HjerkinnPRO restoration of removed roads

Sampling event
最新版本 published by Norwegian Institute for Nature Research on 6月 12, 2023 Norwegian Institute for Nature Research
發布日期:
2023年6月12日
授權條款:
CC-BY 4.0

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說明

HjerkinnPRO: restoration of removed roads. The roads at the Hjerkinn military training area in Dovrefjell, Central Norway, were constructed during the 1960s by adding crushed stone and gravel on top of undisturbed terrain and vegetation. In 2002, a pilot project removing 1.2 km of roads was initiated. An ecological monitoring program was established to evaluate the recovery of the vegetation following removal using different restoration treatments. The pilot project was established along three road sections (sites). To remove the roads in August 2002, a shell-proof excavator first removed the crushed stone down to the original terrain surface. Then the upper soil layer was stirred down to 20 cm as the excavator grab lifted the compressed surface. Four restoration treatments were tested: (1) Soil preparation by stirring as described above (Soil treatment), (2) Fertilization, where 20 g/m2 of granulated N-K-P fertilizer was added to the stirred topsoil, (3) Fertilization and seeding, where 7 g/m2 of commercial seeds of Festuca rubra were added to the stirred and fertilized topsoil. In addition, a fourth restoration treatment, in which the added gravel was not removed, but the topsoil and gravel were stirred together, was tested (No removal of gravel) at two of the three sites. At all sites, vegetation turfs (≤ 1 m2 in size) were transplanted from nearby road margins, at a 5‒10 m planting distance.

資料紀錄

此資源sampling event的資料已發佈為達爾文核心集檔案(DwC-A),其以一或多組資料表構成分享生物多樣性資料的標準格式。 核心資料表包含 246 筆紀錄。

亦存在 2 筆延伸集的資料表。延伸集中的紀錄補充核心集中紀錄的額外資訊。 每個延伸集資料表中資料筆數顯示如下。

Event (核心)
246
Occurrence 
2433
MeasurementOrFacts 
1144

此 IPT 存放資料以提供資料儲存庫服務。資料與資源的詮釋資料可由「下載」單元下載。「版本」表格列出此資源的其它公開版本,以便利追蹤其隨時間的變更。

版本

以下的表格只顯示可公開存取資源的已發布版本。

如何引用

研究者應依照以下指示引用此資源。:

Evju M (2023): HjerkinnPRO restoration of removed roads. v1.0. Norwegian Institute for Nature Research. Dataset/Samplingevent. https://ipt.nina.no/resource?r=hjerkinnpro&v=1.0

權利

研究者應尊重以下權利聲明。:

此資料的發布者及權利單位為 Norwegian Institute for Nature Research。 This work is licensed under a Creative Commons Attribution (CC-BY 4.0) License.

GBIF 註冊

此資源已向GBIF註冊,並指定以下之GBIF UUID: f70bd131-1dff-41a0-b0b3-b5373062239e。  Norwegian Institute for Nature Research 發佈此資源,並經由GBIF Norway同意向GBIF註冊成為資料發佈者。

關鍵字

Samplingevent

聯絡資訊

Marianne Evju
  • 出處
Senior Researcher
Norwegian Institute for Nature Research
NO
Dagmar Hagen
  • 連絡人
Senior Researcher
Norwegian Institute for Nature Research
NO

地理涵蓋範圍

Hjerkinn, Innlandet, Norway

界定座標範圍 緯度南界 經度西界 [62.235, 9.475], 緯度北界 經度東界 [62.24, 9.525]

分類群涵蓋範圍

無相關描述

Kingdom Plantae (vascular plants)

時間涵蓋範圍

彙整期間 2004-2019

計畫資料

In 1999 The Norwegian Parliament closed down the existing military training area of Hjerkinn in the Dovrefjell area, as part of a larger decision on reorganising and updating military training facilities in southern Norway. The decision specified that the closure included restoration of the area for civilian use, future protection and “back to original” ecosystem and landscape quality.

計畫名稱 HjerkinnPRO: Restoration of Hjerkinn militaring training area, Dovrefjell
經費來源 Hjerkinn PRO is funded by Norwegian Ministry of Defence and operated by Norwegian Defence Estate Agency. Research and monitoring was supported by strategic funding to NINA from The Research Council of Norway, project no. 160022/F40.
研究區域描述 The former Hjerkinn military training area is situated at Dovrefjell, Central Norway, between 1000 and 1700 m a.s.l., in one of the last largely intact high mountain ecosystems in Europe. The area covers 165 km2 and was used for military purposes from 1923 to 2008. The study sites were situated in dry and medium-dry alpine heath vegetation dominated by lichens, dwarf shrubs, and some graminoids and forbs.
研究設計描述 The road section in each site was divided into three (four at the two sites where the No removal treatment was included) approximately 100 m long blocks, and restoration treatments were assigned randomly to the blocks. To monitor effects of restoration treatments, 55 permanent plots of 0.5 × 0.5 m were established in 2004, five for each restoration treatment at each site. The plots were randomly placed within blocks and were permanently marked with aluminum poles in the corners and marker sticks, and location was recorded with a handheld GPS. In 2014, we established 15 monitoring plots in intact vegetation in close proximity (10−20 m) to the road section sites to collect data on reference vegetation, i.e., the target for the restoration. At each site, a block of 100 m2 was established in undisturbed vegetation next to the road, and five plots were placed randomly within the block. The vegetation in the treatment plots were monitored in 2004, 2009, 2014, and 2019, i.e. two, seven, 12, and 17 years after restoration, respectively, and reference plots were monitored in 2014 and 2019

參與計畫的人員:

Dagmar Hagen
Marianne Evju

取樣方法

In each plot we recorded the abundance of all vascular plants as sub-plot frequency (i.e., presence-absence in 16 subplots per plot). In addition, we recorded total vegetation cover (visual estimate of percent cover, continuous scale), including cover of bryophytes and lichens.

研究範圍 Three sites (road sections) covering 1.2 km of roads. The road section in each site was divided into three (four at the two sites where the No removal treatment was included) approximately 100 m long blocks, and restoration treatments were assigned randomly to the blocks. To monitor effects of restoration treatments, 55 permanent plots of 0.5 × 0.5 m were established in 2004, five for each restoration treatment at each site (Figure 2). The plots were randomly placed within blocks and were permanently marked with aluminum poles in the corners and marker sticks, and location was recorded with a handheld GPS. In 2014, we established 15 monitoring plots in intact vegetation in close proximity (10−20 m) to the road section sites to collect data on reference vegetation, i.e., the target for the restoration. At each site, a block of 100 m2 was established in undisturbed vegetation next to the road, and five plots were placed randomly within the block. The vegetation in the treatment plots were monitored in 2004, 2009, 2014, and 2019, i.e. two, seven, 12, and 17 years after restoration, respectively, and reference plots were monitored in 2014 and 2019.

方法步驟描述:

  1. NA

引用文獻

  1. Hagen, D., Evju, M., Henriksen, P.S., Solli, S., Erikstad, L. & Bartlett, J. 2022. From military training area to National Park over 20 years: Indicators for outcome evaluation in a large-scale restoration project in alpine Norway. Journal for Nature Conservation 66: 126125. https://doi.org/10.1016/j.jnc.2021.126125
  2. Hagen, D. & Evju, M. 2013. Using short-term monitoring data to achieve goals in a large-scale restoration. Ecology and Society 18(3): 29. https://doi.org/10.5751/es-05769-180329
  3. Evju, M., Hagen, D., Olsen, C. & Mehlhoop, A. C. 2023. Recovery of vegetation on former alpine roads: how long does it take? Nordic Journal of Botany. https://doi.org/10.1111/njb.03984

額外的詮釋資料