cometadata/datacite-titles-descriptions-related-identifiers huggingface dataset:
DOI: 10.6084/m9.figshare.25196837
title: breeding_nest_attempt_data_Feb2024.csvLong-term source-sink dynamics of snail kites during the invasion of a non-native prey

description:   
We use 26 years of data on reproduction, movement, and survival to estimate annual source-sink dynamics of the Everglade snail kite (<em>Rostrhamus sociabilis plumbeus</em>), an endangered wetland-dependent raptor in the United States. The biological invasion of a non-native apple snail <em>(Pomacea maculata</em>) provides a supplementary food source for snail kites and the increased prey availability has been linked to increases in reproduction, survival, body mass, and population growth. This analysis estimates fecundity, survival, and movement parameters as a function of years since invasion and how source-sink dynamics changed over time. 
The Everglade snail kite forms a spatially structured population limited to flooded freshwater wetlands and shallow lakes in peninsular Florida in the United States. Our study area includes all known breeding areas for the Everglade snail kite. Wetlands were grouped into 6 populations based on geographic location and hydrology: Paynes Prairie, Kissimmee River Valley, Okeechobee, Everglades, East, and St. John’s Marsh.
For each vital rate (demographic parameter) we included linear, quadratic, and logarithmic effects of years since <em>P. maculata </em>invasion. We tested for interactive effects between years since invasion and snail kite age because the invasion may have affected younger birds differently. Here, the top models for each demographic rate are presented, please see (Beatty <em>et al.</em> for the full model list).
To compare pre- and post-invasion estimates, a pre-invasion value was estimated for each vital rate using data before each population was invaded. Pre-invasion values were estimated separately to be able to estimate the distinct relationship between vital rates and time since invasion and because we expected patterns in vital rates to be different before the invasion. Pre-invasion estimates are a single value for each population and therefore do not vary with years since invasion.  The Paynes Prairie population did not have snail kites breeding in it until after it was invaded and therefore pre-invasion data is missing for this site and years since invasion represents the number of years since snail kites began breeding in the invaded site.
DOI: 10.6084/m9.figshare.25196837.v1
title: breeding_nest_attempt_data_Feb2024.csvLong-term source-sink dynamics of snail kites during the invasion of a non-native prey

description:   
We use 26 years of data on reproduction, movement, and survival to estimate annual source-sink dynamics of the Everglade snail kite (<em>Rostrhamus sociabilis plumbeus</em>), an endangered wetland-dependent raptor in the United States. The biological invasion of a non-native apple snail <em>(Pomacea maculata</em>) provides a supplementary food source for snail kites and the increased prey availability has been linked to increases in reproduction, survival, body mass, and population growth. This analysis estimates fecundity, survival, and movement parameters as a function of years since invasion and how source-sink dynamics changed over time. 
The Everglade snail kite forms a spatially structured population limited to flooded freshwater wetlands and shallow lakes in peninsular Florida in the United States. Our study area includes all known breeding areas for the Everglade snail kite. Wetlands were grouped into 6 populations based on geographic location and hydrology: Paynes Prairie, Kissimmee River Valley, Okeechobee, Everglades, East, and St. John’s Marsh.
For each vital rate (demographic parameter) we included linear, quadratic, and logarithmic effects of years since <em>P. maculata </em>invasion. We tested for interactive effects between years since invasion and snail kite age because the invasion may have affected younger birds differently. Here, the top models for each demographic rate are presented, please see (Beatty <em>et al.</em> for the full model list).
To compare pre- and post-invasion estimates, a pre-invasion value was estimated for each vital rate using data before each population was invaded. Pre-invasion values were estimated separately to be able to estimate the distinct relationship between vital rates and time since invasion and because we expected patterns in vital rates to be different before the invasion. Pre-invasion estimates are a single value for each population and therefore do not vary with years since invasion.  The Paynes Prairie population did not have snail kites breeding in it until after it was invaded and therefore pre-invasion data is missing for this site and years since invasion represents the number of years since snail kites began breeding in the invaded site.
DOI: 10.6084/m9.figshare.25193708
title: source_sink_vital_rates_Feb2024.csvLong-term source-sink dynamics of snail kites during the invasion of a non-native prey

description:   
We use 26 years of data on reproduction, movement, and survival to estimate annual source-sink dynamics of the Everglade snail kite (<em>Rostrhamus sociabilis plumbeus</em>), an endangered wetland-dependent raptor in the United States. The biological invasion of a non-native apple snail <em>(Pomacea maculata</em>) provides a supplementary food source for snail kites and the increased prey availability has been linked to increases in reproduction, survival, body mass, and population growth. This analysis estimates fecundity, survival, and movement parameters as a function of years since invasion and how source-sink dynamics changed over time. 
The Everglade snail kite forms a spatially structured population limited to flooded freshwater wetlands and shallow lakes in peninsular Florida in the United States. Our study area includes all known breeding areas for the Everglade snail kite. Wetlands were grouped into 6 populations based on geographic location and hydrology: Paynes Prairie, Kissimmee River Valley, Okeechobee, Everglades, East, and St. John’s Marsh.
For each vital rate (demographic parameter) we included linear, quadratic, and logarithmic effects of years since <em>P. maculata </em>invasion. We tested for interactive effects between years since invasion and snail kite age because the invasion may have affected younger birds differently. Here, the top models for each demographic rate are presented, please see (Beatty <em>et al.</em> for the full model list).
To compare pre- and post-invasion estimates, a pre-invasion value was estimated for each vital rate using data before each population was invaded. Pre-invasion values were estimated separately to be able to estimate the distinct relationship between vital rates and time since invasion and because we expected patterns in vital rates to be different before the invasion. Pre-invasion estimates are a single value for each population and therefore do not vary with years since invasion.  The Paynes Prairie population did not have snail kites breeding in it until after it was invaded and therefore pre-invasion data is missing for this site and years since invasion represents the number of years since snail kites began breeding in the invaded site.
DOI: 10.6084/m9.figshare.25193708.v1
title: source_sink_vital_rates_Feb2024.csvLong-term source-sink dynamics of snail kites during the invasion of a non-native prey

description:   
We use 26 years of data on reproduction, movement, and survival to estimate annual source-sink dynamics of the Everglade snail kite (<em>Rostrhamus sociabilis plumbeus</em>), an endangered wetland-dependent raptor in the United States. The biological invasion of a non-native apple snail <em>(Pomacea maculata</em>) provides a supplementary food source for snail kites and the increased prey availability has been linked to increases in reproduction, survival, body mass, and population growth. This analysis estimates fecundity, survival, and movement parameters as a function of years since invasion and how source-sink dynamics changed over time. 
The Everglade snail kite forms a spatially structured population limited to flooded freshwater wetlands and shallow lakes in peninsular Florida in the United States. Our study area includes all known breeding areas for the Everglade snail kite. Wetlands were grouped into 6 populations based on geographic location and hydrology: Paynes Prairie, Kissimmee River Valley, Okeechobee, Everglades, East, and St. John’s Marsh.
For each vital rate (demographic parameter) we included linear, quadratic, and logarithmic effects of years since <em>P. maculata </em>invasion. We tested for interactive effects between years since invasion and snail kite age because the invasion may have affected younger birds differently. Here, the top models for each demographic rate are presented, please see (Beatty <em>et al.</em> for the full model list).
To compare pre- and post-invasion estimates, a pre-invasion value was estimated for each vital rate using data before each population was invaded. Pre-invasion values were estimated separately to be able to estimate the distinct relationship between vital rates and time since invasion and because we expected patterns in vital rates to be different before the invasion. Pre-invasion estimates are a single value for each population and therefore do not vary with years since invasion.  The Paynes Prairie population did not have snail kites breeding in it until after it was invaded and therefore pre-invasion data is missing for this site and years since invasion represents the number of years since snail kites began breeding in the invaded site.
DOI: 10.6084/m9.figshare.25194065.v1
title: survival_movement_data_Feb2024.csvLong-term source-sink dynamics of snail kites during the invasion of a non-native prey

description:   
We use 26 years of data on reproduction, movement, and survival to estimate annual source-sink dynamics of the Everglade snail kite (<em>Rostrhamus sociabilis plumbeus</em>), an endangered wetland-dependent raptor in the United States. The biological invasion of a non-native apple snail <em>(Pomacea maculata</em>) provides a supplementary food source for snail kites and the increased prey availability has been linked to increases in reproduction, survival, body mass, and population growth. This analysis estimates fecundity, survival, and movement parameters as a function of years since invasion and how source-sink dynamics changed over time. 
The Everglade snail kite forms a spatially structured population limited to flooded freshwater wetlands and shallow lakes in peninsular Florida in the United States. Our study area includes all known breeding areas for the Everglade snail kite. Wetlands were grouped into 6 populations based on geographic location and hydrology: Paynes Prairie, Kissimmee River Valley, Okeechobee, Everglades, East, and St. John’s Marsh.
For each vital rate (demographic parameter) we included linear, quadratic, and logarithmic effects of years since <em>P. maculata </em>invasion. We tested for interactive effects between years since invasion and snail kite age because the invasion may have affected younger birds differently. Here, the top models for each demographic rate are presented, please see (Beatty <em>et al.</em> for the full model list).
To compare pre- and post-invasion estimates, a pre-invasion value was estimated for each vital rate using data before each population was invaded. Pre-invasion values were estimated separately to be able to estimate the distinct relationship between vital rates and time since invasion and because we expected patterns in vital rates to be different before the invasion. Pre-invasion estimates are a single value for each population and therefore do not vary with years since invasion.  The Paynes Prairie population did not have snail kites breeding in it until after it was invaded and therefore pre-invasion data is missing for this site and years since invasion represents the number of years since snail kites began breeding in the invaded site.
DOI: 10.25549/usctheses-ouc113090692
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 3]
DOI: 10.25549/usctheses-ouc113090706
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 2]
DOI: 10.25549/usctheses-ouc113090809
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 4]
DOI: 10.25549/usctheses-ouc113090945
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 6]
DOI: 10.25549/usctheses-ouc113090956
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 7]
DOI: 10.15468/8gtq3k
title: CENTERNACH ENERGIE - suivis environnementaux 2019 2020 et 2021-CENTERNACH ENERGIE - Suivis 2021 - Ecoutes chiroptères

description: Suivis environnementaux de parc éolien en exploitation: CENTERNACH ENERGIE. Réalisés dans le cadre du protocole national des suivis post installation publié par le Ministère en mars 2018.
DOI: 10.25549/usctheses-ouc110768643
title: A Study of the term social adaptation as used by selected sociologists
DOI: 10.5281/zenodo.10641000
title: Data for manuscript: "Investigating the celerity of propagation for small perturbations and dispersive sediment aggradation under a supercritical flow"

description: This repository provides raw data corresponding to an aggradation experiment, needed to reproduce the findings of the manuscript "Investigating the celerity of propagation for small perturbations and dispersive sediment aggradation under a supercritical flow".

 A channel may be aggraded by overloaded sediment. In this paper we realize an aggradation experiment and determine the celerity at which an aggradation wave migrates. We also investigate the celerity of aggradation to the celerity of small perturbations, as quantified based on mathematical formulations. The celerities of the two kinds are correlated with each other. However, the celerity of small perturbations is larger than the other one, that is less than a few percent of the water velocity.

The parameters of the performed experiment are as follows:

Water discharge: 7 l/s

Sediment feeding rate: 4.28×10-4  m3/s

Initial sediment transport capacity of the channel: 1.33×10-4 m3/s

Initial slope of the channel: 1.37%

Particle size: 3.8 mm

Particle density: 1443 kg/m3
DOI: 10.5281/zenodo.10641132
title: Data for UVQuanT deliverable D4.2

description: Data required for figures in this report. When three columns are present, the data are formatted as "x","y", "yerror".
DOI: 10.5281/zenodo.10641133
title: Data for UVQuanT deliverable D4.2

description: Data required for figures in this report. When three columns are present, the data are formatted as "x","y", "yerror".
DOI: 10.5066/p1c73qaz
title: Ocular field estimates of exotic annual and perennial grass cover across the Soda Wildfire

description: Data includes functional group cover of exotic annual grasses and deep rooted perennial grasses within the first five years after the 2015 Soda wildfire across different post-fire restoration treatments. Additional landscape and restoration treatment covariates hypothesized to influence post-fire invasive annual grass and perennial grass cover are included.
DOI: 10.5281/zenodo.10641323
title: Observational study of COVID-19 Vaccination in patients with thoracic malignancies: adverse events, breakthrough infections and survival patterns
DOI: 10.5281/zenodo.10641324
title: Observational study of COVID-19 Vaccination in patients with thoracic malignancies: adverse events, breakthrough infections and survival patterns
DOI: 10.5281/zenodo.8173839
title: SJPedPanel: Supplementary Data

description: <em>Supplementary Data for</em> <strong>SJPedPanel: A pan-cancer gene panel for childhood malignancies</strong> ___ Please visit the following GitHub repository for the latest supplementary files/figures. https://github.com/XMaLab/SJPedPanel_Supplementary_Data
DOI: 10.3886/e198225
title: Calendar of Prisoners, England and Wales, 1870, 1883, and 1910

description: Data collected for use in the Northwestern University dissertation "The Economics of Crime in Victorian England," submitted in 2013, and related publications listed here.
description: Any individual appearing as a defendant in a court of Assize or Quarter Sessions in 1870, 1883, or 1910. The data from 1883 also transcriptions from the Central Criminal Court (Old Bailey) as well as more detail such as amount stolen and identity of victims.
description: Transcribed from photographs of the "Calendar of Prisoners" held at the National Archives in Kew (HO 140)
DOI: 10.3886/e198225v1
title: Calendar of Prisoners, England and Wales, 1870, 1883, and 1910

description: Data collected for use in the Northwestern University dissertation "The Economics of Crime in Victorian England," submitted in 2013, and related publications listed here.
description: Any individual appearing as a defendant in a court of Assize or Quarter Sessions in 1870, 1883, or 1910. The data from 1883 also transcriptions from the Central Criminal Court (Old Bailey) as well as more detail such as amount stolen and identity of victims.
description: Transcribed from photographs of the "Calendar of Prisoners" held at the National Archives in Kew (HO 140)
DOI: 10.5281/zenodo.10641333
title: Concatenated coccolithophore abundances

description: Concatenated coccolithophore abundance data. Non-gridded, abudances only, output from the CASCADE dataset.
DOI: 10.5281/zenodo.10641334
title: Concatenated coccolithophore abundances

description: Concatenated coccolithophore abundance data. Non-gridded, abudances only, output from the CASCADE dataset.
DOI: 10.5066/p9mqn1lo
title: Database of Riparian Floodplain Boundaries for the San Carlos and Gila Rivers on the San Carlos Apache Reservation and Upper Gila River Watershed (1935 - 2021)

description: We developed this spatial database of historic and current floodplains to analyze trends in vegetation conditions, identify areas more at risk of degradation, and assess the relationship between riparian vegetation dynamics and climate conditions.Our study area is the riparian areas along the San Carlos River and Gila River within the San Carlos Apache Reservation and the Upper Gila River Level-4 Hydrologic Unit Code (HUC) watershed. The product was developed by digitizing the active channel and primary riparian floodplain using historic 1935 aerial imagery (Arizona State University GeoData, 2021) and National Agriculture Imagery Program (NAIP) aerial imagery from 2019 (U.S. Department of Agriculture, 2021).

This data was used in the development of the following data release: Petrakis, R.E., Norman, L.M., Middleton, B.R., 2023, Mapping Riparian Vegetation Response to Climate Change on the San Carlos Apache Reservation and Upper Gila River Watershed to Inform Restoration Priorities: 1935 to Present - Database of Trends in Vegetation Properties and Climate Adaptation Variables: U.S. Geological Survey data release, https://doi.org/10.5066/P9HL0N5T.

And in support of the following publication: Petrakis, R.E., Norman, L.M., Middleton, B.R., 2023. Riparian Vegetation Response amid Variable Climate Conditions across the Upper Gila River Watershed: Informing Tribal Restoration Priorities. Frontiers in Environmental Science. https://doi.org/10.3389/fenvs.2023.1179328.

This Parent data release consists of three shapefiles, or Child Items. The first two shapefiles show the extent of the historic (i.e., 1935) and current (i.e., 2019) riparian floodplain, including the active channel and primary riparian floodplain portions, along the San Carlos River and Gila River within the San Carlos Apache Reservation. The first shapefile - 1935 Riparian Floodplain and Active Channel Boundaries for the San Carlos River and Gila River - was produced for 1935, representing historic conditions, by digitizing the active channel and primary riparian floodplain using 1935 aerial imagery. The second shapefile - 2019 Riparian Floodplain and Active Channel Boundaries for the San Carlos River and Gila River - was produced for 2019, representing current conditions, by digitizing the active channel and primary riparian floodplain using National Agriculture Imagery Program (NAIP) aerial imagery from 2019. The final shapefile - 2019 Riparian Floodplain for the San Carlos River and Gila River within the Upper Gila River Level-4 Hydrologic Unit Code Watershed - shows the boundary of the riparian floodplain for the Gila River and San Carlos River across the entire Upper Gila River Level-4 HUC.
DOI: 10.5281/zenodo.10640939
title: Copper Wire Corrosion and Meteorological Conditions in a Hangar

description: Measurement of copper wire corrosion in a hangar (Kbely, Prague) with meteorological data (indoor and outdoor temperature, indoor and outdoor humidity, indoor and outdoor dew point, wind direction, wind speed, pressure above mean sea level). The dataset also includes measurements of pollution (SO2) from a meteorological station (Libuš, Prague) and NO2, PM10, and PM2.5 from Holešovice, Prague. The sampling period is one hour, and the measurements were collected for a duration of 390 days.
DOI: 10.5281/zenodo.8239155
title: Copper Wire Corrosion and Meteorological Conditions in a Hangar

description: Measurement of copper wire corrosion in a hangar (Kbely, Prague) with meteorological data (indoor and outdoor temperature, indoor and outdoor humidity, indoor and outdoor dew point, wind direction, wind speed, pressure above mean sea level). The dataset also includes measurements of pollution (SO2) from a meteorological station (Libuš, Prague) and NO2, PM10, and PM2.5 from Holešovice, Prague. The sampling period is one hour, and the measurements were collected for a duration of 390 days.
DOI: 10.5281/zenodo.8239156
title: Copper Wire Corrosion and Meteorological Conditions in a Hangar

description: Measurement of copper wire corrosion in a hangar (Kbely, Prague) with meteorological data (indoor and outdoor temperature, indoor and outdoor humidity, indoor and outdoor dew point, wind direction, wind speed, pressure above mean sea level). The dataset also includes measurements of pollution (SO2, NO2, PM10, and PM2.5) from a meteorological station (Libuš, Prague). The sampling period is one hour, and the measurements were collected for a duration of 390 days.
DOI: 10.6084/m9.figshare.25101872
title: Mytilus edulis PEI annotation

description: The .gff contains annotation for the <i>Mytilus edulis </i>genome including Augustus predictions (trained with genes from <i>Mytilus galloprovincialis</i>, <i>Mytilus coruscus </i>and <i>Crassostrea virginica)</i>combined with IsoSeq data analyses (65,505 gene models and 129,708 isoforms). The .faa contains translated amino acid sequences of complete CDS from this annotation (45,379 amino acid sequences).
DOI: 10.5281/zenodo.10641377
title: Literature morphometric estimates of cell size
DOI: 10.5281/zenodo.10641378
title: Literature morphometric estimates of cell size
DOI: 10.6084/m9.figshare.25197293
title: QOL Dataset

description: EORTC QLQ scores
DOI: 10.6084/m9.figshare.25197293.v1
title: QOL Dataset

description: EORTC QLQ scores