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growing stock (stemwood) #21
Stemwood volume of living trees and shrubs (standing and lying) with a diameter at breast height (dbh) ≥12 cm with bark.

development stage #20
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)

altitudinal vegetation belts (NaiS; 6 classes) #2633
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).

forest district (2024) #2777
Regional demarcation with the forest districts as a unit. This variable was implemented in the year 2024 and is based on a survey with the cantonal forest services in the years 2022/2023.

accessible forest without shrub forest NFI1-NFI5 #2382
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.

1.4 km grid, subgrids 1-5 #1746
Sub-grids 1, 2, 3, 4 and 5 of the field surveys on the sampling grid with a mesh size of 1.4 km (base grid).

What do the numbers stand for?
What is the purpose of the standard error?
When are two results statistically different?
When is it not sufficient to consider only the standard error?
Two types of changes?
Change analyses: When are the results (not) additive?
Why is a dot (“.”) sometimes given in the cells for standard error or estimated value?
Why are no standard error values shown in some tables?
Negative values for growing stock, increment or fellings?

1. What do the numbers stand for?

The tables mainly show results that were calculated using statistical methods from the data of the sample inventory of the National Forest Inventory (NFI). Such results always consist of two figures: (1) the estimated value and (2) the sampling error, the so-called standard error.

Example 1: Estimated value and standard error

NFI5

volume of deadwood (stemwood)
ownership (2 categories)

regional demarcation: production region

unit: m³/ha

evaluation area: accessible forest without shrub forest

grid: 1.4 km grid, subgrids 1-5

state 2018/26
	production region
	Jura		Plateau		Pre-Alps		Alps		Southern Alps		Switzerland
ownership (2 categories)	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%
public	30	10	17	13	37	9	36	6	26	10	30	4
private	27	17	20	12	50	10	32	8	39	13	34	5
total	29estimated value	9standard error	19	9	44	7	35	5	29	8	32	3

The tables usually show the relative (percentage) standard error (“±%”), but occasionally – in the case of estimated percentages – the absolute standard error (“±”).

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2. What is the purpose of the standard error?

The standard error can be used to define confidence intervals around the estimated value, which contain the true value of the population with a certain statistical certainty.

The statistical certainty is:

68% if the confidence interval is calculated using the standard error
(68% confidence interval = estimated value ± standard error), and
95% if the confidence interval is calculated using twice the standard error
(95% confidence interval = estimated value ± 2 × standard error*)

Example 2: Calculating confidence intervals

LFI5
volume of deadwood (stemwood)
ownership (2 categories)
regional demarcation: production region
unit: m³/ha
evaluation area: accessible forest without shrub forest
grid: 1.4 km grid, subgrids 1-5
state 2018/26
	production region
	Jura
ownership (2 classes)	m³/ha	±%
public	30	10
private	27	17
total	29	9

Question
What are the 68% and 95% confidence intervals of the above estimates?

Procedure

Calculate the absolute standard error (= relative standard error × estimated value / 100)
Calculate the confidence intervals
- 68% confidence interval = estimated value ± absolute standard error
- 95% confidence interval = estimated value ± 2 × absolute standard error

Answer

			Step 1	Step 2

ownership (2 categories)	volume of deadwood Jura NFI5
	estimated value	standard error		confidence interval
		relative	absolute	68%	95%
	m³/ha	±%	±m³/ha	m³/ha	m³/ha
public	30	10	3	27-33	24-36
private	27	17	5	22-32	17-37
total	29	9	3	26-32calculated with the standard error, i.e. 29 ± 3	23-25calculated with twice the standard error, i.e. 29 ± 2 × 3

The volume of deadwood in the Jura is between 26 and 32 m³/ha with a statistical certainty of 68% and between 23 and 35 m³/ha with a statistical certainty of 95%.

The 95% confidence interval is larger than the 68% confidence interval. This results in higher statistical certainty with the 95% confidence interval.

Example 3: Visualisation of the 68% and 95% confidence intervals

Data: see example 2

When interpreting the results, one must define the level of statistical certainty that one would like to apply to the statement.

The 68% confidence interval is generally used in the National Forest Inventory (NFI).

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3. When are two results statistically different?*

This can be checked by comparing the confidence intervals of two estimated values:

If the 68% confidence intervals of two estimates do not overlap, it can be assumed with some certainty that the two populations differ.
If the 95% confidence intervals of two estimates do not overlap, it can be assumed with high certainty that the two populations differ.

Example 4: Interpretation of two results from the same inventory

NFI5
growing stock (stemwood)
ownership (2 categories)
regional demarcation: production region
unit: m³/ha
evaluation area: accessible forest without shrub forest
grid: 1.4 km grid, subgrids 1-5
state 2018/26
	production region
	Jura		Plateau		Pre-Alps		Alps		Southern Alps		Switzerland
ownership (2 categories)	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%
public	331	3	311	3	405	4	300	3	256	5	314	2
private	387	5	432	4	454	4	348	4	285	6	398	2
total	345	2	363	2	431	2	314	2	262	4	343	1

	case 2						case 1

case 1

Question
Is the growing stock per hectare greater in the Alps than in the Southern Alps?

Procedure

Calculate the absolute standard errors
Calculate the confidence intervals depending on the desired level of statistical certainty:
- 68% confidence intervals (some certainty; absolute standard error)
- 95% confidence intervals (high certainty; twice the absolute standard error)
Assess whether the confidence intervals corresponding to the desired level of statistical certainty do not overlap

Answer

ownership (2 categories)	growing stock NFI5
	Alps					Southern Alps
	estimated value	standard error		confidence interval		estimated value	standard error		confidence interval
		relative	absolute	68%	95%		relative	absolute	68%	95%
	m³/ha	±%	±m³/ha	m³/ha	m³/ha	m³/ha	±%	±m³/ha	m³/ha	m³/ha
total	314	2	6	308-320	302-326	262	4	10	252-272	242-282

Neither the 68%-confidence intervals nor the 95%-confidence intervals overlap (pairs of values in ).

In this case, the level of statistical certainty selected has no influence on the result.

Overall, this means that there is high statistical certainty that the growing stock per hectare is greater in the Alps than in the Southern Alps.

Case 2

Question
Is the growing stock per hectare greater in the Plateau than in the Jura?

Procedure

See case 1.

Answer

ownership (2 categories)	growing stock NFI5
	Jura					Plateau
	estimated value	standard error		confidence interval		estimated value	standard error		confidence interval
		relative	absolute	68%	95%		relative	absolute	68%	95%
	m³/ha	±%	±m³/ha	m³/ha	m³/ha	m³/ha	±%	±m³/ha	m³/ha	m³/ha
total	345	2	7	338-352	331-359	363	2	7	356-370	349-377

The 68%-confidence intervals do not overlap (pairs of values in ).
In contrast, the 95%-confidence intervals overlap (pairs of values in ).

In this case, the level of statistical certainty selected has an influence on the interpretation of the results. At the 68% confidence interval level, the conclusion is that the growing stock per hectare is higher in the Plateau than in the Jura. At the 95% confidence interval level, however, this conclusion cannot be drawn.

Considering both confidence interval levels, it can be said that there is some, but not high, statistical certainty that the growing stock per hectare is greater in the Plateau than in the Jura.

The confidence intervals can also be used to determine whether a value estimated with a sample from the National Forest Inventory (NFI) deviates from a target value (e.g. from Swiss forest policy) or whether a change between two inventories is statistically certain.

Example 5: Interpretation of two results from different inventories

ownership (2 categories)	growing stock Plateau*
	NFI4		NFI5
	m³/ha	±%	m³/ha	±%
public	340	3	309	3
private	447	4	432	4
total	386	2	363	2
* accessible forest without shrub forest NFI4/NFI5

Question
Has the growing stock per hectare in the Plateau decreased from NFI4 to NFI5?

Procedure

Calculate the absolute standard errors
Calculate the confidence intervals depending on the desired level of statistical certainty:
- 68% confidence intervals (some certainty; absolute standard error)
- 95% confidence intervals (high certainty; twice the absolute standard error)
Assess whether the confidence intervals corresponding to the desired level of statistical certainty do not overlap.

Answer

ownership (2 categories)	growing stock Plateau*
	NFI4					NFI5
	estimated value	standard error		confidence interval		estimated value	standard error		confidence interval
		relative	absolute	68%	95%		relative	absolute	68%	95%
	m³/ha	±%	±	m³/ha	m³/ha	m³/ha	±%	±	m³/ha	m³/ha
public	340	3	11	329-351	318-362	309	3	11	298-320	287-331
private	447	4	16	431-463	415-479	432	4	17	415-449	398-466
total	386	2	8	378-394	370-402	363	2	9	354-372	345-381
* accessible forest without shrub forest NFI4/NFI5

The 68%-confidence intervals do not overlap in the public forest (pairs of values in ), but they do in the private forest and the total forest (pairs of values in ). At the certainty level of the 68% confidence intervals, it can be concluded that the growing stock per hectare in the public forest of the Plateau has decreased. For the private forest, as well as for the total forest, the decrease is not statistically certain at this level.

The 95%-confidence intervals overlap in all three categories. At the certainty level of the 95% confidence intervals, it is therefore not certain that the growing stock has decreased, even for the public forest.

See also examples 6 and 7, in which changes between two inventories are interpreted using the more sensitive metric of net change.

For many target variables in the NFI, it is possible to determine whether a change between two inventories is statistically certain, not only by comparing the states in the two inventories (see example 5), but also by analysing the net change** between the two inventories.

To do this, one must first define the level of statistical certainty that one would like to apply to the statement (as done above):

A net change has occurred with some certainty if the relative standard error is less than 100% or if the confidence interval calculated with the absolute standard error (68% confidence interval) does not include the value 0.
A net change has occurred with high certainty if twice the relative standard error is less than 100% or if the confidence interval calculated with twice the absolute standard error (95% confidence interval) does not include the value 0.

Example 6: Interpretation of net changes with the relative standard error

ownership (2 categories)	change in growing stock from NFI4 to NFI5, Plateau*
	estimated value	standard error
	m³/ha	±%
public	-34	30
private	-9	147
total	-23	34
* accessible forest without shrub forest NFI4/NFI5

Question
Has the growing stock per hectare in the Plateau decreased from NFI4 to NFI5?

Procedure

Define the level of statistical certainty (68% or 95% confidence interval)
Determine whether:
- the relative standard error is less than 100% (certainty level of the 68% confidence interval)
- twice the relative standard error is less than 100% (certainty level of the 95% confidence interval)

Answer

ownership (2 categories)	change in growing stock from NFI4 to NFI5, Plateau*
	estimated value	standard error
		single	double
	m³/ha	±%	±%
public	-34	30	60
private	-9	147	294
total	-23	34	68
* accessible forest without shrub forest NFI4/NFI5

The single relative standard error is less than 100% for both the public forest and the total forest (highlighted values). For the private forest, however, it is greater than 100% (highlighted values). At the certainty level of the 68% confidence interval, it can be concluded that the growing stock in the Plateau has decreased in the public forest and in total. For the private forest, on the other hand, the decrease in stock is not statistically certain at this level.

The same conclusion is reached in this example with the certainty level of the 95% confidence interval, as twice the relative standard error is again less than 100% for both the public forest and the total forest.

Overall, this means that there is high statistical certainty that the growing stock per hectare has decreased in the public forest in the Plateau, as well as overall. For private forests, on the other hand, the decrease in stock is not statistically certain (as twice the relative standard error and the relative standard error are both less than 100%).

Example 7: Interpretation of net changes with the absolute standard error

ownership (2 categories)	change in growing stock from NFI4 to NFI5, Plateau*
	estimated value	standard error
	%	±
public	-10	3
private	-2	3
total	-6	2
* accessible forest without shrub forest NFI4/NFI5

Question
Has the growing stock per hectare in the Plateau decreased from NFI4 to NFI5?

Procedure

Define the level of statistical certainty (68% or 95% confidence interval)
Calculate the confidence interval based on the defined certainty level
- 68% confidence interval with the absolute standard error
- 95% confidence interval with twice the absolute standard error
Determine whether the corresponding confidence interval does not include the value 0

Answer

ownership (2 categories)	change in growing stock from NFI4 to NFI5, Plateau*
	estimated value	standard error		confidence interval
		single	double	68%	95%
	%	±	±	%	%
public	-10	3	6	-13 to -7	-16 to -4
private	-2	3	6	-5 to +1	-8 to +4
total	-6	2	4	-8 to -4	-10 to -2
* accessible forest without shrub forest NFI4/NFI5

Neither the 68% nor the 95% confidence interval includes the value 0 for the public forest or for the total forest. At both certainty levels, this leads to the conclusion that the growing stock in the Plateau has decreased in the public forest and in total. For the private forest, on the other hand, the decrease in stock is not statistically certain (as the confidence intervals include the value 0).

Net changes can be interpreted using the absolute or relative standard error (see examples 6 and 7). It is advisable to use the absolute standard error if the estimated value in the table is shown as a percentage (%; as in example 7), and the relative standard error if the estimated value in the table is shown in absolute terms (m³, m³/ha, pc, m²; as in example 6). This means that the standard error can be taken directly from the table and does not need to be converted.

To assess whether a change is statistically certain, it is advisable to analyse the net change between the two inventories wherever possible. Net changes are more sensitive than status comparisons, which makes it easier to detect differences statistically. See examples 6 and 7 (net change) and 7 (comparison of two results from different inventories).

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4. When is it not sufficient to consider only the standard error?

The National Forest Inventory (NFI) is a sample-based large-scale inventory whose sample areas are arranged on a grid with a mesh size of 1.4 km × 1.4 km. The NFI was designed in such a way that the growing stock for Switzerland as a whole can be predicted with a maximum standard error of 1%.

If results are requested for individual regions or for individual classes, the standard error quickly becomes much larger. This is because the number of sample areas and subjects (e.g. sample trees, young forest plants, pieces of deadwood) analysed for the queried combination of variable expressions* is considerably lower than for the total.

Example 8: Standard error and combination of variable expressions

region	growing stock
	total		maple		sycamore		Norway maple
	estimated value	standard error	estimated value	standard error	estimated value	standard error	estimated value	standard error
	m³/ha	±%	m³/ha	±%	m³/ha	±%	m³/ha	±%
Switzerland	343	1	12	5	11	5	1	20
production region "Plateau"	363	2	15	10	14	11	0	50
Canton of Aargau	289	7	15	20	13	20	1	63

The standard error increases as the level of detail increases.

Large standard errors are to be expected if:

forest districts are selected as the regional demarcation or results for small cantons (e.g. Appenzell Innerrhoden, Nidwalden) are queried,
a classification variable with many classes is selected (e.g. tree species in 56 classes),
several classification variables are combined with each other (e.g. main tree species and development stage).

Large standard errors are an indication that the estimate may have been based on too small a number of sample areas or subjects and that the result of the estimate therefore may not be reliable.

For the target variable “number of stems of young forest plants with browsing damage” (browsing intensity), an uncertain estimate is not necessarily recognisable by a large standard error. This is because this target variable is a quotient estimator**, which is – due to the survey method – only based on a small number of assessed young forest plants for rarer tree species (e.g. pine, larch, Arolla pine, oak, chestnut). Accordingly, for this target variable one should always check how many young forest plants were assessed for the individual estimates. As a rule of thumb, at least 30 young forest plants per estimate should have been assessed for browsing in order to obtain a reliable estimate.

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5. Two types of changes?

There are two types of changes in the National Forest Inventory (NFI):

The first type of change involves specific target variables for change components such as increment, fellings or mortality. These target variables are only available for two consecutive measurement cycles, e.g. NFI4 to NFI5. When change components are analysed, the classification variable expression of the second measurement cycle is generally assigned to the first measurement cycle. These analyses therefore do not take into account any change in the expression (e.g. from private to public ownership) from the earlier to the later measurement cycle.
In the second type of change, the difference in target variables, such as stem number, growing stock or forest area, is used to calculate the net change between two measurement cycles. These target variables are usually used to represent states, e.g. that in NFI5, but can also show the net change between any two measurement cycles, e.g. between NFI1 and NFI5. In these net change analyses, the change in expression is taken into account for some of the classification variables, including “tree condition” and “forest, non-forest”. In this way, it can be seen, for example, that the forest area has increased. For the remaining classification variables, the expressions are regarded as static. This means that the most recent state – whether it was assessed in a measurement cycle (e.g. “primary forest function NFI5”) or taken from an external data source (e.g. “protection forest [2022]”) – is assigned to all measurement cycles.

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6. Change analyses: When are the results (not) additive?

The results are:

additive if they are reported as the total change between two measurement dates. For example, the fellings for the various production regions reported in cubic metres (m³) can be added together to obtain the total fellings for Switzerland.
not additive if they are reported as a change per year (e.g. m³/year). For example, the fellings for the various production regions reported in cubic metres per year (m³/year) cannot be added together to obtain the total fellings for Switzerland.

Example 9: : Additivity/non-additivity of changes

	growing stock: total change between NFI4 and NFI5 (in 1000 m³)*
	Jura		Plateau		Pre-Alps		Alps		Southern Alps		Switzerland
higher/lower altitude zone	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%
lower altitude zone	-3759.0	28	-4909.1	36	-1025.2	133	-317.1	195	3464.1	31	-6546.3	42
higher altitude zone	574.3	117	-328.0	62	1093.0	123	7128.4	21	666.7	93	9134.3	24
total	-3184.7	40	-5237.1	34	67.9	2805	6811.3	23	4130.8	30	2588.1	136
	* accessible forest without shrub forest NFI4/NFI5
	additive

	growing stock: annual change between NFI4 and NFI5 (in 1000 m³/year)*
	Jura		Plateau		Pre-Alps		Alps		Southern Alps		Switzerland
higher/lower altitude zone	1000 m³/year	±%	1000 m³/year	±%	1000 m³/year	±%	1000 m³/year	±%	1000 m³/year	±%	1000 m³/year	±%
lower altitude zone	-421.1	28	-560.6	36	-115.7	133	-35.9	195	389.5	31	-740.7	42
higher altitude zone	64.7	117	-38.3	62	122.4	123	810.4	21	74.9	93	1032.7	24
total	-357.3	40	-598.4	34	7.6	2805	773.8	23	464.4	30	292.7	136
	* accessible forest without shrub forest NFI4/NFI5
	not additive

The non-additivity of changes expressed per year arises because the total change is divided by the average number of years between the two measurement dates in the domain* under consideration, and this average number of years varies slightly depending on the domain.

Example 10: Average number of years per domain

domain		mean number of years*
production region	higher/lower altitude zone
Mittelland	-	8.75
Plateau	higher altitude zone	8.56
Plateau	lower altitude zone	8.76
Southern Alps	-	8.90
Southern Alps	higher altitude zone	8.90
Southern Alps	lower altitude zone	8.89
* between the NFI4 and NFI5 measurements in the accessible forest without shrub forest

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7. Why is a dot (“.”) sometimes given in the cells for standard error or estimated value?

In the calculation of a results table, data is not always available for all combinations of variable expressions*. In most cases, this indicates that the variable estimated with the relevant target variable does not occur or only occurs very rarely. The value 0 is then usually used. However, as this value is not based on any direct measurements, a dot (“.”) is given for the associated standard error. If reference is made to the assumed value of 0 in the calculation, e.g. in the case of percentages or certain change estimates, no value can be used. In this case, a dot (“.”) is given for the estimated value and the standard error.

For example, no Arolla pines have yet been found and measured in the Plateau in the National Forest Inventory (NFI) (growing stock of Arolla pine by production region). It can therefore be assumed that the values are missing because the Arolla pine actually does not occur in the Plateau, and therefore the growing stock in that region must be 0.

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8. Why are no standard error values shown in some tables?

The data in these tables originates from a complete survey and not from a sample inventory. Accordingly, it is not necessary to specify a standard error because there is no uncertainty due to sampling.

The forest road network survey that the National Forest Inventory (NFI) periodically carries out with the local forestry services is an example of such a complete survey.

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9. Negative values for growing stock, increment or fellings?

A negative value is possible if the result could only be calculated on the basis of a few trees. The estimate is therefore not reliable. This is also reflected in the standard error, which is usually extremely large for negative stock, increment or felling values.

Negative values can occur because, when the stemwood volume of the tally trees is determined, the volume estimated solely on the basis of the diameter at breast height (DBH) (tariff volume) is adjusted using the volume of the tally trees estimated on the basis of DBH, diameter at 7 m height and tree height. This procedure enables an unbiased and more accurate calculation of the stemwood volume. However, it can lead to negative values for all target variables that are based on the stemwood volume of the tally trees (e.g. growing stock, increment, fellings) if the number of tally trees in the selected combination of variable expressions* is small.

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NFI5
growing stock (stemwood)
development stage · altitudinal vegetation belts (NaiS; 6 classes)
regional demarcation: forest district (2024)
unit: 1000 m³
evaluation area: accessible forest without shrub forest NFI1-NFI5
grid: 1.4 km grid, subgrids 1-5
state 2018/26
		forest district (2024)
		AG01		AG02		AG03		AG04		AI01		AR01		BE01		BE02		BE03		BE04		BSBL01		BSBL02		BSBL03		BSBL04		FR01		FR02		FR03		FR04		GE01		GL01		GR01		GR02		GR03		GR04		GR05		JU01		LU01		LU02		LU03		NE01		NE02		NE03		NE04		NE06		NW01		OW01		OW02		SG01		SG02		SG03		SG04		SG05		SH01		SO01		SO02		SO03		SO04		SZ01		SZ02		SZ03		TG01		TG02		TG03		TI01		TI02		TI03		TI04		TI05		TI06		TI07		TI08		TI09		UR01		UR02		UR03		VD02		VD03		VD04		VD05		VD06		VD07		VD08		VD09		VD11		VD12		VD14		VD15		VD16		VD18		VD20		VD22		VS01		VS02		VS03		ZG01		ZH01		ZH02		ZH03		ZH04		ZH05		ZH06		ZH07		lakes		Switzerland
development stage	altitudinal vegetation belts (NaiS; 6 classes)	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%	1000 m³	±%
n/a	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	158	.	10	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	119	.	0	.	0	.	34	86	70	70	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	23	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	414	50
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	2	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	81	85	214	71	127	65	0	.	0	.	0	.	4	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	68	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	59	81	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	8	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	562	36
	lower and upper montane	0	.	0	.	0	.	0	.	0	.	36	.	34	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	2	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	97	.	0	.	0	.	11	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	170	.	0	.	16	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	10	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	375	54
	submontane	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	73	.	0	.	0	.	0	.	0	.	0	.	0	.	34	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	17	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	14	.	0	.	0	.	0	.	0	.	0	.	0	.	115	.	25	73	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	52	.	0	.	0	.	0	.	0	.	52	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	3	.	0	.	0	.	0	.	384	42
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	total	0	.	0	.	0	.	0	.	0	.	36	.	194	83	10	.	73	100	0	.	0	.	0	.	0	.	0	.	0	.	34	.	0	.	0	.	0	.	2	.	119	100	0	.	81	85	248	62	197	48	17	.	0	.	0	.	4	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	68	.	0	.	0	.	111	88	0	.	0	.	11	.	0	.	0	.	0	.	115	.	25	73	0	.	0	.	59	81	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	52	.	170	.	0	.	16	.	0	.	52	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	23	100	8	.	10	.	0	.	0	.	0	.	0	.	0	.	3	.	0	.	0	.	0	.	1736	22
young growth/ thicket	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	251	68	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	115	99	0	.	94	.	76	71	176	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	23	.	0	.	0	.	0	.	1	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	25	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	761	38
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	360	51	92	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	93	78	0	.	0	.	0	.	250	68	0	.	343	.	694	47	214	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	3	.	0	.	0	.	7	.	0	.	0	.	0	.	28	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	72	.	0	.	0	.	0	.	0	.	4	77	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	37	.	0	.	0	.	0	.	72	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	34	100	57	73	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	2359	25
	lower and upper montane	0	.	0	.	0	.	0	.	0	.	133	72	491	68	315	50	2	.	0	.	0	.	0	.	0	.	0	.	0	.	43	.	113	97	0	.	0	.	46	100	87	.	19	.	17	100	0	.	0	.	35	73	25	.	191	.	198	68	0	.	0	.	0	.	49	.	0	.	0	.	0	.	14	77	52	.	0	.	26	100	4	.	0	.	66	.	0	.	23	100	1	.	0	.	14	.	74	77	67	.	0	.	0	.	117	.	0	.	51	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	25	100	0	.	0	.	0	.	0	.	0	.	-12	.	0	.	0	.	0	.	148	77	82	100	0	.	0	.	26	.	0	.	0	.	10	.	0	.	0	.	0	.	0	.	78	71	38	.	6	.	186	61	0	.	0	.	12	.	0	.	0	.	2871	19
	submontane	154	72	57	71	72	.	28	56	0	.	0	.	183	79	8	.	328	62	73	.	46	.	9	.	0	.	0	.	0	.	31	100	0	.	101	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	63	77	0	.	130	70	0	.	0	.	0	.	52	.	0	.	0	.	0	.	0	.	0	.	0	.	19	100	0	.	10	.	0	.	13	.	0	.	33	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	99	81	65	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	174	72	0	.	0	.	0	.	0	.	1747	21
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	24	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	27	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	51	62
	total	154	72	57	71	72	.	28	56	0	.	133	72	1284	34	415	44	330	61	73	100	46	.	9	.	0	.	0	.	0	.	73	72	206	64	101	.	24	71	46	100	452	49	19	.	454	78	770	43	389	60	98	56	25	.	321	66	198	68	0	.	0	.	52	.	52	95	0	.	0	.	30	81	14	77	52	.	19	100	55	70	14	77	0	.	80	85	0	.	55	72	1	.	0	.	14	.	146	63	67	.	0	.	0	.	117	.	4	77	51	.	0	.	0	.	27	.	0	.	0	.	0	.	0	.	63	72	0	.	0	.	0	.	72	.	0	.	-12	.	0	.	0	.	99	81	213	62	82	100	0	.	0	.	26	100	0	.	0	.	10	.	0	.	34	100	82	59	0	.	78	71	38	.	6	.	186	61	174	72	0	.	12	.	0	.	0	.	7789	12
pole timber	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	181	43	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	34	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	55	83	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	270	36
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	27	.	0	.	0	.	160	71	239	67	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	3	.	0	.	65	.	0	.	0	.	0	.	113	.	0	.	0	.	0	.	0	.	33	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	316	57	0	.	35	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	991	30
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	639	41	0	.	0	.	17	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	175	86	97	.	396	40	724	35	75	81	0	.	0	.	0	.	160	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	8	.	0	.	48	.	24	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	77	.	0	.	0	.	0	.	0	.	184	50	164	73	0	.	1	.	0	.	0	.	0	.	2	.	0	.	0	.	0	.	299	76	47	.	181	75	152	.	0	.	0	.	39	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	367	42	376	43	446	50	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	4696	14
	lower and upper montane	0	.	0	.	0	.	22	.	0	.	266	88	535	42	442	43	790	41	207	52	51	.	62	.	78	84	0	.	0	.	0	.	281	57	184	61	0	.	448	64	0	.	0	.	0	.	242	60	0	.	532	62	317	63	482	63	547	45	271	65	135	73	0	.	50	70	0	.	177	80	112	70	6	.	268	61	178	72	148	79	0	.	146	.	46	.	249	62	86	69	40	.	120	.	420	51	372	66	95	.	50	.	0	.	97	.	0	.	78	73	0	.	378	50	0	.	241	64	528	42	19	.	42	88	99	.	258	77	0	.	25	.	63	73	85	.	245	66	0	.	0	.	0	.	158	86	0	.	0	.	67	.	48	.	77	.	98	.	0	.	44	.	0	.	16	.	16	119	120	71	0	.	108	82	76	73	284	87	0	.	0	.	0	.	0	.	11725	10
	submontane	433	40	401	39	363	54	183	63	0	.	0	.	25	.	21	.	961	25	0	.	189	53	138	63	253	71	0	.	85	.	143	97	0	.	300	79	0	.	0	.	0	.	33	.	0	.	0	.	0	.	151	72	149	72	241	59	0	.	99	58	0	.	47	.	0	.	0	.	0	.	0	.	159	.	52	.	0	.	0	.	0	.	0	.	273	58	0	.	0	.	89	71	47	.	0	.	0	.	0	.	315	53	223	59	246	69	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	95	.	61	.	0	.	152	.	438	62	0	.	51	.	130	74	0	.	42	.	0	.	202	79	0	.	34	.	0	.	68	.	0	.	0	.	239	56	0	.	107	.	359	51	43	.	172	59	405	51	242	63	383	47	0	.	8842	10
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	195	77	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	76	.	117	91	332	49	57	.	687	39	167	64	53	.	384	51	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	71	.	0	.	0	.	0	.	92	76	39	59	51	60	0	.	0	.	0	.	0	.	0	.	24	.	0	.	0	.	0	.	2345	19
	total	433	40	401	39	363	54	205	57	0	.	266	88	1199	29	463	41	1751	23	224	48	241	47	200	53	331	57	0	.	85	.	143	97	281	57	484	54	0	.	448	64	202	76	130	79	396	40	1320	27	495	38	682	51	465	48	724	46	708	41	370	50	135	73	47	.	50	70	0	.	177	80	112	70	172	92	320	53	226	60	172	70	0	.	146	100	318	52	249	62	86	69	129	58	168	77	420	51	448	57	95	.	364	48	223	59	344	57	187	49	352	44	183	68	710	35	57	.	928	33	809	33	74	76	426	46	99	.	258	77	331	69	167	65	305	51	237	74	397	56	438	62	39	.	51	.	289	58	0	.	42	.	67	.	250	66	149	71	132	79	0	.	113	72	830	30	432	38	787	33	120	71	107	.	467	44	119	59	457	59	428	48	242	63	383	47	0	.	28869	6
young timber	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	52	.	0	.	367	48	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	74	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	379	60	134	76	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1007	31
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	275	58	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	225	.	0	.	0	.	26	.	89	70	0	.	0	.	0	.	20	.	0	.	0	.	0	.	0	.	0	.	200	.	0	.	519	77	0	.	0	.	76	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	177	76	0	.	61	.	0	.	0	.	55	.	0	.	0	.	0	.	0	.	53	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	51	.	184	71	188	78	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	2199	27
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	262	64	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	85	.	0	.	0	.	0	.	0	.	333	71	670	56	313	59	595	52	553	53	0	.	0	.	0	.	76	.	0	.	0	.	0	.	0	.	0	.	0	.	113	.	0	.	0	.	0	.	52	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	80	.	39	.	124	.	0	.	0	.	0	.	141	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	118	.	0	.	0	.	0	.	0	.	700	40	782	58	397	66	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	5432	17
	lower and upper montane	72	.	0	.	0	.	0	.	218	.	284	71	385	55	578	55	710	46	1129	33	0	.	49	.	246	71	0	.	163	.	514	56	540	55	269	.	0	.	402	53	236	.	96	.	0	.	343	60	0	.	1161	39	137	.	502	62	179	71	0	.	263	87	0	.	17	.	0	.	434	78	37	.	312	62	0	.	624	60	738	51	294	.	58	.	310	70	0	.	370	58	146	71	0	.	0	.	129	.	0	.	374	73	0	.	105	.	0	.	70	.	0	.	23	.	416	57	213	71	455	70	803	43	224	71	492	55	0	.	0	.	314	57	77	.	54	.	0	.	0	.	243	70	0	.	0	.	80	.	259	71	364	83	80	.	124	.	0	.	0	.	0	.	0	.	0	.	288	60	222	.	118	.	0	.	841	49	427	59	0	.	0	.	0	.	0	.	18614	9
	submontane	143	.	574	44	131	70	553	55	0	.	0	.	0	.	508	59	1596	32	0	.	0	.	162	.	0	.	0	.	113	.	257	76	0	.	162	82	0	.	0	.	202	76	156	96	0	.	0	.	0	.	16	405	242	.	462	53	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	153	.	110	.	0	.	0	.	60	.	0	.	578	45	99	.	-1	.	82	89	180	76	89	.	0	.	0	.	0	.	167	74	373	58	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	249	.	0	.	97	.	58	.	154	.	0	.	0	.	0	.	65	.	146	78	0	.	0	.	323	62	252	64	0	.	221	73	57	.	0	.	0	.	0	.	0	.	11	.	0	.	117	.	0	.	252	78	271	71	265	72	71	.	454	60	0	.	10231	11
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	308	72	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	427	60	0	.	164	79	179	85	1062	35	158	71	262	68	403	46	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	71	.	0	.	0	.	0	.	0	.	0	.	0	.	193	66	43	.	31	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	3301	18
	total	215	74	574	44	131	70	553	55	218	.	284	71	923	34	1086	40	2305	26	1129	33	0	.	211	80	246	71	0	.	276	72	856	42	540	55	431	70	0	.	402	53	996	43	922	45	366	52	1271	34	1008	35	1177	39	379	73	964	41	275	54	0	.	263	87	0	.	17	.	0	.	634	62	151	79	984	47	110	.	624	60	865	45	354	85	58	.	889	38	99	.	369	58	228	56	180	76	89	.	129	.	0	.	374	73	167	74	478	50	0	.	673	44	74	.	249	58	595	47	1275	31	748	47	1103	35	751	36	741	50	0	.	150	74	513	46	231	75	54	.	0	.	0	.	309	59	146	78	0	.	80	.	654	43	616	56	198	72	346	59	57	.	0	.	0	.	1323	29	1143	42	914	38	222	.	235	71	0	.	1093	41	698	45	265	72	71	.	454	60	0	.	40784	6
medium timber	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	40	.	608	43	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	210	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	859	39
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	588	57	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	580	51	233	75	872	55	169	.	780	46	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	367	71	30	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	96	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	280	.	54	.	304	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	4354	21
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	396	74	168	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	377	.	0	.	0	.	0	.	0	.	264	85	536	63	342	72	1575	34	2204	29	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	45	.	0	.	0	.	0	.	175	.	0	.	144	.	0	.	0	.	0	.	0	.	0	.	0	.	210	.	0	.	0	.	0	.	0	.	0	.	70	.	208	71	0	.	0	.	0	.	0	.	364	71	136	71	271	.	0	.	451	.	593	71	0	.	104	.	145	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	938	52	496	61	644	52	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	10858	14
	lower and upper montane	254	75	0	.	0	.	0	.	812	59	1000	60	1535	35	1056	45	923	59	2930	26	114	.	281	71	315	80	0	.	524	64	385	55	1152	42	258	.	0	.	1035	40	775	52	360	76	0	.	72	.	0	.	1549	32	275	59	303	60	405	73	338	75	231	73	125	.	0	.	517	63	984	53	140	85	517	71	793	59	435	75	521	52	153	.	2229	33	555	51	791	53	556	47	0	.	1019	43	163	71	530	62	758	49	0	.	0	.	97	.	0	.	0	.	0	.	60	.	86	.	45	.	334	71	154	.	367	60	285	.	277	.	142	.	279	.	93	.	221	.	308	76	0	.	1066	40	0	.	262	68	1051	36	73	.	409	59	0	.	247	.	195	.	437	71	0	.	0	.	0	.	787	46	154	.	726	50	523	74	722	45	681	50	0	.	0	.	0	.	0	.	37748	7
	submontane	1141	37	328	58	427	60	57	107	0	.	0	.	0	.	0	.	2253	28	0	.	0	.	410	73	572	53	0	.	0	.	388	.	0	.	859	49	0	.	0	.	108	.	0	.	0	.	0	.	0	.	439	62	641	62	902	52	0	.	0	.	0	.	120	.	0	.	0	.	0	.	0	.	0	.	0	.	68	.	0	.	0	.	0	.	963	41	391	58	72	.	429	52	349	78	0	.	0	.	401	72	197	71	467	51	130	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	96	.	0	.	0	.	300	.	277	71	111	.	0	.	46	.	0	.	0	.	210	.	134	.	257	73	180	.	0	.	0	.	0	.	0	.	0	.	300	71	101	.	387	51	0	.	71	.	137	.	382	60	278	71	0	.	15382	10
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	301	71	0	.	0	.	0	.	0	.	88	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	104	.	0	.	348	68	724	48	0	.	0	.	197	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	94	.	0	.	0	.	0	.	0	.	0	.	0	.	199	71	16	.	0	.	0	.	0	.	0	.	0	.	0	.	60	.	0	.	0	.	0	.	2129	26
	total	1395	33	328	58	427	60	57	107	812	59	1000	60	2520	28	1224	41	3176	26	2930	26	114	.	691	52	887	45	0	.	524	64	1149	50	1152	42	1117	44	301	71	1035	40	1727	32	1129	41	1215	44	1944	29	3593	21	1988	28	916	47	1205	42	405	73	338	75	231	73	245	71	0	.	517	63	1029	51	140	85	517	71	793	59	679	55	521	52	298	71	2229	33	1518	32	1182	40	629	43	429	52	1368	38	373	64	530	62	1159	40	197	71	467	51	227	71	70	.	575	52	134	80	60	.	434	58	769	46	698	50	291	63	835	48	285	.	729	73	735	60	375	79	293	58	366	72	608	62	277	71	1177	38	0	.	308	60	1051	36	167	71	619	51	134	.	504	61	375	71	437	71	0	.	1417	41	776	48	1735	33	454	58	827	45	910	48	722	45	752	46	197	76	382	60	278	71	0	.	71329	5
old timber	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	71	.	0	.	0	.	206	71	744	43	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	559	46	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1580	28
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	919	46	128	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1295	43	0	.	1270	42	1183	44	2549	29	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	154	.	0	.	0	.	0	.	82	.	196	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	349	72	0	.	0	.	0	.	0	.	0	.	195	.	216	75	112	.	0	.	0	.	0	.	335	72	45	.	0	.	0	.	228	.	0	.	141	.	0	.	108	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1959	30	766	50	1438	39	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	13668	12
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	2583	32	109	.	0	.	207	.	0	.	0	.	0	.	0	.	255	.	119	.	349	74	390	71	0	.	859	63	1862	38	250	71	2148	35	4294	23	1342	40	0	.	0	.	0	.	207	.	0	.	0	.	0	.	0	.	0	.	0	.	532	75	463	58	0	.	0	.	192	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	233	76	209	.	170	.	0	.	0	.	0	.	384	71	317	.	1105	40	113	.	0	.	0	.	0	.	246	88	301	.	339	80	150	.	180	.	817	63	599	76	895	65	0	.	0	.	148	.	0	.	0	.	0	.	0	.	0	.	55	.	0	.	0	.	0	.	0	.	1824	37	1074	51	2095	33	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	27411	9
	lower and upper montane	196	.	20	.	0	.	753	50	2199	39	2831	33	3447	28	7050	19	2460	31	3406	23	0	.	0	.	577	76	0	.	0	.	1493	45	1782	35	1443	45	0	.	1011	48	552	59	1251	37	262	71	479	72	0	.	3478	25	762	50	2167	37	2696	32	455	72	788	60	125	.	615	58	1517	40	943	51	0	.	2034	40	1989	39	912	63	1636	37	2152	39	2811	31	284	.	716	49	0	.	482	71	471	59	1583	43	1573	39	1622	40	931	50	0	.	0	.	0	.	401	.	0	.	293	72	373	64	0	.	262	73	0	.	476	69	417	71	111	.	259	.	417	73	617	66	348	71	394	71	0	.	1175	42	321	.	0	.	257	.	1114	46	285	71	602	58	112	.	459	52	97	.	510	71	0	.	0	.	645	62	420	73	467	71	0	.	1790	38	883	56	0	.	0	.	192	.	0	.	77648	5
	submontane	439	53	591	55	803	50	2719	27	0	.	0	.	737	59	1311	37	5663	18	0	.	165	.	477	61	233	72	252	.	469	72	219	.	0	.	315	72	0	.	0	.	118	.	0	.	0	.	0	.	0	.	1651	39	526	58	681	50	0	.	109	73	0	.	305	.	0	.	0	.	0	.	0	.	0	.	242	.	0	.	142	.	151	.	0	.	1199	42	924	48	79	.	532	52	0	.	189	.	0	.	0	.	695	61	1638	37	1604	34	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	310	.	0	.	381	75	0	.	130	.	0	.	0	.	0	.	0	.	189	.	218	.	188	.	147	.	0	.	179	.	0	.	0	.	83	.	0	.	329	71	265	75	0	.	520	59	636	56	282	60	559	48	0	.	29598	7
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	151	.	0	.	0	.	0	.	0	.	0	.	73	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	120	.	169	.	62	.	0	.	440	60	272	80	130	.	383	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	142	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1941	28
	total	635	48	611	53	803	50	3473	24	2199	39	2831	33	7686	18	8598	16	8123	15	3613	23	165	.	477	61	811	58	252	.	725	58	1830	39	2131	31	2148	34	151	.	1870	39	3898	25	1500	33	3680	25	6162	19	4707	21	5129	21	1287	38	2848	31	2903	30	564	60	788	60	430	76	615	58	1517	40	1097	46	532	75	2497	34	2231	37	993	58	2166	31	2303	37	2811	31	1482	39	1640	34	79	.	1014	43	471	59	2353	33	1782	36	1791	37	1626	39	1638	37	1604	34	579	58	1055	52	1387	35	468	52	373	64	440	60	869	43	421	61	1160	45	756	53	488	60	439	72	1375	44	1526	45	1351	47	775	52	0	.	1454	36	321	.	0	.	257	.	1114	46	475	59	875	47	300	73	606	46	97	.	689	58	4484	21	1839	36	4260	23	420	73	796	51	265	75	1790	38	1403	41	636	56	282	60	752	44	0	.	151846	3
mixed	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	282	64	1297	29	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	86	.	76	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	461	41	316	47	52	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	2572	19
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	2454	28	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	443	64	643	43	604	57	517	43	920	40	1488	32	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	231	89	158	.	0	.	0	.	348	99	0	.	75	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	275	66	550	51	379	66	0	.	0	.	0	.	230	75	76	.	0	.	80	.	181	.	119	.	0	.	159	80	27	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	77	.	0	.	0	.	0	.	0	.	1834	40	1238	31	592	46	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	13699	11
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	2183	28	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	93	.	0	.	0	.	0	.	210	75	441	58	443	47	786	38	1612	30	655	48	0	.	155	.	0	.	75	.	0	.	0	.	0	.	0	.	0	.	0	.	699	52	133	72	0	.	0	.	62	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	210	72	63	.	63	.	0	.	0	.	0	.	388	72	256	.	299	81	86	.	0	.	0	.	204	75	0	.	0	.	122	.	0	.	304	64	0	.	245	78	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	69	.	0	.	0	.	0	.	0	.	777	37	2348	27	1006	37	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	13989	10
	lower and upper montane	102	.	0	.	0	.	88	.	291	.	200	71	2013	29	4396	19	379	60	1989	26	0	.	0	.	88	.	0	.	0	.	152	.	926	39	377	71	0	.	970	44	639	44	788	46	0	.	231	.	0	.	1944	33	937	44	304	65	2115	30	102	.	1670	30	476	52	779	49	1784	32	227	87	134	96	654	52	696	59	0	.	573	54	1044	45	1186	43	121	.	85	.	389	77	111	.	185	72	150	.	207	75	162	87	327	63	0	.	0	.	0	.	1562	83	0	.	99	80	422	51	235	76	314	54	313	65	60	.	129	.	0	.	237	.	252	71	0	.	826	55	470	.	0	.	641	46	0	.	0	.	1205	28	179	59	746	43	265	71	0	.	69	.	0	.	0	.	0	.	0	.	1235	37	251	73	0	.	0	.	109	69	132	73	0	.	0	.	0	.	0	.	39745	7
	submontane	232	70	274	54	325	53	0	.	0	.	0	.	176	.	505	51	803	46	0	.	318	61	0	.	223	66	0	.	84	.	0	.	0	.	430	72	0	.	0	.	0	.	212	74	0	.	0	.	0	.	928	40	869	53	530	61	307	74	19	.	0	.	251	72	49	.	0	.	0	.	0	.	0	.	0	.	567	63	92	.	246	.	0	.	336	71	57	.	0	.	0	.	276	58	0	.	0	.	0	.	268	71	0	.	200	73	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	352	.	0	.	161	.	61	.	0	.	0	.	0	.	7	.	0	.	0	.	0	.	0	.	131	.	0	.	373	71	71	.	0	.	0	.	297	.	0	.	0	.	0	.	0	.	274	.	413	58	0	.	204	73	204	71	310	68	36	.	0	.	11470	12
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	285	71	113	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	86	.	90	.	134	92	0	.	168	66	545	44	380	58	295	61	291	57	578	50	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	226	71	72	72	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	3262	18
	total	334	57	274	54	325	53	88	.	291	.	200	71	6827	16	4902	18	1182	36	1989	26	318	61	0	.	310	55	0	.	84	.	244	73	926	39	807	51	0	.	1622	33	1724	27	2047	27	1302	29	3330	21	3553	19	2872	26	1961	32	834	45	2498	27	121	86	1670	30	727	42	828	47	1784	32	227	87	1065	41	944	41	696	59	567	63	1075	44	1290	41	1261	40	457	58	143	72	389	77	111	.	461	45	360	59	269	62	225	69	595	47	0	.	286	59	753	46	2589	52	754	47	353	46	967	33	615	46	1043	32	681	40	638	46	683	59	181	.	821	45	313	61	404	57	853	54	470	.	7	.	641	46	0	.	0	.	1205	28	309	54	746	43	785	43	71	.	69	.	0	.	297	.	3073	26	4128	18	2958	22	251	73	274	.	413	58	109	69	336	52	204	71	310	68	36	.	0	.	84736	4
total	n/a	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.
	upper subalpine	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	71	.	0	.	52	.	529	45	3197	18	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	120	77	150	70	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1454	27	660	42	52	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	6286	13
	subalpine	0	.	0	.	0	.	0	.	0	.	0	.	4646	20	138	93	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	443	64	3004	24	837	46	2753	27	2568	26	5391	18	0	.	0	.	0	.	20	.	0	.	0	.	0	.	0	.	0	.	354	71	255	81	676	63	0	.	82	.	621	65	0	.	75	.	0	.	0	.	0	.	0	.	0	.	349	72	0	.	0	.	0	.	0	.	0	.	473	56	1311	33	587	48	61	.	0	.	0	.	734	44	121	73	0	.	80	.	408	71	204	66	141	.	255	62	135	82	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	77	.	0	.	0	.	0	.	0	.	4464	22	2267	25	2557	28	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	36086	7
	high-montane	0	.	0	.	0	.	0	.	0	.	0	.	6425	18	369	60	0	.	224	93	0	.	0	.	0	.	0	.	255	.	673	61	442	61	390	71	0	.	1068	52	3325	26	1996	29	4409	21	9707	13	5169	18	0	.	155	.	0	.	522	54	0	.	0	.	0	.	3	.	0	.	45	.	1352	40	603	47	0	.	223	81	357	59	144	.	68	100	0	.	0	.	0	.	0	.	0	.	652	48	420	58	233	78	0	.	0	.	0	.	1031	39	945	47	1463	34	200	71	0	.	0	.	648	48	423	57	697	61	499	60	601	79	1376	40	1004	53	1200	44	1192	52	0	.	0	.	186	82	0	.	0	.	0	.	0	.	0	.	242	61	0	.	0	.	0	.	0	.	4641	20	5140	19	4587	20	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	65306	5
	lower and upper montane	623	48	20	.	0	.	863	45	3520	29	4750	24	8439	15	13836	12	5264	20	9661	13	166	76	392	55	1304	42	0	.	687	54	2586	30	4794	19	2531	32	0	.	3914	21	2290	28	2513	26	279	67	1366	35	0	.	8698	15	2452	26	3949	25	6141	18	1167	39	3088	24	726	42	1510	35	3819	23	2765	30	424	46	3537	27	3798	26	2150	36	3642	23	3647	28	6429	19	1381	34	1840	31	1521	31	780	48	1796	30	2341	32	2884	26	2703	28	1682	35	0	.	415	50	0	.	2162	63	0	.	853	35	1296	31	733	39	1894	27	1289	33	1169	37	1447	36	646	55	638	59	1288	38	850	50	1704	35	1405	44	16	.	3126	23	321	.	568	44	2675	22	1626	34	1871	29	1022	40	561	55	821	40	544	60	555	66	0	.	16	.	2982	24	1244	37	1349	37	637	63	3724	23	2408	29	0	.	12	.	192	.	0	.	188726	3
	submontane	2542	22	2225	22	2121	26	3541	23	0	.	0	.	1121	44	2354	26	11676	12	73	.	718	39	1197	38	1281	32	252	.	752	50	1071	47	0	.	2168	29	0	.	0	.	428	52	401	55	0	.	0	.	0	.	3265	24	2427	30	2945	24	307	74	227	44	0	.	775	49	49	.	0	.	0	.	0	.	312	70	404	67	653	56	235	72	467	63	0	.	3362	22	1472	35	197	57	1132	32	853	41	278	75	0	.	401	72	1475	35	2610	26	2579	25	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	602	72	0	.	258	73	311	51	577	62	0	.	833	53	722	46	307	60	347	45	241	52	0	.	496	49	652	50	927	43	738	43	417	58	0	.	544	65	0	.	0	.	332	47	300	71	928	44	1424	29	295	68	1411	30	1650	30	1288	30	1710	27	0	.	77654	4
	hyperinsubric and colline	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	475	55	0	.	0	.	0	.	0	.	876	39	185	72	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	86	.	90	.	757	42	391	57	726	33	1156	32	3293	19	892	36	735	37	1944	26	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	165	71	0	.	0	.	71	.	0	.	0	.	0	.	626	40	324	52	154	44	0	.	0	.	0	.	0	.	0	.	83	77	0	.	0	.	0	.	13029	8
	total	3166	20	2245	22	2121	26	4404	20	3520	29	4750	24	20632	9	16697	10	16939	10	9958	12	884	34	1589	32	2585	26	252	.	1694	35	4330	23	5236	18	5089	21	475	55	5426	19	9118	14	5748	17	7494	16	15046	10	13943	10	11963	12	5033	19	6895	17	6990	17	1393	33	3088	24	1501	32	1562	34	3819	23	3164	27	2030	30	5129	22	4202	25	3108	28	4855	20	4259	25	6573	19	4744	18	3312	23	1717	28	1913	27	2648	24	3620	24	3304	24	3337	25	3157	24	2610	26	3080	22	1593	31	5295	29	2591	24	1840	22	2452	22	4026	17	4168	18	2569	22	3810	20	2627	28	1655	40	2476	28	2743	27	2883	27	3031	29	2238	34	738	45	3620	21	669	53	809	34	2675	22	2286	27	2523	25	2267	26	1370	33	1238	33	544	60	1098	46	11185	13	8408	14	10664	13	1544	33	2276	28	2060	28	4019	22	3819	21	1733	29	1299	30	1903	26	0	.	387089	1

Table citation

Abegg, M.; Ahles, P.; Allgaier Leuch, B.; Cioldi, F.; Didion, M.; Düggelin, C.; Fischer, C.; Herold, A.; Meile, R.; Rohner, B.; Rösler, E.; Speich, S.; Temperli, C.; Traub, B.,
2023: Swiss national forest inventory - Result table No. 2278362. Birmensdorf, Swiss Federal Research Institute WSL

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