Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway

Positive and negative effects on ecosystem services from plantation forestry in Europe have led to conflicts regarding non-native tree species. Sitka spruce (Picea sitchensis (Bong.) Carr.) is the most common plantation species in northwest Europe, covering 1.3 Mha. In costal Norway, Sitka spruce wa...

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Published in:Forests
Main Authors: Per Holm Nygaard, Bernt-Håvard Øyen
Format: Article in Journal/Newspaper
Language:English
Published: MDPI AG 2017
Subjects:
Online Access:https://doi.org/10.3390/f8010024
https://doaj.org/article/abfde05d362e49ebb6af8f2950f02182
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spelling ftdoajarticles:oai:doaj.org/article:abfde05d362e49ebb6af8f2950f02182 2023-05-15T17:39:23+02:00 Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway Per Holm Nygaard Bernt-Håvard Øyen 2017-01-01T00:00:00Z https://doi.org/10.3390/f8010024 https://doaj.org/article/abfde05d362e49ebb6af8f2950f02182 EN eng MDPI AG http://www.mdpi.com/1999-4907/8/1/24 https://doaj.org/toc/1999-4907 1999-4907 doi:10.3390/f8010024 https://doaj.org/article/abfde05d362e49ebb6af8f2950f02182 Forests, Vol 8, Iss 1, p 24 (2017) Sitka spruce non-native spread distances invasive species habitat invasibility management Plant ecology QK900-989 article 2017 ftdoajarticles https://doi.org/10.3390/f8010024 2022-12-30T23:13:51Z Positive and negative effects on ecosystem services from plantation forestry in Europe have led to conflicts regarding non-native tree species. Sitka spruce (Picea sitchensis (Bong.) Carr.) is the most common plantation species in northwest Europe, covering 1.3 Mha. In costal Norway, Sitka spruce was intentionally introduced and is currently occupying about 50,000 ha. Sitka spruce was blacklisted in Norway in 2012, mainly based on the risk for invasive spreading, but little quantitative documentation exists on spread. Here we quantify spread from plantations into abandoned heathland and pastures in thirteen sites where natural regeneration occurs. Spread distances and zero-square distributions related to the nearest edge of the parent stand were fitted by use of Weibull. The median expansion rate was 0.8 m·year−1 in north Norway and 4.4 m·year−1 in west Norway. The maximum establishment distance measured was 996 m. A peak in sapling density occurred within 50 m from the edge, and there was a general decrease in saplings with increasing distance. Conversely, increase in zero-squares percentages occurred with increasing distance. We argue that inclusion of abundance in assessing spread is necessary to define invasiveness. Based on spread models and prevailing forestry practices we recommend that the establishment of new Sitka spruce plantations within 200 m of protected areas should be avoided. Article in Journal/Newspaper North Norway Directory of Open Access Journals: DOAJ Articles Norway Carr ENVELOPE(130.717,130.717,-66.117,-66.117) Forests 8 1 24
institution Open Polar
collection Directory of Open Access Journals: DOAJ Articles
op_collection_id ftdoajarticles
language English
topic Sitka spruce
non-native
spread distances
invasive species
habitat invasibility
management
Plant ecology
QK900-989
spellingShingle Sitka spruce
non-native
spread distances
invasive species
habitat invasibility
management
Plant ecology
QK900-989
Per Holm Nygaard
Bernt-Håvard Øyen
Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
topic_facet Sitka spruce
non-native
spread distances
invasive species
habitat invasibility
management
Plant ecology
QK900-989
description Positive and negative effects on ecosystem services from plantation forestry in Europe have led to conflicts regarding non-native tree species. Sitka spruce (Picea sitchensis (Bong.) Carr.) is the most common plantation species in northwest Europe, covering 1.3 Mha. In costal Norway, Sitka spruce was intentionally introduced and is currently occupying about 50,000 ha. Sitka spruce was blacklisted in Norway in 2012, mainly based on the risk for invasive spreading, but little quantitative documentation exists on spread. Here we quantify spread from plantations into abandoned heathland and pastures in thirteen sites where natural regeneration occurs. Spread distances and zero-square distributions related to the nearest edge of the parent stand were fitted by use of Weibull. The median expansion rate was 0.8 m·year−1 in north Norway and 4.4 m·year−1 in west Norway. The maximum establishment distance measured was 996 m. A peak in sapling density occurred within 50 m from the edge, and there was a general decrease in saplings with increasing distance. Conversely, increase in zero-squares percentages occurred with increasing distance. We argue that inclusion of abundance in assessing spread is necessary to define invasiveness. Based on spread models and prevailing forestry practices we recommend that the establishment of new Sitka spruce plantations within 200 m of protected areas should be avoided.
format Article in Journal/Newspaper
author Per Holm Nygaard
Bernt-Håvard Øyen
author_facet Per Holm Nygaard
Bernt-Håvard Øyen
author_sort Per Holm Nygaard
title Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
title_short Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
title_full Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
title_fullStr Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
title_full_unstemmed Spread of the Introduced Sitka Spruce (Picea sitchensis) in Coastal Norway
title_sort spread of the introduced sitka spruce (picea sitchensis) in coastal norway
publisher MDPI AG
publishDate 2017
url https://doi.org/10.3390/f8010024
https://doaj.org/article/abfde05d362e49ebb6af8f2950f02182
long_lat ENVELOPE(130.717,130.717,-66.117,-66.117)
geographic Norway
Carr
geographic_facet Norway
Carr
genre North Norway
genre_facet North Norway
op_source Forests, Vol 8, Iss 1, p 24 (2017)
op_relation http://www.mdpi.com/1999-4907/8/1/24
https://doaj.org/toc/1999-4907
1999-4907
doi:10.3390/f8010024
https://doaj.org/article/abfde05d362e49ebb6af8f2950f02182
op_doi https://doi.org/10.3390/f8010024
container_title Forests
container_volume 8
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container_start_page 24
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