This report documents the status and trends of Cumberland-Piedmont Network (CUPN) National Park Units. They were designed collaboratively between CUPN staff and NatureServe and finalized in 2019.
ABLI - BIRT 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
ABLI - KNOB 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
CARL 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
CHCH - CHIC 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
CHCH - LOOK 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
COWP 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
CUGA 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
FODO - DONE 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
FODO - HEIM 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
GUCO 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
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Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
KIMO 2016
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Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
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Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
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Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
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CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
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High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
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High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
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Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
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Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
LIRI 2016
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Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
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Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
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CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
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High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
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High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
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Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
MACA 2016
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Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
NISI 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
|
CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
RUCA 2016
|
Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
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CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
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Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
SHIL 2016
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Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
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Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
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CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
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High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
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High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
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Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
STRI 2016
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Tree growth rate |
Canopy tree growth (together with mortality rates) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Tree mortality |
Canopy mortality rates (together with tree growth) provide an integrative, quantitative metric of tree health and vitality. Relative basal area growth rate (% basal area / year) of canopy trees is calculated from repeated measurements of bole diameter at breast height (dbh) measurements Annual mortality rate (% stems / year) of canopy trees is also calculated from repeated observation. |
|
Snag abundance |
The CUPN Forest Monitoring Protocol defines snags as lacking any living tissue at or above DBH, are a minimum of 10 cm DBH and lean less than 45º from vertical. Dead trees leaning greater than 45º are treated as coarse woody debris (refer to SOP 6: Tree Measurements). This metric is intended to measure the abundance/volume of snags and determine whether there is a sufficient quantity of snags to support healthy ecosystem function. |
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CWD Volume |
Dead wood, in the form of standing dead trees (snags) and fallen coarse woody debris (CWD) are important structural features of forest stands that provide habitat for wildlife and fungi. This metric assesses the density of snags and volume of CWD in relationship to live tree density and volume. |
|
High priority exotic plant species richness |
This metric assesses the presence of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
High priority exotic plant cover |
This metric assesses the abundance of key invasive exotic plant species within CUPN forested, woodland and successional ecosystems. |
|
Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
This metric assesses the amount of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all oak plus hickory tree saplings (0 - 5 cm dbh ) are totaled across the eight 10 m2 nested subplots. From the total number oak plus hickory tree saplings, the number of oak plus hickory saplings per hectare is calculated. |
|
Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
This metric assesses the proportion of oak and hickory sapling regeneration in the forest understory. Oak – hickory forests might not have adequate advanced regeneration of those saplings to remain oak – hickory forests in the future. All saplings (at least 137 cm tall, and 0 – 10 cm dbh) are tallied by species and size class in eight 10 m2 nested subplots within the larger full 400 m2 plot. Within each forest vegetation monitoring plot, all saplings and all oak plus hickory tree saplings (0 - 5 cm dbh) are totaled across the eight 10 m2 nested subplots. The total number of oak plus hickory tree saplings per hectare is divided by the number of all tree saplings per hectare, the result is expressed as percent. |
2B Tree growth rate |
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2C Tree mortality |
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2D Snag abundance |
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2E CWD Volume |
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3B High priority exotic plant species richness |
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3C High priority exotic plant cover |
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3F Oak sustainability index (only applied to plots of oak-hickory  or ruderal forests) |
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3G Percent of Saplings that are Oak or Hickory (only applied to plots of oak-hickory or ruderal forests) |
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