Ellsworth Huntington’s (1914) giant sequoia ages and tree-ring measurements from 458 stumps in Sequoia National Forest and Mountain Home Grove
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These data include giant sequioa (Sequoiadendron giganteum) age and tree-ring data from measurements on 458 stumps. The original data were recorded on paper data sheets by Ellsworth Huntington and his assistants in 1911 and 1912; their methods are elaborated in Huntington (1914), and further details can be found in Stephenson and Demetry (1995). We entered the data from photocopies of the original data sheets which, to the best of our knowledge, reside at Yale University. The photocopies apparently were made in the late 1960s or early 1970s and were housed in Sequoia National Park’s archives. Most of Huntington’s 458 measured giant sequoia stumps were in or near what is now the Hume Lake District of Sequoia National Forest (Giant Sequoia National Monument), California, particularly the Converse Basin Grove; however, about 17 percent came from in or near what is now Mountain Home Demonstration State Forest, about 70 km to the SSE. Data for each tree (stump) consist of from one to five readings of the widths (to the nearest 0.5 mm) of groups of 10 tree rings along unique radii. When only one or two radii were measured on a stump, we entered the data for each radius. When three, four, or five radii were measured, we entered data from two radii whose directions differed by at least 90 degrees, whenever possible. The choice of entering data from widely separated radii was made by Stephenson and Demetry (1995), who wished to determine the effects of two widely separated increment cores on the accuracy and precision of age estimates for giant sequoias. Sometimes, “DO NOT USE” was written by Huntington across a radius’ readings, usually because that radius came out several to many decades younger than the oldest radius for that tree. If such a radius normally would fit our criterion to be entered in the database (because it was separated by at least 90 from the other radius we entered), a judgement was made. Generally, if the difference was at least 50 years, a different radius whose count better agreed with the largest count was chosen, regardless of its direction. References: Douglass, A. E. 1919. Climatic Cycles and Tree Growth, A Study of the Annual Rings of Trees in Relation to Climate and Solar Activity. Carnegie Institute of Washington. 127 pages. Huntington, E. 1914. The Climatic Factor as Illustrated in Arid America. Carnegie Institute of Washington Publication No. 192. 341 pages. Stephenson, N. L., and A. Demetry. 1995. Estimating ages of giant sequoias. Canadian Journal of Forest Research 25:223-233.
Sequoia foliage dieback and tree-ring data from Sequoia National Park
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These datasets provide spatially-explicit estimates of the magnitude of giant sequoia foliage dieback along selected trail corridors in Sequoia and Kings Canyon national parks, California, from 2014 through 2017. They additionally provide giant sequoia tree-ring measurements, through the year 1989, for two locations in the Giant Forest grove, Sequoia National Park, California. These data support the following publications: Nathan L. Stephenson, Adrian J. Das, Nicholas J. Ampersee, Kathleen G. Cahill, Anthony C. Caprio, John E. Sanders, A. Park Williams, Patterns and correlates of giant sequoia foliage dieback during California’s 2012–2016 hotter drought, Forest Ecology and Management, Available online 7 November 2017, ISSN 0378-1127, https://doi.org/10.1016/j.foreco.2017.10.053. Martin, R. E., G. P. Asner, E. Francis, A. Ambrose, W. Baxter, A. J. Das, N. R. Vaughn, T. Paz-Kagan, T. Dawson, K. Nydick, and N. L. Stephenson. Submitted. Remote measurement of canopy water content in giant sequoias (Sequoiadendron giganteum) during drought. Submitted to special section in Forest Ecology and Management.
Sequoia foliage dieback and tree-ring data from Sequoia National Park
공공데이터포털
These datasets provide spatially-explicit estimates of the magnitude of giant sequoia foliage dieback along selected trail corridors in Sequoia and Kings Canyon national parks, California, from 2014 through 2017. They additionally provide giant sequoia tree-ring measurements, through the year 1989, for two locations in the Giant Forest grove, Sequoia National Park, California. These data support the following publications: Nathan L. Stephenson, Adrian J. Das, Nicholas J. Ampersee, Kathleen G. Cahill, Anthony C. Caprio, John E. Sanders, A. Park Williams, Patterns and correlates of giant sequoia foliage dieback during California’s 2012–2016 hotter drought, Forest Ecology and Management, Available online 7 November 2017, ISSN 0378-1127, https://doi.org/10.1016/j.foreco.2017.10.053. Martin, R. E., G. P. Asner, E. Francis, A. Ambrose, W. Baxter, A. J. Das, N. R. Vaughn, T. Paz-Kagan, T. Dawson, K. Nydick, and N. L. Stephenson. Submitted. Remote measurement of canopy water content in giant sequoias (Sequoiadendron giganteum) during drought. Submitted to special section in Forest Ecology and Management.
Ring widths, scans of samples, and ancillary data from Sequoia sempervirens (coast redwood) trees and stumps at Fort Ross and Gualala, sampled for dendroseismology in 2021–2024
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Sequoia sempervirens (coast redwood) trees were sampled for a dendroseismological investigation along the North Coast Section of the San Andreas Fault, and the data were fully analyzed, interpreted, and discussed in a journal article and supplemental material (Carroll et al., in review). Here, were provide data associated with this work: 1200 dpi resolution images of tree cores and stumps, raw ring width measurements for living trees and stumps with associated crossdating categories, standard tree and location chronologies with sample depths, and descriptions of tree cores. Please refer to the journal article and supplemental material for full details, supporting material, and context. Tree ring samples were collected at two locations: Fort Ross Historic State Park (Fort Ross) and Gualala Redwood Timber Company (Gualala). Eleven living trees (8 at Fort Ross, 3 at Gualala) were climbed with ropes, and 5-mm-diameter increment cores were collected at various positions on the main and reiterated trunks. Skilled sawyers took plunge cuts from 23 Sequoia stumps at Gualala, sometimes taking multiple pieces from one stump. Ring series were scanned at 1200 dpi. Child folders include scans of living tree and stump samples. Pencil marks guide crossdating, but final dating is expressed in the ring width files with associated crossdating categories. Ring widths were measured to 0.001 mm precision using WinDendro software (v.2009b, Régent Instruments Inc., Québec, Canada). Crossdating proceeded using a multi-pronged approach combining visual assessment of marker years with correlation analysis, fully detailed in the journal article. Due to the complex nature of crossdating Sequoia, every year was assigned a level of crossdating confidence following previously defined protocol (Carroll et al., 2014; Carroll and Sillett, 2023) with categories of high and moderate confidence to distinguish sections with some ambiguity. For example, moderate confidence applied when missing ring(s) were known, but the placement may be in several positions. Undated rings were either 1) bound by dated rings, allowing the number of missing rings and total radial growth to be determined or 2) not bound by dated rings, as may occur for inner rings. File “Tree Ring Widths_Carroll et al 2025.xlsx” lists ring width measurements in microns for 126 series from 11 living Sequoia trees at Fort Ross and Gualala. Crossdating categories are color coded, and these categories must be considered for proper use of the data. Measurements with no highlighting are dated with high confidence, measurements highlighted in orange are dated with moderate confidence, measurements highlighted in red are undated. Undated rings do not correspond with calendar years. Zeros (0s) reflect missing rings. Zeros (0s) in undated (red) sections reflect a known number of missing rings but unknown annual placement. Green highlighting reflects broken or crumbly sections. File "TreeRingWidths.json" provides these same data in a more easily machine-readable format. File “Tree Core Logsheet_Carroll et al 2025.csv” lists descriptions associated with these series. File “Stump Ring Widths_Carroll et al 2025.xlsx” lists ring width measurements in microns for 37 sections from 23 Sequoia stumps at Gualala. Crossdating categories are color coded, and these categories must be considered for proper use of the data. Dated or partially dated paths are listed in columns B to S and correspond with calendar years in the first column. Measurements with no highlighting are dated with high confidence, measurements highlighted in orange are dated with moderate confidence, measurements highlighted in red are undated (and do not correspond with calendar years). Zeros (0s) in undated (red) sections reflect a known number of missing rings but unknown annual placement. Completely undated paths are listed in columns U to AM, do not correspond with calendar years, and are listed in descending order (from outer ring toward center).
Assessment of Giant Sequoia Mortality and Regeneration within Burned Groves in Sequoia and Kings Canyon National Parks - dataset as delivered
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Provided are data containing condition assessments on individual giant sequoia (Sequoiadendron giganteum; SEGI) stems and post-fire regeneration counts within Board Camp, Suwanee, New Oriole Lake, Homer’s Nose, and a subset of Redwood Mountain and Dillonwood groves of Sequoia and Kings Canyon national parks, respectively. Stem data contain condition-related attributes (e.g., spatial location, diameter breast height, status - live or dead, percent canopy that is live, scorched or torched). Regeneration plots are located using a spatially-balanced sampling design (Generalized Random Tessellation Stratified - 'GRTS'). Each regeneration plot is a fixed radius circle (11.35 meters or 17.84 meters) and contain count data of giant sequoia seedlings.
Assessment of Giant Sequoia Mortality and Regeneration within Burned Groves in Sequoia and Kings Canyon National Parks (ver. 3.0, September 2024)
공공데이터포털
Provided are data containing condition assessments on individual giant sequoia (Sequoiadendron giganteum; SEGI) stems and post-fire regeneration counts within Board Camp, Suwanee, New Oriole Lake, Homer’s Nose, and a subset of Redwood Mountain and Dillonwood groves of Sequoia and Kings Canyon national parks, respectively. Stem data contain condition-related attributes (e.g., spatial location, diameter breast height, status - live or dead, percent canopy that is live, scorched or torched). Regeneration plots are located using a spatially-balanced sampling design (Generalized Random Tessellation Stratified - 'GRTS'). Each regeneration plot is a fixed radius circle (11.35 meters or 17.84 meters) and contain count data of giant sequoia seedlings.
Assessment of Giant Sequoia Mortality and Regeneration within Burned Groves in Sequoia and Kings Canyon National Parks (ver. 3.0, September 2024)
공공데이터포털
Provided are data containing condition assessments on individual giant sequoia (Sequoiadendron giganteum; SEGI) stems and post-fire regeneration counts within Board Camp, Suwanee, New Oriole Lake, Homer’s Nose, and a subset of Redwood Mountain and Dillonwood groves of Sequoia and Kings Canyon national parks, respectively. Stem data contain condition-related attributes (e.g., spatial location, diameter breast height, status - live or dead, percent canopy that is live, scorched or torched). Regeneration plots are located using a spatially-balanced sampling design (Generalized Random Tessellation Stratified - 'GRTS'). Each regeneration plot is a fixed radius circle (11.35 meters or 17.84 meters) and contain count data of giant sequoia seedlings.
Seedling and tree data from Sequoia National Park and Yosemite National Park
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These tables include data from 25 long-term forest plots located in either Sequoia or Yosemite national park. Trees in these plots (established between 1982 and 2001) are censused annually for mortality and measured for diameter every 4 to 6 years. Plots were mostly 1 hectare (ha) in size (range 0.9 – 2.5 ha) and contained at least two 25 by 25 meter seedling sub-plots to monitor natural seedling recruitment. The largest plot, at 2.5 ha, included four such seedling sub-plots. Each sub-plot was divided into 5 by 5 meter quadrats. In almost all the plots these seedling sub-plots were established in 1999, but four plots (those with names starting with FF) were added to the study in 2002 and seedling data was only available from this date. Seedlings taller than 10 centimeters (which were at least 3 years old) were given numbered tags so that their survival and height class could be recorded individually. If there were more than 20 seedlings per quadrat of a species entering the greater-than-10 centimeters category, a sample of 20 was tagged, but this was unusual. Individual-level mortality and growth could be tracked for these seedlings. In each annual seedling census, the presence of the tagged seedling (live or dead) was recorded and it was assigned to a height category (10-25 cm, 25-50 cm, 50-75 cm, 75-100 cm, and 100-137 cm). Those that grew to 137 centimeters (tall enough to record a diameter-at-breast height (DBH)) were re-tagged as trees. This release contains 2 CSV and 3 TXT files: TaggedSdl.txt, PlotInfogeneral.txt, quadrat_precise.csv, treedata.csv, and treeyears.txt.
Seedling and tree data from Sequoia National Park and Yosemite National Park
공공데이터포털
These tables include data from 25 long-term forest plots located in either Sequoia or Yosemite national park. Trees in these plots (established between 1982 and 2001) are censused annually for mortality and measured for diameter every 4 to 6 years. Plots were mostly 1 hectare (ha) in size (range 0.9 – 2.5 ha) and contained at least two 25 by 25 meter seedling sub-plots to monitor natural seedling recruitment. The largest plot, at 2.5 ha, included four such seedling sub-plots. Each sub-plot was divided into 5 by 5 meter quadrats. In almost all the plots these seedling sub-plots were established in 1999, but four plots (those with names starting with FF) were added to the study in 2002 and seedling data was only available from this date. Seedlings taller than 10 centimeters (which were at least 3 years old) were given numbered tags so that their survival and height class could be recorded individually. If there were more than 20 seedlings per quadrat of a species entering the greater-than-10 centimeters category, a sample of 20 was tagged, but this was unusual. Individual-level mortality and growth could be tracked for these seedlings. In each annual seedling census, the presence of the tagged seedling (live or dead) was recorded and it was assigned to a height category (10-25 cm, 25-50 cm, 50-75 cm, 75-100 cm, and 100-137 cm). Those that grew to 137 centimeters (tall enough to record a diameter-at-breast height (DBH)) were re-tagged as trees. This release contains 2 CSV and 3 TXT files: TaggedSdl.txt, PlotInfogeneral.txt, quadrat_precise.csv, treedata.csv, and treeyears.txt.
Seed and Associated Tree Data from Long Term Research Plots in Sequoia and Yosemite National Parks (ver. 2.0, December 2024)
공공데이터포털
This dataset was used as part of a continent-wide analysis of tree fecundity and its association with climate and tree size. This dataset consists of: plotinfo.csv, which contains basic attribute information for the field plots where the data were collected; seeddata.csv, which contains the data for seeds collected (how many, what type, etc.); trapxycoord.csv, which contains location and identification information for the seed traps used to collect the seeds; treexycoord.csv, which contains location and attribute information for the standing trees in the plot where the seeds were collected; and treedata.csv, which contains data on the size and species of standing trees in the plot where the seeds were collected.