Disturbance history affects dead wood abundance in Newfoundland boreal forests

Dead wood (dead standing tree (snag), woody debris (WD), buried wood, and stump) abundance was estimated in Newfoundland balsam fir (Abies balsamea (L.) Mill.) and black spruce (Picea mariana (Mill.) BSP) forests regrown following natural and anthropogenic disturbances. Although harvesting left few...

Full description

Bibliographic Details
Published in:Canadian Journal of Forest Research
Main Author: Moroni, Martin T
Format: Article in Journal/Newspaper
Language:English
Published: Canadian Science Publishing 2006
Subjects:
Online Access:http://dx.doi.org/10.1139/x06-195
http://www.nrcresearchpress.com/doi/pdf/10.1139/x06-195
id crcansciencepubl:10.1139/x06-195
record_format openpolar
spelling crcansciencepubl:10.1139/x06-195 2024-09-15T18:19:58+00:00 Disturbance history affects dead wood abundance in Newfoundland boreal forests Moroni, Martin T 2006 http://dx.doi.org/10.1139/x06-195 http://www.nrcresearchpress.com/doi/pdf/10.1139/x06-195 en eng Canadian Science Publishing http://www.nrcresearchpress.com/page/about/CorporateTextAndDataMining Canadian Journal of Forest Research volume 36, issue 12, page 3194-3208 ISSN 0045-5067 1208-6037 journal-article 2006 crcansciencepubl https://doi.org/10.1139/x06-195 2024-08-01T04:10:01Z Dead wood (dead standing tree (snag), woody debris (WD), buried wood, and stump) abundance was estimated in Newfoundland balsam fir (Abies balsamea (L.) Mill.) and black spruce (Picea mariana (Mill.) BSP) forests regrown following natural and anthropogenic disturbances. Although harvesting left few snags standing, natural disturbances generated many snags. Most were still standing 2 years after natural disturbance, but almost all had fallen after 33–34 years. Snag abundance then increased in stands aged 86–109 years. Natural disturbances generated little WD 0–2 years following disturbance. Harvesting, however, immediately generated large amounts of WD. Thirty-two to forty-one years following disturbance, most harvesting slash had decomposed, but naturally disturbed sites had large amounts of WD from collapsed snags. Harvested sites contained less WD 32–72 years following disturbance than naturally disturbed sites. Amounts of WD in black spruce regrown following harvesting and fire converged 63–72 years following disturbance, despite significant initial differences in WD quantities, diameter distribution, and decay classes. Abundance of WD increased from sites regrown 32–72 years following disturbance to older sites. Precommercial thinning had a minor impact on dead wood stocks. Stumps contained minor biomass. Buried wood and WD biomass were equivalent at some sites. Article in Journal/Newspaper Newfoundland Canadian Science Publishing Canadian Journal of Forest Research 36 12 3194 3208
institution Open Polar
collection Canadian Science Publishing
op_collection_id crcansciencepubl
language English
description Dead wood (dead standing tree (snag), woody debris (WD), buried wood, and stump) abundance was estimated in Newfoundland balsam fir (Abies balsamea (L.) Mill.) and black spruce (Picea mariana (Mill.) BSP) forests regrown following natural and anthropogenic disturbances. Although harvesting left few snags standing, natural disturbances generated many snags. Most were still standing 2 years after natural disturbance, but almost all had fallen after 33–34 years. Snag abundance then increased in stands aged 86–109 years. Natural disturbances generated little WD 0–2 years following disturbance. Harvesting, however, immediately generated large amounts of WD. Thirty-two to forty-one years following disturbance, most harvesting slash had decomposed, but naturally disturbed sites had large amounts of WD from collapsed snags. Harvested sites contained less WD 32–72 years following disturbance than naturally disturbed sites. Amounts of WD in black spruce regrown following harvesting and fire converged 63–72 years following disturbance, despite significant initial differences in WD quantities, diameter distribution, and decay classes. Abundance of WD increased from sites regrown 32–72 years following disturbance to older sites. Precommercial thinning had a minor impact on dead wood stocks. Stumps contained minor biomass. Buried wood and WD biomass were equivalent at some sites.
format Article in Journal/Newspaper
author Moroni, Martin T
spellingShingle Moroni, Martin T
Disturbance history affects dead wood abundance in Newfoundland boreal forests
author_facet Moroni, Martin T
author_sort Moroni, Martin T
title Disturbance history affects dead wood abundance in Newfoundland boreal forests
title_short Disturbance history affects dead wood abundance in Newfoundland boreal forests
title_full Disturbance history affects dead wood abundance in Newfoundland boreal forests
title_fullStr Disturbance history affects dead wood abundance in Newfoundland boreal forests
title_full_unstemmed Disturbance history affects dead wood abundance in Newfoundland boreal forests
title_sort disturbance history affects dead wood abundance in newfoundland boreal forests
publisher Canadian Science Publishing
publishDate 2006
url http://dx.doi.org/10.1139/x06-195
http://www.nrcresearchpress.com/doi/pdf/10.1139/x06-195
genre Newfoundland
genre_facet Newfoundland
op_source Canadian Journal of Forest Research
volume 36, issue 12, page 3194-3208
ISSN 0045-5067 1208-6037
op_rights http://www.nrcresearchpress.com/page/about/CorporateTextAndDataMining
op_doi https://doi.org/10.1139/x06-195
container_title Canadian Journal of Forest Research
container_volume 36
container_issue 12
container_start_page 3194
op_container_end_page 3208
_version_ 1810458318205878272