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Inventory
Topic
(12)
All areas classified as shrub forest according to the NFI forest definition.
(36)
Area with clearly visible traces on the forest floor from timber harvesting vehicles such as tractors, forwarders and harvesters.
(12'707)
All areas designated as forest according to the NFI forest definition. The forest definition includes shrub forest. The target variable "forest area" is also used when classifying the total area as forest or non-forest.
(4)
Forest area stocked with young forest plants between 10 and 129 cm in length, having a specific type of damage. The target variable 469 and 468 are used to calculate the quotient target variable «forest area acc. to type of damage (young forest plants ≤129 cm) divided by forest area with damage assessment (young forest plants ≤129 cm)». The latter corresponds to the mean damage percentage of the forest area stocked with young forest plants between 10 and 129 cm in length. An independent mean damage percentage is calculated for each listed damage type, as young forest plants can have several types of damage simultaneously. Depending on the inventory, either only trees (NFI3, NFI5) or trees and selected shrub species (NFI4) were recorded as young trees.
(4)
Forest area stocked with young forest plants from 130 cm in length up to 11.9 cm in diameter at breast height (DBH), having a specific type of damage. The target variable 469 and 468 are used to calculate the quotient target variable «forest area acc. to type of damage (young forest plants≥130 cm) divided by forest area with damage assessment (young forest plants≥130 cm)». The latter corresponds to the mean damage percentage of the forest area stocked with young forest plants from 130 cm in length up to 11.9 cm DBH. An independent mean damage percentage is calculated for each listed damage type, as young forest plants can have several types of damage simultaneously. Depending on the inventory, either only trees (NFI3, NFI5) or trees and selected shrub species (NFI4) were recorded as young trees.
(36)
Forest area classified according to its functions (including "no special forest function"), as determined in the interview survey with the local forest services. A forest area can fulfil several forest functions at the same time, and can thus contribute to the forest area of several forest functions.
(7)
Forest area subject to the natural hazard processes rockfall, avalanche, hillslope debris flow/landslide and channel processes within the protection forest designated by the cantons according to the harmonised criteria of SilvaProtect-CH as of 2022. Since a protection forest can provide protection against various natural hazard processes at the same time, it can contribute to the forest area of several dfiferent processes. No natural hazard processes are shown for Canton Aargau because the protection forest there had not yet been designated in the reference year (2022).
(18)
Area of forest with recreational uses such as walking, hiking, jogging, cycling, biking, skiing and snowboarding, cross-country skiing, snowshoeing, horse-riding, camping, other activities, or no activities. Since different recreational activities may take place in a forest at the same time, this forest may contribute to the area of several recreation types.
(42)
Forest area in which specific measures for the conservation or promotion of biodiversity have been implemented since the last inventory. Only measures that have been explicitly subsidised as 'biodiversity' measures are taken into account. Since several biodiversity measures may be implemented in a forest area at the same time, this area may contribute to the total area of several different biodiversity measures.
(32)
Ratio of the different damage events (e.g. wind, insects) which led to damage gaps. The ratio is determined on the basis of those damage gaps that account for at least 10% of the interpretation area (50 × 50 m) and on which, according to the information provided by the local forest services, only one damage event occurred. The target value thus allows comparisons of inventories from NFI3 onwards.
(615)
Sum of the stem cross-sectional areas at a height of 1.3 m (level for measuring diameter at breast height [dbh]) of living trees and shrubs (standing and lying) with a dbh ≥12 cm.
(96)
Sum of the stem cross-sectional areas at a height of 1.3 m (level for measuring diameter at breast height [dbh]) of all dead trees and shrubs (standing and lying) with a dbh ≥12 cm.
(16)
Sum of the stem cross-sectional areas at a height of 1.3 m (level for measuring diameter at breast height [dbh]) of all dead trees and shrubs (standing and lying) with a dbh ≥12 cm according to the method used in NFI1. In NFI1, dead trees were only included if their wood was still usable.
(150)
Sum of the stem cross-sectional areas at a height of 1.3 m (level for measuring diameter at breast height [dbh]) of all living and dead trees and shrubs (standing and lying) with a dbh ≥12 cm. The total basal area corresponds to the sum of the basal area and the deadwood basal area.
(12)
Sum of the stem cross-sectional areas at a height of 1.3 m (level for measuring diameter at breast height [dbh]) of all living and dead trees and shrubs (standing and lying) with a dbh ≥12 cm according to the method used in NFI1. In NFI1, dead trees were only included if their wood was still usable. The total basal area NFI1 corresponds to the sum of the basal area and the deadwood basal area NFI1.
(24)
Dry weight (mass) of standing and lying deadwood, determined with the help of the species- and decomposition-dependent wood densities of the following components: 1) stemwood, merchantable branchwood, branch brushwood and roots of standing and lying dead trees and shrubs with a diameter at breast height (dbh) ≥12 cm without stem breakage; 2) stemwood of the still standing stump, branch brushwood and roots of standing dead trees and shrubs ≥12 cm dbh with stem breakage and 3) LIS-deadwood, i.e. the lying deadwood with a diameter ≥7 cm (merchantable wood without merchantable wood pieces in heaps of branches), which cannot be assigned to a tree or shrub ≥12 cm dbh.
(24)
Dry weight (mass) of the so-called LIS deadwood, i.e. lying deadwood with a diameter ≥7 cm (merchantable wood; excluding merchantable wood pieces in heaps of branches), which cannot be assigned to a tree or shrub with a diameter at breast height (dbh) ≥12 cm. The mass is determined with the help of species- and decomposition-dependent wood densities.
(72)
Dry weight (mass) of living trees and shrubs with a diameter at breast height (dbh) ≥12 cm. The tree parts considered are: the roots, stemwood, branchwood and needles/leaves.
(36)
Dry weight (mass) of the aboveground parts of living trees and shrubs with a diameter at breast height (dbh) ≥12 cm. The tree parts included are: stemwood, branchwood and needles/leaves.
(24)
Dry weight (mass) of lying dead trees and shrubs with a diameter at breast height (dbh) ≥12 cm. This mass is determined with the help of species- and decomposition-dependent wood densities from the tree parts: roots, stemwood and, depending on the degree of decomposition, also the merchantable branchwood.
(24)
Dry weight (mass) of standing dead trees and shrubs with a diameter at breast height (dbh) ≥12 cm. This mass is determined with the help of species- and decomposition-dependent wood densities from the tree parts roots, stemwood and, depending on the degree of decomposition, also the merchantable branchwood.
(63)
Dry weight (mass) of the stumps ≥7 cm in diameter, i.e. the aboveground, woody parts of trees or shrubs below the felling cut or (in the case of natural decay) below the break surface. The maximum height of a stump is 1.3 m; if it is >1.3 m, it is treated as a snag. The mass is determined on the basis of species- and decomposition-dependent wood densities.
(32)
Dry weight (mass) of branches <7 cm with bark from living trees and shrubs with a diameter at breast height (dbh) ≥12 cm.
(32)
Dry weight (mass) of branches with a diameter ≥7 cm from living trees and shrubs with a diameter at breast height (dbh) ≥12 cm.
(32)
Dry weight (mass) of the needles and leaves of the living trees and shrubs with a diameter at breast height (dbh) ≥12 cm.
(40)
Dry weight (mass) of the belowground part (roots) of living trees and shrubs with a diameter at breast height (dbh) ≥12 cm. The dimensions of the roots are determined according to Zell and Wutzler.
(48)
Dry weight (mass) of the stemwood with bark of the living trees and shrubs with a diameter at breast height (dbh) ≥12 cm.
(24)
Number of microhabitats on standing living trees and shrubs ≥12 cm in diameter at breast height (dbh). Microhabitats are defined as: fungal fruiting bodies; areas on the stem where moss, lichen or ivy covers more than 10%; woodpecker breeding cavity; shallow tree cavity; wide crack; bark pocket; fresh break; dendrotelm; canker or burr; buttress-root concavity; deep tree cavity; area of exposed bare wood larger than a hand; stag-headedness; resin flow; insect damage (foot of trunk /trunk/stem); >20% dead branches.
(27)
Number of standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) on which a microhabitat was found. Since various microhabitats at a time may be found on the same tree, the tree may contribute to the number of stems (standing-living) of several different microhabitats. Microhabitats are defined as: fungal fruiting bodies; areas on the stem where moss, lichen or ivy covers more than 10%; woodpecker breeding cavity; shallow tree cavity; wide crack; bark pocket; fresh break; dendrotelm; canker or burr; buttress-root concavity; deep tree cavity; area of exposed bare wood larger than a hand; stag-headedness; resin flow; insect damage (foot of trunk /trunk/stem); >20% dead branches.
(26)
Wood volume of the stem without bark and stump ≥7 cm in diameter (limit for merchantable wood) of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm that were harvested between two inventories and were alive during the earlier inventory.
(404)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that were harvested between two inventories.
(372)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that were harvested, died or disappeared between two inventories.
(20)
Volume of stemwood with bark of all trees and shrubs ≥12 cm diameter at breast height (dbh) that were felled, died or disappeared between two inventories with the cause of death given.
(12)
Wood volume of branches ≥7cm in diameter with bark (limit for merchantable wood of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm that were harvested between two inventories and were alive during the earlier inventory.
(12)
Wood volume of the stem without bark and stump and the branches with bark ≥7 cm in diameter (limit for merchantable wood) of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm that were harvested between two inventories and were alive during the earlier inventory. The target variable "merchantable timber harvested" is an approximation of the amount of usable wood. It comes closest to the volume of timber harvested recorded in the Swiss Forest Statistics.
(156)
Volume of stemwood with bark of all trees and shrubs ≥12 cm diameter at breast height (dbh) that were removed from the forest because of damage that occurred between two inventories rather than due to silvicultural planning. The characteristic is derived at the sample plot level from the fellings of the tally trees and the proportion of sanitary/salvage fellings (according to information from the foresters).
(24)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that were not removed from the forest as part of silvicultural planning, but because they had been damaged by insects between two inventories. The variable is derived at the sample plot level from the harvested tally trees and the proportion of sanitary/salvage fellings (according to information provided by the foresters).
(24)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that were not removed from the forest as part of silvicultural planning, but because they had been damaged by wind between two inventories. The variable is derived at the sample plot level from the harvested tally trees and the proportion of sanitary/salvage fellings (according to information provided by the foresters).
(27)
Length of the forest edge calculated on the basis of the forest boundary lines determined in the aerial photo.
(180)
Proportion of the forest edge with a certain characteristic (e.g. structural diversity, diversity of woody species or forest edge structure) in the total forest edge. The forest edge is the border or transition area between the vegetation form of forest and other elements of the landscape.
(857)
Proportion of sample plots that meet the forest definition of NFI, i.e. are covered by "forest without shrub forest" or "shrub forest".
(584)
Increase in stemwood volume between two inventories of all surviving trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark, the stemwood volume of all ingrowing trees and shrubs with bark, and the modelled increase in the stemwood volume of the losses with bark during half the inventory period.
(388)
Increase in the stemwood volume between two inventories of all surviving trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark, the stemwood volume of all ingrowing trees and shrubs with bark, and the modelled increase in the stemwood volume of the losses with bark during half the inventory period minus the volume of mortality. The net increment thus corresponds to the increment (=gross increment) minus the volume of mortality.
(2)
Die gewichtete ZG-Nr. 336 berücksichtigt nicht alle im Datensatz vorhandenen Strassen-/Streckenabschnitte mit ihrer jeweils erfassten vollen Länge. Je nach Lage können Strassen-/Streckenabschnitte z.B. im freien Feld weggelassen, oder nur zu 50% ihrer Länge berücksichtigt werden. Zu den LFI-Waldstrassen zählen nur die zum Zeitpunkt der LFI-Erhebung in den aktuellen Erschliessungsdaten explizit verfügbaren Strassen-/Streckenabschnitte. Die in der LFA.WASTRA-Tabellenbeschreibung genannten Bedingungen müssen bei der Verwendung der ZG eingehalten werden.
(3)
Die gewichtete ZG-Nr. 345 berücksichtigt die vorhandenen Strassen-/Streckenabschnitte, die im Schutzwaldperimeter und gleichzeitig innerhalb des Waldes der LFI-Waldmaske liegen. Der Schutzwaldperimeter wurde vom BAFU als GIS-Datei zur Verfügung gestellt (Stand 2013).
Die Strassen-/Streckenabschnitte werden nur teilweise mit ihrer jeweils erfassten vollen Länge berücksichtigt, sondern sind gewichtet. Je nach Lage können Strassen-/Streckenabschnitte z.B. im freien Feld weggelassen, oder nur zu 50% ihrer Länge berücksichtigt werden. Die verwendete flächendeckende Walddefinition orientiert sich an der Waldmaske auf der Basis des Vegetationshöhenmodells und ist nicht identisch mit den Waldkriterien und Punktentscheiden des LFI und/oder mit den Waldkriterien des Schutzwaldes. Zu den LFI4-Waldstrassen im Schutzwald zählen nur die zum Zeitpunkt der LFI4-Erhebung explizit verfügbaren Strassen-/Streckenabschnitte.
Die in der LFA.WASTRA-Tabellenbeschreibung genannten Bedingungen müssen bei der Verwendung der ZG eingehalten werden.
(372)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that were harvested, died or disappeared between two inventories.
(20)
Volume of stemwood with bark of all trees and shrubs ≥12 cm diameter at breast height (dbh) that were felled, died or disappeared between two inventories with the cause of death given.
(304)
Stemwood volume of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm with bark that died naturally between two inventories (e.g. due to windthrow or insects) or disappeared (e.g. due to avalanches), but that were not harvested. Mortality is the sum of natural losses and the remaining mortality.
(184)
Number of stems of dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm.
(12)
Number of stems of dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm recorded according to the NFI1 method. In NFI1, dead trees were only included if their wood was still usable. In addition, lying but still green trees were classified as deadwood.
(1'993)
Number of stems of living trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm.
(24)
Number of living conifers and conifers ≥10 cm in height and ≤11.9 cm in diameter at breast height (dbh).
(72)
Number of stems of conifers and broadleaves 10 to 129 cm in height on which browsing on the shoot from the previous year was detected. Since a different method was used for assessing browsing traces in NFI2, the browsing intensity was overestimated in comparison with in the inventories from NFI4 on. Thus, only increases in browsing intensity can be clearly determined in comparisons with NFI2. For a reliable estimate, at least 30 individuals per estimated value (table cell) should have been assessed for browsing. Therefore, the corresponding tables with the target variable "Number of trees assessed for browsing (no extrapolation)" should also be consulted.
(48)
Actual number of conifers and broadleaves assessed for browsing during the field survey (no extrapolation).
(52)
Measure of the density of a stocking calculated from the number of stems per hectare (in NFI trees and shrubs with a diameter at breast height [dbh] ≥12 cm) and the mean diameter. With a callipering threshold of 0 cm, the SDI is largely independent of the site quality, tree species composition and stand age.
(1'442)
Number of stems of all living and dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm. The total number of stems is the sum of the number of stems and the number of deadwood stems.
(102)
Number of stems of all living and dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm according to the method used in NFI1. In NFI1, dead trees were only included if their wood was still usable. The total number of stems NFI1 is the sum of the number of stems and the number of deadwood stems NFI1.
(126)
Number of living and dead trees and shrubs (standing and lying) ≥12 cm diameter at breast heigth (dbh) with damage. Only the two most important forms of damage to a tree are recorded. Since a tree may be damaged in different ways, it may contribute more than once to the total number of stems with the two most important forms of damage.
(144)
Stemwood volume of standing dead trees and shrubs with a diameter at breast height (dbh) ≥12 cm less the volume of broken stem pieces, plus the volume of lying deadwood ≥7 cm in diameter (merchantable wood) without merchantable pieces in heaps of branches.
(200)
Volume of lying deadwood ≥7 cm in diameter (merchantable wood) without merchantable wood pieces in heaps of branches.
(84)
Volume of lying deadwood ≥7 cm in diameter (merchantable wood), including merchantable pieces of wood in piles of branches.
(63)
Volume of stumps ≥7 cm in diameter, i.e. the aboveground, woody parts of trees or shrubs below the felling cut or (in the case of natural decay) below the break surface. The maximum height of a stump is 1.3 m; if it is >1.3 m, it is treated as a snag.
(3'117)
Stemwood volume of living trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark.
(1'318)
Stemwood volume of all living and dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark. The total wood volume is the sum of the growing stock and deadwood volumes.
(72)
Stemwood volume of all living and dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark according to the method used in NFI1. In NFI1, dead trees were only included if their wood was still usable.
(174)
Wood volume of the stem without bark or stump ≥7 cm in diameter (limit for merchantable wood) of all trees and shrubs with a diameter at breast height (dbh) ≥12 cm, based on the stem-form functions according to Kaufmann (2001). The definition of the assortments is based on the 2010 edition of the Swiss trading customs for raw timber (HG 2010).
(982)
Volume of stemwood of all dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark.
(52)
Stemwood volume of all dead trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark recorded according to the NFI1 method. In NFI1, dead trees were only included if their wood was still usable. In addition, lying but still green trees were classified as deadwood.
(48)
Measure for the ecological assessment of forest stands, derived from the number of woody species with a diameter at breast height (dbh) ≥12 cm and the occurrence of woody species of special ecological significance (willows, birches, alders, native poplars, oaks, chestnut, cherry, wild fruit and Sorbus species) in the upper layer.
(12)
Number of tree and shrub species with a diameter at breast height (dbh) ≥12 cm within the 200 m² circle on the sample plot.
(40)
Number of species of trees and shrubs that occur within the 200 m² circle on the sample plot with at least one living individual ≥40 cm high.
Classification
(10)
Horizontal distance that the timber travels on a road with limited truck drivability to the point of sale (timber yard or railway station) in four classes. Restricted truck access means that the road cannot be used by trucks with fewer than 4 axles due to permanent bottlenecks or places with a load capacity of less than 28 tonnes. Reference: Forest Service Survey (MID 3060: Vortransportlinie)
(223)
Altitude above sea level in classes of 200 m. Reference: Digital height model DHM 25 from Swisstopo
(641)
Altitude above sea level in classes of 400 m. Reference: Digital height model DHM 25 from Swisstopo
(574)
Altitudinal vegetation belts in the system used in the guidelines for monitoring the sustainability and performance of protection forests (NaiS; Frehner et al. 2005) – in ten classes, whereby the classes «hyperinsubric», «colline» and «colline with beech» and «lower and upper montane» only occur in the Southern Alps (S), the classes «submontane», «lower montane», «upper montane» only in the Northern Alps (N) and the classes «high montane», «subalpine» and «upper subalpine» on both sides of the Alps. The information is based on the altitudinal vegetation belts determined by experts (accessible forest sample plots of NFI4 on the 1.4-km network; Arge Frehner et al. 2020), as well as on the altitudinal vegetation belts modelled for the period 1981-2010 (other sample plots; Zischg et al. 2021). n/a: located above the forest boundary modelled by Zischg et al. and sometimes in the area of lakes, which were relatively roughly cut out by Zischg et al.
(296)
Altitudinal vegetation belts in the system used in the guidelines for monitoring the sustainability and performance of protection forests (NaiS; Frehner et al. 2005), reduced to three classes. The variable represents a simplification of the NaiS altititudinal vegetation belts in six classes (NAISHSTKOMB6KL) in which the class «hyperinsubric and colline» is mearged with «submontane» to form the class «hyperinsubric, colline, submontane», the class «lower and upper montane» with «high montane» to form the class «montane» and the class «subalpine» with «upper subalpine» to form the class «subalpine». The information is based on the altitudinal vegetation belts determined by experts (accessible forest sample plots of NFI4 on the 1.4-km network; Arge Frehner et al. 2020), as well as on the altitudinal vegetation belts modelled for the period 1981-2010 (other sample plots; Zischg et al. 2021). n/a: located above the forest boundary modelled by Zischg et al. and sometimes in the area of lakes, which were relatively roughly cut out by Zischg et al.
(4'157)
Altitudinal vegetation belts in the system used in the guidelines for monitoring the sustainability and performance of protection forests (NaiS; Frehner et al. 2005), reduced to six classes. The variable represents a simplification of the NaiS altitudinal vegetation belts with ten classes (NAISHSTKOMB) in which the classes «hyperinsubric» and «colline» are merged with «colline with beech» to form the class «hyperinsubric and colline» and the class «lower montane» with «upper montane» and «lower/upper montane» to form the class «lower and upper montane». The information is based on the altitudinal vegetation belts determined by experts (accessible forest sample plots of NFI4 on the 1.4-km network; Arge Frehner et al. 2020), as well as on the altitudinal vegetation belts modelled for the period 1981-2010 (other sample plots; Zischg et al. 2021). n/a: located above the forest boundary modelled by Zischg et al. and sometimes in the area of lakes, which were relatively roughly cut out by Zischg et al.
(20)
Sample plots classified: «no», «one», «two» or «more than two» red wood ant-heaps in the 500 m² circle. Reference: Field Survey (MID 837: Ameisenhaufennummer)
(324)
Sample plots without/with gaps ≥100 m² from canopy edge to canopy edge that intersect with the interpretation area (50 × 50 m), classified according to the area of the largest gap into five classes. Reference: aerial photo interpretation
(210)
Aspect, classified into the following five classes: North, East, South, West and indeterminate. «Indeterminate» means that the slope is ≤10%. Reference: Field Survey (MID 191: Azimut der Exposition)
(96)
Aspect, classified into the following nine classes: North, North-East, East, South-East, South, South-West, West, North-West and indeterminate. «Indeterminate» means that the slope is ≤10%. Reference: Field Survey (MID 191: Azimut der Exposition)
(180)
Basal area of standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) per hectare – in four classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(42)
Type of subsidised measure implemented since the last Inventory as part of the biodiversity promotion programme. Reference: Forest Service Survey (MID 2016: Biodiversitätsmassnahmen)
(140)
Ecological value of the forest as a habitat for animals and plants – in three classes. Its value as a biotope is based on the three indicators «naturalness of the proportion of conifers», «diversity of woody species» and «structural diversity».
(10)
Obstruction directly at the forest edge that makes it difficult or impossible for humans or animals to enter or leave the forest or restricts the spread of the shrub belt or herbaceous fringe - in ten classes. Reference: Field Survey (MID 982: Art der Waldrandbegrenzung)
(32)
Cause of the damage gap, e.g. storm, drought, insect or fungal infestation or timber harvesting. Reference: Forest Service Survey (MID 600: Art der Schadenflächen)
(63)
Cause of damage to trees and shrubs ≥12 cm in diameter at breast height (dbh) – in ten classes. Eight of these classes focus exclusively on standing living trees and shrubs with dbh ≥12 cm, while one class applies to lying living trees and shrubs with dbh ≥12 cm, and one to dead trees and shrubs with dbh ≥12 cm. Reference: Field Survey (MID 1029: Baumschadenursache, MID 1018: Baumzustand)
(20)
Reason why trees and shrubs ≥12 cm in diameter at breast height (dbh) have died or disappeared since the last Inventory. Reference: Forest Service Survey (MID 2046: Absterbegrund - toter/fehlender Probebaum)
(24)
Type of certificate: FSC and/or PEFC (NFI4, NFI5) or FSC and/or Q (PEFC) (NFI3). Reference: Forest Service Survey (MID 602: Zertifizierungs-Label)
(3'447)
Type of trees and shrubs ≥12 cm in diameter at breast height (dbh) in two classes (conifers or broadleaves). Reference: Field Survey (MID 50: Baumart)
(438)
Measure of inter-tree crowding of the tree crowns in a stand. Reference: Field Survey (MID 266: Schlussgrad)
(24)
Size of the adjacent areas on which the trees were so severely damaged during an event (e.g. storm, drought, insect or fungal infestation, or timber harvest) that they died immediately or are most likely to soon die – in five classes..Reference: Field Survey (MID 996: Fläche des Schadens am Probeflächenzentrum), together with Forest Service Survey (MID 600: Art der Schadenflächen)
(4)
Damage to young forest plants 10-129 cm in length. Reference: Field Survey (MID 127: Gipfeldürre, MID 174: Verbiss des Leittriebes, MID 977: Fegeschaden, MID 987: Schälschaden, MID 184: Krankheit; MID 183: Holzereischaden, MID 185: anderer Schaden)
(4)
Damage to young forest plants ≥130 cm in length and ≤11.9 cm in diameter at breast height (dbh). Browsing is not assessed on young forest plants ≥ 130 cm, but only on those ≤129 cm (see classification variable «Damage to young forest plants (≤129 cm)» (2980; JWSCHADENKL). Reference: Field Survey (MID 127: Gipfeldürre, MID 977: Fegeschaden, MID 987: Schälschaden, MID 184: Krankheit; MID 183: Holzereischaden, MID 185: anderer Schaden)
(40)
Proportion of bark cover on dead trees and shrubs (standing and lying) ≥12 cm in diameter at breast height (dbh) – in three classes. Reference: Field Survey (MID 418: Totholz - Rindendeckung)
(32)
Number of shrubs ≥10 cm in length growing on a lying dead tree or shrub ≥12 cm in diameter at breast height (dbh) – in five classes. Reference: Field Survey (MID 425: Strauchpflanzen auf Totholz)
(9)
Species group (conifers or broadleaves) of lying deadwood. Reference: Field Survey (MID 907: LIS-Totholz – Laub- oder Nadelholz)
(76)
Stage of wood decay in dead trees and shrubs (standing and lying) ≥12 cm in diameter at breast height (dbh) – in three classes. Reference: Field Survey (MID 419: Totholz - Festigkeit)
(40)
Stage of decay of wood in dead trees and shrubs (standing and lying) ≥12 cm in diameter at breast height (dbh) – in five classes. Reference: Field Survey (MID 419: Totholz - Festigkeit)
(32)
Number of young broadleaves or conifers ≥10 cm growing on a lying dead tree or shrub ≥12 cm in diameter at breast height (dbh) – in three classes. Reference: Field Survey (MID 426: Verjüngung auf Totholz)
(567)
Proportion of the ground area covered by tree crowns according to the aerial photo interpretation – in five 20-percent classes. The percentage is calculated using the 25 grid points on the interpretation area (50 × 50 m). Reference: aerial photo interpretation
(288)
Proportion of the ground area that is covered by established regeneration, i.e. by living coniferous and broadleaved trees ≥1.3 m in height and 11.9 cm in diameter at breast height (dbh). Reference: Field Survey (MID 273: Deckungsgrad der gesicherten Verjüngung)
(20)
Proportion of ground area covered by ferns, grasses, herbs, Rubus species, (tall) herbaceous perennials and dwarf shrubs (e.g. vaccinia, Alpenrose or juniper). Reference: Field Survey (MID 278: Bodenvegetations-Deckungsgrad).
(20)
Proportion of the ground area covered by trees and shrubs with a height of 0.5-3.0 m and by branches of taller individuals of the same species in the same area. Reference: Field Survey (MID 277: Strauchschicht-Deckungsgrad)
(20)
Proportion of the ground area covered with berry bushes (blackberry, raspberry, blueberry, cowberry, bog bilberry, and cranberry). Reference: Field Survey (MID 279: Beerensträucher-Deckungsgrad)
(140)
Degree of damage to trees and shrubs ≥12 cm in diameter at breast height (dbh) classified into six classes according to the damage occurred. Reference: Field Survey (MID 1027: Baumschadenart, MID 1018: Baumzustand)
(110)
Degree of damage to forest stands in six classes, derived from the mean degree of damage to trees and shrubs ≥12 cm in diameter at breast height (dbh) weighted with the basal area. Reference: Field Survey (MID 1027: Baumschadenart, MID 1018: Baumzustand)
(877)
Proportions of conifers and broadleaves making up the stand structure, classified according to their proportional basal areas into four classes: pure conifer forest: 91-100 % conifers, mixed conifer forest: 51-90 % conifers, mixed broadleaved forest: 11-50 % conifers and pure broadleaved forest: 0-10 % conifers. Reference: Field Survey (MID 265: Mischungsgrad)
(208)
Proportion of the area covered by regeneration, i.e. broadleaves and conifers ≥10 cm in height and ≤11.9 cm in diameter at breast height (dbh) - in seven classes. The variable has been in use since NFI3 (2004-2006). For comparisons going back to NFI2 (1993-1995), the variable «degree of regeneration cover (6 classes)» can be used. Reference: Field Survey (MID 270: Verjüngungs-Deckungsgrad)
(10)
Density of shelterbelt (forest mantle) and shrub belt with foliage from the ground to a height of 2 m - in four classes. Reference: Field Survey (MID: 43: Waldranddichte)
(837)
Stage of stand development, defined by the dominant diameter at breast height (dbhdom = dbh of the 100 largest [thickest] trees per hectare). Young growth/thicket: dbhdom <12 cm, pole timber: dbhdom 12-30 cm, young timber: dbhdom 31-40 cm, medium timber : dbhdom 41-50 cm, old timber: dbhdom >50 cm, mixed: trees of different development stages, no development stage predominant or groups of different development stages covering < 500 m². Reference: Field Survey (MID 261: Entwicklungsstufe)
(80)
Diameter at breast height (dbh) of trees and shrubs ≥12 cm dbh in the two classes: «≤30 cm dbh» or «>30 cm dbh. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(12)
Diameter at breast height (dbh) of trees and shrubs ≥12 cm – in classes of 20 cm. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(132)
Diameter at breast height (dbh) of trees and shrubs ≥12 cm dbh - in classes of 4 cm. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(588)
Diameter at breast height (dbh) of trees and shrubs ≥12 cm dbh, classified in main diameter classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(880)
Diameter at breast height (dbh) of the trees and shrubs ≥12 cm dbh – in ten classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(77)
Diameter of lying deadwood – in 4 classes. Reference: Field Survey (MID 459: Durchmesser 1, MID 460: Durchmesser 2)
(30)
Ecological value of the forest edge according to the number of woody species present, as well as the weighted proportion of thorny shrubs, short-lived, light-demanding softwoods (birches, alders, poplars and willows) and other ecologically valuable woody species (e.g. oaks and rowan) – in three classes. Reference: Field Survey (MID 568: Pflanzenarten am Waldrand)
(20)
Ecological value of the forest stand according to the number of woody species present, as well as the presence of woody species of special ecological importance (willows, birches, alders, native poplars, native oaks, chestnut, cherry tree, Malus spp., Pyrus spp., Sorbus spp. and Scots pine) in the upper layer – in three classes. Reference: Field Survey (MID 50: Baumart, MID 65: Schicht)
(16)
Indication of whether alien woody species (tree or shrub neophytes) ≥12 cm in diameter at breast height (dbh) dominate the growing stock, i.e. account for at least 50% of the growing stock – in two classes. Reference: Field Survey (MID 50: Baumart, MID 1018: Baumzustand, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(40)
Indication as to whether invasive or non-invasive alien woody species («tree or shrub neophytes») ≥12 cm in diameter at breast height (dbh) dominate the growing stock, i.e. account for at least 50% of the growing stock – in three classes. The classification as «invasive» is based on the 2022 publication «Invasive alien species in Switzerland» of the Federal Office for the Environment (FOEN) (UW-2220-E). Reference: Field Survey (MID 50: Baumart, MID 1018: Baumzustand, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(24)
Indication as to whether introduced woody species (tree- or shrub-like neophytes) ≥12 cm in diameter at breast height (dbh) dominate the growing stock, i.e. account for at least 50% of the growing stock, classified into the three classes: «not dominated by introduced species», «dominated by introduced species other than black locust», «dominated by introduced, invasive black locust». Black locust is the only invasive introduced species that has been recorded separately in all NFI inventories to date. The classification as «invasive» corresponds to the publication «Alien species in Switzerland» of the Federal Office for the Environment (FOEN) from 2022 (UW-2220-E). Reference: Field Survey (MID 50: Baumart, MID 1018: Baumzustand, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(72)
Mean age of the 100 largest standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) per hectare – in five classes. Reference: Field Survey (MID 826: Baumalter)
(60)
Diameter at breast height (dbh) of the 100 largest (thickest) standing living trees and shrubs ≥12 cm dbh per hectare – in eight classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(72)
Mean diameter at breast height (dbh) of the 100 largest standing living trees ≥12 cm in diameter at breast height (dbh) per hectare – in five classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(84)
Location inside or outside the catchment area of a spring whose water is fed either directly and unfiltered into the drinking-water supply, or is used at least temporarily or partially as drinking water for the public. Reference: Forest Service Survey (MID 603: Wald im Einzugsgebiet von gefassten Trinkwasserquellen)
(8)
Sample plots with/without dry stone walls and piles of stones on the interpretation area (50 × 50 m), classified according to the type of objects. Reference: Field Survey (MID 217: Trockenmauer und Steinhaufen)
(10)
Ecological value of the forest edge as a habitat for animals and plants, classified into three classes according to the structural diversity and diversity of woody species along the forest edge. Reference: Field Survey (various attributes)
(40)
Sample plots without/with damage gaps on the interpretation area, and the extent of damage classified into ten classes according to the proportion of the forested interpretation area that is damaged. Reference: Field Survey (MID 601: Ausmass der Schadenfläche)
(10)
Distance - measured horizontally - that the timber is transported from the felling site to a road that is at least 2.50 m wide and dimensioned for an axle load of at least 10 tonnes - in four classes. Any hauling on a road does not count to the extraction distance. Reference: Forest Service Survey (MID 3000: Rückelinie)
(144)
Combination of the 18 groups of NaiS site types, each with a similar objective for the main tree species (NAISGGROB20), into 10 large associations known as «forest formations». *As the characterisation of the site types in the NaiS-NFI project is on a small scale, it is possible that non-forest site types such as meadow, pasture and rock may be present in sample plots that are classified as «forest» in NFI. Similarly, «forest without shrub forest“ may also contain «shrub forest» site types.
(36)
Forest functions of considerable local importance according to forest plans or an assessment by the local forest service. It's possible for there to be several forest functions of considerable local importance at the same time. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'agricultural use' according to forest plans or an assessment by the local forest service. The forest function 'agricultural use' generally includes wooded pastures and nut orchards. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(6)
Presence of the forest function «carbon sink» according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'drinking-water protection' according to forest plans or an assessment by the local forest service. The forest function «drinking-water protection» generally includes groundwater protection zones and drinking-water catchment areas. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'game protection' according to forest plans or an assessment by the local forest service. As a rule, the forest function 'game protection' includes seasonal grazing areas and game reserves. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'landscape protection' according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'military' according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'nature conservation' according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(82)
Presence of the forest function «protection against natural hazards» according to forest plans or an assessment by the local forest service. The term «natural hazards» refers to avalanches, rockfall, landslides, landslides and channel processes. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(110)
Presence of the forest function 'recreation' according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'timber production' according to forest plans or an assessment by the local forest service. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(102)
Presence of the forest function 'windbreak' according to forest plans or an assessment by the local forest service. The forest function 'windbreak' generally includes the forests or forest strips that protect agricultural land against wind. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(96)
Intensity of forest management, classified in three classes according to site quality and the time of the last treatment. Reference: Forest Service Survey (MID 607: Anzahl Jahre seit dem letzten Eingriff); modelled site quality (total growth performance according to Keller 1978)
(22)
Indication as to whether forest planning documents exist at the local level (operational plan, silvicultural project, etc.) and/or at the cantonal level (forest development plan or regional/cantonal forest plan). These documents provide the basis for the forest manager to make silvicultural or operational decisions, irrespective of the year they were produced. Reference: Forest Service Survey (MID 2028: lokale forstliche Planungswerke, MID 803: Stand der Waldentwicklungspläne WEP)
(3)
STRBREITE gibt an, wie breit der betreffende Strecken-/Strassenabschnitt ist. Lastwagenstrassen im Schweizer Wald müssen, um in der Erschliessungserhebung erfasst zu werden, eine Mindestbreite von 2.50 m aufweisen, wobei der Strassenoberbau mindestens für eine Achslast von 10 t ausgelegt sein muss. Im Rahmen der Försterumfrage des LFI4 wurden zusätzliche Informationen erhoben. Dabei steht nicht die lastwagenbefahrbare Strasse nach LFI mit 10 t Achslast und einer Mindestbreite von 2.50 m im Fokus, sondern die für die Holzabfuhr relevante Strasse mit mindestens 3 m Fahrbahnbreite und genügender Tragfähigkeit für Fahrzeuge mit einem Gesamtgewicht ab 26 t.
(722)
Classification of forests into 12 classes («types») according to their development, structure and management. Unlike in the 17-class forest-type classification, in this 12-class classification all development stages (from young growth to timber) are subsumed in the class «uniform high forest». Reference: Field Survey (MID 255: Nutzungskategorie, MID 257: Waldtyp nach Aufnahmeanleitung LFI, MID 260: Waldform, MID 267: Bestandesstruktur, MID 261: Entwicklungsstufe)
(132)
Classification of forests according to their establishment, structure and management into 17 classes («types»). In contrast to the forest typology with 12 classes, the forest typology with 17 classes defines each development stage (young growth to timber) as an individual class. Reference: Field Survey (MID 255: Nutzungskategorie, MID 257: Waldtyp nach Aufnahmeanleitung LFI, MID 260: Waldform, MID 267: Bestandesstruktur, MID 261: Entwicklungsstufe)
(1'214)
Classification of the forest according to the forest decision and accessibility into the three classes «accessible forest without shrub forest», «inaccessible forest without shrub forest» and «shrub forest».
(672)
Type of forest in two classes: «forest without shrub forest» or «shrub forest». Reference: Field Survey (MID 816) or - if the forest is inaccessible – aerial photo interpretation
(125)
Land cover, classified as one of three categories: 'forest without shrub forest', 'shrub forest' and 'non-forest', based on the NFI forest definition. Reference: Field Survey (MID 816), or if inaccessible, aerial photo interpretation.
(70)
Land cover classified into the two classes: «forest» (i.e. forest without shrub forest or shrub forest) and «non-forest» according to the forest definition of the NFI. Reference: Field Survey or, in if inaccessible – aerial photo interpretation
(8)
Sample plots without/with geomorphological objects (e.g. bands of rock, boulders, limestone pavements or gullies) on the interpretation area (50 × 50 m), classified according to the type of the largest object. Reference: Field Survey (MID 218: Geomorphologische Objekte, Kleinrelief)
(392)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) into two classes according to their dbh: «not giant» (dbh ≤80 cm) or «giant» (dbh >80 cm). Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(48)
Zones around groundwater wells and groundwater recharging facilities that are designated by the canton as in the public interest for protecting drinking water. How strict the property restrictions and/or management requirements are depends on the protection zone,. The variable reflects the protection zone categories applicable since 2016 in accordance with Art. 121 of the Waters Protection Ordinance (SR 814.201) and the status of designation by the cantons on 8 July 2022 (download of data from geodienste.ch).
(10)
Value of the forest edge as a habitat - in three classes, derived from its vertical and horizontal structure, without taking the herbaceaous fringe into account - in three classes. Reference: Field Survey (MID 37: Waldrandaufbau, MID 42: Waldrandverlauf, MID 43: Waldranddichte, MID 38: Waldmantelbreite, MID 39: Strauchgürtelbreite)
(32)
Value of the forest stand as a habitat – in three classes, derived from the attributes: development stage, crown closure, stand structure, proportion of old timber, degree of damage to the stand, presence of forest or stand edge, occurrence and type of gaps in the stand, degree of cover of the herb layer, degree of cover of berry bushes as well as the occurrence of stumps, lying deadwood, snags and piles of branches. Reference: Field Survey (various attributes)
(20)
Habitat quality assessed according to the types of deadwood present. It is considered «high» if the three deadwood types «snagss», «branch and wood piles» and «stumps and lying deadwood» are present on the interpretation area, «moderate» if two types are present, and «low» if none or only one type is present.
(30)
Indication as to whether the timber harvesting (felling, processing, extraction and hauling) is carried out wholly or in part by the forest enterprise itself or by a contractor. If an intervention has been carried out since the last Inventory, the information is based on the actual type of operation; if no intervention has been carried out, it is based on the type of operation that the district forester thinks would have been carried out at the time of the current Inventory. Reference: Forest Service Survey (MID 351: Ausführung der Holzernte)
(2'911)
Areas in higher and lower altitude zones classified according to the system used for altitudinal vegetation belts in the guidelines for monitoring the sustainability and performance of protection forests (NaiS; Frehner et al. 2005). The boundary between the higher and lower altitudes runs between the «upper montane» and «lower montane» levels on the Northern Alps and between the «high montane» and «upper/lower montane» levels to the Southern Alps. The information is based on the altitudinal vegetation belts determined by experts (accessible forest sample plots of NFI4 on the 1.4-km network; Arge Frehner et al. 2020), as well as on the altitudinal vegetation belts modelled for the period 1981-2010 (other sample plots; Zischg et al. 2021). n/a: located above the forest boundary modelled by Zischg et al. and sometimes in the area of lakes, which were relatively roughly cut out by Zischg et al.
(10)
Sample plots with/without signs on the interpretation plot (50 × 50 m) that the forest stand or forest site is subject to very intense (excessive) recreational use or other strong human influence (e.g. landfill, land drainage, construction). Where there are such signs, indication of the type of overuse or disturbance. Reference: Field Survey (MID 219: Spuren von Überbelastungen und Störungen)
(168)
Located in/outside a groundwater protection zone. The cantons demarcate groundwater protection zones around groundwater wells and groundwater recharging facilities to protect drinking water where this is in the public interest. The indicator variable combines the various protection zone categories in force since 2016 in accordance with Art. 121 of the Waters Protection Ordinance (SR 814.201) into one class. Data status: 8 July 2022 (download from geodienste.ch).
(8)
Sample plots without/with a distinct vertical stand edge («inner forest edge») on the interpretation area (50 × 50 m). If an inner edge is present, what the lower of the two stands consists of is also indicated. Reference: Field Survey (MID 281: Innenränder)
(61)
Sample plots with/without current recreational use within a radius of 100 m around the sample plot centre, classified according to visitor frequency as a measure of the intensity of recreational use. No recreational use: <10 persons/year; very low intensity: <1 person/day; low: 1-10 persons/day; moderate: 11-100 persons/day; high: 101-500 persons/day; very high: >500 persons/day based on the entire year or the relevant season, taking into account all types of recreational use. Reference: Forest Service Survey (MID 330: Intensität der aktuellen Erholungsnutzung)
(36)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) into the three classes: «introduced tree species», «native tree species» and «indeterminable and/or shrub species». Introduced tree species are tree species that have been intentionally or unintentionally introduced by humans into habitats outside their natural range. With this classification attribute, which is used in all inventories, the Japanese larch (L. kaempferi) and introduced arboreal willow species are not counted as introduced tree species, because they are recorded together with related native species in certain inventories. The Japanese larch (Larix kaempferi), for example, is grouped together with the European larch (L. decidua). Reference: Field Survey (MID 50: Baumart)
(36)
Introduced tree species ≥12 cm in diameter at breast height (dbh), recorded in all the Inventories, classified into the eight classes: Austrian pine (Pinus nigra), Weymouth pine (Pinus strobus), Douglas fir (Pseudotsuga menziesii), red oak (Quercus robur), non-native poplars (Populus [other introduced]), black locust (Robinia pseudoacacia), other introduced tree species (including sequoia, redwood, thuja, cedar, tree-of-heaven, horse-chestnut, tulip-tree). The remaining woody species (native tree species and all shrub species) are summarised in one class.
(24)
Length of lying dead trees and shrubs ≥12 cm in diameter at breast height (dbh) up to the limit for merchantable wood (7 cm in diameter) – in six classes. If an individual tree is broken, the lengths of all the parts are added together. Reference: Field Survey (MID 415: Stücklänge liegender Probebäume)
(24)
Sample plots with/without tracks of timber-harvesting vehicles such as tractors, forwarders and harvesters on the forest floor within the 200 m² circle, classified according to where the tracks occur. Reference: Field Survey (MID 545: Schadenumgebung)
(9)
Location of the tracks of timber harvesting vehicles such as tractors, forwarders and harvesters – in four classes. Reference: Field Survey (MID 955: Bodenschadenumgebung)
(38)
Machines or tools used for felling and processing the trees. If an intervention has taken place since the last Inventory, the data is based on the means actually used. If no intervention has taken place, it is based on the means that would have been used in the case of an intervention at the time of the current Inventory, according to the district forester's assessment. Reference: Forest Service Survey (MID 352: Art der Holzernte)
(3'225)
Type of trees and shrubs ≥12 cm in diameter at breast height (dbh) with the ten most common species or species groups in Switzerland ('main tree species') categorised, and the classes 'other conifers' and 'other broadleaves' for the remaining species. The main tree species are: spruce (Picea spp.), fir (Abies spp.), pine (Pinus sylvestris, P. nigra, P. strobus, P. mugo subsp. uncinata), larch (Larix spp.), Arolla pine (Pinus cembra), beech (Fagus sylvatica), maple (Acer spp.), ash (Fraxinus spp.), oak (Quercus spp.) and chestnut (Castanea sativa). Reference: Field Survey (MID 50: Baumart)
(94)
Species of young forest plants ≥10 cm in height and ≤11.9 cm in diameter at breast height (dbh) with individual classes for the ten most important species or species groups in Switzerland («main tree species»), as well as the classes «other conifers», «other broadleaves» and «species not assessed in all inventories». The main tree species are spruce (Picea spp.), fir (Abies spp.), pine (Pinus sylvestris, P. nigra, P. strobus, P. mugo subsp. uncinata), larch (Larix spp. ), Arolla pine (Pinus cembra), beech (Fagus sylvatica), maple (Acer spp.), ash (Fraxinus spp.), oak (Quercus spp.) and chestnut (Castanea sativa). Reference: Field Survey (MID 1051: Jungwaldpflanzenart - Zählung)
(27)
Type of microhabitat that occurs at least once on a tree or shrub ≥12 cm in diameter at breast height (dbh). Reference: Field Survey (MID 819: Bemerkung zu Ex-LFI-Probebaum, MID1027: Baumschadenart, MID 1035-1049: Baummikrohabitate)
(7)
Natural hazard processes that can occur in forests designated as protection forests by the cantons according to the harmonised criteria of SilvaProtect. Reference: Losey & Wehrli (2013)
(168)
Correspondence between the actual proportion of conifers in a stand and the postulated natural proportion of conifers in the corresponding potential natural vegetation (PNV). Reference: NaiS site types, aggregated into groups with similar mixing and regeneration objectives («Gfein») according to the NaiS-NFI project (Arge Frehner et al. 2020) for the PNV; classification of the proportion of conifers according to the Kienast method; Field Survey (MID 50: Baumart, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(100)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) into four classes according to the number of visible cases of damage or the condition of the tree (living/dead, standing/lying). Reference: Field Survey (MID 1018: Baumzustand, MID 1027: Baumschadenart)
(48)
Number of natural hazard processes that can occur simultaneously in forest designated «protection forest» by the cantons (as of 2022) according to the harmonised criteria of SilvaProtect-CH (as of 2022). The following four natural hazard processes can be considered: rockfall, avalanches, hillslope debris flows/landslides, channel processes. Reference: GIS data from the FOEN, 2022
(180)
Number of standing living trees and shrubs ≥24 cm in diameter at breast height (dbh) – in classes of 100. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang, MID 1018: Baumzustand)
(180)
Number of standing living trees and shrubs ≥36 cm in diameter at breast height (dbh) – in classes of 100. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang, MID 1018: Baumzustand)
(180)
Number of standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) per hectare – in classes of 100. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang, MID 1018: Baumzustand)
(112)
Number of tree and shrub species in the upper stand layer – in six classes. The information refers to the relevant stand on the interpretation area (50 × 50 m) and only takes into account species with a cover ≥5%. Reference: Field Survey (MID 242: Baumart in der Oberschicht)
(30)
Number of tree and shrub species present along the forest edge – in five classes. The data is for a distance of 50 m along the edge of the forest. Reference: Field Survey (MID 568: Pflanzenarten am Waldrand)
(96)
Classification of forest stands according to the dominant diameter at breast height (dbhdom), i.e. the 100 largest (thickest) standing living trees per hectare, as: «old timber stand» (dbhdom >50 cm) or «not old timber stand». Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(1'980)
Forest ownership, classified according to the two categories: 'public' and 'private'. Reference: Forest Service Survey (MID 365: Eigentum)
(141)
Forest ownership at the time of NFI5, classified into the two classes: «public» and «private». The attribute is used in analyses of change to ensure that changes in ownership do not influence the results. Reference: Forest Service Survey (MID 365: Eigentum)
(132)
Ownership of the forest, categorised according to the 7 types 'federal government', 'canton', 'municipality', 'citizens' community', 'corporation', 'individual private ownership' and 'company'. Reference: Forest Service Survey (MID 365: Eigentum)
(80)
Sample plots with/without traces of grazing by livestock pasturing in the relevant stand on the interpretation area (50 × 50 m), as well as intensity and recency of pasturing based on the occurrence and freshness of pasturing signs, especially tracks and droppings. Reference: Field Survey (MID 205: Beweidungsintensität)
(10)
Sample plots with either no wood pile or with at least one compact wood pile ≥30 cm in height and 3 m² in area on the interpretation area (50 × 50 m) left in the stand after harvesting. Reference: Field Survey (MID 209: Asthaufen)
(12)
Level of potential demand for local recreation, classified into five classes according to a model that estimates the number of permanently occupied and temporarily occupied/unoccupied dwellings within a radius of two kilometres. The variable is only available for NFI2 and NFI3.
(132)
Tree species group (conifers or broadleaves) with the larger basal area. For the calculation, the standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) were taken into account. Reference: Field Survey (MID 1018: Baumzustand, MID 50: Baumart, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(186)
Main tree species with the largest basal area. For the calculation, the standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) were taken into account. Reference: Field Survey (MID 1018: Baumzustand, MID 50: Baumart, MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(16)
Sample plots with/without at least one still clearly recognisable root plate that protrudes at least 30 cm above the terrain. Reference: Field Survey (MID 227: Wurzeltellerklasse)
(16)
Sample plots with/without at least one pile of soil or mulch, created by the decay of a root plate and protruding at least 30 cm above the terrain. Reference: Field Survey (MID 227: Wurzeltellerklasse)
(48)
Sample plots with/without tracks of timber-harvesting vehicles such as tractors, forwarders and harvesters on the forest floor within the 200 m² circle. If there are tracks, indication of the track type. In the case of track type 3 (severe disturbance), it can be assumed that the damage to the soil fertility will be significant and long term (Lüscher et al. 2016). Reference: Field Survey (MID 544: Fahrzeugspuren, MID 496: Bodenschadentyp)
(24)
Type of the most important forest function relevant for managing the forest according to forest plans or an assessment by the local forest service during NFI4 (2009-2017). Reference: Forest Service Survey (MID 911: Vorrangfunktion 2)
(57)
Type of the most important forest function relevant for management according to forest plans or an assessment by the local forest service during NFI5 (2018-2026). Reference: Forest Service Survey (MID 911: Vorrangfunktion 2)
(31)
Presence of the primary function «nature and landscape conservation», classified into the four classes: «landscape protection», «nature conservation», «game protection» or «other» according to forest plans or an assessment by the local forest service during NFI5 (2018-2026). Reference: Forest Service Survey (MID 911: Vorrangfunktion 2)
(166)
Presence of the primary function: «nature conservation» according to forest plans or an assessment by the local forest service during NFI5 (2018-2026). Reference: Forest Service Survey (MID 911: Vorrangfunktion 2)
(60)
Proportion of conifers in the basal area of standing living trees and shrubs ≥12 cm in diameter at breast height (dbh) – in four classes. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang)
(230)
Percentage of sanitary/salvage fellings in total fellings - in three classes. Reference: Forest Service Survey (MID 344: Anteil Zwangsnutzung)
(971)
Area in/outside a forest that provides protection against avalanches which the cantons designated «protective forest» according to the harmonised criteria of SilvaProtect-CH in 2022. Reference: GIS data from FOEN, 2022
(971)
Area in/outside a forest that provides protection against channel processes which the cantons designated «protective forest» according to the harmonised criteria of SilvaProtect-CH in 2022. Reference: GIS data from FOEN, 2022
(971)
Area in/outside a forest that provides protection against hillslope debris flows/landslides which the cantons designated «protective forest» according to the harmonised criteria of SilvaProtect-CH in 2022. Reference: GIS data from FOEN, 2022
(971)
Area in/outside a forest that provides protection against rockfall processes which the cantons designated «protective forest» according to the harmonised criteria of SilvaProtect-CH in 2022. Reference: GIS data from FOEN, 2022
(1'017)
Area inside/outside the protective forest that the cantons had designated in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013). In 2022, Canton Aargau had not yet designated its protective forest. Reference: GIS data from FOEN, 2022
(52)
Main reason for sanitary/salvage felling. Reference: Forest Service Survey (MID 345: Ursache der Zwangsnutzung)
(180)
Main reason for sanitary/salvage felling. Reference: Forest Service Survey (MID 345: Ursache der Zwangsnutzung)
(29)
Sample plots without/with recreation infrastructure (paths and specific recreation facilities) on the interpretation area (50 × 50 m). Reference: Field Survey (MID 220: Erholungseinrichtungen)
(7)
Sample plots with/without current recreational use 'camping' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'cross-country skiing' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'cycling' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'hiking' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'horse-riding' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'jogging' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'mountain biking' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'other activities' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'ski- and snowboarding' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'snowshoeing' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(7)
Sample plots with/without current recreational use 'walking' within a radius of 100 m around the sample plot centre. The type of recreation is recorded with a visitor frequency ≥10 persons per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(18)
Sample plots with/without recreational use within a radius of 100 m around the sample plot centre, with details about the recreational activity (e.g. walking, jogging or biking). Recreational activities are recorded if the visitor frequency is ≥10 people per year. Reference: Forest Service Survey (MID 329: Art der aktuellen Erholungsnutzung)
(410)
Proportion of the area covered by regeneration, i.e. broadleaved and coniferous trees ≥10 cm in height and ≤11.9 cm in diameter at breast height (dbh), in six classes. The feature is available as of NFI2 (1993-1995). Reference: Field Survey (MID 270: Verjüngungs-Deckungsgrad)
(570)
Type of forest reserve («natural forest reserve», «special forest reserve“ or «other forest»), based on the forest reserves as designated by the cantons (as of 2023) and the forest/non-forest decision of the respective Inventory. Reference: GIS data from FOEN, 2023, and Field Survey (MID 816) or – if the forest is inaccessible – aerial photo interpretation
(20)
Presence of non-forestry buildings and facilities, such as railway lines, main roads, power- and pipelines or residential areas, which potentially impede logging, i.e. tree felling and processing. Reference: Field Survey (MID 207: Einschränkungen für die Holzhauerei)
(30)
Sample plots with/without current recreational use within a radius of 100 m around the sample plot centre, classified according to seasonality of recreational use (all year round, almost only during the growing season, almost only in winter). Reference: Forest Service Survey (MID 403: Saisonalität der aktuellen Erholungsnutzung)
(30)
Type of transition line between the forest and the open land along the forest edge - in five classes. Reference: Field Survey (MID 42: Waldrandverlauf)
(30)
Indication as to whether a silvicultural treatment took place since the last inventory. Reference: Forest Service Survey (MID 611: Art alle Eingriffe seit Referenzdatum)
(548)
Production capacity of the site in kilograms per hectare and year based on the total mean increment (TMI) according to Keller (1978) - in four classes. Low: TMI ≤1500 kg/(ha/year), moderate: TMI 1501-3000 kg/(ha/year), good: TMI 3001-4500 kg/(ha/year), very good: TMI >4500 kg/(ha/year).
(4)
Size of young forest plants 10-129 cm in length. Reference: Field Survey (MID 507: Jungwaldklasse)
(4)
Size of young forest plants ≥130 cm in length and ≤11.9 cm in diameter at breast height (dbh). Reference: Field Survey (MID 507: Jungwaldklasse)
(134)
Size of young forest plants ≥10 cm in height and ≤11.9 cm in diameter at breast height (dbh) – in five size classes (two height and three dbh classes). Reference: Field Survey (MID 507: Jungwaldklasse)
(114)
Forest area under the same management – in eight classes. Several forest owners form a management unit («enterprise») if they have joined forces to manage their forests permanently (and not just for one logging operation). Reference: Forest Service Survey (MID 410: Grösse der Bewirtschaftungseinheit)
(652)
Slope in classes of 20%. Reference: Digital height model DHM 25 from Swisstopo
(48)
Slope in classes of 40%. Reference: Digital height model DHM 25 from Swisstopo
(10)
Sample plots with/without standing dead trees («snags») ≥20 cm in diameter at breast height (dbh) on the interpretation area (50 × 50 m), which together reach a volume of at least 1 m³. Reference: Field Survey (MID 211: Dürrständer)
(102)
Presence of a forest function that is locally very important according to forest plans or an assessment by the local forest service – in two classes (present/absent). Forest functions include e.g. timber production, protection against natural hazards, nature conservation and drinking water protection. Reference: Forest Service Survey (MID 327: Spezielle Waldfunktionen)
(24)
Age of the stand – in classes of 20 years. Reference: Field Survey (MID 264: Bestandesalter)
(306)
Age of the stand – in classes of 40 years. Reference: Field Survey (MID 264: Bestandesalter)
(144)
Density of a stand – in four classes. The Stand Density Index (SDI) is calculated on the basis of the number of stems per hectare of trees and shrubs ≥12 cm in diameter at breast height (dbh) and the mean diameter. Reference: Field Survey (MID 60: Brusthöhendurchmesser, MID 62: Umfang, MID 1018: Baumzustand)
(60)
Stand in which the existing regeneration is very important because it is most likely to form the future main stand. In NFI, this is understood to mean the development stage young growth/thicket, regeneration under shelterwood and selection-type high forest. Reference: Field Survey (MID 261: Entwicklungsstufe, MID 433: Waldbauliche Beurteilung, MID 267: Bestandesstruktur); Forstdienstbefragung (MID 611: Art alle Eingriffe seit Referenzdatum)
(16)
Classification of tree collectives into three classes in order to distinguish small collectives (group [500-900 m²] and groves [1000-4900 m²]) from stands in the sense of silvicultural theory (≥5000 m²). Reference: Field Survey (MID 259: Bestandesgrösse)
(858)
Mechanical resistence of a stand to abiotic and biotic stresses within the next 10 to 20 years – in three classes. Reference: Field Survey (MID 310: Gesamtstabilität)
(384)
Vertical structure (stratification) of a stand, defined on the basis of the degrees of cover of the upper, middle and lower layers. Reference: Field Survey (MID 267: Bestandesstruktur)
(69)
Indication as to whether the current main stand (i.e. the trees of the upper layer) originated from natural regeneration (100% natural regeneration), artificial regeneration (<20% natural regeneration) or mixed regeneration (20-99% natural regeneration). Reference: Forest Service Survey (MID 404: Art der Bestandesentstehung)
(10)
Type and intensity of direct or indirect human interventions in the forest edge - in eight classes. Reference: Field Survey (MID 44: Waldrandzustand)
(84)
Status and type of certification. Reference: Forest Service Survey (MID 319: Art der Zertifizierung)
(60)
Status of the forest development plan or a comparable cantonal forest planning document. Reference: Forest Service Survey (MID 803: Stand der Waldentwicklungspläne)
(36)
Information on whether the forest road network has been completed or whether an improvment is in progress (construction, project planning) or planned according to the current transportation system plan. Reference: Forest Service Survey (MID 614: Erschliessungsabsichten)
(24)
Height of the still standing stem section of broken snags, i.e. of standing dead trees and shrubs ≥12 cm in diameter at breast height (dbh) – in six classes. Reference: Field Survey (MID 829: Schafthöhe gebrochener Probebaum)
(10)
Formation of the transition from forest to open land - in seven classes. Reference: Field Survey (MID 37: Waldrandaufbau)
(18)
Species group (conifers or broadleaves) of stumps ≥7 cm in diameter. Reference: Field Survey (MID 970: Stocktotholz - Baumart)
(18)
Stage of wood decomposition of stumps ≥7 cm in diameter – in five classes. Reference: Field Survey (MID 971: Stocktotholz - Festigkeit)
(10)
Sample plots with/without stumps and lying deadwood on the interpretation area. «With» applies if there are at least five tree stumps ≥30 cm in diameter and 20 cm in height or a lying tree ≥30 cm in diameter at breast height (dbh) on the interpretation area. Reference: Field Survey (MID 210: Stöcke)
(10)
Classification of the open land adjacent to the forest edge - in eleven classes. Reference: Field Survey (MID 46: Waldrandumgebung)
(102)
Sorting of roundwood into four diameter classes on the basis of the 2010 and 2021 editions of the Swiss Trading Customs for Raw Timber (HG 2010, Waldwirtschaft Schweiz et al. 2010). Classes 1 and 2, 3 and 4, as well as 5 and 6 of the HG 2010 are each combined into one class.
(10)
Techniques used in timber harvesting, i.e. for felling, processing and extracting trees – in twelve classes. If timber has been harvested since the last Inventory, the information is based on the procedures actually used. If, on the other hand, no harvesting has taken place, it is based on the procedures which, according to the district forester's assessment, would have been used in the case of an intervention at the time of the current Inventory. Abbreviations: LO: logging, EX: extraction, PS: pre-skidding, FE: felling, PRO: processing, CH: chopping, AS: assortment, FT: full tree. Reference: Forest Service Survey (MID 352: Art der Holzhauerei, MID: 3001: Rückemittel)
(729)
Number of years since the last silvicultural treatment – in classes of ten years. Silvicultural treatments include harvesting and tending interventions, planting and afforestation, as well as sanitary and safety interventions. Reference: Forest Service Survey (MID: 607: Anzahl Jahre seit dem letzten Eingriff)
(78)
Number of years since the last silvicultural treatment in classes of five or ten years. Silvicultural treatments include harvesting and tending interventions, planting and afforestation, as well as sanitary and safety interventions. Reference: Forest Service Survey (MID: 607: Anzahl Jahre seit dem letzten Eingriff)
(9)
Number of years since the last silvicultural treatment – in classes of 50 years. Silvicultural treatments include harvesting and tending interventions, planting and afforestation, as well as sanitary and safety interventions. Reference: Forest Service Survey (MID: 607: Anzahl Jahre seit dem letzten Eingriff)
(136)
Number of years until the next silvicultural treatment according to the forest planning schedule. Silvicultural treatments include harvesting and tending interventions, planting and afforestation, as well as sanitary and safety interventions. Reference: Forest Service Survey (MID 337: Zeitpunkt des nächsten Eingriffs)
(10)
Sample plots with/without traces of erosion due to water on at least 100 m² (sum of eroded parts) of the interpretation area (50 × 50 m). Reference: Field Survey (MID 194: Erosion durch Wasser) or – if the forest is inaccessible – aerial photo interpretation
(12)
Sample plots with/without extensive traces of forest fire (e.g. burnt ground vegetation, charred parts of tree or soil layers) on the interpretation plot (50 × 50 m). Reference: Field Survey (MID 203: Spuren von Waldbrand)
(24)
Sample plots with/without traces of landslides (e.g. a toe or crack, and trees leaning uphill) on at least 100 m² of the interpretation area (50 × 50 m). Reference: Field Survey (MID 193: Rutschung)
(126)
Sample plots with/without traces of livestock pasturing in the relevant stand on the interpretation area (50 × 50 m). Traces could be: presence of pasturing livestock, faeces, fresh tracks, resting places, torn hairs and traces of browsing or fraying, and indication of the livestock class in the case of pasturing. Reference: Field Survey (MID 204: Beweidungsart)
(72)
Sample plots with/without current traces of rockfall on the interpretation plot (50 × 50 m). Reference: Field Survey (MID 195: Steinschlag)
(12)
Sample plots with/without traces of snow movement, i.e. snow creep, snow sliding or avalanches on the interpretation area (50 × 50 m). Reference: Field Survey (MID 202: langsame Schneebewegung und MID 400: Lawinenspuren)
(9)
Type of tracks of timber harvesting vehicles such as tractors, forwarders and harvesters on the forest floor – in three classes. For track type 3 (severe disturbance), it can be assumed that the soil fertility is significantly and permanently damaged (Lüscher et al. 2016). Reference: Field Survey (MID 954: Bodenschadentyp LIS)
(5)
STRBEFAHR gibt an, mit welchem Lastwagentyp eine Strasse befahren werden kann. Dabei sind Achsenzahl und Gesamtgewicht des LKW für die Klassierung ausschlaggebend. Lastwagenstrassen im Schweizer Wald müssen, um in der Erschliessungserhebung erfasst zu werden, eine Mindestbreite von 2.50 m aufweisen, wobei der Strassenoberbau mindestens für eine Achslast von 10 t ausgelegt sein muss. Im Rahmen der Försterumfrage des LFI4 wurden zusätzliche Informationen erhoben. Dabei steht nicht die lastwagenbefahrbare Strasse nach LFI mit 10 t Achslast und einer Mindestbreite von 2.50 m im Fokus, sondern die für die Holzabfuhr relevante Strasse mit mindestens 3 m Fahrbahnbreite und genügender Tragfähigkeit für Fahrzeuge mit 3 Achsen und einem Gesamtgewicht ab 26 t.
(306)
Information about the large- and small-scale infrastructure used for the extraction and transport of timber. Reference: Forest Service survey (MID 326: Erschliessungskonzept)
(66)
Estimated age of living trees and shrubs (standing and lying) ≥12 cm in diameter at breast height (dbh) – in classes of 40 years. Reference: Field Survey (MID 826: Baumalter)
(228)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) as standing or lying, and as living or dead. Reference: Field Survey (MID 58: Bemerkungen, MID 1018: Baumzustand)
(517)
Type of trees and shrubs ≥12 cm in diameter at breast height (dbh). The three most common species or species groups in Switzerland (spruce - Picea spp.; fir - Abies spp.; beech - Fagus sylvatica) are in individual classes, while the remaining species are classified as «other conifers» or «other broadleaves». Reference: Field Survey (MID 50: Baumart)
(185)
Type of trees and shrubs ≥12 cm in diameter at breast height (dbh) – in 56 classes. The species (or species groups) not explicitly listed are subsumed in the classes «other conifers», «other broadleaved trees» and «other shrubs». Reference: Field Survey (MID 50: Baumart)
(1'116)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) as living or dead. Reference: Field Survey (MID 58: Bemerkungen, MID 1018: Baumzustand)
(246)
Classification of trees and shrubs ≥12 cm in diameter at breast height (dbh) into standing or lying. Reference: Field Survey (MID 58: Bemerkungen, MID 1018: Baumzustand)
(96)
Sorting of roundwood into five length classes (4 for conifers, 1 for broadleaves) on the basis of the 2010 and 2021 editions of the Swiss Trading Customs for Raw Timber (HG 2010, Waldwirtschaft Schweiz et al. 2010). Reference: Forest Service Survey (MID 2020: Längensortierung des Nadelrundholzes)
(78)
Type of damage to trees and shrubs ≥12 cm in diameter at breast height (dbh) – in thirteen classes. Eleven of these classes focus exclusively on standing living trees and shrubs with dbh ≥12 cm, while one class applies to lying living trees and shrubs with dbh ≥12 cm , and one to dead trees and shrubs with dbh ≥12 cm. Reference: Field Survey (MID 1027: Baumschadenart, MID 1018: Baumzustand)
(10)
Sample plots with/without gaps ≥10 × 10 m from crown edge to crown edge and cover with woody plants of maximum 20% that intersect with the interpretation area. Classified into different gap types according to the predominant surface of the largest gap. Reference: Field Survey (MID 221: Lückentyp)
(14)
Indication of how the stand was treated during the last intervention. Reference: Forest Service Survey (MID 610: Kalenderjahr alle Eingriffe seit Referenzdatum, MID 611: Art alle Eingriffe seit Referenzdatum)
(184)
Indication of how the stand is likely to be treated in the next intervention, taking into account local forest functions and planning. Reference: Forest Service Survey (MID 335: Art des nächsten Eingriffs)
(64)
Type of stand establishment, with natural and artificial regeneration distinguished. Reference: Field Survey (MID 275: Verjüngungsart)
(6)
Type of shrub forest, i.e. «pure shrub forest» or «shrub forest with trees» according to the interpretation of aerial photos. Reference: Aerial photo interpretation
(32)
Sample plots with/without tracks of timber-harvesting vehicles such as tractors, forwarders and harvesters on the forest floor within the 200 m² circle. Reference: Field Survey (MID 544: Fahrzeugspuren)
(8)
Sample plots without/with water bodies on the interpretation area (50 × 50 m), classified according to the type of the largest water body. Pond: 1-200 m², small lake: >200 m², creek: channel width <2 m, stream: 2-5 m, river: > 5 m. Reference: Field Survey (MID 401: Gewässer)
(10)
Width of the shelterbelt (forest mantle), i.e. the part of the forest edge consisting of single individuals or graded rows of typical edge trees, i.e. trees with crowns that are one-sided and rather long – in four classes. Reference: Field Survey (MID 38: Waldmantelbreite)
(10)
Width of the shrub belt, i.e. that part of the forest edge which lies between the forest mantle and the herbaceous fringe and consists of woody plants (in NFI such plants ≤12 cm in diameter at breast height (dbh), excluding dwarf shrubs). Reference: Field Survey (MID 39: Strauchgürtelbreite)
(12)
Presence of woodpecker cavities on dead trees and shrubs (standing and lying) ≥12 cm in diameter at breast height (dbh). In NFI5, information on woodpecker breeding cavities can be found via the topic (target variable): «Number of stems (standing-living) with microhabitat». However, this refers to the standing living trees and not, as here, to the standing or lying dead trees. Reference: Field Survey (MID 490: Totholz Spechtloch)
(36)
Year in which the forest was (re)afforested during past centuries – in classes of ten years. Reference: Forest Service Survey (MID 332: Jahr der Aufforstung)
(8)
Year in which the forest was (re)afforested in the past – in five classes: «before 1851», «1851-1900», «1901-1950», «1951-2006», or «no afforestation/afforestation unknown.». Reference: Forest Service Survey (MID 332: Jahr der Aufforstung)
(28)
Year in which the forest was (re)afforested in earlier periods in six classes: before 1851; 1851-1900; 1901-1950; 1951-2000; 2001-2020; oe «no afforestation/afforestation unknown». Reference: Forest Service Survey (MID 332: Jahr der Aufforstung)
(36)
Year in which the forest development plan or a comparable cantonal planning document was put into effect – in six classes. Reference: Forest Service Survey (MID 804: Kalenderjahr der Inkraftsetzung des Waldentwicklungsplans WEP)
(16)
Sample plots without/with grazing and year when last grazed on by livestock. Reference: Forest Service Survey (MID 341: Jahr der letzten Beweidung)
region
(28'189)
Division of Switzerland into 14 regions (2 in the Jura, 3 on the Plateau, 3 in the Pre-Alps, 5 in the Alps and 1 in the Southern Alps). The economic regions are a subdivision of the production regions according to economic-geographical criteria.
(28'190)
Demarcation of Switzerland into five regions (Jura, Plateau, Pre-Alps, Alps and Southern Alps) with relatively uniform growth and timber production conditions. The production regions were established by the Federal Office of Forestry long before the first National Forest Inventory (NFI1, 1983-1985). With a small exception along Lake Geneva, the boundaries of the production regions still follow the municipal boundaries of the time. Unlike the NFI, the Forestry Statistics of the Federal Statistical Office don't use the production regions as demarcation but rather the forestry zones, whose boundaries are somewhat different.
(28'190)
Demarcation of Switzerland used in NFI for protective forest analyses. The six protective forest regions were derived from the economic regions by combining individual regions according to natural and statistical criteria.
(28'118)
Regional demarcation with the cantons as a unit, with the two half-cantons, Basel-Land and Basel-Stadt, combined into one canton for statistical reasons.
(28'190)
Demarcation of Switzerland into six regions with similar flora and fauna. The six regions correspond to the basic categories in the publication «The Biogeographical Regions of Switzerland», which was published by FOEN in 2022.
(28'114)
Regional demarcation with the forest districts as a unit. This variable is based on a survey of the cantonal forest services in winter 2022/2023.
evaluation area
(822)
Area that meets the forest definition of the NFI, i.e. is «forest without shrub forest» or «shrub forest», and can be reached on foot.
(710)
Area accessible on foot that meets the NFI's definition of forest in both NFI4 (2009-2017) and NFI5 (2018-2026), i.e. was either «forest without shrub forest» or «shrub forest».
(7'632)
Forest of which less than two-thirds is covered with shrubs that can be accessed on foot.
(118)
Forest that was less than two-thirds covered with shrubs and accessible on foot in both NFI1 (1983-1985) and NFI2 (1993-1995).
(10'070)
Forest that was less than two-thirds covered with shrubs in the five inventories NFI1 (1983-1985), NFI2 (1993-1995), NFI3 (2004-2006), NFI4 (2009-2017) and NFI5 (2018-2026) and was accessible on foot.
(340)
Forest that was less than two-thirds covered with shrubs and accessible on foot in both NFI2 (1993-1995) and NFI3 (2004-2006).
(340)
Forest that was less than two-thirds covered with shrubs in both NFI3 (2004-2006) and NFI4 (2009-2017) and could be reached on foot.
(4'567)
Forest that was less than two-thirds covered with shrubs in both NFI4 (2009-2017) and NFI5 (2018-2026) and is accessible on foot.
(1'465)
Area that meets the NFI's definition of 'forest', i.e. is «a forest without shrub forest» or «a shrub forest».
(72)
Forest edge in the NaiS altitudinal vegetation belts: «hyperinsubric», «colline», «colline with beech», «submontane», «lower montane», «upper montane», «lower/upper montane» and «high montane». Reference: Field Survey (MID 29: Waldrandbeschreibung)
(72)
Forest edge in the NaiS altitudinal vegetation belts «hyperinsubric», «colline», «colline with beech», «submontane», «lower montane», «upper montane», «lower/upper montane» and «high montane», which was recorded during the four Inventories NFI2, NFI3, NFI4 and NFI5. Reference: Field Survey (MID 29: Waldrandbeschreibung)
(36)
Forest edge in the NaiS altitudinal vegetation belts: «hyperinsubric», «colline», «colline with beech», «submontane», «lower montane», «upper montane», «lower/upper montane» and «high montane», which was recorded during the two inventories NFI4 and NFI5. Reference: Field Survey (MID 29: Waldrandbeschreibung)
(710)
Area that meets the NFI's definition of forest in both NFI4 (2009-2017) and NFI5 (2018-2026), i.e. was either «forest without shrub forest» or «shrub forest».
(234)
Accessible forest without shrub forest («a.f.w.s.f.»), i.e. forest that is less than two-thirds covered with shrubs and can be accessed on foot, which is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(70)
Accessible forest, i.e. «forest without shrub forest» or «shrub forest» that can be accessed on foot and is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(47)
Area designated in both the NFI4 (2009-2017) and the NFI5 (2018-2026) as «accessible forest», i.e. «forest without shrub forest» or «shrub forest» that can be accessed on foot and is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(234)
Area designated in the five Inventories NFI1 (1983-1985), NFI2 (1993-1995), NFI3 (2004-2006), NFI4 (2009-2017) and NFI5 (2018-2026) as «accessible forest without shrub forest» (a.f.w.s.f.), i.e. «forest without shrub forest» that can be accessed on foot and is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(115)
Area designated in both NFI4 (2009-2017) and NFI5 (2018-2026) as «accessible forest without shrub forest» (a.f.w.s.f.), i.e. «forest without shrub forest» that can be accessed on foot and is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(102)
Forest, i.e. «forest without shrub forest» or «shrub forest», that is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(47)
Area that, in both the NFI4 (2009-2017) and the NFI5 (2018-2026), conforms with the NFI's definition of «forest», i.e. «forest without shrub forest» or «shrub forest», and is situated in a forest that the cantons designated «protective forest» in 2022 according to the harmonised criteria of SilvaProtect-CH (Losey & Wehrli 2013).
(12)
Forest that is more than two-thirds covered with shrubs. Shrub forests include Alpine alder and pine forests in particular, but also hazel forests and similar stands. Reference: Field Survey (MID 576: Deckungsgrad Sträucher), and sometimes also aerial photo interpretation
(88)
Stockable part of the accessible forest without shrub forest, i.e. accessible forest without shrub forest excluding the area of forest roads, recreational facilities, streams, avalanche paths, etc.
(64)
Forest that was less than two-thirds covered with shrubs in the four inventories NFI2 (1993-1995), NFI3 (2004-2006), NFI4 (2009-2017) and NFI5 (2018-2026), was accessible on foot and could be stocked, i.e. did not contain forest roads, recreational facilities, streams, avalanche paths, etc.
(222)
Area of Switzerland or a region (e.g. production region or canton) regardless of its cover. In NFI, the total area is made up of the components «forest without shrub forest», «shrub forest» and «non-forest».
grid
(19'467)
Sub-grids 1, 2, 3, 4 and 5 of 9 on the sampling grid with a mesh size of 1.4 km (base grid).
(8'722)
NFI's sampling grid with a mesh size of 1.4 km. The 1.4-km grid is the grid size covering all the previous terrestrial Inventories, which is why it is also called the base grid.
LFI5 2018/26
economic region
proportion of forest plots
vehicle tracks·slope (in 20% classes)
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
proportion of forest plots
vehicle tracks·slope (in 20% classes)
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
proportion of forest plots
vehicle tracks·slope (in 20% classes)
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
cause of damage gap
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
cause of damage gap
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
cause of damage gap
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
altitudinal vegetation belts (NaiS; 6 classes)·cause of damage gap
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
altitudinal vegetation belts (NaiS; 6 classes)·cause of damage gap
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
altitudinal vegetation belts (NaiS; 6 classes)·cause of damage gap
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
higher/lower altitude zone·cause of damage gap
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
higher/lower altitude zone·cause of damage gap
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
higher/lower altitude zone·cause of damage gap
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
ownership (2 categories)·cause of damage gap
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
ownership (2 categories)·cause of damage gap
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
ratio of the types of damage gaps
ownership (2 categories)·cause of damage gap
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
root mass of living trees / biomass of living trees
conifers and broadleaves
accessible forest without shrub forest
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
root mass of living trees / biomass of living trees
conifers and broadleaves
accessible forest without shrub forest NFI1-NFI5
1.4 km grid, subgrids 1–5 of 9
LFI5 2018/26
economic region
root mass of living trees / biomass of living trees
conifers and broadleaves
accessible forest without shrub forest NFI4/NFI5
1.4 km grid, subgrids 1–5 of 9