridge-water-temperature.html) provided by the daily SST satellite readings from NOAA. The panels used in this experiment were of the same design and specification as described in Ashton et al., (2017) Current Biology 27: 2698-2705. In total, 12 panels were mounted on to 4 steel frames (3 panels per frame, 4 replicates per treatment (control, +1°C, +2°C)). The thickness of the layer of water warmed to the same temperature as the panel surface varies with the flow rate of water across the panel. Trials in a flume system showed it is always more than 1.5 mm and can be as much as 3-5 mm in low flow conditions (Peck, pers. comm.). No animal grew beyond the 2mm layer for the duration of each deployment. The panels were deployed on the seabed at a depth of 10m below the lowest tide mark and 50-100m from the shore. Power to, and control of the panels was conducted from a nearby building. The experiment was conducted for 13 months from June 2015 through June 2016. Panels were first deployed on the 05/06/15 and photographed regularly during each 3 month deployment period. Each deployment lasted 3 months, at which point the panels were retrieved, photographed and sampled before being scrapped clean and re-deployed. This interval was dictated by the growth rate of colonisers in summer, which reached high levels of panel surface coverage within this time but were still growing inside the heated boundary layer of the plates. Panel photography and sampling: At regular intervals, the panels were lifted onto the side of a boat and brought to the shore near the sampling sites but held under water at all times. Panels were photographed using a Nikon D7000 with a Nauticam Underwater housing and a 60 mm macro lens (following Ashton et al., 2017)). Panels that were deployed during the winter period (December-March) were not photographed in between the start and end of the deployment, due to low recruitment and slow growth during the winter months. At the end of each deployment all panels were brought back to inland aquaria at the School of Ocean Sciences at Bangor University for sampling. After sampling, panels were scraped clean and re-deployed. Analyses of community composition and species: For each deployment, species composition was assessed under low power microscopy (10x) with the use of local taxonomic guides. Where species with unconfirmed taxonomic IDs were present, these were sampled and stored in 95% ethanol for subsequent DNA barcoding using18S rRNA primers (NSF4 and NSR581). The community growth on panels was analysed for the percentage area and species composition across the different treatments (control, +1, +2) seasonally (summer, autumn and spring). Species richness and diversity: Presence and percentage cover data for sessile taxa on panels at the end of each sampling period were extracted from photographs using the colour threshold plugin in Fiji. A two-way analysis of variance (ANOVA) was performed in the R environment for statistical computing to examine differences in percentage cover across seasons and treatment. Post-hoc Tukey tests were performed using the agricolae package. Presence and percentage cover data for sessile taxa on panels at the end of each sampling period were compared using multivariate analysis models in the R environment for statistical computing using the vegan package. The reference model included an interaction term between treatment, month, frame and panel. Spirobranchus growth rates: S. triqueter (n=30 per panel) were identified and measured for growth during each sampling period using Fiji (ImageJ). The area around each worm was traced and growth rates were calculated following Bowden et al., (2006) using the formula: µ= In(N/N0) / t where µ = growth rate, N = area at the end of the growth period, N0 = area at the start of the growth period and t = growth period in days. Growth rates were analysed using a general linear model (GLM) in the R environment using the glm function. Post-hoc Tukey tests were performed using the agricolae package. |
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| Temporal Coverage: | |
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| Start Date | 2015-06-05 |
| End Date | 2016-06-30 |
| Spatial Coverage: | |
| Latitude | |
| Southernmost | 53.2307 |
| Northernmost | 53.2307 |
| Longitude | |
| Westernmost | -4.1537 |
| Easternmost | -4.1537 |
| Altitude | |
| Min Altitude | N/A |
| Max Altitude | N/A |
| Depth | |
| Min Depth | N/A |
| Max Depth | N/A |
| Location: | |
| Location | United Kingdom |
| Detailed Location | North Wales, Menai Strait |
| Data Collection: | Image processing: Photoshop CS5 Image data processing: Fiji (Image J) Statistical analysis: R studio |
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| Data Storage: | R files: - mds.R: mds plots in R code. It is well annotated throughout. - Adonis.R: PERMANOVA analysis R code. It is well annotated throughout. - GLM_R.R: Anova analysis R code for Spirobranchus. It is well annotated throughout. Table with details of panel deployments: rtf Data files: - Panel power recording sheet: .cvs file describing weather, tidal conditions, electricity supply and equipment checks: Columns comprise: PSU (panel control unit), Date, Time (24 hour clock), Tidal Height, Weather, Visual check of cables and cable protection (Green pipe, Cable pipe, Cable house), V (Volts), A (Amps). - Bangor Transformed Species Composition: .cvs file describing total percentage cover per panel per treatment for 6 main species used in the analysis (arcsin transformed). Columns comprise Treatment (0 = control, 1 = +1 panels, 2 = +2 panels), Species, Asin transformed, Panel number, Month and Year of measurements. - Biodiversity cover: .cvs listing season, treatment (0 = control, 1 = +1 panels, 2 = +2 panels), species, percentage cover. - Seasonal percentage cover: .cvs listing season, treatment (0 = control, 1 = +1 panels, 2 = +2 panels), percentage cover, standard error. - Percentage cover per month: .cvs listing month, year, treatment (0 = control, 1 = +1 panels, 2 = +2 panels), percentage cover, standard error. - Spirobranchus growth rates: .cvs listing season, treatment (0 = control, 1 = +1 panels, 2 = +2 panels), growth rate, standard error. - Composite stitched photographs from panels: Files: .jpg |
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