{"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":"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":"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":"2024-08-13T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology"],"authorGivenName":["J.","S.","E.J. ","T.","M."],"authorFamilyName":["Scheffler","Tomlinson","Carnell","Liska","Lofts","Bullock","Vieno"],"authorFullName":["Scheffler, J.","Tomlinson, S.","Carnell, E.J.","Liska, T.","Lofts, S.","Bullock, J.","Vieno, M."],"authorOrcid":["https://orcid.org/0000-0002-7398-4237","https://orcid.org/0000-0002-3237-7596","https://orcid.org/0000-0003-0870-1955","https://orcid.org/0000-0001-9500-0633","https://orcid.org/0000-0002-3627-851X","https://orcid.org/0000-0003-0529-4020","https://orcid.org/0000-0001-7741-9377"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset is a model output from the European Monitoring and Evaluation Programme (EMEP) model applied to the UK (EMEP4UK) driven by Weather and Research Forecast model meteorology (WRF). It provides annual total atmospheric deposition of cadmium, copper, nickel, lead, zinc, sulphur, and nitrogen over the UK on a 3x3 km2 grid for the years 2040, 2070 and 2100 under the Shared Socioeconomic Pathways (SSPs) 1-5. SSPs are future scenarios based on narratives of possible socio-economic pathways.\nThe EMEP4UK model version used here is rv4.36, and the WRF model version is the 4.2.2.\nThis work was supported by the Natural Environment Research Council award number NE/R016429/1 as part of the UK-SCAPE programme delivering National Capability.\n","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/R016429/1 "],"identifier":"eec9634d-ba2b-4553-a65d-ef6ce4c40ebc","incomingCitationCount":0,"givenName":["J.","S.","E.J. ","T.","M."],"familyName":["Scheffler","Tomlinson","Carnell","Liska","Lofts","Bullock","Vieno"],"fullName":["Scheffler, J.","Tomlinson, S.","Carnell, E.J.","Liska, T.","Lofts, S.","Bullock, J.","Vieno, M."],"keyword":["Environmental risk","aerosol","EMEP","EMEP4UK","European Monitoring and Evaluation Programme","sulphur oxide","nitrogen oxides","reduced nitrogen","cadmium","copper","nickel","lead","zinc","sulphur","nitrogen","UK-SCAPE"],"keywordsTheme":["Environmental risk"],"keywordsOther":["aerosol","EMEP","EMEP4UK","European Monitoring and Evaluation Programme","sulphur oxide","nitrogen oxides","reduced nitrogen","cadmium","copper","nickel","lead","zinc","sulphur","nitrogen","UK-SCAPE"],"licence":"Open government licence","lineage":"Daily average concentrations for a model domain covering the UK with a resolution of about 3x3 km2 were calculated using the EMEP4UK atmospheric chemistry transport model. The model was evaluated using the UK Automatic Urban and Rural Network (AURN) monitoring stations. R was used to access the AURN dataset to evaluate the EMEP4UK model output.\nTo assess and control the quality of the heavy metal data, we used observations from the Defra UK Heavy Metals Network and historical observation from NETCEN.\n\nThe data were processed from the full EMEP4UK model output to a subset containing essential variables only. The Climate Data Operators version 1.9.10 was used to subset the model output.\n","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/0000-0002-7398-4237","https://orcid.org/0000-0002-3237-7596","https://orcid.org/0000-0003-0870-1955","https://orcid.org/0000-0001-9500-0633","https://orcid.org/0000-0002-3627-851X","https://orcid.org/0000-0003-0529-4020","https://orcid.org/0000-0001-7741-9377"],"organisation":["UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/eec9634d-ba2b-4553-a65d-ef6ce4c40ebc","10.5285/eec9634d-ba2b-4553-a65d-ef6ce4c40ebc"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Riahi, K., van Vuuren, D. P., Kriegler, E., Edmonds, J., O’Neill, B. C., Fujimori, S., Bauer, N., Calvin, K., Dellink, R., Fricko, O., Lutz, W., Popp, A., Cuaresma, J. C., Kc, S., Leimbach, M., Jiang, L., Kram, T., Rao, S., Emmerling, J., Ebi, K., Hasegawa, T., Havlik, P., Humpenöder, F., Da Silva, L. A., Smith, S., Stehfest, E., Bosetti, V., Eom, J., Gernaat, D., Masui, T., Rogelj, J., Strefler, J., Drouet, L., Krey, V., Luderer, G., Harmsen, M., Takahashi, K., Baumstark, L., Doelman, J. C., Kainuma, M., Klimont, Z., Marangoni, G., Lotze-Campen, H., Obersteiner, M., Tabeau, A., and Tavoni, M.: The Shared Socioeconomic Pathways and their energy, land use, and greenhouse gas emissions implications: An overview, Global Environmental Change, 42, 153–168, https://doi.org/10.1016/j.gloenvcha.2016.05.009, 2017."],"supplementalName":["Skamarock, W. C., J. B. Klemp, J. Dudhia, D. O. Gill, Z. Liu, J. Berner, W. Wang, J. G. Powers, M. G. Duda, D. M. Barker, and X.-Y. Huang, 2019: A Description of the Advanced Research WRF Version 4. NCAR Tech. Note NCAR/TN-556+STR, 145 pp.","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. https://doi.org/10.5065/D6M043C6. Accessed  01012022  ","The EU EMEP emissions center ","The UK National Atmospheric Emissions Inventory ","The Republic of Ireland national emissions inventory","Baker, S.J., 2001. Trace and Major Elements in the Atmosphere at Rural Locations in the UK: Summary of Data for 1999 (No. AEAT/R/ENV/0264). National Environmental Technology Centre.","SSP scenarios"],"title":"Heavy metal, nitrogen, and sulphur atmospheric deposition from the European Monitoring and Evaluation Program Model for the UK (EMEP4UK) for 2040, 2070 and 2100 under the Shared Socioeconomic Pathway scenarios 1-5","topic":["0/Environmental risk/"],"version":1.0,"view":["public","crimar"],"shortenedDescription":"This dataset is a model output from the European Monitoring and Evaluation Programme (EMEP) model applied to the UK (EMEP4UK) driven by Weather and Research Forecast model meteorology (WRF). It provides annual total atmospheric deposition of cadmium, copper, nickel,..."},{"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":"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":"2020-05-07T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","Institute of Environmental Assessment and Water Research"],"authorGivenName":["C.L.","C.","M. ","N.A.","L.A."],"authorFamilyName":["Barnett","Wells","Izquierdo","Beresford","Walker"],"authorFullName":["Barnett, C.L.","Wells, C.","Izquierdo, M.","Beresford, N.A.","Walker, L.A."],"authorOrcid":["https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise stable element concentrations for a range of elements, radionuclide activity concentrations for the isotopes K-40 and Cs-137 and radionuclide and stable element concentration ratios.\n\nSamples of soil, water, vegetation (grasses, trees, herbaceous plants and shrubs), fungi, earthworms, bees, wood mice, bank voles, common frogs, frogspawn and European toads were collected between March 2015 and October 2016 from two forests in north-east England. The study was conducted to target representative terrestrial species of the ICRPs Reference Animals and Plants.\n\nFunding for this work was via the TREE project funded by NERC, the Environment Agency and Radioactive Waste Management Ltd. under the RATE programme.","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council","Environment Agency","Radioactive Waste Management Ltd"],"grant":["NE/L000318/1"],"identifier":"8f85c188-a915-46ac-966a-95fcb1491be6","incomingCitationCount":1,"givenName":["Cath","C.L.","C.","M. ","N.A.","L.A."],"familyName":["Barnett","Wells","Izquierdo","Beresford","Walker"],"fullName":["Barnett, C.","Barnett, C.L.","Wells, C.","Izquierdo, M.","Beresford, N.A.","Walker, L.A."],"keyword":["TREE","Radioecology","Environmental risk","Environmental survey","radionuclide","caesium"],"keywordsProject":["TREE"],"keywordsTheme":["Radioecology","Environmental risk","Environmental survey"],"keywordsOther":["radionuclide","caesium"],"licence":"Open government licence","lineage":"Data consist of stable element and radionuclide concentrations, and estimated concentration ratios for biota, soil and water collected from two forests in north-east England (March 2015 to October 2016). Samples were analysed by ICP-MS and, where sample size was sufficient, gamma analysis.\n\nSoil: pH and loss on ignition were determined.\n\nWater: Samples were filtered through Whatman 541 filter paper. \n\nWood mice: Trapping was conducted using \"Longworth\" traps. Randomly selected individuals were dissected and a beetle (Dermestes maculatus) colony was used to clean the bones of soft tissue. \n\nBank voles: Trapping was conducted as for Wood mice. Vole samples were ashed. \n\nBee species: Pan traps were placed on the ground. Bees collected were bulked by species and homogenised in an agate mortar. \n\nEarthworms: Worms were collected by digging to circa 30 cm, they were rinsed in de-ionised water and placed on damp tissue paper to allow gut evacuation. Samples were bulked by species and homogenised by agate mortar. \n\nCommon frogs and spawn: Frogs were collected by hand during darkness. Randomly selected individuals were dissected and a beetle colony used to clean bones. Spawn samples were washed in de-ionised water and freeze-dried prior to homogenisation in an agate mortar. \n\nEuropean toads: Toads were collected as for frogs. Randomly selected individuals had their gastrointestinal tract removed, the remaining carcass was washed in de-ionised water and then ashed. \n\nRoe deer: Deer were obtained via the Forestry Commission. Animals were dissected and all bone/carcass samples were cleaned by placing in a beetle colony. Tissue samples were freeze dried and homogenised using an agate mill or mortar. \n\nPine Trees: Samples were collected of small branches, needles and heartwood core (sampled using an increment borer). Samples were air dried (~20oC) and the needles and branches subsequently finely ground using an agate mill or mortar (dependent upon size); the core samples were reduced manually to ~5mm in diameter. \n\nWild grasses: Samples of both leaf and flowering stems were collected. They were air dried and finely ground (using an agate mill or mortar dependent upon sample size). \nHerbaceous plants and shrubs: Opportunistic samples were collected from a variety of species abundant at the main sampling sites and from areas where the roe deer were obtained.  Samples were air dried and finely ground (using an agate mill or mortar). \n\nFungi: Opportunistic samples of fungal fruiting bodies were collected mainly from areas where the roe deer were obtained. Samples were identified by species, oven dried (~60oC) and subsequently finely ground (~2mm) using either an agate mortar or \"coffee\" grinder depending upon sample size. Species were bulked by sampling location and, were possible, by feeding strategy. \n\nICP-MS analysis was conducted using a Thermo-Fisher Scientific iCAP-Q. Samples subjected to ashing pre-treatment had undissolved black particles in the solutions which suggests digestion was incomplete. Similarly, TMAH digestion is not able to fully digest plant material therefore variable degrees of dissolution were observed; pine tree core samples showed poor dissolution rates and therefore the iodine concentrations reported may be underestimated. Digestion of replicates, reference materials and blanks were undertaken to check accuracy and precision. Detection limits were calculated as three times the standard deviation of the reagent blanks. \n\nGamma analysis was conducted using hyper-pure germanium detectors calibrated for efficiency using a certified reference solution (National Physics Laboratory R08-04). Spectra were analysed using Canberra Apex software and activity concentrations decay corrected to the day of sampling. Replicate analyses were conducted on random samples and process blanks for quality assurance purposes. ","locations":["POLYGON((-2.892 53.197, -2.892 55.44, 1.197 55.44, 1.197 53.197, -2.892 53.197))"],"orcid":["https://orcid.org/0000-0002-8722-0238"],"organisation":["UK Centre for Ecology & Hydrology","Institute of Environmental Assessment and Water Research","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/8f85c188-a915-46ac-966a-95fcb1491be6","10.5285/8f85c188-a915-46ac-966a-95fcb1491be6"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Transfer parameters for ICRP reference animals and plants collected from a forest ecosystem. Barnett, C.L.; Beresford, N.A.; Walker, L.A.; Baxter, M.; Wells, C.; Copplestone, D. (2014). Radiation and Environment Biophysics, 53, 125-149. "],"title":"Element and radionuclide concentrations in wildlife (including representative species of the ICRP's Reference Animals and Plants) and associated soils from forests in north-east England, 2015-2016","topic":["0/Radioecology/","0/Environmental risk/","0/Environmental survey/"],"version":1.0,"view":["public","jgar"],"shortenedDescription":"Data comprise stable element concentrations for a range of elements, radionuclide activity concentrations for the isotopes K-40 and Cs-137 and radionuclide and stable element concentration ratios.\n\nSamples of soil, water, vegetation (grasses, trees, herbaceous plants..."},{"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":"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":"2017-06-01T00:00:00.000+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":"2022-10-19T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","University of Liverpool","National Grid"],"authorGivenName":["C.J.","S.","J.R.","A.J.","D."],"authorFamilyName":["Feeney","Godfrey","Cooper","Plater","Dodds"],"authorFullName":["Feeney, C.J.","Godfrey, S.","Cooper, J.R.","Plater, A.J.","Dodds, D."],"authorOrcid":["https://orcid.org/0000-0003-2175-1842","https://orcid.org/0000-0001-7480-5758","https://orcid.org/0000-0003-4957-2774","https://orcid.org/0000-0001-7043-227X"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset contains information about predicted future erosion hazards to electricity transmission towers at a site in the Mersey River valley. River channel change and floodplain erosion rates were simulated under 6 hypothetical flow scenarios, covering the years 2018 to 2050. These scenarios include: “baseline” where we assumed the 32 years of flow from 2018 to 2050 matched the preceding 32-year period; and “plus 10, 20, 30, 40 & 50%” where we assumed daily averaged flow magnitudes increased by 10, 20, 30, 40 or 50%, depending on the scenario. Simulations were run using the CAESAR-Lisflood landscape evolution model. Input files that were used to drive the simulations include a 15-metre resolution DEM covering a ~4.5 km long reach of river valley, and daily-averaged flow inputs (m3 s-1). Landscape changes over time were extracted at the locations of each electricity transmission tower, with the severity of erosion used to judge the relative risks of each tower from future climate change.\n\nThe work was supported by the Natural Environment Research Council (Grant NE/S01697X/1) as part of the project: ‘Erosion Hazards in River Catchments: Making Critical Infrastructure More Climate Resilient’.","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":[" NE/S01697X/1 NE/R016429/1 "],"identifier":"78bc21a9-39e0-4efc-992c-5587439fe6be","incomingCitationCount":1,"givenName":["C.J.","S.","J.R.","A.J.","D.","Christopher"],"familyName":["Feeney","Godfrey","Cooper","Plater","Dodds"],"fullName":["Feeney, C.J.","Godfrey, S.","Cooper, J.R.","Plater, A.J.","Dodds, D.","Feeney, C."],"keyword":["Environmental risk","CAESAR-Lisflood","erosion","hazard","climate change","river","floodplain","infrastructure","electricity"],"keywordsTheme":["Environmental risk"],"keywordsOther":["CAESAR-Lisflood","erosion","hazard","climate change","river","floodplain","infrastructure","electricity"],"licence":"Open government licence","lineage":"Historic river channel changes were quantified for the years 1976-2018 by digitising channel boundaries from old Ordnance Survey maps and aerial imagery. Floodplain erosion and deposition rates (m2 yr-1) were estimated by overlaying the digitised channel features to create a time-series of landscape evolution. The years 1976-2018 represent a combined overlapping record where we have available OS maps and aerial imagery, as well as continuous recorded daily-averaged flow data for the Ashton Weir (station no. 69007) from the National River Flow Archive. The CAESAR-Lisflood model was calibrated using this historic flow series and a modified version of a LiDAR DEM from the Environment Agency. Simulation results during calibration were compared against digitised historic channel changes, with the 2 best results chosen for simulation of future flow scenarios. A total of 12 simulations was run to determine which of 40 electricity transmission towers would be at greatest risk from river channel erosion. These 12 simulations consist of the 2 calibrated models × 6 hypothetical future flow scenarios.\n\nThe CAESAR-Lisflood model simulates processes using deterministic algorithms. This means that without changing inputs, the model can be run repeatedly and return an identical result. Input files necessary to run the CAESAR-Lisflood model are included in this dataset so that this repeatability can be independently verified. R code is also provided to allow the user to reproduce most of the analyses reported in the associated paper.\n\nRiver channel change is a “chaotic” process, which means prediction of its future dynamics is riddled with uncertainties. Added to this, our chosen flow scenarios are hypothetical, and constructed by multiplying the most recent historical 32-year flow record by 1-1.5 depending on the scenario. Thus, care should be taken when interpreting our results. We suggest that we can accurately pinpoint which towers are most at risk from future erosion, but not the exact timings of these risks.","locations":["POLYGON((-2.4 53.43, -2.4 53.46, -2.34 53.46, -2.34 53.43, -2.4 53.43))"],"orcid":["https://orcid.org/0000-0003-2175-1842","https://orcid.org/0000-0001-7480-5758","https://orcid.org/0000-0003-4957-2774","https://orcid.org/0000-0001-7043-227X"],"organisation":["UK Centre for Ecology & Hydrology","University of Liverpool","National Grid","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/78bc21a9-39e0-4efc-992c-5587439fe6be","10.5285/78bc21a9-39e0-4efc-992c-5587439fe6be"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["If the user wishes to recreate the model outputs, they will need to use the CAESAR-Lisflood model, which is available from:\n\nWe would also recommend using version 4 of R to run any of the R scripts"],"title":" Predicted erosion hazards to electricity transmission towers in the Mersey River valley under hypothetical future flow scenarios, 2018-2050","topic":["0/Environmental risk/"],"version":1.0,"view":["public","clwe"],"shortenedDescription":"This dataset contains information about predicted future erosion hazards to electricity transmission towers at a site in the Mersey River valley. River channel change and floodplain erosion rates were simulated under 6 hypothetical flow scenarios, covering the years..."},{"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":"2025-02-26T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology"],"authorGivenName":["E.","S.J.","S."],"authorFamilyName":["Carnell","Tomlinson","Reis"],"authorFullName":["Carnell, E.","Tomlinson, S.J.","Reis, S."],"authorOrcid":["https://orcid.org/0000-0003-0870-1955","https://orcid.org/0000-0002-3237-7596","https://orcid.org/0000-0003-2428-8320"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset contains gridded human population with a spatial resolution of 1 km x 1 km for the UK based on Census 2021 (Census 2022 for Scotland) and Land Cover Map 2021 input data. Data on population distribution for the United Kingdom is available from statistical offices in England, Wales, Northern Ireland and Scotland and provided to the public e.g. via the Office for National Statistics (ONS). Population data is typically provided in tabular form or, based on a range of different geographical units, in file types for geographical information systems (GIS), for instance as ESRI Shapefiles. The geographical units reflect administrative boundaries at different levels of detail, from Devolved Administration to Output Areas (OA), wards or intermediate geographies. While the presentation of data on the level of these geographical units is useful for statistical purposes, accounting for spatial variability for instance of environmental determinants of public health requires a more spatially homogeneous population distribution. For this purpose, the dataset presented here combines 2021/2022 UK Census population data on Output Area level with Land Cover Map 2021 land-use classes 'urban' and 'suburban' to create a consistent and comprehensive gridded population data product at 1 km x 1 km spatial resolution. The mapping product is based on British National Grid (OSGB36 datum).","documentType":"GEMINI_DOCUMENT","funder":["Department for Environment Food and Rural Affairs"],"identifier":"7beefde9-c520-4ddf-897a-0167e8918595","incomingCitationCount":0,"givenName":["E.","S.J.","S."],"familyName":["Carnell","Tomlinson","Reis"],"fullName":["Carnell, E.","Tomlinson, S.J.","Reis, S."],"keyword":["UK","Mapping","Environmental risk","population","land cover","Gridded"],"keywordsPlace":["UK"],"keywordsTheme":["Mapping","Environmental risk"],"keywordsOther":["population","UK","land cover","Gridded"],"licence":"Open government licence","lineage":"Census data from the Office of National Statistics, National Records for Scotland and Northern Ireland Statistics and Research Agency have been downloaded as CSV/Excel files.\nLand Cover Map 2021 raster data has been obtained from UKCEH.\nOutput Area (/Data Zone) geography data (Extent of the Realm), were obtained for England & Wales, Northern Ireland, and Scotland.\nThe processing steps are detailed in the Supporting Documentation.\nTo ensure consistency of the final product, total population numbers were compared, at each processing step, with the official 2021/2022 Census totals. As a result, the final output file is consistent with the Census total population for the UK in 2021.\n","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/0000-0003-0870-1955","https://orcid.org/0000-0002-3237-7596","https://orcid.org/0000-0003-2428-8320"],"organisation":["UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/7beefde9-c520-4ddf-897a-0167e8918595","10.5285/7beefde9-c520-4ddf-897a-0167e8918595"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Census data from the Office of National Statistics, National Records for Scotland and Northern Ireland Statistics and Research Agency"],"supplementalName":["Land Cover Map 2021 (25m rasterised land parcels, GB)  ","Land Cover Map 2021 (25m rasterised land parcels, NI)  ","England and Wales Output Areas","Scotland Output Areas","Northern Ireland Data Zones"],"title":"UK gridded population at 1 km resolution for 2021 based on Census 2021/2022 and Land Cover Map 2021","topic":["0/Mapping/","0/Environmental risk/"],"version":1.0,"view":["public","tinzha"],"shortenedDescription":"This dataset contains gridded human population with a spatial resolution of 1 km x 1 km for the UK based on Census 2021 (Census 2022 for Scotland) and Land Cover Map 2021 input data. Data on population distribution for the United Kingdom is available from statistical..."},{"publicationDate":"2022-06-27T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","Sayers and Partners Consultancy"],"authorGivenName":["A.","V.A.","E.J.","P.","S."],"authorFamilyName":["Griffin","Kay","Bell","Stewart","Sayer","Carr"],"authorFullName":["Griffin, A.","Kay, A.","Bell, V.A.","Stewart, E.J.","Sayer, P.","Carr, S."],"authorOrcid":["https://orcid.org/0000-0001-8645-4561","https://orcid.org/0000-0002-5526-1756","https://orcid.org/0000-0002-0792-5650","https://orcid.org/0000-0003-4246-6645","https://orcid.org/0000-0003-2160-1959"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset is a set of 24 gridded netcdf files, each including data describing a total of 14,400 widespread flooding events across mainland GB, with event selection based on a peaks-over-threshold approach. The data describes peak river flow in m3/s and the associated annual probability of exceedance for each 1km grid-square on the GB river network. The data is extracted from daily time series data from the Grid-to-Grid model, using UKCP18 12km regional projections from 12 members of a perturbed parameter ensemble, over the periods Dec 1980 – Nov 2010 and Dec 2050 – Nov 2080 (based on 360-day years). Multi-day events were summarised by taking cell-wise flow maxima. \n\nThis data was generated for use in analysis of risk through catastrophe modelling using the Future Flows Explorer. It was generated and interpreted by UKCEH, working with Sayers & Partners Consultancy, as part of the AquaCAT project, part of the UK Climate Resilience Programme.","documentType":"GEMINI_DOCUMENT","identifier":"26ce15dd-f994-40e0-8a09-5f257cc1f2ab","incomingCitationCount":2,"givenName":["Adam","A.","V.A.","E.J.","P.","S."],"familyName":["Griffin","Kay","Bell","Stewart","Sayer","Carr"],"fullName":["Griffin, A.","Kay, A.","Bell, V.A.","Stewart, E.J.","Sayer, P.","Carr, S."],"keyword":["Hydrology","Environmental risk","Flood frequency"],"keywordsTheme":["Hydrology","Environmental risk"],"keywordsOther":["Flood frequency"],"licence":"Open government licence","lineage":"Hydrological flow records were generated using Grid-to-Grid and UKCP18 12km regional projections. Widespread events were selected for which daily flow exceeded a 99.5% percentile simultaneously over at least 20km^2. Multi-day events (consecutive days for which the above conditions were met) are summarised by pointwise maxima of flow.\n\nProbabilities of exceedance are computed pointwise using a mixed distribution, with an empirical distribution used for non-extreme values (below the 99.5% percentile) and a Generalised Pareto distribution used above, both fitted to the full time series of daily flow.","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/0000-0001-8645-4561","https://orcid.org/0000-0002-5526-1756","https://orcid.org/0000-0002-0792-5650","https://orcid.org/0000-0003-4246-6645","https://orcid.org/0000-0003-2160-1959"],"organisation":["UK Centre for Ecology & Hydrology","Sayers and Partners Consultancy","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/26ce15dd-f994-40e0-8a09-5f257cc1f2ab","10.5285/26ce15dd-f994-40e0-8a09-5f257cc1f2ab"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology","Sayers and Partners Consultancy"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Peak flow and probability of exceedance data for Grid-to-Grid modelled widespread flooding events across mainland GB from 1980-2010 and 2050-2080","topic":["0/Hydrology/","0/Environmental risk/"],"version":1.0,"view":["public","danor"],"shortenedDescription":"This dataset is a set of 24 gridded netcdf files, each including data describing a total of 14,400 widespread flooding events across mainland GB, with event selection based on a peaks-over-threshold approach. The data describes peak river flow in m3/s and the associated..."},{"publicationDate":"2025-05-27T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology"],"authorGivenName":["M.J.","L.K.","D.J.E.","M.","A.","M.A.","E.","M.D."],"authorFamilyName":["Bowes","Armstrong","Nicholls","Williams","O’Brien","Duenas-Lopez","Duke","Juergens"],"authorFullName":["Bowes, M.J.","Armstrong, L.K.","Nicholls, D.J.E.","Williams, M.","O’Brien, A.","Duenas-Lopez, M.A.","Duke, E.","Juergens, M.D."],"authorOrcid":["https://orcid.org/0000-0002-0673-1934","https://orcid.org/0000-0002-6526-589X"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"This dataset comprises weekly water quality monitoring data of seven sites along the River Thames, UK, and sixteen of its major tributaries from Feburary 2009 to December 2023. Monitored determinands include major nutrient fractions, anions, cations, metals, pH, alkalinity, and chlorophyll. This catchment-wide biogeochemical monitoring platform captures changes in the water quality of the Thames basin during a period of rapid change, related to increasing pressures (due to a rapidly growing human population, increasing water demand and climate change) and improvements in sewage treatment processes and agricultural practices. The dataset provides the research community with a valuable data and modelling resource for furthering our understanding of pollution sources and dynamics, and vital underpinning environmental data required to best manage this vital drinking water resource, which is key for the sustainability of the city of London and the wider UK economy. ","documentType":"GEMINI_DOCUMENT","identifier":"703af27b-ce8c-44e0-ac20-b46e391a64ef","incomingCitationCount":0,"givenName":["M.J.","L.K.","D.J.E.","M.","A.","M.A.","E.","M.D."],"familyName":["Bowes","Armstrong","Nicholls","Williams","O’Brien","Duenas-Lopez","Duke","Juergens"],"fullName":["Bowes, M.J.","Armstrong, L.K.","Nicholls, D.J.E.","Williams, M.","O’Brien, A.","Duenas-Lopez, M.A.","Duke, E.","Juergens, M.D."],"keyword":["Thames Catchment","Southeast England","Environmental risk","Water quality","water quality","chemistry","Nutrients","river pollution"],"keywordsPlace":["Thames Catchment","Southeast England"],"keywordsTheme":["Environmental risk","Water quality"],"keywordsOther":["water quality","chemistry","Nutrients","river pollution"],"licence":"Open government licence","lineage":"All water samples were collected by fieldworkers from the UK Centre for Ecology & Hydrology (UKCEH), Wallingford.  All chemical analysis was carried out by the Nutrient Chemistry Laboratories at CEH Wallingford.  ","locations":["POLYGON((-1.846 51.276, -1.846 52.176, 1.208 52.176, 1.208 51.276, -1.846 51.276))"],"orcid":["https://orcid.org/0000-0002-0673-1934","https://orcid.org/0000-0002-6526-589X"],"organisation":["UK Centre for Ecology & Hydrology","NERC EDS Environmental Information Data Centre"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/703af27b-ce8c-44e0-ac20-b46e391a64ef","10.5285/703af27b-ce8c-44e0-ac20-b46e391a64ef"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["Bowes, M. J., Armstrong, L. K., Harman, S. A., Wickham, H. D., Nicholls, D. J. E., Scarlett, P. M., Roberts, C., Jarvie, H. P., Old, G. H., Gozzard, E., Bachiller-Jareno, N., & Read, D. S. (2018). Weekly water quality monitoring data for the River Thames (UK) and its major tributaries (2009–2013): the Thames Initiative research platform. Earth System Science Data, 10(3), 1637–1653. https://doi.org/10.5194/essd-10-1637-2018\n"],"title":"Weekly water quality data from the River Thames and its major tributaries, 2009-2023","topic":["0/Environmental risk/","0/Water quality/"],"version":1.0,"view":["public","katwri"],"shortenedDescription":"This dataset comprises weekly water quality monitoring data of seven sites along the River Thames, UK, and sixteen of its major tributaries from Feburary 2009 to December 2023. Monitored determinands include major nutrient fractions, anions, cations, metals, pH, alkalinity,..."},{"publicationDate":"2022-09-22T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology","Chornobyl Center for Nuclear Safety","University of Salford"],"authorGivenName":["C.L.","S.","C.","E.","M.D.","N.A."],"authorFamilyName":["Barnett","Gashchak","Wells","Guliaichenko","Wood","Beresford"],"authorFullName":["Barnett, C.L.","Gashchak, S.","Wells, C.","Guliaichenko, E.","Wood, M.D.","Beresford, N.A."],"authorOrcid":["https://orcid.org/0000-0001-9723-7247","https://orcid.org/0000-0002-7582-6742","https://orcid.org/0000-0002-0635-2387","https://orcid.org/0000-0002-8722-0238"],"authorRor":["https://ror.org/00pggkr55"],"catalogue":"eidc","description":"Data comprise a catalogue of motion activated digital trap camera images obtained from cameras located in the Red Forest, Chornobyl (Ukraine) over a period of a year (September 2016 - September 2017); images are included. In total 45,859 images were captured; of these 19,393 contained identifiable species or organism types, 565 recorded people, 349 were of species that could not be determined and 25,552 images recorded nothing. In addition there were 687 images of members of the research team setting up and servicing the cameras. All images, with the exception of those that recorded people or camera setup/service, are included as part of the dataset.\n\nSite characteristics and descriptions for each camera location are provided (e.g. site location, estimates of ambient dose rate, activity concentration of Cs-137 and Sr-90 in soil, Cs-137 and Sr-90 deposition, extent of fire damage, vegetation and forest cover and density and water proximity). The same person recorded all descriptive parameters. Information related to each cameras deployment is also provided; this includes camera deployment periods, number of days deployed and a summary of the images (e.g. number of images with mammals, birds or insects in, number of images with nothing in, number of images with people in) and the total number of triggering events recorded. Also provided are indicative weighted absorbed dose rates estimated using the ERICA Tool v2.0 https://erica-tool.com/ for a ‘large mammal’ and ‘red fox’.\n\nSpecies definitively captured on the motion activated digital trap cameras were:Brown hare, Eurasian elk, Eurasian lynx, European badger, Domesticated dog (feral), Grey wolf, Przewalski's horse, Raccoon dog, Red deer, Red fox, Red squirrel, Roe deer, Wild boar, Black grouse, Common blackbird, Common buzzard, Common wood pigeon, Eurasian bittern, Eurasian hoopoe, Eurasian Jay, Eurasian sparrowhawk, Eurasian woodcock, European nightjar, European robin, Fieldfare, Great egret, Great grey shrike, Great spotted woodpecker, Great tit, Hazel grouse, Mistle thrush, Red backed shrike and Song thrush. Others identified to genus level include:Marten sp., Finch sp., Shrike sp., Thrush sp. There were also some mammal and bird species which were unidentifiable.\n\nSite descriptions, camera information, a summary of the contents of the image catalogue, summaries of mammals and birds by setup, site and camera and all the trap camera images have been provided as part of this dataset.","documentType":"GEMINI_DOCUMENT","funder":["Natural Environment Research Council"],"grant":["NE/P015212/1"],"identifier":"bf82cec2-5f8a-407c-bf74-f8689ca35e83","incomingCitationCount":0,"givenName":["Cath","C.L.","S.","C.","E.","M.D.","N.A."],"familyName":["Barnett","Gashchak","Wells","Guliaichenko","Wood","Beresford"],"fullName":["Barnett, C.","Barnett, C.L.","Gashchak, S.","Wells, C.","Guliaichenko, E.","Wood, M.D.","Beresford, N.A."],"keyword":["Chornobyl","Chornobyl Exclusion Zone (CEZ)","Chernobyl","Ukraine","Radioecology","Motion activated trap camera","Image","Wildfire","Activity concentration","Cs-137","Sr-90","Dose rate","Lepus europaeus","Alces alces","Lynx lynx","Meles meles","Canis lupus","Nyctereutes procyonoides","Cervus elaphus","Vulpes vulpes","Sciurus vulgaris","Capreolus capreolus","Sus scrofa","Lyrurus tetrix","Turdus merula","Buteo buteo","Coturnix coturnix","Gallinago gallinago","Columba palumbus","Crex crex","Botaurus stellaris","Upupa epops","Garrulus glandarius","Accipiter nisus","Scolopax rusticola","Caprimulgus europaeus","Erithacus rubecula","Turdus pilaris","Egretta alba","Lanius excubitor","Dendrocopos major","Parus major","Tetrastes bonasia","Poecile palustris","Turdus viscivorus","Lanius collurio","Turdus philomelos","Equus ferus przewalskii","Canis lupus familiaris","Martes (genus)","Muridae (family)","Fringillidae (family)","Lepidoptera (order)","Araneae (order)","Odonata (order)","Insecta (class)","radionuclide","mammal","wildlife","bird","deposition"],"keywordsPlace":["Chornobyl","Chornobyl Exclusion Zone (CEZ)","Chernobyl","Ukraine"],"keywordsTheme":["Radioecology"],"keywordsOther":["Motion activated trap camera","Image","Wildfire","Activity concentration","Cs-137","Sr-90","Dose rate","Lepus europaeus","Alces alces","Lynx lynx","Meles meles","Canis lupus","Nyctereutes procyonoides","Cervus elaphus","Vulpes vulpes","Sciurus vulgaris","Capreolus capreolus","Sus scrofa","Lyrurus tetrix","Turdus merula","Buteo buteo","Coturnix coturnix","Gallinago gallinago","Columba palumbus","Crex crex","Botaurus stellaris","Upupa epops","Garrulus glandarius","Accipiter nisus","Scolopax rusticola","Caprimulgus europaeus","Erithacus rubecula","Turdus pilaris","Egretta alba","Lanius excubitor","Dendrocopos major","Parus major","Tetrastes bonasia","Poecile palustris","Turdus viscivorus","Lanius collurio","Turdus philomelos","Equus ferus przewalskii","Canis lupus familiaris","Martes (genus)","Muridae (family)","Fringillidae (family)","Lepidoptera (order)","Araneae (order)","Odonata (order)","Insecta (class)","radionuclide","mammal","wildlife","bird","deposition"],"licence":"Open government licence","lineage":"The NERC funded RED FIRE project conducted studies in the Red Forest (located within the Chornobyl Exclusion Zone, Ukraine) over the course of a year following a severe fire in 2016 when approximately 80% of the forest was burnt. The study involved placing 21 motion activated digital trap cameras across the Red Forest from September 2016 to September 2017.\n\nImages and the image and camera metadata were downloaded by Chornobyl Center from each camera memory card on three occasions over the study period. The images (and some videos) and image metadata was then supplied to UKCEH by Chornobyl Center as .jpeg. .avi and MSExcel files respectively. Image catalogues were then populated by UKCEH using this information. For quality control purposes this data was then compared to a second set of data entered into a second catalogue by staff at the Chornobyl Centre for Nuclear Safety; any disparities were investigated and amended where necessary.Site descriptions and camera information was supplied to UKCEH by Chornobyl Center as MSExcel files.\n\nAll data were supplied to EIDC as .csv; .jpeg or .avi files.","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/0000-0001-9723-7247","https://orcid.org/0000-0002-7582-6742","https://orcid.org/0000-0002-0635-2387","https://orcid.org/0000-0002-8722-0238"],"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/bf82cec2-5f8a-407c-bf74-f8689ca35e83","10.5285/bf82cec2-5f8a-407c-bf74-f8689ca35e83"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Motion-activated camera trap images of wildlife from the Red Forest, Chornobyl, Ukraine, 2016-2017","topic":["0/Radioecology/"],"version":1.0,"view":["public","phtr"],"shortenedDescription":"Data comprise a catalogue of motion activated digital trap camera images obtained from cameras located in the Red Forest, Chornobyl (Ukraine) over a period of a year (September 2016 - September 2017); images are included. In total 45,859 images were captured; of these..."},{"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":"2018-02-20T00:00:00.000+00:00","authorAffiliation":["Centre for Ecology & Hydrology","Chernobyl Centre for Nuclear Safety","Unaffiliated"],"authorGivenName":["N.A.","S.","C.L.","A.","E.","C.","J.S."],"authorFamilyName":["Beresford","Gaschak","Barnett","Maksimenko","Guliaichenko","Wells","Chaplow"],"authorFullName":["Beresford, N.A.","Gaschak, S.","Barnett, C.L.","Maksimenko, A.","Guliaichenko, E.","Wells, C.","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 activity concentrations, stable element concentrations and both radionuclide and stable element concentration ratios for vegetation and wildlife samples collected in the Chernobyl Exclusion Zone (CEZ) in 2014.  Estimated absorbed dose rates for wildlife in the CEZ are also presented.\n\nSamples of soil, wild grass, earthworms, bees and other insects, small mammals, pine trees and frogs were collected in May and June 2014; frogspawn was collected in April 2015. Data were used to assess the uptake of radionuclides by wildlife living in the Chernobyl Exclusion Zone (CEZ) and also absorbed dose rates.\n\nThe 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).\n\nFunding for this work was via the TREE project funded by the NERC, Environment Agency and Radioactive Waste Management Ltd. under the RATE programme.","documentType":"GEMINI_DOCUMENT","identifier":"ae02f4e8-9486-4b47-93ef-e49dd9ddecd4","incomingCitationCount":3,"givenName":["N.A.","S.","C.L.","A.","E.","C.","J.S."],"familyName":["Beresford","Gaschak","Barnett","Maksimenko","Guliaichenko","Wells","Chaplow"],"fullName":["Beresford, N.A.","Gaschak, S.","Barnett, C.L.","Maksimenko, A.","Guliaichenko, E.","Wells, C.","Chaplow, J.S."],"keyword":["Chernobyl exclusion zone (CEZ)","Ukraine","Chornobyl","TRansfer - Exposure – Effects (TREE)","Radioactivity And The Environment (RATE)","Environmental survey","Soil","Pollution","Radioecology","ICRP","Reference animals and plant","americium","stable element","plutonium","strontium","caesium"],"keywordsPlace":["Chernobyl exclusion zone (CEZ)","Ukraine","Chornobyl"],"keywordsProject":["TRansfer - Exposure – Effects (TREE)","Radioactivity And The Environment (RATE)"],"keywordsTheme":["Environmental survey","Soil","Pollution","Radioecology"],"keywordsOther":["ICRP","Reference animals and plant","americium","stable element","plutonium","strontium","caesium"],"licence":"Open government licence","lineage":"The sampling site (0.4 km2) was located towards the western edge of the Red Forest, approximately 5 km west-southwest of the Chernobyl Unit Number 4).  The site was not within the area where pine trees were killed by high exposure levels in 1986. Most of the site was formerly used as kitchen gardens ('dacha') by the residents of Pripyat. With the exception of Pinus sylvestris, all samples were collected from an area of the former kitchen gardens with a number of fruit trees which was about 0.06 km2 in area; this is subsequently referred to as the 'inner sampling area'. The predominant soil type of the sampling site was soddy-podzolic sandy loam and the surrounding habitats were largely deciduous woodland (some of which was previously agricultural land) and marsh.\n All samples were collected over a period of about 1 month in May/June 2014. Although sampling was focussed on species falling into the ICRP RAP definitions (after Barnett et al. 2014), additional species caught were analysed for 90Sr and 137Cs activity concentrations. \n\nSample types include wild grass, pine tree, earthworm, bee and other insects, small mammals (mice, vole, doormouse, shrew), amphibians and soil.","locations":["POLYGON((22.129 44.39, 22.129 52.376, 40.218 52.376, 40.218 44.39, 22.129 44.39))"],"orcid":["https://orcid.org/0000-0002-8722-0238","https://orcid.org/0000-0002-8058-8697"],"organisation":["Centre for Ecology & Hydrology","Chernobyl Centre for Nuclear Safety","Unaffiliated","NERC EDS Environmental Information Data Centre","NERC Environmental Information Data Centre","UK Centre for Ecology & Hydrology"],"recordType":"Dataset","resourceIdentifier":["https://catalogue.ceh.ac.uk/id/ae02f4e8-9486-4b47-93ef-e49dd9ddecd4","10.5285/ae02f4e8-9486-4b47-93ef-e49dd9ddecd4"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","supplementalDescription":["TRansfer - Exposure - Effects (TREE)","Radioactivity & the Environment (RATE) "],"supplementalName":["TREE project website","RATE programme weblink"],"title":"A 'Reference Site' in the Chernobyl Exclusion Zone: radionuclide and stable element data, and estimated dose rates","topic":["0/Environmental survey/","0/Soil/","0/Pollution/","0/Radioecology/"],"version":1.0,"view":["public","phtr","jgar"],"shortenedDescription":"Data comprise radionuclide activity concentrations, stable element concentrations and both radionuclide and stable element concentration ratios for vegetation and wildlife samples collected in the Chernobyl Exclusion Zone (CEZ) in 2014.  Estimated absorbed dose rates..."},{"publicationDate":"2021-02-01T00:00:00.000+00:00","authorAffiliation":["UK Centre for Ecology & Hydrology"],"authorGivenName":["J.S.","N.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":"The data comprise collated data on calcium and magnesium (milligrams per kilogram dry mass) in plants used as human and animal food (including fruit, vegetables, grasses, nuts and seeds) from global literature published between 1982 and 2019. Where reported strontium values are also included. Each data point is referenced.","documentType":"GEMINI_DOCUMENT","identifier":"6a0552d9-b9f8-4b5d-809d-47c9bf64ef94","incomingCitationCount":0,"givenName":["Jacky","J.S.","N.A.","C.L."],"familyName":["Chaplow","Beresford","Barnett"],"fullName":["Chaplow, J.","Chaplow, J.S.","Beresford, N.A.","Barnett, C.L."],"keyword":["CONFIDENCE","CONCERT","Environmental risk","Radioecology","magnesium","EURATOM","strontium","calcium"],"keywordsProject":["CONFIDENCE","CONCERT"],"keywordsTheme":["Environmental risk","Radioecology"],"keywordsOther":["magnesium","EURATOM","strontium","calcium"],"licence":"Open government licence","lineage":"Data were collated from published global literature and converted to milligrams per kilogram dry mass. If the water content had already been accounted for in the published data, the water_content_% column contains n/a. Where water content was not already accounted for in the data, the percentage water content is provided and was applied to the data. The data were filtered and the ranges checked; outlier values were checked for accuracy. Each data point is referenced and a full list of references is provided in the supporting document.","locations":["POLYGON((-180 -90, -180 90, 180 90, 180 -90, -180 -90))"],"orcid":["https://orcid.org/0000-0002-8058-8697","https://orcid.org/0000-0002-8722-0238"],"organisation":["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/6a0552d9-b9f8-4b5d-809d-47c9bf64ef94","10.5285/6a0552d9-b9f8-4b5d-809d-47c9bf64ef94"],"resourceStatus":"Available","resourceType":"Dataset","rightsHolder":["UK Centre for Ecology & Hydrology"],"ror":["https://ror.org/00pggkr55","https://ror.org/04xw4m193"],"state":"published","title":"Calcium and magnesium concentrations in plants used as human and animal foods derived from global literature","topic":["0/Environmental risk/","0/Radioecology/"],"version":1.0,"view":["public","clwe"],"shortenedDescription":"The data comprise collated data on calcium and magnesium (milligrams per kilogram dry mass) in plants used as human and animal food (including fruit, vegetables, grasses, nuts and seeds) from global literature published between 1982 and 2019. Where reported strontium..."},{"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 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