{"numFound":30,"page":1,"rows":20,"url":"http://catalogue.ceh.ac.uk/eidc/documents?facet=resourceStatus%7CAvailable&facet=rightsHolder%7CUK+Centre+for+Ecology+%26+Hydrology&facet=topic%7C0%2FEnvironmental+risk%2F&facet=topic%7C0%2FRadioecology%2F&facet=recordType%7CDataset","nextPage":"http://catalogue.ceh.ac.uk/eidc/documents?page=2&facet=resourceStatus%7CAvailable&facet=rightsHolder%7CUK+Centre+for+Ecology+%26+Hydrology&facet=topic%7C0%2FEnvironmental+risk%2F&facet=topic%7C0%2FRadioecology%2F&facet=recordType%7CDataset","results":[{"publicationDate":"2015-03-04T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["C.L.","C.","S.","H.J.","J.M.","A.J.","I.J.","N.A."],"authorFamilyName":["Barnett","Wells","Thacker","Guyatt","Fletcher","Lawlor","Winfield","Beresford"],"authorFullName":["Barnett, C.L.","Wells, C.","Thacker, S.","Guyatt, H.J.","Fletcher, J.M.","Lawlor, A.J.","Winfield, I.J.","Beresford, N.A."],"authorOrcid":["https://orcid.org/0000-0002-8788-8449","https://orcid.org/0000-0001-9296-5114","https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise concentrations of elements in ashed fish sampled from lakes in the English Lake District in 2012 and 2013. Fish were collected from three lakes (Windermere, Bassenthwaite Lake and Derwent Water) by the Centre for Ecology & Hydrology (CEH) Lake Ecosystems group. Fish species collected were Roach (Rutilus rutilus), Perch (Perca fluviatilis), Ruffe (Gymnocephalus cernuus), Brown trout (Salmo trutta), Pike (Esox lucius) and Vendace (Coregonus albula). All samples were ashed prior to analysis by ICPMS or ICPOES to determine elemental concentrations.","documentType":"GEMINI_DOCUMENT","identifier":"ed90df1b-462c-46bb-afbd-59794fb03f6b","incomingCitationCount":1,"givenName":["Cath","C.L.","C.","S.","H.J.","J.M.","A.J.","I.J.","N.A."],"familyName":["Barnett","Wells","Thacker","Guyatt","Fletcher","Lawlor","Winfield","Beresford"],"fullName":["Barnett, C.","Barnett, C.L.","Wells, C.","Thacker, S.","Guyatt, H.J.","Fletcher, J.M.","Lawlor, A.J.","Winfield, I.J.","Beresford, N.A."],"keyword":["Lake District","Windermere","Bassenthwaite Lake","Derwent Water","Radioecology","Water quality","Coregonus albula","Esox lucius","Salmo trutta","Gymnocephalus cernua","Perca fluviatilis","Rutilus rutilus"],"keywordsPlace":["Lake District","Windermere","Bassenthwaite Lake","Derwent Water"],"keywordsTheme":["Radioecology","Water quality"],"keywordsOther":["Coregonus albula","Esox lucius","Salmo trutta","Gymnocephalus cernua","Perca fluviatilis","Rutilus rutilus"],"licence":"Open government licence","lineage":"Fish were collected in 2012 and 2013 from Windermere, Bassenthwaite Lake and Derwent Water in the English Lake District. Species collected were: Roach (Rutilus rutilus), Perch (Perca fluviatilis), Ruffe (Gymnocephalus cernuus), Brown trout (Salmo trutta), Pike (Esox lucius) and Vendace (Coregonus albula). Samples were frozen to minus 20 degrees Centigrade as soon as possible after collection. Fish samples were thoroughly defrosted, weighed and gutted prior to the whole-fish being ashed at 500°C. The ash was then weighed. Ashed fish samples were digested using an aqua regia reagent (fresh 3:1 mixture of concentrated HNO3 and HCl aristar grade) at 175°C for 12 minutes using a microwave oven (CEM, MarsXpress). Analysis of the ashed fish digests was then conducted by ICPMS (Perkin Elmer, NeXION 300D) or ICPOES (Perkin Elmer, 7300 DV). ICPMS measurements were made using two types of instrument operation, either quantitative or semi-quantitative (using Perkin Elmer Total Quant software). The quantitative measurements were made using external calibration after spiking the digests with 10 microgram per litre Ga, In and Re as internal standards to compensate for instrumental drift and matrix effects. The semi-quantitative measurements were made using the ICPMS instrument operating in kinetic energy discrimination (KED) mode with the addition of helium gas. The semi-quantitative and quantitative modes differed as the former used an element concentration to intensity response curve to extrapolate concentrations over a wide mass range. ICPMS and ICPOES instrument limits of detection (LOD) were calculated using mean and standard deviation measurements for the digestion reagent blank (yb, plus sb where yb is blank concentration and sb is three standard deviations of the blank). Method LODs were then calculated taking into account the dilution arising from the digestion procedure. Note that for some elements determined using the semi-quantitative ICPMS method it was not possible to determine instrument LODs from the analysis of a digestion reagent blank and in these cases the instrument LODs were estimated from an assessment of instrument sensitivity and assigned a values of 0.001 microgram per litre (equivalent to a mean method LOD of 0.001 milligrams per kilogram). Results are reported as milligrams per kilogram fresh weight (converted from ash weight using fresh to ash weight ratio for each sample).","locations":["POLYGON((-8.648 49.864, -8.648 60.861, 1.768 60.861, 1.768 49.864, -8.648 49.864))"],"orcid":["https://orcid.org/0000-0002-8788-8449","https://orcid.org/0000-0001-9296-5114","https://orcid.org/0000-0002-8722-0238"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["1420712455477","https://catalogue.ceh.ac.uk/id/ed90df1b-462c-46bb-afbd-59794fb03f6b","10.5285/ed90df1b-462c-46bb-afbd-59794fb03f6b"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Elemental concentrations in fish from lakes in Northwest England","topic":["0/Radioecology/","0/Water quality/"],"version":1.0,"view":["public","clamw"],"shortenedDescription":"Data comprise concentrations of elements in ashed fish sampled from lakes in the English Lake District in 2012 and 2013. Fish were collected from three lakes (Windermere, Bassenthwaite Lake and Derwent Water) by the Centre for Ecology & Hydrology (CEH) Lake Ecosystems..."},{"publicationDate":"2018-08-30T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["B.A.","R.F."],"authorFamilyName":["Woodcock","Pywell"],"authorFullName":["Woodcock, B.A.","Pywell, R.F."],"authorOrcid":["https://orcid.org/0000-0003-0300-9951","https://orcid.org/0000-0001-6431-9959"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset describes an experimental test of potential over yielding effects on fruit set and average fruit size for tomato plants grown in the presence of three pollinator combinations: (1) the bumblebee Bombus terrestris (2) Lasioglossum spp. and (3) and additive combination of B. terrestris and Lasioglossum spp. \n\nThe experimental design includes no pollinator controls nested within individual tomato plants exposed to the above pollinator species treatment combinations.  This research was undertaken in 2017 and funded though a UKCEH Commercial Innovation Fund (National Capability) project supported by the Natural Environmental Research Council (Project NEC06344).","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"identifier":"94925db4-eeeb-4f3d-ae19-42a3380636e5","incomingCitationCount":0,"givenName":["Ben","B.A.","R.F."],"familyName":["Woodcock","Pywell"],"fullName":["Woodcock, B.","Woodcock, B.A.","Pywell, R.F."],"keyword":["Agriculture","Biodiversity","Environmental risk","Pollinators","bumblebee","Bombus terrestris","bees","Lasioglossum pauxillum","Lasioglossum malachurum"],"keywordsTheme":["Agriculture","Biodiversity","Environmental risk","Pollinators"],"keywordsOther":["bumblebee","Bombus terrestris","bees","Lasioglossum pauxillum","Lasioglossum malachurum"],"licence":"Open government licence","lineage":"Three treatment combinations of bee pollinators foraging on tomatoes were compared: \n  1) B. terrestris alone (a single 30-40 worker colony);\n  2) Lasioglossum spp. alone, predominantly malachurum but with some pauxillum);\n  3) a combination of B. terrestris (a single 30-40 worker colony) and Lasioglossum spp.. \n\nAll experiments were undertaken under field conditions within three, 2 x 3 m net cages designed to hold free flying bees.   B. terrestris colonies were obtained as commercially available stock (Biobest Ltd) but there is no equivalent for Lasioglossum spp..  To address this resident populations of L. malachurum and L. pauxillum were identified. These were found on bare and compacted soil oil of arable field corners.  Over populations of Lasioglossum spp. two net cages were established, with a third in close proximity although not covering populations of the Lasioglossum spp..  Into this latter cage a B. terrestris colony (30-40 workers) was established.  A further B. terrestris colony (30-40 workers) was allowed to forage in one of the cages covering Lasioglossum nests (Treatment 3), while the other was left without such a colony (Treatment 2).   Population density of Lasioglossum in both cages was broadly equivalent, with c. 4.2 (± 0.8) nest borrows m-2.  Treatment combinations were additive in terms of bee density reflecting likely practice under greenhouse growing conditions.  Nets were only positioned over supporting cages on days when the experiment was being undertaken, to prevent starving of wild Lasioglossum populations.  \n\nAs tomato plants produce no nectar it was necessary to cage a small quantity of Asteraceae garden plants to provide a nectar source for the bees. Experimental tomato plants (var. 'Moneymaker') were established under controlled greenhouse conditions where pollinators were excluded and were translocated to the experimental site when they had multiple flowering stems.  Assessments were restricted to the first five mature flowers on each stem; subsequent flowers were removed. On each plant two flowering stems were selected, one was left open to pollination in the cages with treatments 1-3, the other was treated as a control and covered in a small net bag to prevent access by pollinators.   Batches of five plants were placed in each of the three cages for a four-day period, with this repeated four times.  After each period of exposure all plants were returned to greenhouse conditions and left to mature.  When tomatoes had reached the same point of maturation (deep red colour) the number of fruits produced was counted (out of a maximum of five  per stem) and the individual mass of each fruit was determined.","locations":["POLYGON((-1.196 51.632, -1.196 51.634, -1.195 51.634, -1.195 51.632, -1.196 51.632))"],"orcid":["https://orcid.org/0000-0003-0300-9951","https://orcid.org/0000-0001-6431-9959"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/94925db4-eeeb-4f3d-ae19-42a3380636e5","10.5285/94925db4-eeeb-4f3d-ae19-42a3380636e5"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Pollination of tomatoes by the bees Bombus terrestris and Lasioglossum spp.","topic":["0/Agriculture/","0/Biodiversity/","0/Environmental risk/","0/Pollinators/"],"version":1.0,"view":["public","phtr"],"shortenedDescription":"This dataset describes an experimental test of potential over yielding effects on fruit set and average fruit size for tomato plants grown in the presence of three pollinator combinations: (1) the bumblebee Bombus terrestris (2) Lasioglossum spp. and (3) and additive..."},{"publicationDate":"2021-02-26T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","Chernobyl Centre for Nuclear Safety","University of Salford"],"authorGivenName":["C.L.","S.","A. ","J.S.","M.D. ","N.A."],"authorFamilyName":["Barnett","Gashchak","Maksimenko","Chaplow","Wood","Beresford"],"authorFullName":["Barnett, C.L.","Gashchak, S.","Maksimenko, A.","Chaplow, J.S.","Wood, M.D.","Beresford, N.A."],"authorOrcid":["https://orcid.org/0000-0001-9723-7247","https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-0635-2387","https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/052dx1v90","https://ror.org/01tmqtf75"],"catalogue":"eidc","description":"Data comprise plot details and radionuclide activity concentrations for Sr-90, Cs-137, Am-241, Pu-238, Pu-239 and Pu-240 in ‘grassy’ vegetation and soil. These radionuclide activity concentrations have been used to make estimations of total weighted absorbed doses to grassy vegetation, deciduous trees and bacteria; no dose rate estimates for grassy vegetation have been made for those sites where grassy vegetation was absent.\n\nRadiation from the 1986 Chernobyl nuclear power plant accident killed coniferous trees in a 4-6 km2 area of forest to the west of the power plant. This area is now known as the 'Red Forest’ and it has subsequently regenerated with understorey vegetation and deciduous trees; it is the most anthropogenically contaminated radioactive ecosystem on Earth. In July 2016 a severe fire burnt (to varying degrees) c. 80 percent of the Red Forest; this presented a unique opportunity to study the impact of radiation on the recovery of forest ecosystems exposed to a secondary stressor (fire). To investigate this, in September 2017 the RED FIRE project set up sixty study plots in the Red Forest (in burnt and unburnt areas) with a further nine plots established close to Buriakivka village (approximately 8 km from the Red Forest).\n\nVegetation samples from each plot were harvested using shears in September 2017. Each sample was sorted into ‘grassy’ and ‘other’ vegetation; these were air-dried (20-25 degrees Celsius) and the grassy vegetation samples homogenised prior to radionuclide analyses.\n\nSoil core samples collected in September 2017 were bulked, homogenised and sub-samples taken for determination of pH and percentage moisture determined by oven drying (approximately 60 degrees Celsius) to a constant mass. The remaining soil sample was used for the determination of radionuclide activity concentrations; prior to analyses, these samples were dried at approximately 80 degrees Celsius.\n\nThis work was funded by the NERC, Grant Ref: NE/P015212/1 (RED FIRE: Radioactive Environment Damaged by fire: a Forest In Recovery)","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/P015212/1"],"identifier":"60782622-7bfa-4615-a9e3-0a802a9f4674","incomingCitationCount":0,"givenName":["C.L.","S.","A. ","J.S.","M.D. ","N.A."],"familyName":["Barnett","Gashchak","Maksimenko","Chaplow","Wood","Beresford"],"fullName":["Barnett, C.L.","Gashchak, S.","Maksimenko, A.","Chaplow, J.S.","Wood, M.D.","Beresford, N.A."],"keyword":["high-purity germanium γ-detector ","β-spectrometer ","MKS-01R meter","Chernobyl","Red Forest","Chornobyl","Radioecology","Plot experiment","radionuclide activity","Environmental Risk from Ionising Contaminants: Assessment and Management (ERICA)","RED FIRE","bacterium","grass","deciduous tree","radionuclide"],"keywordsInstrument":["high-purity germanium γ-detector ","β-spectrometer ","MKS-01R meter"],"keywordsPlace":["Chernobyl","Red Forest","Chornobyl"],"keywordsTheme":["Radioecology"],"keywordsOther":["Plot experiment","radionuclide activity","Environmental Risk from Ionising Contaminants: Assessment and Management (ERICA)","RED FIRE","bacterium","grass","deciduous tree","radionuclide"],"licence":"Open government licence","lineage":"Cs-137 activity concentrations were determined in grassy vegetation and soil using a high-purity germanium γ-detector (Model GC3019, Canberra-Packard, Connecticut, USA). A standard 137Cs/152Eu source (OISN-1; Applied Ecology Laboratory of Environmental Safety Centre, Odessa, Ukraine) was used for calibration. The minimal detectable activity was approximately 0.18 Bq per sample with uncertainties of approximately 10-15 percent (p=0.95) depending on the sample type. \n\nSr-90 activity concentrations were determined in soil and grassy vegetation samples using a β-spectrometer (EXPRESS-01) with a thin-filmed (0.1 mm) plastic scintillator detector. No radiochemical pre-treatment was required and samples were analysed as a solid matrix. Daily calibrations were conducted. Spectra were processed by correlating the sample spectra with those obtained from standard sources and those obtained from background measurements; uncertainties were approximately 20 percent (p=0.95).\nPrior to processing to determine activity concentrations of 241Am and Pu isotopes in soil samples, 242Pu and 243Am were added as yield tracers. Samples were dissolved in HF followed by treatment with HNO3, HCl, H3BO3+HNO3 and 8M HNO3. Plutonium and Am were separated using anion exchange resin (Bio Rad AG 1 × 8, 100-200 mesh). The Pu fraction was evaporated. Americium was precipitated with calcium oxalate and then separated using TRU resin columns; lanthanides were removed using an anion exchange resin column. Thin alpha sources of each separated actinide element were prepared by micro co-precipitation with neodymium fluoride and analysed using a Canberra Alpha Analyst alpha spectrometer. Counting errors were typically <20 percent.\n\nTo estimate the activity concentrations of Am-241 and Pu-isotopes for grassy vegetation transfer parameters (CRwo-soil) for Agrostis gigantea from a site within the Red Forest were used (Beresford et al. 2020; Table 4) together with the appropriate measured soil activity concentration (DM). To estimate Sr-90 and Cs-137 activity concentrations in deciduous trees CRwo-soil values from sites within the CEZ were used (Holiaka et al. 2020) together with the measured soil activity concentrations (dry mass); for Am-241 and Pu-isotopes CRwo-soil values for Pinus sylvestris (wood) from a site within the Red Forest were used (Beresford et al. 2020; Table 4).\n\nWeighted absorbed dose rate estimations for grassy vegetation and deciduous tree wood were made using the ERICA Tool http://www.erica-tool.com/ (version 1.3) and the revised ‘R&D128’ spreadsheet model (https://wiki.ceh.ac.uk/display/rpemain/Ar+-+Kr+-+Xe+dose+calculator) was used to estimate the weighted absorbed dose to bacteria. The ambient dose rate (µSv h-1) on the soil surface was measured at each study plot using a MKS-01R meter.","locations":["POLYGON((30.001 51.342, 30.001 51.415, 30.091 51.415, 30.091 51.342, 30.001 51.342))"],"orcid":["https://orcid.org/0000-0001-9723-7247","https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-0635-2387","https://orcid.org/0000-0002-8722-0238"],"organisation":["UK Centre for Ecology & Hydrology","Chernobyl Centre for Nuclear Safety","University of Salford","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/60782622-7bfa-4615-a9e3-0a802a9f4674","10.5285/60782622-7bfa-4615-a9e3-0a802a9f4674"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/052dx1v90","https://ror.org/01tmqtf75","https://ror.org/04xw4m193"],"state":"published","supplementalName":["TREE website","REDFIRE website","CHAR webpage"],"title":"Soil and vegetation radionuclide activity concentrations and calculated dose rates from the Red Forest, Chernobyl, Ukraine, 2016-2017","topic":["0/Radioecology/"],"version":1.0,"view":["public","danor"],"shortenedDescription":"Data comprise plot details and radionuclide activity concentrations for Sr-90, Cs-137, Am-241, Pu-238, Pu-239 and Pu-240 in ‘grassy’ vegetation and soil. These radionuclide activity concentrations have been used to make estimations of total weighted absorbed doses to..."},{"publicationDate":"2013-12-31T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","The Food and Environment Research Agency","University of Stirling"],"authorGivenName":["C.L.","N.A.","L.A.","M.","C.","D."],"authorFamilyName":["Barnett","Beresford","Walker","Baxter","Wells","Copplestone"],"authorFullName":["Barnett, C.L.","Beresford, N.A.","Walker, L.A.","Baxter, M.","Wells, C.","Copplestone, D."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-1471-7075"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/045wgfr59"],"catalogue":"eidc","description":"This dataset presents the results of an initial sampling exercise conducted at a terrestrial site in northwest England in summer 2010. The following samples of terrestrial Reference Animals and Plants (RAPs) were obtained from an area of circa 0.4 km squared: Molinia caerulea (ICRP RAP Wild Grass defined as Poaceae); Picea sitchensis (ICRP RAP Pine Tree defined as Pinaceae); Apis spp., Bombus spp., Nomada spp. (ICRP RAP Bee defined as Apidea); Apodemus sylvaticus (ICRP RAP Rat defined as Muridae); Earthworms (species in the Family Lumbricidae as defined for the ICRP RAP Earthworm); Deer (belonging to the Family Anatidae (i.e. the ICRP RAP Deer). Soil samples were also collected from throughout the sampling area. All samples were analysed for multiple elements using ICP-MS/ICP-OES and most for gamma-emitting radionuclides. Results have been used to derive biota-soil concentration ratios. The ICRP have published their framework for radiation protection of the environment (ICRP Publication 108). This describes the use of RAPs as the basis for their framework. The RAPs are generalised to the taxonomic level of Family. Publication 108 presented dose coefficient values for the selected RAPs and also reviewed data on the effects of ionising radiation to suggest Derived Consideration Reference Levels for each RAP. In summer 2010 the ICRP released a further report on their protection framework for consultation. This report presented transfer parameter values (organism-media concentration ratios) for Reference Animals and Plants. The report also raised the possibility of identifying a series of sites where samples of each Reference Animal and Plant, and their different lifestages, could be collected and analysed. It was suggested that the resultant data would constitute a set of reference values analogous to approaches used by the ICRP for human radiological protection.","documentType":"GEMINI_DOCUMENT","identifier":"e40b53d4-6699-4557-bd55-10d196ece9ea","incomingCitationCount":6,"givenName":["Cath","C.L.","N.A.","L.A.","M.","C.","D."],"familyName":["Barnett","Beresford","Walker","Baxter","Wells","Copplestone"],"fullName":["Barnett, C.","Barnett, C.L.","Beresford, N.A.","Walker, L.A.","Baxter, M.","Wells, C.","Copplestone, D."],"keyword":["Cumbria","United Kingdom","Pollution","Radioecology","radioecology","ICRP RAP","chemical analysis","pine tree","deer","mice","TREE","COMET","bee","earthworm","grass","soil","radionuclide","natural radioactivity"],"keywordsPlace":["Cumbria","United Kingdom"],"keywordsTheme":["Pollution","Radioecology"],"keywordsOther":["radioecology","ICRP RAP","chemical analysis","pine tree","deer","mice","TREE","COMET","bee","earthworm","grass","soil","radionuclide","natural radioactivity"],"licence":"Open government licence","lineage":"The study site (circa 0.4 km2 in area) was located in a managed coniferous forestry plantation (c. 25 km2) in north-west England (NGR 3325 4917). It was largely a mixture of established coniferous plantation with an understory of predominantly grass and sedge species. Samples (bee, earthworm, sitka spruce, wood mouse, purple moor grass and soil) were collected from this area with the exception of Capreolus capreolus (Roe deer) which were collected from within the forest at distances of less than 2 km to the north and east of the main study site. Samples were collected between August 2010 and February 2011. The locations of all sampling sites were recorded using a hand held GPS. Biota and associated soils samples were analysed for stable element by ICP-MS by the Food and Environment Research Agency using methods accredited by the United Kingdom Accreditation Service (UKAS). Sub samples were analysed to determine their C and N concentrations and samples with a higher mass were also analysed for gamma emitting radionuclides by CEH using a method also accredited by UKAS. The Percentage Loss on Ignition (LOI) and pH was also determined in the soil samples. For full details relating to each sample type collected in this study, 'please refer to the Online Resource: Supporting Documentation 'Materials and Methods_ICRP_RAP'.","locations":["POLYGON((-6.45 49.86, -6.45 55.81, 1.76 55.81, 1.76 49.86, -6.45 49.86))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-1471-7075"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","The Food and Environment Research Agency","University of Stirling","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["1314185575812","https://catalogue.ceh.ac.uk/id/e40b53d4-6699-4557-bd55-10d196ece9ea","10.5285/e40b53d4-6699-4557-bd55-10d196ece9ea"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/045wgfr59","https://ror.org/04xw4m193"],"state":"published","title":"Element and radionuclide concentrations in representative species of the ICRP's Reference Animals and Plants and associated soils from a forest in north-west England","topic":["0/Pollution/","0/Radioecology/"],"version":1.0,"view":["public","rjsc"],"shortenedDescription":"This dataset presents the results of an initial sampling exercise conducted at a terrestrial site in northwest England in summer 2010. The following samples of terrestrial Reference Animals and Plants (RAPs) were obtained from an area of circa 0.4 km squared: Molinia..."},{"publicationDate":"2021-07-07T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","Chornobyl Center for Nuclear Safety","University of Salford"],"authorGivenName":["C.L.","S.","C.","A.","J.","M.D.","N.R.","N.A."],"authorFamilyName":["Barnett","Gashchak","Wells","Maksimenko","Chaplow","Wood","Parekh","Beresford"],"authorFullName":["Barnett, C.L.","Gashchak, S.","Wells, C.","Maksimenko, A.","Chaplow, J.","Wood, M.D.","Parekh, N.R.","Beresford, N.A."],"authorOrcid":["https://orcid.org/0000-0001-9723-7247","https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-0635-2387","https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/052dx1v90","https://ror.org/01tmqtf75"],"catalogue":"eidc","description":"Data comprise site location, soil chemistry (pH, soil moisture), soil radionuclide activity concentrations (the isotopes measured were: Americium-241, Caesium-137, Plutonium-238, -239 and -240, Strontium-90 (K-40 and U-238 activity concentrations were estimated from stable element data) and soil biological activity (derived from application of  bait lamina sticks) at 18 sites in the Chernobyl Exclusion Zone (CEZ), Ukraine in 2016; data for four sites in 2005 are also presented. Estimate absorbed radionuclide dose rates to soil invertebrates and bacteria are also presented. The primary purpose of these data was to enable an evaluation of the potential impact of radiation on soil organisms. The work was carried out by UKCEH, Chernobyl Centre for Nuclear Safety and the University of Salford. Funding for this work was via the TREE project funded by NERC, Environment Agency and Radioactive Waste Management Ltd. under the RATE programme.\n","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/L000393/1"],"identifier":"19babe1c-b3a3-488c-b4fe-ebb4ab9237d8","incomingCitationCount":0,"givenName":["N.A.","C.L.","S.","C.","A.","J.","M.D.","N.R."],"familyName":["Beresford","Barnett","Gashchak","Wells","Maksimenko","Chaplow","Wood","Parekh"],"fullName":["Beresford, N.A.","Barnett, C.L.","Gashchak, S.","Wells, C.","Maksimenko, A.","Chaplow, J.","Wood, M.D.","Parekh, N.R."],"keyword":["Chernobyl","Chornobyl","Chornobyl Exclusion Zone","Environmental risk","Soil","Activity concentration","dose rate","CEZ","detritivorous arthropod","bacteria","soil","annelid","radionuclide","radiation dose"],"keywordsPlace":["Chernobyl","Chornobyl","Chornobyl Exclusion Zone"],"keywordsTheme":["Environmental risk","Soil"],"keywordsOther":["Activity concentration","dose rate","CEZ","detritivorous arthropod","bacteria","soil","annelid","radionuclide","radiation dose"],"licence":"Open government licence","lineage":"In 2005 four sites referred to as Low, Medium, High (on the basis of their anticipated soil radionuclide activity concentrations) and Dead (an area where pine trees were killed in 1986) were sampled. In 2016 a further 18 sites (categorised on the basis of simplified habitat groups: ‘Coniferous’ or ‘Deciduous’ woodland; ‘Red Forest’) were sampled. Bait lamina sticks were applied to the soil and left for 18 days. After removal the bait lamina sticks were wiped and assessed for evidence of feeding. After removal of the bait lamina, soil was sampled and measurements of pH, moisture content and radionuclide activity concentrations were determined. \nField notes were transposed to MSExcel files, bait lamina readings and basic soil chemistry data were directly input to MSExcel files and radionuclide activity concentration data were supplied to UKCEH by Chornobyl Center as MSExcel files.  All data were supplied to EIDC as csv files.\n","locations":["POLYGON((29.401 50.553, 29.401 51.575, 30.895 51.575, 30.895 50.553, 29.401 50.553))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0001-9723-7247","https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-0635-2387"],"organisation":["UK Centre for Ecology & Hydrology","Chornobyl Center for Nuclear Safety","University of Salford","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/19babe1c-b3a3-488c-b4fe-ebb4ab9237d8","10.5285/19babe1c-b3a3-488c-b4fe-ebb4ab9237d8"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/052dx1v90","https://ror.org/01tmqtf75","https://ror.org/04xw4m193"],"state":"published","title":"Soil biological activity in the Chernobyl Exclusion Zone, Ukraine, September 2005 and spring 2016","topic":["0/Environmental risk/","0/Soil/"],"version":1.0,"view":["public","danor"],"shortenedDescription":"Data comprise site location, soil chemistry (pH, soil moisture), soil radionuclide activity concentrations (the isotopes measured were: Americium-241, Caesium-137, Plutonium-238, -239 and -240, Strontium-90 (K-40 and U-238 activity concentrations were estimated from..."},{"publicationDate":"2015-10-06T00:00:00.000+00:00","authorAffiliation":["University of Copenhagen","Centre for Ecology & Hydrology"],"authorGivenName":["N.","N.J.","C.","D.J."],"authorFamilyName":["Cedergreen","Nørhave","Svendsen","Spurgeon"],"authorFullName":["Cedergreen, N.","Nørhave, N.J.","Svendsen, C.","Spurgeon, D.J."],"authorOrcid":["https://orcid.org/0000-0003-3264-8760"],"authorRor":["https://ror.org/035b05819","https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise body length (micrometres) of nematode (Caenorhabditis elegans) offspring from a laboratory study in which animals were exposed to control (0 copper) or copper dosed agar at different average temperatures (8 to 24 °C)) and under fluctuation conditions of low (plus or minus 4 °C) and high (plus or minus 8 °C) amplitude (average temperatures of 12, 16, 20 °C and 16 °C respectively)","documentType":"GEMINI_DOCUMENT","identifier":"af125e27-3b70-4f0a-81fb-a7eb10f64ef7","incomingCitationCount":1,"givenName":["N.","N.J.","C.","D.J.","Claus"],"familyName":["Cedergreen","Nørhave","Svendsen","Spurgeon"],"fullName":["Cedergreen, N.","Nørhave, N.J.","Svendsen, C.","Spurgeon, D.J."],"keyword":["Environmental risk","Pollution","Caenorhabditis elegans"],"keywordsTheme":["Environmental risk","Pollution"],"keywordsOther":["Caenorhabditis elegans"],"licence":"Open government licence","lineage":"Experimental design\nCulture conditions for test organism: C. elegans (N2 Bristol strain) from the C. elegans Genetics Centre, University of Minnesota) were cultivated in darkness at 20°C on nematode growth medium (NGM) agar plates and fed Escherichia coli of uracil deficient strain OP50. At least 2 weeks before the start of all experiments new cultures were initiated at the selected test temperatures to acclimatize the worms through several generations. Cultures were maintained by transferring a chunk of agar and associated eggs, juvenile and adult worms from an existing culture to freshly prepared NGM agar plates weekly.\n\nSet-up of toxicity tests: Exposures were conducted at steady temperatures of 8, 12, 16, 20 and 24°C and variable temperature scenarios with daily fluctuations of +/- 4°C in the ranges 8-16°C (12°C average), 12-20°C (16°C average) and 16-24°C (20°C average) and daily fluctuations of +/- 8°C in the ranges 8-24°C (16°C average). Temperatures were changed with a rate of 4°C per hour. Separate toxicity tests with copper were conducted under all temperature regimes using concentration known to result in changes in measured traits. Copper concentrations used were 0, 1, 3, 8, 20 and 40 mg Cu/L agar. The highest concentrations equate to levels 2-3 orders of magnitude greater than those found in surface waters and soil pore waters from uncontaminated sites, but are comparable to soil pore water concentrations in heavily polluted soils. \n\nA stock solution of CuCl2 in demineralized water (2 g Cu/L) was made and used throughout the experiment. This copper stock solution was added to the NGM agar while liquid and mixed. Batches of NGM were produced every five days during the course of the experiment to minimize immobilization of copper in the agar. All tests were conducted using synchronized cohorts of nematodes produced from adults selected from the main stock cultures acclimatized at each temperature scenario. To generate these cohorts, adult hermaphrodite worms were selected from the acclimatized cultures and placed on Petri dishes with copper spiked NGM and E. coli and left at the test temperatures for 4 hours (6 hours for 8°C to ensure sufficient eggs were laid). After this time, the adults were removed and the eggs laid in the 4 (6) hour period left to hatch. The offspring (the test organisms), once hatched and grown to the L4 larval stage on the copper spiked plates, were transferred to 12-well plates with copper spiked NGM and E. coli, with one individual per well. There were 12 replicate worms for each treatment, except the controls of 24°C constant, 8-16°C, 8-24°C and 16-24°C which had 36 replicates, and the 8°C test in which we could not always obtain 12 worms for each treatment, hence, between 6 and 12 worms were used. \n\nDuring the test, the nematodes were moved to new wells in fresh plates every day. These transfers and the associated observations allowed calculation of the time taken until first egg was laid and subsequently daily egg production. The daily transfer and counting were repeated through both the reproductive and senescence stages until death (determined by the lack of response to being probed). Fertile eggs and hatched juveniles were counted as offspring, while visibly infertile eggs were excluded from brood size counts. At regular intervals, nematode length in micrometers was measured using a Nikon DS-Fi1 camera connected to a Nikon SMZ 800 stereomicroscope. Body length was measured using the program Nikon NIS Elements Imaging Software 3.2 to provide a description of growth pattern. \n\nCopper analysis: The copper content in the water fraction of the agar was determined one and five days after production. This allowed us to distinguish dissolved copper and agar bound copper (which may not have been fully bioavailable). Samples of NGM from each produced batch were saved in centrifuge tubes and, after one or five days, centrifuged at 10000 G for five minutes to separate water and agar. A sample of the water fraction was removed and acidified. The analyses were performed on a graphite furnace AAS (Perkin Elmer Zeeman 5100, Waltham, MA) . Blanks, spiked reference samples and a standard reference material NIST 1577c (bovine liver) were included in the analysis to confirm validity. \n\nData structure: Data structure for columns.\n\nPlate: Gives the TC-plate number. Treatments were randomised at different plates.\nReplicate: Gives the replicate number\nCu: Gives the Cu-concentrations in mg/L agar\nDay: Gives the day after the eggs are layed.\nLength: Is given in µm (micrometers). Length measurements on individuals were started when the worms reached the L4 larval stage and were moved to individual wells.\n\nOffspring: Is the number of fertile eggs and larvae counted. If there are no eggs a zero is written. When the nematode is dead, nothing is written in the cell henceforth. All times after the last zero, the worm is dead. The experiment is terminated when the last worm died, indicated by end of the orange area.\n\nStatistics: Differences between temperature treatments for brood size, lifespan and maximal length of non-Cu exposed nematodes were tested by a one-way ANOVA with a Tukey post hoc analysis using the R statistical software version 2.12.0 (http://www.r-project.org/).\n\nThe average cumulative egg production as a function of time for each treatment was described by a three parameter log-logistic sigmoid model (equation 1) using the statistical software R version 2.12.0 within the DRC package.. \n\ny = d/(1+(x/e)^b)\t\t\t\t\t\t\t(Equation 1)\n\nwhere d is the maximum number of eggs produced, e is the time when half the maximum number of eggs is produced, b is proportional to the slope of the sigmoid curve at e, y is the accumulated number of produced eggs and x is the time. From this model the estimated time to first egg (TFE) was calculated by solving x for y equal to 1/d. The DRC package returns a standard error with the estimate.","orcid":["https://orcid.org/0000-0003-3264-8760"],"organisation":["University of Copenhagen","Centre for Ecology & Hydrology","UK Centre for Ecology & Hydrology","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/af125e27-3b70-4f0a-81fb-a7eb10f64ef7","10.5285/af125e27-3b70-4f0a-81fb-a7eb10f64ef7"],"resourceStatus":"Available","resourceType":"Non-geographic dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/035b05819","https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Temperature and copper effects on the nematode Caenorhabditis elegans ","topic":["0/Environmental risk/","0/Pollution/"],"version":1.0,"view":["public","jone"],"shortenedDescription":"Data comprise body length (micrometres) of nematode (Caenorhabditis elegans) offspring from a laboratory study in which animals were exposed to control (0 copper) or copper dosed agar at different average temperatures (8 to 24 °C)) and under fluctuation conditions of..."},{"publicationDate":"2015-07-17T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["J.S.","Nick A.","C.L."],"authorFamilyName":["Chaplow","Beresford","Barnett"],"authorFullName":["Chaplow, J.S.","Beresford, N.A.","Barnett, C.L."],"authorOrcid":["https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise radiocaesium concentrations in soil, vegetation, wildlife and fungi analysed from samples collected from throughout Great Britain after the 1986 Chernobyl accident by the Centre for Ecology & Hydrology (CEH), formerly the Institute of Terrestrial Ecology (ITE). National level vegetation surveys were conducted in May 1986, October 1986 and Spring 1987. More intensive surveys of vegetation (grass and heather) and wildlife (grouse, fox, etc.) in restricted areas were carried out in Cumbria, Wales and North Yorkshire in 1989, 1990, 1991 and 1993. Surveys of fungi were carried out between 1994 and 1997. The data are suitable for interpolation to create spatially variable surfaces suitable for input into models.","documentType":"GEMINI_DOCUMENT","identifier":"d0a6a8bf-68f0-4935-8b43-4e597c3bf251","incomingCitationCount":3,"givenName":["Nick A.","J.S.","C.L."],"familyName":["Beresford","Chaplow","Barnett"],"fullName":["Beresford, N.A.","Chaplow, J.S.","Barnett, C.L."],"keyword":["North Wales","Great Britain","Yorkshire","Chornobyl exclusion zone","Pollution","Radioecology","radioecology","radionuclide","radiocaesium","heather","COMET","TREE","Chornobyl","grass","wildlife","vegetation","soil","fungus","deposition","radioactive contamination","accident"],"keywordsPlace":["North Wales","Great Britain","Yorkshire","Chornobyl exclusion zone"],"keywordsTheme":["Pollution","Radioecology"],"keywordsOther":["radioecology","radionuclide","radiocaesium","heather","COMET","TREE","Chornobyl","grass","wildlife","vegetation","soil","fungus","deposition","radioactive contamination","accident"],"licence":"Open government licence","lineage":"Vegetation was clipped from 1 metre squared quadrats to a height of 1 centimetre above ground level. Samples were dried at 80 degrees centigrade, weighed, ground and counted in plastic containers (130 millilitre) on a NaI(T1) detector to determine the radiocaesium activity. The most active samples were recounted on a high resolution germanium detector. Soil type was noted at each site (Soil survey 1983). Soil samples were allocated to a series of textural categories (Clay (particles of less than 2 m in diameter); Silt (particles of 2-40 micron diameter); Sand (particles of 50 micron -2millimetre diameter); Organic (humified plant material); Loam (significant quantities of material from 3 or more categories). Soil pH was determined using an antimony electrode pH meter. Animal samples consisted of necks and rumen contents from 70 red deer (Cervus elaphus), whole bodies of three species of lagomorphs (25 rabbits (Oryctolagus cuniculus) and 2 black hares (Lepus capensis), two species of grouse (13 red grouse (Lagopus lagopus), 4 black game (Tetrao tetrix), and 22 foxes (Vulpes vulpes) totalling 141 flesh and 94 gut samples. Samples of flesh were removed from the neck of the deer, from the legs and back of the hares, rabbits and foxes, and from the breast muscle of the grouse. These were weighed fresh and placed in standard counting containers which were kept in a deep freeze until required for analysis. Each sample was thawed for 24 hours prior to counting. Samples were analysed by high resolution gamma spectrometry using either hyperpure germanium or germanium lithium detectors with relative efficiencies of 20 to 25 percent. Counting times varied between 25k to 80k seconds. Detectors were calibrated. The column headings for Easting, Northing and Sampling_date' in dataset 4 are labelled incorrectly. The correct order should be column C Sampling_date, column D Easting, column E Northing.","locations":["POLYGON((-8.648 49.864, -8.648 60.861, 1.768 60.861, 1.768 49.864, -8.648 49.864))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["1409748590053","https://catalogue.ceh.ac.uk/id/d0a6a8bf-68f0-4935-8b43-4e597c3bf251","10.5285/d0a6a8bf-68f0-4935-8b43-4e597c3bf251"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Howard, B. J., Beresford, N. A., Burrow, L., Shaw, P. V., & Curtis, E. J. C. (1987). A comparison of caesium 137 and 134 activity in sheep remaining on upland areas contaminated by Chernobyl fallout with those removed to less active lowland pasture. Journal of the Society for Radiological Protection, 7(2), 71-73.","Horrill, A.D.; Howard, D.M. (1991).  Chernobyl fallout in three areas of upland pasture in West Cumbria. Journal of Radiological Protection, 11 (4). 249-257. ","Howard, B. J., & Beresford, N. A. (1989). Chernobyl radiocaesium in an upland sheep farm ecosystem. British Veterinary Journal, 145(3), 212-219. ","Dighton, J., & Horrill, A. D. (1988). Radiocaesium accumulation in the mycorrhizal fungi Lactarius rufus and Inocybe longicystis, in upland Britain, following the Chernobyl accident. Transactions of the British Mycological Society, 91(2), 335-337. ","Horrill, A.D.; Lowe, V.W.; Howson, G.. 1988 Chernobyl fallout in Great Britain. Final report. NERC/Institute of Terrestrial Ecology, 55pp. (T07006e1) (Unpublished)","Beresford, N. A., Howard, B. J., Barnett, C. L., & Crout, N. M. J. (1992). The uptake by vegetation of chernobyl and aged radiocaesium in upland West Cumbria. Journal of Environmental Radioactivity, 16(2), 181-195. ","Howard B. J.; Beresford, N. A.; Hove, K. (1991).  Transfer of Radiocaesium to Ruminants in Natural and Semi-natural Ecosystems and Appropriate Countermeasures. Health Physics 61, 6.","Wright, S. M., Smith, J. T., Beresford, N. A., & Scott, W. A. (2003). Monte-Carlo prediction of changes in areas of west Cumbria requiring restrictions on sheep following the Chernobyl accident. Radiation and Environmental Biophysics, 42(1), 41-47. ","Smith, J. T., Comans, R. N. J., Beresford, N. A., Wright, S. M., Howard, B. J., & Camplin, W. C. (2000). Chernobyl's legacy in food and water. Nature, 405(6783), 141-141. ","Beresford, N. A., Barnett, C. L., Wright, S. M., Howard, B. J., & Crout, N. M. J. (2007). Factors contributing to radiocaesium variability in upland sheep flocks in west Cumbria (United Kingdom). Journal of Environmental Radioactivity, 98(1-2), 50-68. "],"supplementalName":["Journal paper"],"title":"Post Chernobyl surveys of radiocaesium in soil, vegetation, wildlife and fungi in Great Britain","topic":["0/Pollution/","0/Radioecology/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise radiocaesium concentrations in soil, vegetation, wildlife and fungi analysed from samples collected from throughout Great Britain after the 1986 Chernobyl accident by the Centre for Ecology & Hydrology (CEH), formerly the Institute of Terrestrial Ecology..."},{"publicationDate":"2017-04-21T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["D."],"authorFamilyName":["Hewitt"],"authorFullName":["Hewitt, D."],"authorOrcid":["https://orcid.org/0000-0001-8297-0294"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data includes impacts on root nodule biomass, stomatal conductance, injury rates, and N-fixation in the white clover cultivar (T. repens cv. crusader). An ozone-exposure experiment was conducted in solardomes during the spring and summer of year 2012 on modern clover (Trifolium spp.) cultivars. The effects of ozone pollution (30, 35, 40, 45, 52, 67 parts per billion (ppb) treatment means) on the growth and functioning of the clover cultivars was investigated. Both cultivars had positive increases in ozone-injury rates, although stomatal conductance was unaffected by ozone exposure. Reductions in root nodule biomass and nodule number occurred in white clover, and red clover displayed an increase in nodule density. Nitrogen fixation rates were suppressed in white clover, which could have important implications for the sustainability of managed pasture. The work was carried out as part of a NERC funded PhD. Project number NEC04456. ","documentType":"GEMINI_DOCUMENT","identifier":"b63fbb6c-5030-43a1-b0ea-160bb5a83078","incomingCitationCount":0,"givenName":["G.","D."],"familyName":["Mills","Hewitt"],"fullName":["Mills, G.","Hewitt, D."],"keyword":["Abergwyngregyn","Environmental risk","Pollution","Solar Dome","Soladome","Cultivar","Seedlings","ozone","nitrogen fixation"],"keywordsPlace":["Abergwyngregyn"],"keywordsTheme":["Environmental risk","Pollution"],"keywordsOther":["Solar Dome","Soladome","Cultivar","Seedlings","ozone","nitrogen fixation"],"licence":"Open government licence","lineage":"White clover (Trifolium repens cv. Crusader) and red clover (Trifolium pratense cv. Merviot) were exposed to elevated ozone (mean concentrations 30, 35, 40, 45, 52, 67 parts per billion (ppb)) in solardomes for a period of 12 weeks in the early summer of year 2012. Data was first recorded in the field in field notebooks, and was then transferred to electronic copies (MS Excel worksheets). Data was then exported as .csv files for ingestion into the Environmental Information Data Centre.","locations":["POLYGON((-4.018 53.237, -4.018 53.239, -4.016 53.239, -4.016 53.237, -4.018 53.237))"],"orcid":["https://orcid.org/0000-0001-8297-0294"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/b63fbb6c-5030-43a1-b0ea-160bb5a83078","10.5285/b63fbb6c-5030-43a1-b0ea-160bb5a83078"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Effect of ozone on modern clover cultivars","topic":["0/Environmental risk/","0/Pollution/"],"version":1.0,"view":["public","danor"],"shortenedDescription":"Data includes impacts on root nodule biomass, stomatal conductance, injury rates, and N-fixation in the white clover cultivar (T. repens cv. crusader). An ozone-exposure experiment was conducted in solardomes during the spring and summer of year 2012 on modern clover..."},{"publicationDate":"2016-11-04T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","ECOMatters Inc"],"authorGivenName":["B.J.","C.","C.L.","S."],"authorFamilyName":["Howard","Wells","Barnett","Sheppard"],"authorFullName":["Howard, B.J.","Wells, C.","Barnett, C.L.","Sheppard, S."],"authorOrcid":["https://orcid.org/0000-0002-9698-9524"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise radioactivity transfer parameter and concentration ratio values for gastrointestinal contents of ruminants (cows and goats) to milk. The derived transfer values and concentration ratios were originally reported in the Handbook of Parameter Values for the Prediction of Radionuclide Transfer in Terrestrial and Freshwater Environment. Technical Reports Series TRS 472  but now include newly compiled data for both goat and cow milk.","documentType":"GEMINI_DOCUMENT","identifier":"7713d170-f6a3-4aa7-83c8-fe91278517ce","incomingCitationCount":1,"givenName":["B.J.","C.","C.L.","S."],"familyName":["Howard","Wells","Barnett","Sheppard"],"fullName":["Howard, B.J.","Wells, C.","Barnett, C.L.","Sheppard, S."],"keyword":["Pollution","Radioecology","Radionuclides","transfer parameter","cow milk","concentration ratio"],"keywordsTheme":["Pollution","Radioecology"],"keywordsOther":["Radionuclides","transfer parameter","cow milk","concentration ratio"],"licence":"Open government licence","lineage":"The transfer parameter table for cow milk data published in the table has been created using a compilation of transfer parameter values in a dataset held by the Centre for Ecology & Hydrology. The transfer parameter values have been derived using procedures for data collation and reporting agreed by the International Atomic Energy Agency's EMRAS programme working group that compiled TRS 472 (IAEA, 2010).  Quality control procedures were agreed by the working group to ensure that only data which fulfilled various criteria were included. The QC and data compilation procedures are briefly outlined in (IAEA 2010) and more fully in IAEA (2009). In the following IAEA MODARIA programme, further data quality control was performed, the procedures for which are outlined in the goat milk paper in Howard et al (2016).","orcid":["https://orcid.org/0000-0002-9698-9524"],"organisation":["Centre for Ecology & Hydrology","ECOMatters Inc","UK Centre for Ecology & Hydrology","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/7713d170-f6a3-4aa7-83c8-fe91278517ce","10.5285/7713d170-f6a3-4aa7-83c8-fe91278517ce"],"resourceStatus":"Available","resourceType":"Non-geographic dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["International Atomic Energy Agency (IAEA) . Handbook of Parameter Values for the Prediction of Radionuclide Transfer in Terrestrial and Freshwater Environment. Technical Reports Series No. 472. IAEA, Vienna, 2010."],"title":"Transfer of radionuclides to cow and goat milk","topic":["0/Pollution/","0/Radioecology/"],"version":1.0,"view":["public","rstu"],"shortenedDescription":"Data comprise radioactivity transfer parameter and concentration ratio values for gastrointestinal contents of ruminants (cows and goats) to milk. The derived transfer values and concentration ratios were originally reported in the Handbook of Parameter Values for the..."},{"publicationDate":"2017-04-21T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["D."],"authorFamilyName":["Hewitt"],"authorFullName":["Hewitt, D."],"authorOrcid":["https://orcid.org/0000-0001-8297-0294"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"The data are biomass and ozone-injury data for white clover (Trifolium repens). Dataset concerns a 2014 study on the effects of Jasmonic acid/cutting in modulating the response of clover to ozone. A short-term (4-week) ozone-exposure experiment was conducted in 2014 to investigate the interactive effects of cutting on ozone-induced responses in white clover (Trifolium repens). A strong interaction was found in root biomass and root nodule biomass in cut white clover plants in a high ozone background (45-67 parts per billion (ppb) treatment mean), suggesting ozone-impacts on root nodule biomass occur through limitation of carbon availability. The work was carried out as part of a NERC funded PhD.","documentType":"GEMINI_DOCUMENT","identifier":"10c6df00-c7ef-444b-951f-33a2c0072bec","incomingCitationCount":0,"givenName":["Gina","D."],"familyName":["Mills","Hewitt"],"fullName":["Mills, G.","Hewitt, D."],"keyword":["Abergwyngregyn","Environmental risk","Pollution","Trifolium repens"],"keywordsPlace":["Abergwyngregyn"],"keywordsTheme":["Environmental risk","Pollution"],"keywordsOther":["Trifolium repens"],"licence":"Open government licence","lineage":"A short-term (four-week) ozone-exposure experiment was conducted in 2014 to investigate the interactive effects of cutting on ozone-induced responses in white clover (Trifolium repens). Seedlings were propagated in early Spring 2014. After three weeks, to introduce a soil microbe, pots were inoculated with a soil slurry mixture. Pots were then divided between 3 treatments: uncut pots (controls), with a single cut to four centimetre (cm)m height immediately prior to ozone exposure and uncut, with a weekly application of Methyl-Jasmonate solution during the experiment. The seedlings were grown on for four weeks then exposed to random ozone profiles for four weeks. \nA representative quarter of each pot was selected and recordings of healthy, injured or senesced leaves made on in weeks 2, 3 and 4. The harvest of above and below-ground biomass was performed after four weeks on each pot. Shoot biomass, and root biomass from a representative quarter of the pot, were dried for a minimum of 48 hours at 60 degrees Celsius. Root nodule biomass was also excised from the root system, and was air dried, sized and weighed. Root biomass, nodule mass and nodule numbers per pot were calculated. Leaf area index (LAI) of undamaged leaves was determined from dried forage. Mean injury and senescence data across the recordings was determined for each pot, and was arcsine transformed prior to analysis. Injury and senescence data, and selected biomass data, were then analysed by analysis of variance (ANOVA), with ozone background and treatment applied as factors. \n\nPost-hoc Tukey's honest significant difference tests were used to determine the significance of factors where appropriate. Relationships between total root nodule biomass and biomass, and raw injury parameters for each treatment were also investigated via Pearson's correlation analysis. All analyses were conducted in R Software (version 3.1.2).  \n\nData was first recorded in the field in field notebooks, and was then transferred to electronic copies (MS Excel worksheets). Data was then exported as .csv files for ingestion into the Environmental Information Data Centre.","locations":["POLYGON((-4.018 53.237, -4.018 53.239, -4.016 53.239, -4.016 53.237, -4.018 53.237))"],"orcid":["https://orcid.org/0000-0001-8297-0294"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/10c6df00-c7ef-444b-951f-33a2c0072bec","10.5285/10c6df00-c7ef-444b-951f-33a2c0072bec"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Influence of Jasmonic acid on the response of pasture to ozone","topic":["0/Environmental risk/","0/Pollution/"],"version":1.0,"view":["public","danor"],"shortenedDescription":"The data are biomass and ozone-injury data for white clover (Trifolium repens). Dataset concerns a 2014 study on the effects of Jasmonic acid/cutting in modulating the response of clover to ozone. A short-term (4-week) ozone-exposure experiment was conducted in 2014..."},{"publicationDate":"2016-07-11T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","Albert-Ludwigs-University of Freiburg"],"authorGivenName":["M.","S.","K.","J."],"authorFamilyName":["Tanguy","Bachmair","Stahl","Hannaford"],"authorFullName":["Tanguy, M.","Bachmair, S.","Stahl, K.","Hannaford, J."],"authorOrcid":["https://orcid.org/0000-0002-1516-6834","https://orcid.org/0000-0002-5256-3310"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/0245cg223"],"catalogue":"eidc","description":"This dataset consists in a collection of remotely sensed drought indicators time series. The data was extracted from CEH's gridded remotely sensed drought indicators product (Tanguy et al., 2016; http://doi.org/10.5285/4e0d0e50-2f9c-4647-864d-5c3b30bb5f4b), which has gridded data for Europe for three drought indicators:\n - the Vegetation Condition Index (VCI) based on satellite product NDVI (Normalised Difference Vegetation Index);\n - the Temperature Condition Index (TCI) based on remotely sensed LST (Land Surface Temperature);\n - the Vegetation Health Index (VHI) which is a combination of VCI and TCI.\n\nThese three drought indicators have been extracted for European NUTS regions (level 0, 1, 2 and 3). These have been masked with a land use land cover map to be able to study different responses for various land cover types. A simplified LULC was created, with only four classes: forest, crop, shrub and grass. One extra time series was created for all classes together.","documentType":"GEMINI_DOCUMENT","identifier":"5b3fcf9f-19d4-4ad3-a8bb-0a5ea02c857e","incomingCitationCount":1,"givenName":["M.","S.","K.","J."],"familyName":["Tanguy","Bachmair","Stahl","Hannaford"],"fullName":["Tanguy, M.","Bachmair, S.","Stahl, K.","Hannaford, J."],"keyword":["Environmental risk","Vegetation Condition Index ","VCI","Normalised Difference Vegetation Index","NVDI","moderate-resolution imaging spectroradiometer","MODIS","Land Surface Temperature","LST","Temperature Condition Index ","TCI","DrIVER","NUTS","crops","shrubs","monitoring and early warning system","Nomenclature of Territorial Units for Statistics","Nomenclature des unités territoriales statistiques","drought","grass","forest","land cover","land use"],"keywordsTheme":["Environmental risk"],"keywordsOther":["Vegetation Condition Index ","VCI","Normalised Difference Vegetation Index","NVDI","moderate-resolution imaging spectroradiometer","MODIS","Land Surface Temperature","LST","Temperature Condition Index ","TCI","DrIVER","NUTS","crops","shrubs","monitoring and early warning system","Nomenclature of Territorial Units for Statistics","Nomenclature des unités territoriales statistiques","drought","grass","forest","land cover","land use"],"licence":"Open government licence","lineage":"Time series for three drought indicators based on remote sensing have been extracted for European NUTS regions (level 0, 1, 2 and 3). The Nomenclature of Territorial Units for Statistics, (NUTS, for the French Nomenclature des unités territoriales statistiques), developed by the European Union, is a geocode standard for referencing the administrative divisions of countries for statistical purposes. A land use mask was applied to extract the time series, to differentiate the contribution of crops, grass, forest and shrubs. There is also one time series for each NUTS region which includes all classes. The land cover product used to produce the mask was remote sensing MODIS product MCD12C1 (year 2012) which has a 0.05 degree resolution. The three drought indicators extracted are (i) the Vegetation Condition Index (VCI) based on satellite product NDVI (Normalised Difference Vegetation Index) (ii) the Temperature Condition Index based on remotely sensed LST (Land Surface Temperature) and (iii) the Vegetation Health Index (VHI) which is a combination of VCI and TCI. These indicators were first calculated as a gridded product for Europe with a 0.05 degree resolution and monthly time step (2000-2015), using MODIS product MOD13C2 for NDVI, and MODIS product MOD11C3 for LST, following methodology described by Kogan (1995; https://doi.org/10.1016/0273-1177(95)00079-T). The time series were then extracted applying the simplified land use classification mask (crops, forest, grass, shrubs) to each NUTS region, and an additional time series for all classes. For each time step, a value was produced only if at least 50% of the pixels within the non-masked area had valid values.\n\nNOTE: there are two types of \"No Data\" value. Value '--' means there were no pixels with valid values within the non-masked area. Value 'nan' means there were some pixels with valid values within the non-masked area, but these covered less than 50% of the area. These time steps were discarded as less than 50% was considered not representative enough of the whole area.\n","locations":["POLYGON((-15 30, -15 75, 45 75, 45 30, -15 30))"],"orcid":["https://orcid.org/0000-0002-1516-6834","https://orcid.org/0000-0002-5256-3310"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","Albert-Ludwigs-University of Freiburg","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/5b3fcf9f-19d4-4ad3-a8bb-0a5ea02c857e","10.5285/5b3fcf9f-19d4-4ad3-a8bb-0a5ea02c857e"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/0245cg223","https://ror.org/04xw4m193"],"state":"published","title":"Drought indicator time series for European NUTS regions based on remote sensing data (2000-2015)","topic":["0/Environmental risk/"],"version":1.0,"view":["public","phtr"],"shortenedDescription":"This dataset consists in a collection of remotely sensed drought indicators time series. The data was extracted from CEH's gridded remotely sensed drought indicators product (Tanguy et al., 2016; http://doi.org/10.5285/4e0d0e50-2f9c-4647-864d-5c3b30bb5f4b), which has..."},{"publicationDate":"2016-09-15T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["S.M."],"authorFamilyName":["Wright"],"authorFullName":["Wright, S.M."],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Prediction of Caesium-137 (Cs-137) deposition from atmospheric nuclear weapons tests. The methodology uses a ratio of Cs-137 deposition and precipitation measured at Milford Haven by the Atomic Energy Authority extrapolated across Great Britain using a 5 by 5 km resolution UKCIP precipitation dataset. The prediction is for 31 December 1985. ","documentType":"GEMINI_DOCUMENT","identifier":"c3e530bf-af20-43fc-8b4b-92682233ff08","incomingCitationCount":1,"givenName":["Simon","S.M."],"familyName":["Wright"],"fullName":["Wright, S.","Wright, S.M."],"keyword":["Scotland","Wales","England","Great Britain","Mapping","Radioecology","Radiocaesium","Cs137","Atmospheric nuclear weapons tests","radioecology","rain","atmospheric precipitation","nuclear hazard"],"keywordsPlace":["Scotland","Wales","England","Great Britain"],"keywordsTheme":["Mapping","Radioecology"],"keywordsOther":["Radiocaesium","Cs137","Atmospheric nuclear weapons tests","radioecology","rain","atmospheric precipitation","nuclear hazard"],"licence":"Open government licence","lineage":"The methodlogy used to estimate Cs137 deposition from atmospheric nuclear weapons tests was originally developed in the Artic Monitoring and Assessment Programme (AMAP) to estimate rates of radiocaesium transfer from soil to vegetation and food products. The method was then used to estimate Cs137 deposition from atmospheric nuclear weapons tests in Great Britain to allow quantification of Cs137 from the Chernobyl accident in 1986. \nSee also: Wright, S.M., Howard, B.J., Strand, P. Nylen, T & Sickel, M.A.K. 1999 Prediction of 137Cs deposition from atmospheric nuclear weapons tests within the Arctic. Environmental Pollution, 104, 131-143.","locations":["POLYGON((-13.01 47.819, -13.01 61.132, 3.555 61.132, 3.555 47.819, -13.01 47.819))"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/c3e530bf-af20-43fc-8b4b-92682233ff08","10.5285/c3e530bf-af20-43fc-8b4b-92682233ff08"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Wright, S.M., Howard, B.J., Strand, P. Nylen, T & Sickel, M.A.K. 1999 Prediction of 137Cs deposition from atmospheric nuclear weapons tests within the Arctic. Environmental Pollution, 104, 131-143."],"title":"Predicted Caesium-137 deposition from atmospheric nuclear weapons tests","topic":["0/Mapping/","0/Radioecology/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Prediction of Caesium-137 (Cs-137) deposition from atmospheric nuclear weapons tests. The methodology uses a ratio of Cs-137 deposition and precipitation measured at Milford Haven by the Atomic Energy Authority extrapolated across Great Britain using a 5 by 5 km resolution..."},{"publicationDate":"2017-07-11T00:00:00.000+00:00","authorAffiliation":["University of Extremadura","University of Nottingham","Centre for Ecology & Hydrology"],"authorGivenName":["J.","M.","S.","C.","C.L.","Nicholas A.","A.","J.M.","J.G.","E.","J.S."],"authorFamilyName":["Guillén","Izquierdo","Young","Wells","Barnett","Beresford","Baeza","Salas","Muñóz-Serrano","Corrales-Vázquez","Muñoz-Muñoz","Tovar","Chaplow"],"authorFullName":["Guillén, J.","Izquierdo, M.","Young, S.","Wells, C.","Barnett, C.L.","Beresford, N.A.","Baeza, A.","Salas, A.","Muñóz-Serrano, A.","Corrales-Vázquez, J.M.","Muñoz-Muñoz, J.G.","Tovar, E.","Chaplow, J.S."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"authorRor":["https://ror.org/0174shg90","https://ror.org/01ee9ar58","https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise stable element concentrations in terrestrial Reference Animals and Plants (RAPs) and corresponding whole-body concentration ratios determined in two different Mediterranean ecosystems: a Pinewood and a Dehesa (grassland with disperse tree cover). The International Commission on Radiological Protection (ICRP) RAPs considered in the Pinewood ecosystem were Pine Tree and Wild Grass; whereas in the Dehesa ecosystem those considered were Deer, Rat, Earthworm, Bee, Frog, Duck and Wild Grass.\n\nThe data include: elemental concentrations in soils; elemental concentrations in  plants, invertebrates, vertebrate tissues and estimated concentrations for vertebrate whole-organisms; individual concentration ratios (relating the fresh matter concentration in organisms to the dry matter concentration in soil); vertebrate species tissue masses; fresh to dry matter data for invertebrate species; geometric and arithmetic mean and standard deviation summaries for elemental concentrations and concentration ratios.\n\nElemental concentrations presented include  I, Li, Be, B, Na, Mg, Al, P, S, K. Ca, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Rb, Sr, Mo, Ag, Cd, Cs, Ba, Tl, Pb and U.","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/L000318/1"],"identifier":"a1ab8c79-3426-43a4-ab42-6d1b218d1cc6","incomingCitationCount":2,"givenName":["Nicholas A.","J.","M.","S.","C.","C.L.","A.","J.M.","J.G.","E.","J.S."],"familyName":["Beresford","Guillén","Izquierdo","Young","Wells","Barnett","Baeza","Salas","Muñóz-Serrano","Corrales-Vázquez","Muñoz-Muñoz","Tovar","Chaplow"],"fullName":["Beresford, N.A.","Guillén, J.","Izquierdo, M.","Young, S.","Wells, C.","Barnett, C.L.","Baeza, A.","Salas, A.","Muñóz-Serrano, A.","Corrales-Vázquez, J.M.","Muñoz-Muñoz, J.G.","Tovar, E.","Chaplow, J.S."],"keyword":["Dehesa","Spain","Radioecology","Apis mellifera","Pelophylax perezi","Briza minor","Apodemus sylvaticus","Cervus elaphus","Anas platyrhynchos"],"keywordsPlace":["Dehesa","Spain"],"keywordsTheme":["Radioecology"],"keywordsOther":["Apis mellifera","Pelophylax perezi","Briza minor","Apodemus sylvaticus","Cervus elaphus","Anas platyrhynchos"],"licence":"Open government licence","lineage":"Samples of earthworms (Lumbricidae spp), bees (Apis mellifera), frogs (Pelophylax perezi), rats (Apodemus sylvaticus), deer (Cervus elaphus): duck (Anas platyrhynchos), wild grass (Briza minor), pine tree and soil were collected. Samples were prepared for analysis (dried and ground where applicable) and digested prior to ICP-MS analysis. Iodine analysis was also performed. Full materials and methods available by downloading the supporting documentation.","locations":["POLYGON((-7.539 37.864, -7.539 40.584, -4.747 40.584, -4.747 37.864, -7.539 37.864))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"organisation":["UK Centre for Ecology & Hydrology","University of Extremadura","University of Nottingham","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/a1ab8c79-3426-43a4-ab42-6d1b218d1cc6","10.5285/a1ab8c79-3426-43a4-ab42-6d1b218d1cc6"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/0174shg90","https://ror.org/01ee9ar58","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Barnett, C.L., Beresford, N.A., Walker, L.A., Baxter, M., Wells, C., & Copplestone, D. (2013). Transfer parameters for ICRP reference animals and plants collected from a forest ecosystem. Radiation and Environmental Biophysics, 53(1), 125-149","IAEA (Contributors: Howard, B.J., Beresford, N.A.,Barnett, C.L.,  Wells, C.) 2014 Handbook of parameter values for the prediction of radionuclide transfer to wildlife. Technical Reports Series No. 479 (Beresford, N.A., Howard, B.J. [Eds]) IAEA, Vienna. "],"title":"Elemental concentrations in representative species of the ICRP's Reference Animals and Plants and associated soils in terrestrial Mediterranean ecosystems in Spain","topic":["0/Radioecology/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise stable element concentrations in terrestrial Reference Animals and Plants (RAPs) and corresponding whole-body concentration ratios determined in two different Mediterranean ecosystems: a Pinewood and a Dehesa (grassland with disperse tree cover). The International..."},{"publicationDate":"2016-07-11T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","Albert-Ludwigs-University of Freiburg"],"authorGivenName":["M.","S.","K.","J."],"authorFamilyName":["Tanguy","Bachmair","Stahl","Hannaford"],"authorFullName":["Tanguy, M.","Bachmair, S.","Stahl, K.","Hannaford, J."],"authorOrcid":["https://orcid.org/0000-0002-1516-6834","https://orcid.org/0000-0002-5256-3310"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/0245cg223"],"catalogue":"eidc","description":"This dataset comprises three gridded drought indicators based on remote sensing data for Europe. The data has a spatial resolution of 0.05 degree and a temporal resolution of 1 month for the period going from 2000 to 2015. The three drought indicators are: \n the Vegetation Condition Index (VCI) based on satellite product NDVI (Normalised Difference Vegetation Index);\n  - the Temperature Condition Index (TCI) based on remotely sensed LST (Land Surface Temperature)\n  - the Vegetation Health Index (VHI) which is a combination of VCI and TCI, calculated using MODIS products","documentType":"GEMINI_DOCUMENT","identifier":"4e0d0e50-2f9c-4647-864d-5c3b30bb5f4b","incomingCitationCount":1,"givenName":["M.","S.","K.","J."],"familyName":["Tanguy","Bachmair","Stahl","Hannaford"],"fullName":["Tanguy, M.","Bachmair, S.","Stahl, K.","Hannaford, J."],"keyword":["Environmental risk","Vegetation Condition Index","VCI","NDVI","Normalised Difference Vegetation Index","Temperature Condition Index","TCI","LST","Land Surface Temperature","VHI","Vegetation Health Index","MODIS","moderate-resolution imaging spectroradiometer","DrIVER","monitoring and early warning system","drought"],"keywordsTheme":["Environmental risk"],"keywordsOther":["Vegetation Condition Index","VCI","NDVI","Normalised Difference Vegetation Index","Temperature Condition Index","TCI","LST","Land Surface Temperature","VHI","Vegetation Health Index","MODIS","moderate-resolution imaging spectroradiometer","DrIVER","monitoring and early warning system","drought"],"licence":"Open government licence","lineage":"Three gridded drought indicators based on remote sensing were calculated for Europe. The data has a spatial resolution of 0.05 degree and a temporal resolution of 1 month for the period going from 2000 to 2015. The three drought indicators are (i) the Vegetation Condition Index (VCI) based on satellite product NDVI (Normalised Difference Vegetation Index) (ii) the Temperature Condition Index based on remotely sensed LST (Land Surface Temperature) and (iii) the Vegetation Health Index (VHI) which is a combination of VCI and TCI. For NDVI, MODIS product MOD13C2 was used, and for LST, MODIS product MOD11C3 was used. VCI, TCI and VHI were derived using methodology described by Kogan (Kogan, F.N., 1995; https://doi.org/10.1016/0273-1177(95)00079-T)","locations":["POLYGON((-15 30, -15 75, 45 75, 45 30, -15 30))"],"orcid":["https://orcid.org/0000-0002-1516-6834","https://orcid.org/0000-0002-5256-3310"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","Albert-Ludwigs-University of Freiburg","NERC Environmental Information Data Centre","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/4e0d0e50-2f9c-4647-864d-5c3b30bb5f4b","10.5285/4e0d0e50-2f9c-4647-864d-5c3b30bb5f4b"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/0245cg223","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Kogan, F. N. (1995). Application of vegetation index and brightness temperature for drought detection. In Advances in Space Research (Vol. 15, Issue 11, pp. 91–100). Elsevier BV."],"title":"Gridded drought indices based on remote sensing data for Europe (2000-2015)","topic":["0/Environmental risk/"],"version":1.0,"view":["public","phtr"],"shortenedDescription":"This dataset comprises three gridded drought indicators based on remote sensing data for Europe. The data has a spatial resolution of 0.05 degree and a temporal resolution of 1 month for the period going from 2000 to 2015. The three drought indicators are: \n the Vegetation..."},{"publicationDate":"2017-06-01T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["M."],"authorFamilyName":["Vieno"],"authorFullName":["Vieno, M."],"authorOrcid":["https://orcid.org/0000-0001-7741-9377"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"The European Monitoring and Evaluation Program Unified Model for the UK (EMEP4UK) simulates the year 2001 to 2014 UK daily average atmospheric composition at a horizontal resolution of 5 x 5 km2. The species included in this dataset are surface daily average concentrations of: nitric oxide (NO), nitrogen dioxide (NO2), particulate matter (PM10 and PM2.5), ammonia (NH3), nitric acid (HNO3), sulphur dioxide (SO2), ammonium (NH4+), nitrate (NO3-), sulphate (SO42-), PM2.5 organic matter, and ground level ozone (O3).\n\nThe EMEP4UK model framework consists of an atmospheric chemistry transport model (ACTM) which simulates hourly to annual average atmospheric composition and deposition of various pollutants and the weather research and forecast model (WRF). Pollutants simulated include fine particulate matter (PM10, PM2.5), secondary organic aerosols (SOA), elemental carbon (EC), secondary inorganic aerosols (SIA), sulphur dioxide (SO2), ammonia (NH3), nitrogen oxides (NOx), and ground level ozone (O3). Dry and wet deposition of pollutants are also generated by the EMEP4UK. WRF is used to calculate the required meteorological input data for the ACTM.\n\nThe version of EMEP4UK used to model the 2001-2014 dataset available here is based on the EMEP Meteorological Synthesizing Centre West (MSC-W) model version rv4.4.\n\nA  version of this dataset, calculated using the EMEP model version rv4.17 and the WRF model version 3.7.1 is available at https://doi.org/10.5285/b0545f67-e47c-4077-bf3c-c5ffcd6b72c8\n\nNotes:\nOnly the simulations for the years between 2002-2012 include data for from forest fire.\nThe emissions used for simulating the years 2013 and 2014 are the same as the year 2012 (updated date will be made available as soon as 2013 and 2014 national emission inventory data have been processed).\nThe calculated year 2001-2012 use a different version of the WRF model, moreover for the year 2013 and 2014 the WRF model setup was changed as the specific Humidity is no longer nudged with re-analysis in the WRF simulation.\n\nAcknowledgements required (third-party datasets used to drive the model): The WRF model calculated meteorology uses the dataset from NCEP FNL Operational Model Global Tropospheric Analyses, continuing from July 1999. (http://www.wrf-model.org/). National Centers for Environmental Prediction/National Weather Service/NOAA/U.S. Department of Commerce. 2000, updated daily. NCEP FNL Operational Model Global Tropospheric Analyses, continuing from July 1999. Research Data Archive at the National Center for Atmospheric Research, Computational and Information Systems Laboratory. (http://doi.org/10.5065/D6M043C6). Emissions data from the EMEP emissions center (www.emep.int), and NAEI web site (http://naei.defra.gov.uk).","documentType":"GEMINI_DOCUMENT","identifier":"39c6e02f-11ee-44d5-b587-b225f1a99bc8","incomingCitationCount":0,"givenName":["Massimo","M."],"familyName":["Vieno"],"fullName":["Vieno, M."],"keyword":["Pollution","Climate and climate change","Modelling","Environmental risk","ammonium (NH4+)","ammonia (NH3)","ozone (O3)","sulphur dioxide (SO2)","Nitrogen dioxide","Particulate organic matter","sulphate","nitrate","European Monitoring Evaluation Programme (EMEP)"],"keywordsTheme":["Pollution","Climate and climate change","Modelling","Environmental risk"],"keywordsOther":["ammonium (NH4+)","ammonia (NH3)","ozone (O3)","sulphur dioxide (SO2)","Nitrogen dioxide","Particulate organic matter","sulphate","nitrate","European Monitoring Evaluation Programme (EMEP)"],"licence":"Open government licence","lineage":"The UK Automatic Urban and Rural monitoring Network (AURN) hourly data are used to verify the EMEP4UK model output:\n\nVieno, M., Dore, A. J., Stevenson, D. S., Doherty, R., Heal, M. R., Reis, S., Hallsworth, S., Tarrason, L., Wind, P., Fowler, D., Simpson, D., and Sutton, M. A.: Modelling surface ozone during the 2003 heat-wave in the UK, Atmospheric Chemistry and Physics, 10, 7963-7978 https://doi.org/10.5194/acp-10-7963-2010, 2010\n\nVieno, M., Heal, M. R., Williams, M. L., Carnell, E. J., Nemitz, E., Stedman, J. R., and Reis, S.: The sensitivities of emissions reductions for the mitigation of UK pm2.5, Atmos. Chem. Phys., 16, 265-276 https://doi.org/10.5194/acp-16-265-2016, 2016.\n\nThe UK Acid Gases and Aerosols Network (AGANet) monthy data are also used to verify the EMEP4UK model output:\n\nVieno, M., Heal, M. R., Hallsworth, S., Famulari, D., Doherty, R. M., Dore, A. J., Tang, Y. S., Braban, C. F., Leaver, D., Sutton, M. A., and Reis, S.: The role of long-range transport and domestic emissions in determining atmospheric secondary inorganic particle concentrations across the UK, Atmos. Chem. Phys., 14, 8435-8447 https://doi.org/10.5194/acp-14-8435-2014, 2014\n\nThe EMEP4UK model have been evaluated against other models in the Defra organised model inter-comparison:\n\nCarslaw, D. C.: Report: Defra deposition model evaluation analysis - Phase 1, London, http://uk-air.defra.gov.uk/library/reports?report_id=652, access 01/04/2015, 2011.\nCarslaw, D. C.: Report: Defra regional and transboundary model evaluation analysis - Phase 1, London, http://uk-air.defra.gov.uk/library/reports?report_id=653, access 01/04/2015, 2011.\n\nThe EMEP MSC-W from which the EMEP4UK model is derived is routinely updated and validated in EU: www.emep.int\n\nNo further QA/QC is carried out.","locations":["POLYGON((-11.637 49.007, -11.637 61.37, 4.932 61.37, 4.932 49.007, -11.637 49.007))"],"orcid":["https://orcid.org/0000-0001-7741-9377"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/39c6e02f-11ee-44d5-b587-b225f1a99bc8"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["The EMEP MSC-W from which the EMEP4UK model is derived is routinely updated and validated"],"title":"The EMEP4UK modelled daily atmospheric composition","topic":["0/Pollution/","0/Climate and climate change/","0/Modelling/","0/Environmental risk/"],"version":1.0,"view":["public","phtr"],"shortenedDescription":"The European Monitoring and Evaluation Program Unified Model for the UK (EMEP4UK) simulates the year 2001 to 2014 UK daily average atmospheric composition at a horizontal resolution of 5 x 5 km2. The species included in this dataset are surface daily average concentrations..."},{"publicationDate":"2022-09-06T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology"],"authorGivenName":["E.","J.","G.","P."],"authorFamilyName":["Trill","Robotham","Old","Rameshwaran","Bishop"],"authorFullName":["Trill, E.","Robotham, J.","Old, G.","Rameshwaran, P.","Bishop, J."],"authorOrcid":["https://orcid.org/0000-0002-6233-8942","https://orcid.org/0000-0002-1223-8345","https://orcid.org/0000-0002-4713-1070","https://orcid.org/0000-0002-8972-953X"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset contains high-resolution (5-minute) raw, atmospheric corrected and mean sea level adjusted water level data for 9 flood storage areas (FSAs) in the Littlestock Brook catchment (a tributary of the River Evenlode, Thames Basin) from 2018 to 2022. The dataset also includes the estimated 9 x FSA stored volume time-series, estimated using a depth-stored volume lookup table for each FSA, produced from a digital elevation model of each feature and a depth-area-volume toolset. The annual barometric pressure time-series used to correct water level is also provided.\n\nThis dataset was collected by UKCEH as part of a hydrological monitoring programme for the Littlestock Brook Natural Flood Management scheme. This work was supported by the SPITFIRE NERC DTP (NE/L002531/1) and the SCENARIO NERC DTP (NE/L002566/1).","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/L002531/1","NE/L002566/1"],"identifier":"cf70f798-442a-4775-963c-b6600023830f","incomingCitationCount":0,"givenName":["E.","J.","G.","P."],"familyName":["Trill","Robotham","Old","Rameshwaran","Bishop"],"fullName":["Trill, E.","Robotham, J.","Old, G.","Rameshwaran, P.","Bishop, J."],"keyword":["Oxfordshire","Cotswolds","Thames Basin","Hydrology","Environmental risk","natural flood management (NFM)","flood storage area (FSA)","bund","hydrology","flood","flood risk management"],"keywordsPlace":["Oxfordshire","Cotswolds","Thames Basin"],"keywordsTheme":["Hydrology","Environmental risk"],"keywordsOther":["natural flood management (NFM)","flood storage area (FSA)","bund","hydrology","flood","flood risk management"],"licence":"Open government licence","lineage":"Data were generated using pressure sensors supplied with a factory calibration. A barometric correction was applied to sensor pressure time-series. Barometric corrected pressure data were then calibrated to stage using a linear regression developed between these data and observed stage board readings. After this correction data were quality controlled to flag any spurious readings, which were removed and interpolated if appropriate. Flood Storage Area (FSA) volume for each feature was estimated using a Digital Elevation Model (DEM) produced with LiDAR data. If LiDAR data were not available, as-built manual survey data were interpolated using the Natural Neighbour method. The DEMs were imported into ArcGIS to create a raster and apply a depth-area-volume toolset for each FSA. The continuous corrected water level time-series in each FSA was then used to produce a time-series of stored volume for each FSA, by matching the water level time-series to the depth-stored volume lookup table produced from ArcGIS.","locations":["POLYGON((-1.6 51.85, -1.6 51.88, -1.66 51.88, -1.66 51.85, -1.6 51.85))"],"orcid":["https://orcid.org/0000-0002-6233-8942","https://orcid.org/0000-0002-1223-8345","https://orcid.org/0000-0002-4713-1070","https://orcid.org/0000-0002-8972-953X"],"organisation":["UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/cf70f798-442a-4775-963c-b6600023830f","10.5285/cf70f798-442a-4775-963c-b6600023830f"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"High-resolution time-series of flood storage area water levels and estimated stored volumes in the Littlestock Brook, Thames Basin, England, 2018-2022","topic":["0/Hydrology/","0/Environmental risk/"],"version":1.0,"view":["public","margla"],"shortenedDescription":"This dataset contains high-resolution (5-minute) raw, atmospheric corrected and mean sea level adjusted water level data for 9 flood storage areas (FSAs) in the Littlestock Brook catchment (a tributary of the River Evenlode, Thames Basin) from 2018 to 2022. The dataset..."},{"publicationDate":"2015-06-30T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","Institut de Radioprotection et de Sûreté Nucléaire","Independent Radiological Protection Specialist","Belgian Nuclear Research Centre","University of Salford","National Institute of Radiological Sciences","Centro de Investigaciones Energéticas, Medioambientales y Tecnológicas","International Atomic Energy Agency","Institute for the Application of Nuclear Energy","Scientific & Production Association TYPHOON","McMaster University","Fukushima University","National Radiation Protection Institute","Stockholm University","BfS"],"authorGivenName":["N.A.","K.","C.","S.","J.","M.D.","A.","M.","N.","B.S.","C.L.","T.","J.S."],"authorFamilyName":["Beresford","Beaugelin-Seiller","Wells","Vives-Lynch","Vives i Batlle","Wood","Tagami","Real","Burgos","Fesenko","Cujic","Kryshev","Pachal","Su","Barnett","Uchida","Hinton","Mihalík","Stark","Willrodt","Chaplow"],"authorFullName":["Beresford, N.A.","Beaugelin-Seiller, K.","Wells, C.","Vives-Lynch, S.","Vives i Batlle, J.","Wood, M.D.","Tagami, K.","Real, A.","Burgos, J.","Fesenko, S.","Cujic, M.","Kryshev, A.","Pachal, N.","Su, B.S.","Barnett, C.L.","Uchida, S.","Hinton, T.","Mihalík, J.","Stark, K.","Willrodt, C.","Chaplow, J.S."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/01ha22c77","https://ror.org/020xs5r81","https://ror.org/01tmqtf75","https://ror.org/05szqz470","https://ror.org/05xx77y52","https://ror.org/02zt1gg83","https://ror.org/02mme4d79","https://ror.org/02fa3aq29","https://ror.org/03zjb7z20","https://ror.org/02vwpg498","https://ror.org/05f0yaq80","https://ror.org/02yvd4j36"],"catalogue":"eidc","description":"Data comprise biological and ecological half-life values for marine, freshwater, terrestrial and riparian organisms. The database includes 1908 biological half-life values for 52 elements across a range of wildlife groups (marine, freshwater, terrestrial and riparian). The compilation of values from a range of sources was conducted by an international working group under the auspices of an International Atomic Energy Agency programme.","documentType":"GEMINI_DOCUMENT","identifier":"b95c2ea7-47d2-4816-b942-68779c59bc4d","incomingCitationCount":7,"givenName":["N.A.","K.","C.","S.","J.","M.D.","A.","M.","N.","B.S.","C.L.","T.","J.S.","Nick"],"familyName":["Beresford","Beaugelin-Seiller","Wells","Vives-Lynch","Vives i Batlle","Wood","Tagami","Real","Burgos","Fesenko","Cujic","Kryshev","Pachal","Su","Barnett","Uchida","Hinton","Mihalík","Stark","Willrodt","Chaplow"],"fullName":["Beresford, N.A.","Beaugelin-Seiller, K.","Wells, C.","Vives-Lynch, S.","Vives i Batlle, J.","Wood, M.D.","Tagami, K.","Real, A.","Burgos, J.","Fesenko, S.","Cujic, M.","Kryshev, A.","Pachal, N.","Su, B.S.","Barnett, C.L.","Uchida, S.","Hinton, T.","Mihalík, J.","Stark, K.","Willrodt, C.","Chaplow, J.S.","Beresford, N."],"keyword":["Pollution","Radioecology","radioecology","biological","ecological","elimination","rate","concentration","ratio","marine","terrestrial","wildlife","riparian zone","freshwater","half-life","radionuclide"],"keywordsTheme":["Pollution","Radioecology"],"keywordsOther":["radioecology","biological","ecological","elimination","rate","concentration","ratio","marine","terrestrial","wildlife","riparian zone","freshwater","half-life","radionuclide"],"licence":"Open government licence","lineage":"Prior to beginning the review, a recording sheet (in Microsoft Excel), was designed to allow easy collation of the various components into the final database. The wildlife group categorisations were broadly compatible with those used in the Wildlife Transfer Database (as described by Copplestone et al. 2013) and subsequently by the IAEA (Howard et al. 2013; IAEA 2014). The 'Changeover time' is the intersect of the first and second biological half-lives when two regression lines on a logarithmic scale. No attempt was made to standardise the English common names used; similarly we have not updated Latin species names, but we acknowledge that these may have changed since the original publications.","locations":["POLYGON((-180 -90, -180 90, 180 90, 180 -90, -180 -90))"],"orcid":["https://orcid.org/0000-0002-8722-0238"],"organisation":["Centre for Ecology & Hydrology","Institut de Radioprotection et de Sûreté Nucléaire","Independent Radiological Protection Specialist","Belgian Nuclear Research Centre","University of Salford","National Institute of Radiological Sciences","Centro de Investigaciones Energéticas, Medioambientales y Tecnológicas","International Atomic Energy Agency","Institute for the Application of Nuclear Energy","Scientific & Production Association TYPHOON","McMaster University","Fukushima University","National Radiation Protection Institute","Stockholm University","BfS","UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/b95c2ea7-47d2-4816-b942-68779c59bc4d","10.5285/b95c2ea7-47d2-4816-b942-68779c59bc4d"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/01ha22c77","https://ror.org/020xs5r81","https://ror.org/01tmqtf75","https://ror.org/05szqz470","https://ror.org/05xx77y52","https://ror.org/02zt1gg83","https://ror.org/02mme4d79","https://ror.org/02fa3aq29","https://ror.org/03zjb7z20","https://ror.org/02vwpg498","https://ror.org/05f0yaq80","https://ror.org/02yvd4j36","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Handbook of parameter values for the prediction of radionuclide transfer to wildlife (2014). Technical Reports Series No. 479. IAEA, Vienna."],"title":"A database of radionuclide biological half-life values for wildlife","topic":["0/Pollution/","0/Radioecology/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise biological and ecological half-life values for marine, freshwater, terrestrial and riparian organisms. The database includes 1908 biological half-life values for 52 elements across a range of wildlife groups (marine, freshwater, terrestrial and riparian)...."},{"publicationDate":"2018-02-21T00:00:00.000+00:00","authorAffiliation":["Chornobyl center","Centre for Ecology & Hydrology"],"authorGivenName":["S.P.","Nicholas A.","C.L.","C.","A.","J.S."],"authorFamilyName":["Gaschak","Beresford","Barnett","Wells","Maksimenko","Chaplow"],"authorFullName":["Gaschak, S.P.","Beresford, N.A.","Barnett, C.L.","Wells, C.","Maksimenko, A.","Chaplow, J.S."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise radionuclide concentrations in soils and a range of terrestrial vertebrate species (reptiles, small mammals and birds) sampled in the Chernobyl Exclusion Zone (CEZ) between 1999 and 2008. Reptiles were collected in 1999, 2000, 2001, 2003 and 2007, birds, bats, and small mammals were collected in 2004, 2005, 2007 and 2008. Dose rate data are provided for one study, both as ambient dose rate measurements and also as recorded by thermoluminescent dosimeters attached to small mammal species. The isotopes measured include: Americium-241, Caesium-134 and 137, Cobalt-60, Europium-154 and 155, Potassium-40, Plutonium-238, -239 and -240, Strontium-90. The data were used to assess the concentration of radioactive contamination in soil, consequent uptake of radionuclides by wildlife living in the CEZ and to test prediction of the ERICA Tool assessment model.\n\nThe data were used to assess the uptake of radionuclides by wildlife living in the CEZ and to derive transfer parameters, and also to test predictions of the assessment model the ‘ERICA Tool’.","documentType":"GEMINI_DOCUMENT","identifier":"518f88df-bfe7-442e-97ad-922b5aef003a","incomingCitationCount":0,"givenName":["Nicholas A.","S.P.","C.L.","C.","A.","J.S."],"familyName":["Beresford","Gaschak","Barnett","Wells","Maksimenko","Chaplow"],"fullName":["Beresford, N.A.","Gaschak, S.P.","Barnett, C.L.","Wells, C.","Maksimenko, A.","Chaplow, J.S."],"keyword":["Ukraine","Chernobyl Exclusion Zone (CEZ)","Chornobyl","Environmental survey","Soil","Radioecology","Environmental risk","radioecology","Americium","Europium","Concentration ratio","Terrestrial biota","Transfer parameter","ERICA","TREE","COMET","radionuclide","potassium fertiliser","cobalt","strontium","caesium","plutonium"],"keywordsPlace":["Ukraine","Chernobyl Exclusion Zone (CEZ)","Chornobyl"],"keywordsTheme":["Environmental survey","Soil","Radioecology","Environmental risk"],"keywordsOther":["radioecology","Americium","Europium","Concentration ratio","Terrestrial biota","Transfer parameter","ERICA","TREE","COMET","radionuclide","potassium fertiliser","cobalt","strontium","caesium","plutonium"],"licence":"Open government licence","lineage":"Reptiles were trapped at two sites: 'Red Forest 1' and 'Red Forest2'. Red Forest 1 was approximately 2.6 km south west from the Chernobyl nuclear power plant; trapping occurred over a triangular area of circa 0.15 km2 . Red Forest 2 was approximately 2.7 km south west from the Chernobyl nuclear power plant; and trapping occurred over a square shaped area of circa 0.01 km2. Lacerta agilis were caught in Shermann traps; Natrix natrix were caught by hand. Soil samples (0–10 cm) were collected at  Red Forest 1 in June 2001 and at Red Forest 2 in May 2007. \n\nSmall mammals were trapped (and released in most cases) at three forest sites with differing soil radionuclide activity concentrations (Low, Medium and High) in the Chernobyl exclusion zone. At each site small mammal traps were located in a 100 m x 100 m study area. Soil samples (0-10 cm) were also sampled at these sites. Animals were fitted with thermoluminescent dosimeters.\n\nA range of passerine bird species were collected by mist nets during June 2005, euthanised and retained frozen.  Three species of bats were also collected from the sites during the period May and June 2008 using mist nets. After being euthanised the samples were stored frozen whilst awaiting analyses.","locations":["POLYGON((28.802 50.816, 28.802 51.499, 30.824 51.499, 30.824 50.816, 28.802 50.816))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"organisation":["UK Centre for Ecology & Hydrology","Chornobyl center","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/518f88df-bfe7-442e-97ad-922b5aef003a","10.5285/518f88df-bfe7-442e-97ad-922b5aef003a"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Beresford, N. A., Gaschak, S., Maksimenko, A., & Wood, M. D. (2016). The transfer of 137 Cs, Pu isotopes and 90 Sr to bird, bat and ground-dwelling small mammal species within the Chernobyl exclusion zone. Journal of Environmental Radioactivity, 153, 231-236","Video Abstract for The transfer of 137Cs, Pu isotopes and 90Sr to bird, bat and ground dwelling small mammal species within the Chernobyl exclusion zone","Beresford, N. A., Gaschak, S., Barnett, C. L., Howard, B. J., Chizhevsky, I., Strømman, G., … Copplestone, D. (2008). Estimating the exposure of small mammals at three sites within the Chernobyl exclusion zone – a test application of the ERICA Tool. Journal of Environmental Radioactivity, 99(9), 1496–1502","Barnett, C. L., Gaschak, S., Beresford, N. A., Howard, B. J., & Maksimenko, A. (2009). Radionuclide activity concentrations in two species of reptiles from the Chernobyl exclusion zone. Radioprotection, 44(5), 537–542. "],"supplementalName":["COMET project website","TREE project website"],"title":"Radionuclide data for vertebrates in the Chernobyl Exclusion Zone","topic":["0/Environmental survey/","0/Soil/","0/Radioecology/","0/Environmental risk/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise radionuclide concentrations in soils and a range of terrestrial vertebrate species (reptiles, small mammals and birds) sampled in the Chernobyl Exclusion Zone (CEZ) between 1999 and 2008. Reptiles were collected in 1999, 2000, 2001, 2003 and 2007, birds,..."},{"publicationDate":"2015-11-18T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","British Geological Survey","University of Salford","British Geological Society","School of Natural Sciences"],"authorGivenName":["Nicholas A.","C.L.","D.G.","M.D.","J.D.","N.","D."],"authorFamilyName":["Beresford","Barnett","Jones","Wood","Appleton","Breward","Copplestone"],"authorFullName":["Beresford, N.A.","Barnett, C.L.","Jones, D.G.","Wood, M.D.","Appleton, J.D.","Breward, N.","Copplestone, D."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-4511-4445","https://orcid.org/0000-0002-1468-9545"],"authorRor":["https://ror.org/00pggkr55","https://ror.org/04a7gbp98","https://ror.org/01tmqtf75"],"catalogue":"eidc","description":"Data comprise estimates of activity concentrations of naturally occurring radionuclides (40K, 238U and 232Th series radionuclides) in environmental media (soil and stream sediments and waters) and non-human biota (focusing on the ICRP Reference Animals and Plants). For soil, stream sediments and stream waters data were derived from total K, U and Th concentrations mainly from the ongoing geochemical survey of the United Kingdom (G-BASE), conducted by the British Geological Survey. The geochemical survey data are currently incomplete for England and Wales, but almost complete coverage was obtained for K in stream sediments by using the Wolfson Atlas data for southern England. For U and Th in sediments and K, U and Th in soils, more complete coverage was achieved by geological extrapolation (using relationships between soils/sediments and bedrock/superficial geology). For media and sediments, datasets are provided for both: (i) geometric mean concentrations from measured samples on a 5 x 5 km square basis where data are available; and (ii) extrapolated surfaces covering all of England and Wales. Data for non-human biota are from targeted sampling and analyses and data review.","documentType":"GEMINI_DOCUMENT","identifier":"bb2d7874-7bf4-44de-aa43-348bd684a2fe","incomingCitationCount":0,"givenName":["Nicholas A.","C.L.","D.G.","M.D.","J.D.","N.","D."],"familyName":["Beresford","Barnett","Jones","Wood","Appleton","Breward","Copplestone"],"fullName":["Beresford, N.A.","Barnett, C.L.","Jones, D.G.","Wood, M.D.","Appleton, J.D.","Breward, N.","Copplestone, D."],"keyword":["England","Wales","Radioecology","Soil","Pollution","water","thorium","potassium-40","radioecology","soil","sediment","biota","uranium"],"keywordsPlace":["England","Wales"],"keywordsTheme":["Radioecology","Soil","Pollution"],"keywordsOther":["water","thorium","potassium-40","radioecology","soil","sediment","biota","uranium"],"licence":"Open government licence","lineage":"Please download supporting information for full materials and methods. Alternatively refer to the following journal papers: \nFor soil, water and sediment data: Background exposure rates of terrestrial wildlife in England and Wales N.A. Beresford, C.L. Barnett, D.G. Jones, M.D. Wood, J.D. Appleton, N. Breward, D. Copplestone. Journal of Environmental Radioactivity 99 (2008) 1430-1439. https://doi.org/10.1016/j.jenvrad.2008.03.003 \nFor biota data: Assessment of naturally occurring radionuclides around England and Wales: Application of the G-BASE dataset to estimate doses to non-human species Jones, D. G., Appleton, J. D., Breward, N., Mackenzie, A. C., Scheib, C., Beresford, N. A., … Copplestone, D. (2009). Assessment of naturally occurring radionuclides around England and Wales: Application of the G-BASE dataset to estimate doses to non-human species. Radioprotection, 44(5), 629–634. https://doi.org/10.1051/radiopro/20095116","locations":["POLYGON((-6.452 49.864, -6.452 55.812, 1.768 55.812, 1.768 49.864, -6.452 49.864))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-4511-4445","https://orcid.org/0000-0002-1468-9545"],"organisation":["Centre for Ecology & Hydrology","British Geological Survey","University of Salford","British Geological Society","School of Natural Sciences","Natural Environment Research Council","UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["1271758286281","https://catalogue.ceh.ac.uk/id/bb2d7874-7bf4-44de-aa43-348bd684a2fe","10.5285/bb2d7874-7bf4-44de-aa43-348bd684a2fe"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04a7gbp98","https://ror.org/01tmqtf75","https://ror.org/02b5d8509","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Hosseini, A., Beresford, N. A., Brown, J. E., Jones, D. G., Phaneuf, M., Thørring, H., & Yankovich, T. (2010). Background dose-rates to reference animals and plants arising from exposure to naturally occurring radionuclides in aquatic environments. Journal of Radiological Protection, 30(2), 235-264","Beresford, N.A., Barnett, C.L., Jones, D.G., Wood, M.D., Appleton, J.D., Breward, N., Copplestone D. 2008. Background exposure rates of terrestrial wildlife in England and Wales. J. Environ. Radioact., 99, 1430-1439","Jones, D.G., Appleton, J.D., Breward, N., Mackenzie, A.C., Scheib, C., Beresford, N. A., Barnett, C.L., Wood, M.D., Copplestone D. Assessment of naturally occurring radionuclides around England and Wales: application of the G-BASE dataset to estimate doses to non-human species. Radioprotection (2009) 44, 629-634. ","Hosseini, A., Beresford, N.A., Brown, J.E., Jones, D.G., Phaneuf, M., Thørring, H., & Yankovich, T. (2010). Background dose-rates to reference animals and plants arising from exposure to naturally occurring radionuclides in aquatic environments. Journal of Radiological Protection, 30(2), 235-264","Beresford, N.A., Appleton, J D., Barnett, C.L., Bescoby, M.W., Breward, N., Jones, D.G., MacKenzie, A.C., Scheib, C.,Thørring, H., Wood, M.D. 2007. Assessment of naturally occurring radionuclides around England and Wales. Science Project SC030283. ISBN: 1844325679. Environment Agency, Bristol."],"supplementalName":["Further information about national initiatives on radiological environmental protection"],"title":"Natural radionuclide concentrations in soil, water, sediment and biota in England and Wales","topic":["0/Radioecology/","0/Soil/","0/Pollution/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise estimates of activity concentrations of naturally occurring radionuclides (40K, 238U and 232Th series radionuclides) in environmental media (soil and stream sediments and waters) and non-human biota (focusing on the ICRP Reference Animals and Plants)...."},{"publicationDate":"2016-06-22T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology"],"authorGivenName":["F.K.","P.","H.","G.P."],"authorFamilyName":["Edwards","Scarlett","Vincent","Webb"],"authorFullName":["Edwards, F.K.","Scarlett, P.","Vincent, H.","Webb, G.P."],"authorOrcid":["https://orcid.org/0000-0001-6242-8158"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"The data consist of species level descriptions of macroinvertebrate communities from two abstracted streams in the Lowther catchment, UK, upstream and downstream of abstraction points. Supporting habitat and geographical data are included.","documentType":"GEMINI_DOCUMENT","identifier":"df65085c-d376-413e-9fbc-984f7b332878","incomingCitationCount":0,"givenName":["François","F.K.","P.","H.","G.P."],"familyName":["Edwards","Scarlett","Vincent","Webb"],"fullName":["Edwards, F.","Edwards, F.K.","Scarlett, P.","Vincent, H.","Webb, G.P."],"keyword":["Biodiversity","Land use","Environmental risk","Environmental survey","Paraleptophlebia submarginata","Polycentropus flavomaculatus","Plectrocnemia conspersa","Philopotamus montanus","Siphonoperla torrentium","Potamophylax cingulatus","Potamopyrgus antipodarum","Amphinemura sulcicollis","Chloroperla tripunctata","Electrogena lateralis","Hydropsyche siltalai","Odontocerum albicorne","Rhyacophila dorsalis","Stylodrilus heringianus","Hydropsyche instabilis","Sericostoma personatum","Rhyacophila fasciata","Serratella ignita","Eiseniella tetraedra","Alainites muticus","Polycelis felina","Oreodytes sanmarkii","Dinocras cephalotes","Hydraena gracilis","Gammarus pulex","Isoperla grammatica","Crenobia alpina","Planaria torva","Leuctra hippopus","Leuctra inermis","Limnius volckmari","Ancylus fluviatilis","Baetis rhodani","Baetis scambus","Baetis vernus","Esolus parallelepipedus","Caenis rivulorum","Drusus annulatus","Elmis aenea","Perla bipunctata","Radix balthica","Dixa dilatata","Plea minutissima","Silo pallipes"],"keywordsTheme":["Biodiversity","Land use","Environmental risk","Environmental survey"],"keywordsOther":["Paraleptophlebia submarginata","Polycentropus flavomaculatus","Plectrocnemia conspersa","Philopotamus montanus","Siphonoperla torrentium","Potamophylax cingulatus","Potamopyrgus antipodarum","Amphinemura sulcicollis","Chloroperla tripunctata","Electrogena lateralis","Hydropsyche siltalai","Odontocerum albicorne","Rhyacophila dorsalis","Stylodrilus heringianus","Hydropsyche instabilis","Sericostoma personatum","Rhyacophila fasciata","Serratella ignita","Eiseniella tetraedra","Alainites muticus","Polycelis felina","Oreodytes sanmarkii","Dinocras cephalotes","Hydraena gracilis","Gammarus pulex","Isoperla grammatica","Crenobia alpina","Planaria torva","Leuctra hippopus","Leuctra inermis","Limnius volckmari","Ancylus fluviatilis","Baetis rhodani","Baetis scambus","Baetis vernus","Esolus parallelepipedus","Caenis rivulorum","Drusus annulatus","Elmis aenea","Perla bipunctata","Radix balthica","Dixa dilatata","Plea minutissima","Silo pallipes"],"licence":"Open government licence","lineage":"The waterbodies studied are both tributaries of the Lowther, a sub-catchment of the Eden (Cumbria) catchment. The Heltondale Beck has a total length of 25.1 km and a catchment area of 11.8 square kilometres. The Howes Beck (also known as the Cawdale Beck) has a total length of 17.5 km and a catchment area of 9.1 square kilometres.\n\nSampling took place on the 23rd and 24th September 2010. Sampling reaches were selected approximately 100 metres upstream and downstream of water abstraction points in two streams, the Howes Beck and the Heltondale Beck. Location was recorded on Global Positioning System and a 100 metres sampling reach established around these locations within which the survey was carried out (50 meters upstream and 50 meters downstream). Water depth (centimetres) and wetted width (meters) were recorded at the centre of the 100m reaches as a mean of three readings. Map variables and geology were derived for those point locations using the Intelligent River Network (Version 17), which was first described in Dawson, F. H., Hornby, D. D., & Hilton, J. (2002). A method for the automated extraction of environmental variables to help the classification of rivers in Britain. In Aquatic Conservation: Marine and Freshwater Ecosystems (Vol. 12, Issue 4, pp. 391–403). Wiley. https://doi.org/10.1002/aqc.534\n\nThe habitats in the100 metre reaches were assessed using the River Habitat Survey (RHS) method, for which the standard protocol is described in: Environment Agency. (2003) River Habitat Survey in Britain and Ireland. Field Survey Guidance Manual: 2003 version Environment Agency, Bristol , UK.\n\nFor macroinvertebrate sampling, five riffles were chosen at random within the 100 metre sampling reaches. Macroinvertebrate samples were collected from each of the five riffles using a Surber sample with a mesh size of 250 micrometer and sampling area of 0.0625 square meteres, disturbing the substrate by hand in the sample area to a depth of approximately 5 cm. Samples were then washed into plastic sample bags, labelled and were preserved with a 4 percent formaldehyde solution in the field. In the laboratory, samples were washed through a 250 micormenter sieve and all macroinvertebrates were picked from the samples and identified to the lowest taxonomic level possible, usually species. Valid taxonomic names and unique taxon identification codes were provided in: Davies, C. and Edwards, F.K. (2011) Code list for recording the macroinvertebrates in freshwater in the British Isles. Centre for Ecology & Hydrology, Wallingford.\n\nData entry was validated by crosschecking data print outs with laboratory sheets.","locations":["POLYGON((-2.791 54.569, -2.791 54.632, -2.687 54.632, -2.687 54.569, -2.791 54.569))"],"orcid":["https://orcid.org/0000-0001-6242-8158"],"organisation":["UK Centre for Ecology & Hydrology","Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/df65085c-d376-413e-9fbc-984f7b332878","10.5285/df65085c-d376-413e-9fbc-984f7b332878"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Dawson, F. H., Hornby, D. D., & Hilton, J. (2002). A method for the automated extraction of environmental variables to help the classification of rivers in Britain. In Aquatic Conservation: Marine and Freshwater Ecosystems (Vol. 12, Issue 4, pp. 391–403). Wiley. https://doi.org/10.1002/aqc.534"],"title":"Macroinvertebrates of two abstracted streams: taxon data","topic":["0/Biodiversity/","0/Land use/","0/Environmental risk/","0/Environmental survey/"],"version":1.0,"view":["public","jone"],"shortenedDescription":"The data consist of species level descriptions of macroinvertebrate communities from two abstracted streams in the Lowther catchment, UK, upstream and downstream of abstraction points. 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