Mohonk Preserve Forest Health Monitoring Data

Enregistrements de données

Les données de cette ressource occurrence ont été publiées sous forme d'une Archive Darwin Core (Darwin Core Archive ou DwC-A), le format standard pour partager des données de biodiversité en tant qu'ensemble d'un ou plusieurs tableurs de données. Le tableur de données du cœur de standard (core) contient 4 680 enregistrements.

Cet IPT archive les données et sert donc de dépôt de données. Les données et métadonnées de la ressource sont disponibles pour téléchargement dans la section téléchargements. Le tableau des versions liste les autres versions de chaque ressource rendues disponibles de façon publique et permet de tracer les modifications apportées à la ressource au fil du temps.

Versions

Le tableau ci-dessous n'affiche que les versions publiées de la ressource accessibles publiquement.

Comment citer

Les chercheurs doivent citer cette ressource comme suit:

Garretson A, , Napoli M, Feldsine N, Long E C, Ferreri C T, Erle J C, Quintana Vargas M, Green R, Chinkan C (2022): Mohonk Preserve Forest Health Monitoring Data. v1.1. Mohonk Preserve. Dataset/Occurrence. https://bison.usgs.gov/ipt/resource?r=mohonk-forest-health&v=1.1

Droits

Les chercheurs doivent respecter la déclaration de droits suivante:

L’éditeur et détenteur des droits de cette ressource est Mohonk Preserve. En vertu de la loi, l'éditeur a abandonné ses droits par rapport à ces données et les a dédié au Domaine Public (CC0 1.0). Les utilisateurs peuvent copier, modifier, distribuer et utiliser ces travaux, incluant des utilisations commerciales, sans aucune restriction.

Enregistrement GBIF

Cette ressource a été enregistrée sur le portail GBIF, et possède l'UUID GBIF suivante : 062f3445-944a-4fd4-915a-ed1a1109cf04.  Mohonk Preserve publie cette ressource, et est enregistré dans le GBIF comme éditeur de données avec l'approbation du GBIF-US.

Mots-clé

Occurrence

Contacts

Alexis Garretson

• Fournisseur Des Métadonnées ●
• Créateur ●
• Personne De Contact

Research Associate

Mohonk Preserve

alexis@garretson.net

https://alexis-catherine.github.io/

http://orcid.org/0000-0002-7260-0131

Mohonk Preserve Director of Conservation Science

• Créateur

Director of Conservation Science

Mohonk Preserve

research@mohonkpreserve.org

Megan Napoli

• Fournisseur Des Métadonnées ●
• Créateur ●
• Personne De Contact

Research Ecologist

Mohonk Preserve

mnapoli@mohonkpreserve.org

http://orcid.org/0000-0003-2390-6545

Natalie Feldsine

• Créateur

Research Collection and Citizen Science Coordinator

Mohonk Preserve

http://orcid.org/0000-0003-4331-3042

Elizabeth C Long

• Créateur

Former Director of Conservation Science

Mohonk Preserve

http://orcid.org/0000-0002-7410-5548

Catherine T Ferreri

• Créateur

Field Technician

Mohonk Preserve

Jacob C Erle

• Créateur

Field Technician

Mohonk Preserve

Miriam Quintana Vargas

• Créateur

Field Technician

Mohonk Preserve

Ralph Green

• Créateur

Field Technician

Mohonk Preserve

http://orcid.org/0000-0001-8597-5955

Chris Chinkan

• Créateur

Field Technician

Mohonk Preserve

http://orcid.org/0000-0002-4249-8885

Director of Conservation Science Mohonk Preserve

• Personne De Contact

Director of Conservation Science

Mohonk Preserve

research@mohonkpreserve.org

Mohonk Preserve

• Utilisateur

Mohonk Preserve

Mohonk Preserve

PO Box 715

New Paltz

New York

US

https://www.mohonkpreserve.org/

Couverture géographique

Data were collected from 24 forest plots on Mohonk Preserve property in the Shawangunk Ridge of New Paltz, NY, USA

Couverture temporelle

Méthodes d'échantillonnage

Site Selection & Plot Establishment Prerequisites for plot sites included: 1) plot center is ≥ 15 m from the Preserve boundary, a public road, a carriage road, a perennial stream, a water body, a mowed area, or any obstacle that would interfere with plot establishment; 2) plot is not be located on top of earthworks in cultural area; 3) plot is located in an area of < 30 degree/ 60% slope; and 4) plot is located in an area that is not a safety hazard (e.g. area free of unstable dead trees, pits, slick or unstable surfaces, etc.). Once the plot center was established in a suitable area, the plot boundaries were carefully measured creating a 15 x 15 meters (m) plot (see schematic). Each corner (upper right, UR; upper left, UL; back right, BR; and back left, BL) and mid-point were labeled (upper center, UC; middle right, MR; middle left, ML; and back center, BC). Plot Details Within the 15 x 15 m plot, GPS coordinates, observers, and time range of sampling was recorded. Aspect was recorded in degrees. Downhill and uphill slope of plot was recorded in degrees at plot points UC and BC. The physiographic class (measures of Xeric, Mesic, or Hydric) and the stand structure (Even-aged, Multi-aged, Mosaic, Early successional, or Woodland) were categorized and stunted woodland assessment was recorded (yes or no). Canopy live crown closure of the plot was estimated (<10%, 10-25%, 25-50%, 50-75%, >75%). Percent cover classes (0, 1-5, 5-25, 25-50, 50-75, 75-95, 95-100%) for live vegetation was estimated for cover low (< 0.5 m), cover mid (0.5 – 2 m), and cover high (2 -5 m). Using the same percent cover ranges, cover was also estimated for trampled vegetation, bare soil, exposed bedrock or large rocks (>10cm), bryophyte (non-vascular plant foliage within the plot in the ground layer only; <0.5m), and lichen. Water on the plot was recorded (none, permanent stream/pond, swamp/bog/marsh, ditch/canal, temporary stream, flood zone, vernal pool, or other). Average stand height (m) of plot trees was determined by averaging the height of 3 trees (mix of dominant and co-dominant) using a clinometer. Microtopography presence or absence was recorded. Presence or absence of deer browseline was recorded and assessment of browse impact in the plot was completed using an index of 1 – 5 (1 = very low, 2 = low, 3 = moderate, 4 = high, 5 = very high). Potential plot disturbances to flora within the plot and severity of disturbance were assessed. Tree Sampling Within the 15 x 15 m plot, each tree species >10 cm diameter at breast height (DBH; measured at height of 1.37 m) was tagged numerically with aluminum tree tags. The plot was broken into 4 quarters labeled A-D (A: Northeast; B: Southeast; C: Southwest; D: Northwest). The following parameters were measured for each tree: species identification; DBH (cm); status of life (Alive or Dead) and growth of the tree (Standing, Leaning, Fallen, Broken); tree crown position in the canopy (Dominant, Co-dominant, Intermediate, Sub-canopy, Gap-exploiter, and Open-grown); tree condition (Insect damage, Large dead branches, Small or Large cavities, Burl/galls, Vines in canopy, or if no condition = Healthy); foliage condition (Holes, Necrosis, Chlorosis, Wilting, Leaf loss) and condition severity estimation for both the total foliage and the surface area of the affected foliage (1-10, 10-50, 50-90, 90-100%). For trees that were dead the state of decay was categorized (1 = very little decay, 2 = little decay, 3 = moderate decay, 4= advanced decay, 5= very advanced decay). It was recorded if the tree was forked (yes or no) as well as if the tree was unusual where the DBH was measured (yes or no). For applicable species (Eastern hemlock, Hemlock Woolly Adelgid; American beech, Beech Bark Disease; and White ash, Emerald Ash Borer) an index was estimated for severity of infection (1 = no sign of infection, 2 = some impact, 3 = moderate impact, 4 = severe impact). Regeneration Plot Sampling Three 2 m radius regeneration plots were established four meters from the plot center in the direction of upper right (UR), upper left (UL), and back center (BC), (see schematic). Within each regeneration plot all seedling, sapling, and shrub species were identified. Seedings are defined as live juvenile trees that are ≥15 cm tall and <1 cm DBH. Saplings are defined as juvenile trees ≥ 1 cm and < 10 cm DBH. Shrubs are defined as woody, sub-canopy species (woody vines included) and ≥ 30 cm tall. The number of living stems for each individual species were recorded within these categories. For each seedling species height (cm) was measured in ranges (15-30, 30-100, 100-150, and >150). For each shrub species percent cover (%) was estimated (<1, 1-5, 5-10, 10-25, 25-50, 50-75, 75-95, 95-100). For each sapling, the DBH was measured (cm). Coarse Woody Debris Sampling From the plot center, three 15m transects were established to run through BR, BL, and UC to record the presence or absence of coarse woody debris (CWD; falled trees or any wood ≥10 cm diameter), (see schematic). If CWD was present, the following parameters were recorded: distance (m) to CWD from the plot center, category identification (Deciduous, Coniferous, or Unknown), species identification (if possible), diameter (cm), total length (m), state of decay (1 = very little decay, 2 = little decay, 3 = moderate decay, 4= advanced decay, 5= very advanced decay), whether the CWD was hollow (yes or no), and whether the CWD crossed multiple transects ( yes or no; if yes then the two pieces of CWD were labeled A and B). Quadrat Sampling At the plot’s four corners (BR, BL, UL, UR) and four mid points (UC, UR, MR, ML) a 1m2 quadrat was placed to sample site condition, percent cover, and species richness (see schematic). Each quadrat was recorded to be sampled and trampled (0 = no, 1 = yes). Within the quadrat percent cover (0, <1, 1-2, 2-5, 5-10, 10-25, 25-50, 50-75, 75-95, 95-100%) was estimated for the following categories: bare soil, exposed rock, woody stem, CWD, sphagnum moss, bryophyte (all non-sphagnum), and lichen. Additionally, percent cover (using the same percent ranges) was estimated for all individual species of plants and then each plant was further categorized (Woody = all woody angiosperm and gymnosperm species, Forb = all non-woody angiosperm species, Fern = all vascular plants that reproduce via spores and have neither seeds nor flowers, Sedge = all species in the family Cyperaceae, Grass = all species in the family Poaceae, Rush = all species in the family Juncaceae, and Germinate = woody species with ≤ 2 cotyledons). Species Richness of Plot All flora within a plot was recorded. Each plant was identified to species, genus, or family and categorized (Woody = all woody angiosperm and gymnosperm species, Forb = all non-woody angiosperm species, Fern = all vascular plants that reproduce via spores and have neither seeds nor flowers, Sedge = all species in the family Cyperaceae, Grass = all species in the family Poaceae, Rush = all species in the family Juncaceae, and Germinate = woody species with ≤ 2 cotyledons).

Description des étapes de la méthode:

1. Site Selection & Plot Establishment Prerequisites for plot sites included: 1) plot center is ≥ 15 m from the Preserve boundary, a public road, a carriage road, a perennial stream, a water body, a mowed area, or any obstacle that would interfere with plot establishment; 2) plot is not be located on top of earthworks in cultural area; 3) plot is located in an area of < 30 degree/ 60% slope; and 4) plot is located in an area that is not a safety hazard (e.g. area free of unstable dead trees, pits, slick or unstable surfaces, etc.). Once the plot center was established in a suitable area, the plot boundaries were carefully measured creating a 15 x 15 meters (m) plot (see schematic). Each corner (upper right, UR; upper left, UL; back right, BR; and back left, BL) and mid-point were labeled (upper center, UC; middle right, MR; middle left, ML; and back center, BC). Plot Details Within the 15 x 15 m plot, GPS coordinates, observers, and time range of sampling was recorded. Aspect was recorded in degrees. Downhill and uphill slope of plot was recorded in degrees at plot points UC and BC. The physiographic class (measures of Xeric, Mesic, or Hydric) and the stand structure (Even-aged, Multi-aged, Mosaic, Early successional, or Woodland) were categorized and stunted woodland assessment was recorded (yes or no). Canopy live crown closure of the plot was estimated (<10%, 10-25%, 25-50%, 50-75%, >75%). Percent cover classes (0, 1-5, 5-25, 25-50, 50-75, 75-95, 95-100%) for live vegetation was estimated for cover low (< 0.5 m), cover mid (0.5 – 2 m), and cover high (2 -5 m). Using the same percent cover ranges, cover was also estimated for trampled vegetation, bare soil, exposed bedrock or large rocks (>10cm), bryophyte (non-vascular plant foliage within the plot in the ground layer only; <0.5m), and lichen. Water on the plot was recorded (none, permanent stream/pond, swamp/bog/marsh, ditch/canal, temporary stream, flood zone, vernal pool, or other). Average stand height (m) of plot trees was determined by averaging the height of 3 trees (mix of dominant and co-dominant) using a clinometer. Microtopography presence or absence was recorded. Presence or absence of deer browseline was recorded and assessment of browse impact in the plot was completed using an index of 1 – 5 (1 = very low, 2 = low, 3 = moderate, 4 = high, 5 = very high). Potential plot disturbances to flora within the plot and severity of disturbance were assessed. Tree Sampling Within the 15 x 15 m plot, each tree species >10 cm diameter at breast height (DBH; measured at height of 1.37 m) was tagged numerically with aluminum tree tags. The plot was broken into 4 quarters labeled A-D (A: Northeast; B: Southeast; C: Southwest; D: Northwest). The following parameters were measured for each tree: species identification; DBH (cm); status of life (Alive or Dead) and growth of the tree (Standing, Leaning, Fallen, Broken); tree crown position in the canopy (Dominant, Co-dominant, Intermediate, Sub-canopy, Gap-exploiter, and Open-grown); tree condition (Insect damage, Large dead branches, Small or Large cavities, Burl/galls, Vines in canopy, or if no condition = Healthy); foliage condition (Holes, Necrosis, Chlorosis, Wilting, Leaf loss) and condition severity estimation for both the total foliage and the surface area of the affected foliage (1-10, 10-50, 50-90, 90-100%). For trees that were dead the state of decay was categorized (1 = very little decay, 2 = little decay, 3 = moderate decay, 4= advanced decay, 5= very advanced decay). It was recorded if the tree was forked (yes or no) as well as if the tree was unusual where the DBH was measured (yes or no). For applicable species (Eastern hemlock, Hemlock Woolly Adelgid; American beech, Beech Bark Disease; and White ash, Emerald Ash Borer) an index was estimated for severity of infection (1 = no sign of infection, 2 = some impact, 3 = moderate impact, 4 = severe impact). Regeneration Plot Sampling Three 2 m radius regeneration plots were established four meters from the plot center in the direction of upper right (UR), upper left (UL), and back center (BC), (see schematic). Within each regeneration plot all seedling, sapling, and shrub species were identified. Seedings are defined as live juvenile trees that are ≥15 cm tall and <1 cm DBH. Saplings are defined as juvenile trees ≥ 1 cm and < 10 cm DBH. Shrubs are defined as woody, sub-canopy species (woody vines included) and ≥ 30 cm tall. The number of living stems for each individual species were recorded within these categories. For each seedling species height (cm) was measured in ranges (15-30, 30-100, 100-150, and >150). For each shrub species percent cover (%) was estimated (<1, 1-5, 5-10, 10-25, 25-50, 50-75, 75-95, 95-100). For each sapling, the DBH was measured (cm).
2. Species Richness of Plot All flora within a plot was recorded. Each plant was identified to species, genus, or family and categorized (Woody = all woody angiosperm and gymnosperm species, Forb = all non-woody angiosperm species, Fern = all vascular plants that reproduce via spores and have neither seeds nor flowers, Sedge = all species in the family Cyperaceae, Grass = all species in the family Poaceae, Rush = all species in the family Juncaceae, and Germinate = woody species with ≤ 2 cotyledons).
3. Quadrat Sampling At the plot’s four corners (BR, BL, UL, UR) and four mid points (UC, UR, MR, ML) a 1m2 quadrat was placed to sample site condition, percent cover, and species richness (see schematic). Each quadrat was recorded to be sampled and trampled (0 = no, 1 = yes). Within the quadrat percent cover (0, <1, 1-2, 2-5, 5-10, 10-25, 25-50, 50-75, 75-95, 95-100%) was estimated for the following categories: bare soil, exposed rock, woody stem, CWD, sphagnum moss, bryophyte (all non-sphagnum), and lichen. Additionally, percent cover (using the same percent ranges) was estimated for all individual species of plants and then each plant was further categorized (Woody = all woody angiosperm and gymnosperm species, Forb = all non-woody angiosperm species, Fern = all vascular plants that reproduce via spores and have neither seeds nor flowers, Sedge = all species in the family Cyperaceae, Grass = all species in the family Poaceae, Rush = all species in the family Juncaceae, and Germinate = woody species with ≤ 2 cotyledons).
4. Coarse Woody Debris Sampling From the plot center, three 15m transects were established to run through BR, BL, and UC to record the presence or absence of coarse woody debris (CWD; falled trees or any wood ≥10 cm diameter), (see schematic). If CWD was present, the following parameters were recorded: distance (m) to CWD from the plot center, category identification (Deciduous, Coniferous, or Unknown), species identification (if possible), diameter (cm), total length (m), state of decay (1 = very little decay, 2 = little decay, 3 = moderate decay, 4= advanced decay, 5= very advanced decay), whether the CWD was hollow (yes or no), and whether the CWD crossed multiple transects ( yes or no; if yes then the two pieces of CWD were labeled A and B).

Métadonnées additionnelles