Date (Publication)

2024-06-18

Identifier

https://catalogue.ceh.ac.uk/id/b0afb78e-a0cb-4762-9220-659211ae3a5e

Identifier

doi: / 10.5285/b0afb78e-a0cb-4762-9220-659211ae3a5e

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Ainsworth, R.F., Keller, V., Bachiller- Jareno, N., Jürgens, M. D., Eastman, M., Sadykova, D, Rizzo, C., Scarlett, P., Peirson, G. , Eley, F., Antoniou, V., Cowx, I.G., Johnson, A.C., Nunn, A. D. (2024). Fish abundance, habitat, water quality, flow and climate data from English rivers,1975-2017. NERC EDS Environmental Information Data Centre 10.5285/b0afb78e-a0cb-4762-9220-659211ae3a5e

GEMET - INSPIRE themes, version 1.0

• Habitats and Biotopes

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This resource is available under the terms of the Open Government Licence

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If you reuse this data, you should cite: Ainsworth, R.F., Keller, V., Bachiller- Jareno, N., Jürgens, M. D., Eastman, M., Sadykova, D, Rizzo, C., Scarlett, P., Peirson, G. , Eley, F., Antoniou, V., Cowx, I.G., Johnson, A.C., Nunn, A. D. (2024). Fish abundance, habitat, water quality, flow and climate data from English rivers,1975-2017. NERC EDS Environmental Information Data Centre https://doi.org/10.5285/b0afb78e-a0cb-4762-9220-659211ae3a5e

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textTable Text, table

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1  urn:ogc:def:uom:EPSG::9001

Metadata language

EnglishEnglish

Character set

utf8 UTF8

Topic category

• Biota

Begin date

1975-01-01

End date

2017-12-31

Unique resource identifier

OSGB 1936 / British National Grid

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• Comma-separated values (CSV) ()

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Fish Data Species-specific abundances in English rivers were acquired from the Environment Agency's National Fish Population Database (NFPD), focusing on sites surveyed at least 10 times between 1975 and 2017. Raw fish counts were transformed into densities, with only semi-quantitative surveys (single catch) and the initial catch from quantitative surveys (multiple catch) considered. Qualitative surveys were excluded due to insufficient sampling information. Standard counts were available in the majority of cases. Abundance values were standardized by taking the midpoint of logarithmic ranges (e.g., 5, 55, 550, 5500) for different abundance categories. Densities were then calculated by dividing the standardized abundance by the sampling area and multiplying by 100 (units = 100 m-2). Species in the NFPD dataset were assigned Chempop Species Codes adapted from EA species codes, and when multiple EA species codes matched one Chempop Species Code, their densities were summed for each survey. Data without a Chempop species code (e.g., hybrids or broad categories like "all species") were removed, while surveys with zero fish captures were retained in the dataset. Habitat Quality indicators Habitat scores were obtained from the Environment Agency's River Habitat Survey (RHS) dataset, with ArcGIS used to link fish sites to their nearest RHS site. Two key scores were extracted: the Habitat Modification Score (HMS), which reflects the degree of artificial channel modification, and the Habitat Quality Assessment (HQA), which provides a broad assessment of habitat quality based on the diversity and abundance of natural features in the river channel and riparian zone. The HQA is suitable for comparing similar river types. To enable comparisons with data from 1994, new rules for flow-types and channel vegetation were established and applied across all sites, resulting in the HQA adjusted for 1994 data. The most recent RHS survey data was extracted for this analysis. HABSCORE is a method for evaluating Atlantic salmon (Salmo salar L.) and brown trout (Salmo trutta L.) habitat, generating a Habitat Quality Score (HQS) that quantifies habitat quality in terms of expected fish density at a site (100m-2). These assessments are conducted alongside salmonid surveys, but their frequency is generally lower, and the spatial coverage is dependent on the presence of salmon or trout. HABSCORE data, provided by the Environment Agency as Excel files, was extracted for relevant sites and survey dates, supplemented with historical HABSCORE data held by UoH for the same sites. Land Use Land use in the catchment upstream of fish sites (NFPD) were calculated from the Land Cover Map 2015 (25m raster, GB). The 21 land cover types were grouped to cover four broad categories of: Woodland, Arable, Seminatural and Urban. The catchment tool in DataLabs was used to extract and process the data, which were summed into percentage and areas of each land use group. The sum of the percentages of the grouped categories were checked and were found to fall in the range of 99.96-100.04 %. Water Temperature To assess its influence on fish growth, the cumulative annual degree-days ≥12°C, indicating the total temperature sum for days exceeding 12°C in the year prior to the survey date, was calculated. Water temperature data was sourced from the EA Surface Water Temperature Archive for sites with at least 3 years of records, and daily mean air temperature was collected from the Climate Hydrology and Ecology Research Support System (CHESS). The Baseflow Index for each water temperature gauging station and fish site was determined using the UKCEH National River Flow Archive. Generalized additive mix modeling (GAMM) was chosen to model water temperature, accounting for seasonal and year-to-year variation in water temperature, along with the nonlinear relationship between air and water temperature. Seven GAMM models, each covering a 0.1 BFI range, were developed, with the best model (Model: month, time, and air temperature, using ARMA structures) identified based on evaluation metrics like RMSE, NRMSE, and SI. This model was employed to estimate water temperature for fish sites. River Flow River flow data was sourced from the National River Flow Archive (NRFA) hosted by UKCEH and matched with fish sites based on the shortest distance along the river network. Data was extracted for the 12 months leading up to each fish survey, and various statistics were computed, including mean, median, standard deviation, coefficient of variation, Q5/mean, and Q95/mean. Additionally, threshold statistics were calculated for different percentiles (5, 25, 75, and 95), encompassing the threshold discharge value (estimated discharge quantile), days exceeded, number of exceedance events, and average event length. Water Quality-Effluent dilution factor To gauge river pollution levels across England, the study used the LowFlows2000-WQX (lowFlows2000 Water Quality eXtension) model, which characterizes wastewater discharge by wastewater treatment works (WWTWs) in terms of location, domestic population served, dry weather flow (DWF), and treatment type. It's important to note that only significant WWTWs were considered for computational purposes, based on specific criteria: those in catchments contributing to 95% of each hydrometric area and those accounting for 95% of the total discharged DWF to the estuary, ranked by DWF. The model produced predicted wastewater percentages for all reaches in the modelled river network, which is a truncated version of the 1:50,000 digital river network derived from the UK Ordnance Survey Panorama Data Set. To estimate the percentage of wastewater at each fish site, a python script was used to link each site to the nearest reach in the river network. The results are reported in terms of mean, standard deviation, 90th percentile, and 95th percentile, denoted as EDF_Mn, EDF_SD, EDF_Q90, and EDF_Q95, respectively. Chemical Determinands Chemical concentration data spanning 1960-2017, involving 41 determinands, was extracted from the UK's Environment Agency's Water Quality Data Archive. Fish sites were matched to the nearest chemical determinand site using specific criteria like site distance, sample count, and data collection timeframe through ArcGIS. To identify and exclude erroneous data, a threshold of 10 mg/l was set for some determinands, with values exceeding this threshold omitted from statistical calculations. Handling values below the Limit of Quantification (LoQ) involved three options: setting values to LoQ (LoQ1), setting them to 0 (LoQ2), or setting them to LoQ/2 (LoQ3). For the 12 months preceding the surveys at each fish site, various statistics were computed, including minimum, maximum, median, mean, standard deviation, total sample count, and counts of samples below and above the LoQ. Some sites had to be excluded from the final dataset due to licensing restrictions. Altitude Elevation values for each fish site were extracted from the Integrated Hydrological Digital Terrain Model (IHDTM) using Arc GIS' Extract Multi Values to Points' tool. Two elevation values were calculated: Elevation values corresponding to the value of the IHDTM cell centre. Elevation values corresponding to an average value calculated from the adjacent cells with valid values using bilinear interpolation; NoData values were ignored in the interpolation unless all adjacent cells were NoData. Climate variables The Gulf Stream Index (GSI) data spanning 1975-2017 was obtained from the Plymouth Marine Laboratory website (http://www.pml-gulfstream.org.uk/data.htm). Annual mean data were employed due to substantial month-to-month variability resulting from Gulf Stream meandering (Plymouth Marine Laboratory, 2019). Positive GSI values signify a northward shift from the long-term mean location, while negative values indicate a southward movement. Data for the North Atlantic Oscillation Index (NAOI) spanning 1975-2017 was obtained from the National Centre for Atmospheric Research website (https://www.ncei.noaa.gov/access/monitoring/nao). The NAOI's winter (December-March) station-based index relies on the normalized sea level pressure (SLP) difference between Lisbon, Portugal, and Reykjavik, Iceland, dating back to 1864. Positive NAOI values indicate stronger westerlies over mid-latitudes, more intense North Atlantic weather systems, and wetter/milder conditions in Western Europe.

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EnglishEnglish

Character set

ISO/IEC 8859-1 (also known as Latin 1) 8859 Part 1

Hierarchy level

dataset Dataset

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dataset

Date stamp

2024-10-03T08:39:35

Metadata standard name

UK GEMINI

Metadata standard version

2.3