Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data

The purpose of this experiment is to measure how initially disturbing an area and adding nitrogen over a long time will affect the number of species, the type of species present, the amount of annual growth, and the change from year to year in the growth of each species in a plant community which is...

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Format: Dataset
Language:unknown
Published: 1993
Subjects:
Online Access:http://hdl.handle.net/10255/dryad.10194
http://metacat.lternet.edu/knb/metacat/knb-lter-cdr.799102.2/xml
id ftdryad:oai:v1.datadryad.org:10255/dryad.10194
record_format openpolar
institution Open Polar
collection Dryad Digital Repository (Duke University)
op_collection_id ftdryad
language unknown
topic Cedar Creek Natural History Area
Long Term
Ecology
Successional dynamics
Primary Productivity
Disturbance Patterns
Nutrient Budgets
Nutrient Cycles
Climatic Variation
Biodiversity
Ecosystem functioning
Nitrogen limitation
Fire Frequency
Plant Competition
MISCELLANEOUS LITTER
AGROPYRON REPENS
POA PRATENSIS
MOSSES & LICHENS
SCHIZACHYRIUM SCOPARIUM
ARISTIDA BASIRAMEA
AMBROSIA ARTEMISIIFOLIA ELATIOR
BERTEROA INCANA
ERIGERON CANADENSIS
FRAGARIA VIRGINIANA
LEPIDIUM DENSIFLORUM
OENOTHERA BIENNIS
POLYGONUM CONVOLVULUS
SILENE ANTIRRHINA
HIERACIUM LONGIPILUM
AGROSTIS SCABRA
HEDEOMA HISPIDA
PHYSALIS VIRGINIANA
CHENOPODIUM ALBUM
MISCELLANEOUS HERBS
SETARIA LUTESCENS (GLAUCA)
DIGITARIA ISCHAEMUM
TRAGOPOGON DUBIUS (MAJOR)
ACHILLEA MILLEFOLIUM(LANULOSA)
SETARIA VIRIDIS
ASCLEPIAS SYRIACA
LYCHNIS ALBA
CYPERUS SP
RUDBECKIA SEROTINA
EUPHORBIA SP
CENCHRUS LONGISPINUS
POLYGONUM TENUE
PHYSALIS HETEROPHYLLA
EUPHORBIA GLYPTOSPERMA
LESPEDEZA CAPITATA
PANICUM PRAECOCIOUS
VERBASCUM THAPSUS
PANICUM OLIGOSANTHES
GNAPHALIUM OBTUSIFOLIUM
LACTUCA SP
ANDROPOGON GERARDI
RUMEX ACETOSELLA
CAREX SP
FUNGI
ERAGROSTIS SPECTABILIS
PINUS STROBUS
PHALARIS ARUNDINACEA
ARTEMISIA LUDOVICIANA
EUPHORBIA COROLLATA
RUBUS SP
SORGHASTRUM NUTANS
AMBROSIA CORONOPIFOLIA
TRADESCANTIA OCCIDENTALIS
ROSA ARKANSANA
ASCLEPIAS TUBEROSA
VIOLA PEDATIFIDA
OXYBAPHUS HIRSUTUS
PANICUM PERLONGUM
ARTEMISIA (CAUDATA) CAMPESTRIS
POLYGALA POLYGAMA
SOLIDAGO RIGIDA
CAMPANULA ROTUNDIFOLIA
SOLIDAGO NEMORALIS
CHENOPODIUM LEPTOPHYLLUM
STIPA SPARTEA
LITHOSPERMUM CANESCENS
URTICA DIOICA
ASTER AZUREUS
CIRSIUM ARVENSE
LATHYRUS VENOSUS
EQUISETUM LAEVIGATUM
HELIANTHEMUM BICKNELLII
ANEMONE CYLINDRICA
PANICUM CAPILLARE
spellingShingle Cedar Creek Natural History Area
Long Term
Ecology
Successional dynamics
Primary Productivity
Disturbance Patterns
Nutrient Budgets
Nutrient Cycles
Climatic Variation
Biodiversity
Ecosystem functioning
Nitrogen limitation
Fire Frequency
Plant Competition
MISCELLANEOUS LITTER
AGROPYRON REPENS
POA PRATENSIS
MOSSES & LICHENS
SCHIZACHYRIUM SCOPARIUM
ARISTIDA BASIRAMEA
AMBROSIA ARTEMISIIFOLIA ELATIOR
BERTEROA INCANA
ERIGERON CANADENSIS
FRAGARIA VIRGINIANA
LEPIDIUM DENSIFLORUM
OENOTHERA BIENNIS
POLYGONUM CONVOLVULUS
SILENE ANTIRRHINA
HIERACIUM LONGIPILUM
AGROSTIS SCABRA
HEDEOMA HISPIDA
PHYSALIS VIRGINIANA
CHENOPODIUM ALBUM
MISCELLANEOUS HERBS
SETARIA LUTESCENS (GLAUCA)
DIGITARIA ISCHAEMUM
TRAGOPOGON DUBIUS (MAJOR)
ACHILLEA MILLEFOLIUM(LANULOSA)
SETARIA VIRIDIS
ASCLEPIAS SYRIACA
LYCHNIS ALBA
CYPERUS SP
RUDBECKIA SEROTINA
EUPHORBIA SP
CENCHRUS LONGISPINUS
POLYGONUM TENUE
PHYSALIS HETEROPHYLLA
EUPHORBIA GLYPTOSPERMA
LESPEDEZA CAPITATA
PANICUM PRAECOCIOUS
VERBASCUM THAPSUS
PANICUM OLIGOSANTHES
GNAPHALIUM OBTUSIFOLIUM
LACTUCA SP
ANDROPOGON GERARDI
RUMEX ACETOSELLA
CAREX SP
FUNGI
ERAGROSTIS SPECTABILIS
PINUS STROBUS
PHALARIS ARUNDINACEA
ARTEMISIA LUDOVICIANA
EUPHORBIA COROLLATA
RUBUS SP
SORGHASTRUM NUTANS
AMBROSIA CORONOPIFOLIA
TRADESCANTIA OCCIDENTALIS
ROSA ARKANSANA
ASCLEPIAS TUBEROSA
VIOLA PEDATIFIDA
OXYBAPHUS HIRSUTUS
PANICUM PERLONGUM
ARTEMISIA (CAUDATA) CAMPESTRIS
POLYGALA POLYGAMA
SOLIDAGO RIGIDA
CAMPANULA ROTUNDIFOLIA
SOLIDAGO NEMORALIS
CHENOPODIUM LEPTOPHYLLUM
STIPA SPARTEA
LITHOSPERMUM CANESCENS
URTICA DIOICA
ASTER AZUREUS
CIRSIUM ARVENSE
LATHYRUS VENOSUS
EQUISETUM LAEVIGATUM
HELIANTHEMUM BICKNELLII
ANEMONE CYLINDRICA
PANICUM CAPILLARE
Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
topic_facet Cedar Creek Natural History Area
Long Term
Ecology
Successional dynamics
Primary Productivity
Disturbance Patterns
Nutrient Budgets
Nutrient Cycles
Climatic Variation
Biodiversity
Ecosystem functioning
Nitrogen limitation
Fire Frequency
Plant Competition
MISCELLANEOUS LITTER
AGROPYRON REPENS
POA PRATENSIS
MOSSES & LICHENS
SCHIZACHYRIUM SCOPARIUM
ARISTIDA BASIRAMEA
AMBROSIA ARTEMISIIFOLIA ELATIOR
BERTEROA INCANA
ERIGERON CANADENSIS
FRAGARIA VIRGINIANA
LEPIDIUM DENSIFLORUM
OENOTHERA BIENNIS
POLYGONUM CONVOLVULUS
SILENE ANTIRRHINA
HIERACIUM LONGIPILUM
AGROSTIS SCABRA
HEDEOMA HISPIDA
PHYSALIS VIRGINIANA
CHENOPODIUM ALBUM
MISCELLANEOUS HERBS
SETARIA LUTESCENS (GLAUCA)
DIGITARIA ISCHAEMUM
TRAGOPOGON DUBIUS (MAJOR)
ACHILLEA MILLEFOLIUM(LANULOSA)
SETARIA VIRIDIS
ASCLEPIAS SYRIACA
LYCHNIS ALBA
CYPERUS SP
RUDBECKIA SEROTINA
EUPHORBIA SP
CENCHRUS LONGISPINUS
POLYGONUM TENUE
PHYSALIS HETEROPHYLLA
EUPHORBIA GLYPTOSPERMA
LESPEDEZA CAPITATA
PANICUM PRAECOCIOUS
VERBASCUM THAPSUS
PANICUM OLIGOSANTHES
GNAPHALIUM OBTUSIFOLIUM
LACTUCA SP
ANDROPOGON GERARDI
RUMEX ACETOSELLA
CAREX SP
FUNGI
ERAGROSTIS SPECTABILIS
PINUS STROBUS
PHALARIS ARUNDINACEA
ARTEMISIA LUDOVICIANA
EUPHORBIA COROLLATA
RUBUS SP
SORGHASTRUM NUTANS
AMBROSIA CORONOPIFOLIA
TRADESCANTIA OCCIDENTALIS
ROSA ARKANSANA
ASCLEPIAS TUBEROSA
VIOLA PEDATIFIDA
OXYBAPHUS HIRSUTUS
PANICUM PERLONGUM
ARTEMISIA (CAUDATA) CAMPESTRIS
POLYGALA POLYGAMA
SOLIDAGO RIGIDA
CAMPANULA ROTUNDIFOLIA
SOLIDAGO NEMORALIS
CHENOPODIUM LEPTOPHYLLUM
STIPA SPARTEA
LITHOSPERMUM CANESCENS
URTICA DIOICA
ASTER AZUREUS
CIRSIUM ARVENSE
LATHYRUS VENOSUS
EQUISETUM LAEVIGATUM
HELIANTHEMUM BICKNELLII
ANEMONE CYLINDRICA
PANICUM CAPILLARE
description The purpose of this experiment is to measure how initially disturbing an area and adding nitrogen over a long time will affect the number of species, the type of species present, the amount of annual growth, and the change from year to year in the growth of each species in a plant community which is also relieved of grazing by large and small mammals. This experiment is conducted within fields (A, B, and C) which were initially low in soil nutrients. The ground was disturbed by thoroughly disking the area prior to establishment of the experiment. There are 8 different levels of nitrogen addition with other nutrients added to ensure that nitrogen remains the limiting nutrient, and a control which receives no nutrients. Nitrogen fertilizer (NH4NO3) is applied twice per year, once in early May and once in late June. There are six replicates of each treatment per field. The treatments were randomly assigned to plots of size 4 by 4 meters. The plots are in 6 plot by 9 plot grids with 1 meter aisles between plots. The plot grids are enclosed by a fence to keep out mammalian herbivores. Gophers are trapped and removed as they appear. In the spring of 1992, subexperiments E097 and E098 were established. E097 is in fields A and C where randomly selected plots within each treatment no longer receive fertilizer. E098 is in field B where randomly selected plots within each treatment are burned. Note that the design of E002 is similar to E001 except E002 was thoroughly disked prior to establishment.
format Dataset
title Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
title_short Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
title_full Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
title_fullStr Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
title_full_unstemmed Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data
title_sort long-term nitrogen deposition: effects on succession following major disturbances. year 1991 aboveground biomass data
publishDate 1993
url http://hdl.handle.net/10255/dryad.10194
http://metacat.lternet.edu/knb/metacat/knb-lter-cdr.799102.2/xml
op_coverage The Cedar Creek Natural History Area is located in Anoka and Isanti counties, approximately 30 miles north of Saint Paul, MN. CCNHA lies at the boundary between prairie and forest. It is a mosaic of uplands dominated by oak savanna, prairie, hardwood forest, pine forests,and abandoned agricultural fields and of lowlands comprised of ash and cedar swamps, acid bogs, marshes, and sedge meadows. Large tracts of the pre-agricultural ecosystems of the region are preserved within its boundaries, as is a successional chronosequence of more than 80 old fields of known history.
-93.22445 W -93.16289 E 45.44138 N 45.384865 S
1991
1991
long_lat ENVELOPE(-129.954,-129.954,54.598,54.598)
ENVELOPE(-57.715,-57.715,51.467,51.467)
geographic Cedar Creek
Saint-Paul
geographic_facet Cedar Creek
Saint-Paul
genre Campanula rotundifolia
genre_facet Campanula rotundifolia
op_relation http://metacat.lternet.edu/knb/metacat/knb-lter-cdr.799102.2/xml
knb-lter-cdr.799102.2
http://hdl.handle.net/10255/dryad.10194
op_rights Code of Ethics and Rules for Use of Cedar Creek LTER and Related DataAs a condition for access to data provided by researchers of the Cedar Creek LTER, I, the data user, agrees to abide by the following code of ethics.I agree to notify the Cedar Creek LTER scientists who gathered data if I would like to use those data in any publication. I acknowledge that these data were gathered by Cedar Creek scientists because they had already perceived the importance of these data for a variety of scientific and societal issues. I will provide them with formal recognition that, at their discretion, may include co-authorship or acknowledgements on publications. I realize that the researchers who gathered these data may be using them for scientific analyses, papers or publications that are currently planned or in preparation, and that such activities have precedence over any that I might wish to prepare. In this case, my preparation of any work may be delayed, at the option of the Cedar Creek researchers involved, until their work is completed. Because it may be possible to misinterpret a data set if it is taken out of context, I will seek the assistance and opinion of those Cedar Creek researchers involved in the design of a study and the collection of the data as I analyze the data. Moreover, I realize that this computer data set is not complete, and it may contain errors. The complete data set includes extensive written documentation, which should be referenced to reduce the chance of errors in data and errors of interpretation.
_version_ 1766383851604541440
spelling ftdryad:oai:v1.datadryad.org:10255/dryad.10194 2023-05-15T15:48:44+02:00 Long-Term Nitrogen Deposition: Effects on Succession Following Major Disturbances. Year 1991 Aboveground biomass data The Cedar Creek Natural History Area is located in Anoka and Isanti counties, approximately 30 miles north of Saint Paul, MN. CCNHA lies at the boundary between prairie and forest. It is a mosaic of uplands dominated by oak savanna, prairie, hardwood forest, pine forests,and abandoned agricultural fields and of lowlands comprised of ash and cedar swamps, acid bogs, marshes, and sedge meadows. Large tracts of the pre-agricultural ecosystems of the region are preserved within its boundaries, as is a successional chronosequence of more than 80 old fields of known history. -93.22445 W -93.16289 E 45.44138 N 45.384865 S 1991 1991 1993 text/plain http://hdl.handle.net/10255/dryad.10194 http://metacat.lternet.edu/knb/metacat/knb-lter-cdr.799102.2/xml unknown http://metacat.lternet.edu/knb/metacat/knb-lter-cdr.799102.2/xml knb-lter-cdr.799102.2 http://hdl.handle.net/10255/dryad.10194 Code of Ethics and Rules for Use of Cedar Creek LTER and Related DataAs a condition for access to data provided by researchers of the Cedar Creek LTER, I, the data user, agrees to abide by the following code of ethics.I agree to notify the Cedar Creek LTER scientists who gathered data if I would like to use those data in any publication. I acknowledge that these data were gathered by Cedar Creek scientists because they had already perceived the importance of these data for a variety of scientific and societal issues. I will provide them with formal recognition that, at their discretion, may include co-authorship or acknowledgements on publications. I realize that the researchers who gathered these data may be using them for scientific analyses, papers or publications that are currently planned or in preparation, and that such activities have precedence over any that I might wish to prepare. In this case, my preparation of any work may be delayed, at the option of the Cedar Creek researchers involved, until their work is completed. Because it may be possible to misinterpret a data set if it is taken out of context, I will seek the assistance and opinion of those Cedar Creek researchers involved in the design of a study and the collection of the data as I analyze the data. Moreover, I realize that this computer data set is not complete, and it may contain errors. The complete data set includes extensive written documentation, which should be referenced to reduce the chance of errors in data and errors of interpretation. Cedar Creek Natural History Area Long Term Ecology Successional dynamics Primary Productivity Disturbance Patterns Nutrient Budgets Nutrient Cycles Climatic Variation Biodiversity Ecosystem functioning Nitrogen limitation Fire Frequency Plant Competition MISCELLANEOUS LITTER AGROPYRON REPENS POA PRATENSIS MOSSES & LICHENS SCHIZACHYRIUM SCOPARIUM ARISTIDA BASIRAMEA AMBROSIA ARTEMISIIFOLIA ELATIOR BERTEROA INCANA ERIGERON CANADENSIS FRAGARIA VIRGINIANA LEPIDIUM DENSIFLORUM OENOTHERA BIENNIS POLYGONUM CONVOLVULUS SILENE ANTIRRHINA HIERACIUM LONGIPILUM AGROSTIS SCABRA HEDEOMA HISPIDA PHYSALIS VIRGINIANA CHENOPODIUM ALBUM MISCELLANEOUS HERBS SETARIA LUTESCENS (GLAUCA) DIGITARIA ISCHAEMUM TRAGOPOGON DUBIUS (MAJOR) ACHILLEA MILLEFOLIUM(LANULOSA) SETARIA VIRIDIS ASCLEPIAS SYRIACA LYCHNIS ALBA CYPERUS SP RUDBECKIA SEROTINA EUPHORBIA SP CENCHRUS LONGISPINUS POLYGONUM TENUE PHYSALIS HETEROPHYLLA EUPHORBIA GLYPTOSPERMA LESPEDEZA CAPITATA PANICUM PRAECOCIOUS VERBASCUM THAPSUS PANICUM OLIGOSANTHES GNAPHALIUM OBTUSIFOLIUM LACTUCA SP ANDROPOGON GERARDI RUMEX ACETOSELLA CAREX SP FUNGI ERAGROSTIS SPECTABILIS PINUS STROBUS PHALARIS ARUNDINACEA ARTEMISIA LUDOVICIANA EUPHORBIA COROLLATA RUBUS SP SORGHASTRUM NUTANS AMBROSIA CORONOPIFOLIA TRADESCANTIA OCCIDENTALIS ROSA ARKANSANA ASCLEPIAS TUBEROSA VIOLA PEDATIFIDA OXYBAPHUS HIRSUTUS PANICUM PERLONGUM ARTEMISIA (CAUDATA) CAMPESTRIS POLYGALA POLYGAMA SOLIDAGO RIGIDA CAMPANULA ROTUNDIFOLIA SOLIDAGO NEMORALIS CHENOPODIUM LEPTOPHYLLUM STIPA SPARTEA LITHOSPERMUM CANESCENS URTICA DIOICA ASTER AZUREUS CIRSIUM ARVENSE LATHYRUS VENOSUS EQUISETUM LAEVIGATUM HELIANTHEMUM BICKNELLII ANEMONE CYLINDRICA PANICUM CAPILLARE dataset 1993 ftdryad 2020-01-01T14:23:11Z The purpose of this experiment is to measure how initially disturbing an area and adding nitrogen over a long time will affect the number of species, the type of species present, the amount of annual growth, and the change from year to year in the growth of each species in a plant community which is also relieved of grazing by large and small mammals. This experiment is conducted within fields (A, B, and C) which were initially low in soil nutrients. The ground was disturbed by thoroughly disking the area prior to establishment of the experiment. There are 8 different levels of nitrogen addition with other nutrients added to ensure that nitrogen remains the limiting nutrient, and a control which receives no nutrients. Nitrogen fertilizer (NH4NO3) is applied twice per year, once in early May and once in late June. There are six replicates of each treatment per field. The treatments were randomly assigned to plots of size 4 by 4 meters. The plots are in 6 plot by 9 plot grids with 1 meter aisles between plots. The plot grids are enclosed by a fence to keep out mammalian herbivores. Gophers are trapped and removed as they appear. In the spring of 1992, subexperiments E097 and E098 were established. E097 is in fields A and C where randomly selected plots within each treatment no longer receive fertilizer. E098 is in field B where randomly selected plots within each treatment are burned. Note that the design of E002 is similar to E001 except E002 was thoroughly disked prior to establishment. Dataset Campanula rotundifolia Dryad Digital Repository (Duke University) Cedar Creek ENVELOPE(-129.954,-129.954,54.598,54.598) Saint-Paul ENVELOPE(-57.715,-57.715,51.467,51.467)