Abstract:There is a growing demand for reliable information about land cover and land resources. The Norwegian area frame survey of land cover and outfield land resources (AR18X18) is a response to this demand. AR18X18 provides unbiased land cover and land resource statistics and constitutes a baseline for studying changes in outfield land resources in Norway and a framework for a national land resource accounting system for the outfields. The area frame survey uses a systematic sampling technique with 0.9 km 2 sample … Show more
“…The focus on the chosen vegetation type data, DM method, EVs and spatial scale however, provides only a certain part of the challenges involved in DM transferability. Nevertheless, as high quality vegetation maps remain a key tool for nature management [43], and fieldwork mapping is time-consuming and expensive, we need a better understanding of how to model the distribution of vegetation types from existing data, such as area frame surveys [21]. Spatial modelling techniques, such as the DM methods (e.g.…”
Section: Discussionmentioning
confidence: 99%
“…This grid is in accordance with the Norwegian area frame survey of land cover and outfield land resources [21]. The three vegetation types were treated independently throughout the study.…”
Vegetation mapping using field surveys is expensive. Distribution modelling, based on sample surveys, might overcome this challenge. We tested if models trained from sample surveys could be used to predict the distribution of vegetation types in neighbourhood areas, and how reliable the spatial transferability was. We also tested whether we should use ecological dissimilarity or spatial distance to foresee modelling performance. Maximum entropy models were run for three vegetation types based on a vegetation map within a mountain range. Environmental variables were selected backwards, model complexity was kept low. The models are based on points from a small part of each study site, transferred into the entire sites, and then tested for performance. Environmental distance was tested using principle component analysis. All models had high uncorrected AUC values. The ability to predict presences correctly was low. The ability to predict absences correctly was high. The ability to transfer the distribution model depended on environmental distance, not spatial distance.
“…The focus on the chosen vegetation type data, DM method, EVs and spatial scale however, provides only a certain part of the challenges involved in DM transferability. Nevertheless, as high quality vegetation maps remain a key tool for nature management [43], and fieldwork mapping is time-consuming and expensive, we need a better understanding of how to model the distribution of vegetation types from existing data, such as area frame surveys [21]. Spatial modelling techniques, such as the DM methods (e.g.…”
Section: Discussionmentioning
confidence: 99%
“…This grid is in accordance with the Norwegian area frame survey of land cover and outfield land resources [21]. The three vegetation types were treated independently throughout the study.…”
Vegetation mapping using field surveys is expensive. Distribution modelling, based on sample surveys, might overcome this challenge. We tested if models trained from sample surveys could be used to predict the distribution of vegetation types in neighbourhood areas, and how reliable the spatial transferability was. We also tested whether we should use ecological dissimilarity or spatial distance to foresee modelling performance. Maximum entropy models were run for three vegetation types based on a vegetation map within a mountain range. Environmental variables were selected backwards, model complexity was kept low. The models are based on points from a small part of each study site, transferred into the entire sites, and then tested for performance. Environmental distance was tested using principle component analysis. All models had high uncorrected AUC values. The ability to predict presences correctly was low. The ability to predict absences correctly was high. The ability to transfer the distribution model depended on environmental distance, not spatial distance.
“…RS‐based maps can be obtained for the entire landmass of the world, but are burdened with inherent limitations, e.g., on the number of types into which vegetation or land cover can be correctly classified (Franklin & Wulder, ). RS‐based maps are therefore typically used when broad‐scale or coarse patterns are required (Achard, Eva, Mayaux, Stibig, & Belward, ; Bartholome & Belward, ; Tuanmu & Jetz, ), while RS data have so far not proven useful when higher thematic accuracy is required, e.g., for many research and management purposes (Bekkby, Rinde, Erikstad, & Bakkestuen, ; Strand, ). In order to meet the increasing demand for land use and land cover information, the European Statistical Agency initiated the LUCAS (Land Use/Cover Agricultural Survey) program, organised as a sample‐based area frame field survey, to obtain area‐representative data (Eurostat, ).…”
Aim
Many countries lack informative, high‐resolution, wall‐to‐wall vegetation or land cover maps. Such maps are useful for land use and nature management, and for input to regional climate and hydrological models. Land cover maps based on remote sensing data typically lack the required ecological information, whereas traditional field‐based mapping is too expensive to be carried out over large areas. In this study, we therefore explore the extent to which distribution modelling (DM) methods are useful for predicting the current distribution of vegetation types (VT) on a national scale.
Location
Mainland Norway, covering ca. 324,000 km2.
Methods
We used presence/absence data for 31 different VTs, mapped wall‐to‐wall in an area frame survey with 1081 rectangular plots of 0.9 km2. Distribution models for each VT were obtained by logistic generalised linear modelling, using stepwise forward selection with an F‐ratio test. A total of 116 explanatory variables, recorded in 100 m × 100 m grid cells, were used. The 31 models were evaluated by applying the AUC criterion to an independent evaluation dataset.
Results
Twenty‐one of the 31 models had AUC values higher than 0.8. The highest AUC value (0.989) was obtained for Poor/rich broadleaf deciduous forest, whereas the lowest AUC (0.671) was obtained for Lichen and heather spruce forest. Overall, we found that rare VTs are predicted better than common ones, and coastal VTs are predicted better than inland ones.
Conclusions
Our study establishes DM as a viable tool for spatial prediction of aggregated species‐based entities such as VTs on a regional scale and at a fine (100 m) spatial resolution, provided relevant predictor variables are available. We discuss the potential uses of distribution models in utilizing large‐scale international vegetation surveys. We also argue that predictions from such models may improve parameterisation of vegetation distribution in earth system models.
“…A wall-to-wall vegetation map of each PSU was compiled according to the system for vegetation and land cover mapping at intermediate scale (1: 20,000-1:50,000) (abbreviated VK50) (Rekdal & Larsson 2005). The VK50 nomenclature consists of 45 vegetation types and 9 other land cover types, and operates with a minimum mapping unit (MMU) of 1000 m 2 for rare or especially important vegetation types and 5000 m 2 for common types (Strand 2013). The description of the vegetation classes is mainly based on physiognomy, as it appears from dominant species or species groups, and secondly by characteristic species.…”
Section: Vegetation Mapping Systemsmentioning
confidence: 99%
“…Data from the area frame survey of land cover and outfield land resources in Norway -the 'Norwegian land cover and land resources of the outfields' (Areal regnskap for utmark, abbreviated to AR18X18) (Strand 2013) -were used as a 'test bed'. The survey combines a wall-to-wall mapping of vegetation types with point sampling of detailed vegetation subtypes in the same area.…”
Detailed descriptions of individual vegetation types shown on vegetation maps can improve the ways in which the composition and spatial structure within the types are understood. The authors therefore examined dwarf shrub heath, a vegetation type covering large areas and found in many parts of the Norwegian mountains. They used data from point samples obtained in a wall-to-wall area frame survey. The point sampling method provided data that gave a good understanding of the composition and structure of the vegetation type, but also revealed a difference between variation within the vegetation type itself (intra-class variation) and variation resulting from the inclusion of other types of vegetation inside the map polygons (landscape variation). Intra-class variation reflected differences in the botanical composition of the vegetation type itself, whereas landscape variation represented differences in the land-cover composition of the broader landscape in which the vegetation type was found. Both types of variation were related to environmental gradients. The authors conclude that integrated point sampling method is an efficient way to achieve increased understanding of the content of a vegetation map and can be implemented as a supporting activity during a survey.
ARTICLE HISTORY
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