cometadata/datacite-titles-descriptions-related-identifiers huggingface dataset:
DOI: 10.5281/zenodo.10611685
title: Chapter 2 Section 2.5 - AS regulators

description: Companion datasets of the Thesis titled "Alternative splicing programs in tumor development and progression". This collection corresponds to all data generated in Chapter 2 Section 2.5 Alternative splicing regulators.
DOI: 10.5281/zenodo.10611029
title: ScrumRPG analysis
DOI: 10.5281/zenodo.10641250
title: ScrumRPG analysis
DOI: 10.17909/bsny-4f21
title: Data used in "Atmospheric Retrievals of the Phase-resolved Spectra of Irradiated Brown Dwarfs WD-0137B and EPIC-2122B"

description: Data used in "Atmospheric Retrievals of the Phase-resolved Spectra of Irradiated Brown Dwarfs WD-0137B and EPIC-2122B". Phase curves of irradiated BDs EPIC-2122B and WD-0137B.
DOI: 10.25549/usctheses-ouc113089520
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 2]
DOI: 10.25549/usctheses-ouc113089621
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 3]
DOI: 10.25549/usctheses-ouc113089664
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 1]
DOI: 10.25549/usctheses-ouc113089765
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 6]
DOI: 10.5517/ccdc.csd.cc250yw1
title: CCDC 1996923: Experimental Crystal Structure Determination

description: Related Article: Seyoung Koo, Miae Won, Hao Li, Won Young Kim, Mingle Li, Chenxu Yan, Amit Sharma, Zhiqian Guo, Wei-Hong Zhu, Jonathan L. Sessler, Jin Yong Lee, Jong Seung Kim|2021|Chemical Science|12|10054|doi:10.1039/D1SC02259H
description: Related Article: Jong Seung Kim, Gu Se Young ,Miae Won, Won Young Kim Jonathan L. Sessler, Mingle Li
|2022|U.S.Patents|||
description: An entry from the Cambridge Structural Database, the world’s repository for small molecule crystal structures. The entry contains experimental data from a crystal diffraction study. The deposited dataset for this entry is freely available from the CCDC and typically includes 3D coordinates, cell parameters, space group, experimental conditions and quality measures.
DOI: 10.5517/ccdc.csd.cc280t6b
title: CCDC 2086151: Experimental Crystal Structure Determination

description: Related Article: Florian R. Rehak, Wim Klopper, Jasmin M. Busch,  Olaf Fuhr, Valentina Ferraro, Marianna Kemell, Martin Nieger, Stefan Bräse|2024|CSD Communication|||
description: An entry from the Cambridge Structural Database, the world’s repository for small molecule crystal structures. The entry contains experimental data from a crystal diffraction study. The deposited dataset for this entry is freely available from the CCDC and typically includes 3D coordinates, cell parameters, space group, experimental conditions and quality measures.
DOI: 10.5517/ccdc.csd.cc280t9f
title: CCDC 2086154: Experimental Crystal Structure Determination

description: Related Article: Florian R. Rehak, Wim Klopper, Jasmin M. Busch,  Olaf Fuhr, Valentina Ferraro, Marianna Kemell, Martin Nieger, Stefan Bräse|2024|CSD Communication|||
description: An entry from the Cambridge Structural Database, the world’s repository for small molecule crystal structures. The entry contains experimental data from a crystal diffraction study. The deposited dataset for this entry is freely available from the CCDC and typically includes 3D coordinates, cell parameters, space group, experimental conditions and quality measures.
DOI: 10.25549/usctheses-ouc113089866
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 5]
DOI: 10.25549/usctheses-ouc113089967
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 7]
DOI: 10.25549/usctheses-ouc113089972
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 8]
DOI: 10.25549/usctheses-ouc113089977
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 9]
DOI: 10.25549/usctheses-ouc113090002
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 11]
DOI: 10.25549/usctheses-ouc113090005
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 10]
DOI: 10.25549/usctheses-ouc113090062
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 12]
DOI: 10.25549/usctheses-ouc113090066
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 13]
DOI: 10.25549/usctheses-ouc113090079
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 14]
DOI: 10.25549/usctheses-ouc113090112
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 15]
DOI: 10.25549/usctheses-ouc113090148
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 16]
DOI: 10.25549/usctheses-ouc113090169
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 17]
DOI: 10.25549/usctheses-ouc113090186
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 18]
DOI: 10.25549/usctheses-ouc113090207
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 4]
DOI: 10.25549/usctheses-ouc113090215
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 19]
DOI: 10.25549/usctheses-ouc113090328
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 20]
DOI: 10.25549/usctheses-ouc113090455
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 21]
DOI: 10.25549/usctheses-ouc113090477
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 22]
DOI: 10.25549/usctheses-ouc113090522
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 23]
DOI: 10.25549/usctheses-ouc113090644
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 24]
DOI: 10.25549/usctheses-ouc113090652
title: ?-catenin couples self-renewal, induction... [Chapter 2, Table 25]
DOI: 10.25549/usctheses-ouc113090665
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 1]
DOI: 10.25549/usctheses-ouc113090678
title: ?-catenin couples self-renewal, induction... [Chapter 3, Table 5]
DOI: 10.25345/c5t727s5r
title: MassIVE MSV000094051 - Host lipids regulate multicellular behavior of a predator of a human pathogen
title: Raw proteomics and lipidomics mass spectrometry data from Biomphalaria glabrata hemolymph samples. Hemolymph was collected by the foot-retraction method from: naive NMRI strains, naive M-line strains, or M-line strains infected and shedding PR1 Schistosoma mansoni. Untargeted proteomics analysis completed by the Laboratory for Biological Mass Spectrometry at Indiana University. Lipidomics analysis completed by the Beth Israel Deaconess Medical Center (BIDMC) Metabolomics Core in Boston, MA.
DOI: 10.6084/m9.figshare.25196849.v1
title: yng_fledged_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.25196855
title: time_since_invasion_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.25196855.v1
title: time_since_invasion_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.25196846
title: nest_survival_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.25196846.v1
title: nest_survival_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.25196849
title: yng_fledged_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.25194065
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.