Selection from the list of topics

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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NFI4
volume of bolewood (HG 2010)
type of assortment · ownership (2 categories)
regional demarcation: forest district (2024)
unit: 1000 m³
evaluation area: accessible forest without shrub forest NFI4/NFI5
grid: 1.4 km grid, subgrids 1-5
state 2009/17
		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
type of assortment	ownership (2 categories)	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	.
	public	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0
	private	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	.	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	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	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	0	.	0	0
coniferous wood	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	.
	public	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	12	100	0	.	0	.	0	.	0	.	0	.	0	.	6	100	0	.	0	.	0	.	0	.	0	.	17	100	19	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	9	100	0	.	0	.	13	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	38	100	0	.	0	.	76	100	0	.	0	.	0	.	0	.	0	.	31	100	0	.	0	.	68	60	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	29	73	19	81	0	.	0	.	156	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	494	31
	private	59	100	30	100	0	.	147	100	0	.	0	.	7	100	2	100	80	100	0	.	0	.	21	100	84	100	0	.	0	.	0	.	0	.	21	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	14	100	0	.	0	.	0	.	0	.	167	94	0	.	0	.	0	.	0	.	0	.	0	.	15	100	0	.	103	80	0	.	0	.	0	.	106	72	98	81	0	.	28	100	0	.	26	100	0	.	0	.	57	98	0	.	29	100	0	.	11	100	0	.	0	.	33	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	25	100	0	.	0	.	9	100	19	94	101	100	0	.	0	.	127	100	67	100	0	.	0	.	0	.	0	.	0	.	0	.	1487	24
	total	59	100	30	100	0	.	147	100	0	.	0	.	7	100	2	100	80	100	12	100	0	.	21	100	84	100	0	.	0	.	0	.	6	100	21	100	0	.	0	.	0	.	0	.	17	100	19	100	0	.	0	.	0	.	0	.	0	.	14	100	0	.	0	.	0	.	0	.	167	94	9	100	0	.	0	.	13	100	0	.	0	.	15	100	0	.	103	80	0	.	0	.	0	.	145	59	98	81	0	.	104	78	0	.	26	100	0	.	0	.	57	98	31	100	29	100	0	.	78	53	0	.	0	.	33	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	25	100	0	.	0	.	9	100	47	58	121	85	0	.	0	.	282	59	67	100	0	.	0	.	0	.	0	.	0	.	0	.	1980	19
coniferous shortwood	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	.
	public	496	36	503	42	674	42	912	36	1096	42	978	48	3977	21	1402	34	2333	21	2029	23	38	77	134	69	615	45	0	.	484	53	961	43	860	39	407	70	79	100	1843	28	4507	17	3802	18	4586	19	10693	11	10063	10	250	47	687	35	1200	43	1191	33	0	.	21	100	0	.	0	.	69	100	918	43	1148	36	1351	28	91	88	858	38	1845	28	644	56	803	55	1467	25	1206	32	679	35	476	48	440	44	1961	30	600	44	1331	35	26	100	215	56	503	51	1130	31	2374	25	2204	26	199	47	21	100	54	81	1509	23	627	34	909	36	959	41	539	55	1604	31	368	55	1374	34	585	52	394	63	166	79	744	41	109	72	74	95	760	36	311	58	673	39	770	46	493	62	364	62	0	.	7	100	6233	13	4413	17	6284	15	195	63	273	53	570	42	402	55	549	42	408	66	209	78	545	43	0	.	112856	3
	private	247	58	14	100	0	.	88	59	1205	43	1815	33	12246	11	5537	16	3485	21	1356	36	1	100	16	100	8	100	0	.	155	100	1237	37	1715	39	371	50	36	81	252	66	2173	26	806	42	2063	28	1279	33	405	55	0	.	1689	33	1569	30	4691	21	0	.	231	82	0	.	0	.	0	.	341	52	176	.	730	62	181	61	557	57	384	47	655	60	1839	38	266	57	0	.	0	.	57	80	96	51	167	72	642	51	483	51	712	46	458	49	614	42	138	75	0	.	139	100	0	.	0	.	59	70	0	.	0	.	0	.	341	48	587	61	203	76	267	49	479	48	1543	38	291	62	170	61	71	71	0	.	0	.	233	51	7	100	0	.	147	100	21	100	179	100	0	.	0	.	2599	26	1220	27	1110	33	518	69	170	71	182	81	899	37	969	38	280	65	98	100	173	72	0	.	66145	5
	total	743	31	517	41	674	42	1000	34	2301	30	2794	27	16223	10	6938	15	5819	15	3385	20	39	74	150	62	623	44	0	.	639	47	2199	28	2575	29	778	44	115	73	2095	26	6680	14	4608	17	6650	15	11972	10	10469	10	250	47	2376	25	2769	25	5883	18	0	.	253	75	0	.	0	.	69	100	1259	34	1324	34	2081	29	272	50	1415	32	2230	24	1299	41	2642	31	1733	23	1206	32	679	35	534	43	536	37	2128	29	1242	34	1814	29	737	45	673	38	1117	33	1267	29	2374	25	2343	25	199	47	21	100	113	53	1509	23	627	34	909	36	1300	33	1126	41	1807	29	635	38	1853	28	2128	31	685	45	337	50	815	38	109	72	74	95	993	30	318	56	673	39	917	41	514	60	543	53	0	.	7	100	8832	12	5633	15	7394	14	713	53	442	43	752	37	1301	31	1518	28	688	47	307	62	718	37	0	.	179001	2
coniferous mediumwood	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	.
	public	0	.	44	81	0	.	406	62	0	.	0	.	336	100	350	54	544	47	886	35	0	.	289	77	37	75	180	.	0	.	194	64	571	44	641	51	0	.	1871	35	125	71	47	100	0	.	59	100	0	.	724	36	0	.	63	100	0	.	286	59	15	100	55	100	6	100	76	89	0	.	346	65	453	44	146	100	236	100	243	47	759	49	422	58	0	.	0	.	0	.	0	.	106	61	504	51	793	44	38	100	0	.	158	100	0	.	2	100	183	80	0	.	116	100	0	.	0	.	0	.	0	.	0	.	0	.	112	99	266	100	662	54	117	71	27	100	61	100	0	.	43	100	0	.	31	100	104	100	98	100	0	.	77	100	0	.	0	.	314	71	0	.	108	72	687	39	549	57	208	65	259	73	0	.	7	100	52	100	33	100	280	76	34	82	0	.	16439	9
	private	0	.	15	100	0	.	89	100	0	.	297	100	753	42	1947	29	1806	33	47	100	38	100	0	.	39	100	0	.	0	.	0	.	231	76	70	100	0	.	132	94	0	.	16	100	0	.	0	.	0	.	129	77	204	77	404	70	16	100	0	.	0	.	129	100	0	.	0	.	170	100	0	.	207	100	104	71	0	.	258	77	182	77	1455	37	0	.	0	.	0	.	0	.	0	.	0	.	193	100	0	.	6	100	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	196	100	0	.	169	75	0	.	0	.	43	100	0	.	54	100	0	.	0	.	0	.	0	.	0	.	129	100	0	.	0	.	0	.	94	79	25	100	343	69	73	71	0	.	242	100	110	100	224	56	75	100	0	.	0	.	0	.	0	.	10714	12
	total	0	.	59	65	0	.	496	54	0	.	297	100	1089	42	2297	26	2351	28	933	33	38	100	289	77	76	63	180	.	0	.	194	64	803	38	711	47	0	.	2002	33	125	71	63	79	0	.	59	100	0	.	853	33	204	77	467	62	16	100	286	59	15	100	185	76	6	100	76	89	170	100	346	65	660	43	250	65	236	100	501	46	942	42	1877	31	0	.	0	.	0	.	0	.	106	61	504	51	986	41	38	100	6	100	158	100	0	.	2	100	183	80	0	.	116	100	0	.	0	.	0	.	0	.	0	.	0	.	308	73	266	100	831	45	117	71	27	100	104	72	0	.	97	71	0	.	31	100	104	100	98	100	0	.	206	73	0	.	0	.	314	71	94	79	133	61	1030	35	621	51	208	65	501	61	110	100	230	55	127	72	33	100	280	76	34	82	0	.	27153	7
coniferous longwood	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	.
	public	65	100	69	74	242	63	1007	42	208	100	652	55	184	100	1836	31	656	43	1529	30	14	100	0	.	0	.	0	.	272	75	399	69	655	61	670	58	0	.	75	92	0	.	0	.	0	.	0	.	0	.	3693	23	234	100	274	81	0	.	399	65	766	44	717	41	708	40	974	35	0	.	0	.	0	.	523	51	0	.	183	91	196	100	0	.	334	71	0	.	203	98	0	.	0	.	0	.	264	73	28	100	189	88	202	75	358	62	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	41	71	0	.	0	.	105	100	0	.	997	37	151	75	492	45	797	31	489	55	554	40	549	51	47	100	266	58	155	100	210	100	0	.	0	.	250	74	291	72	0	.	14	100	1	100	0	.	0	.	141	100	165	82	0	.	24494	8
	private	16	100	26	100	0	.	0	.	288	100	46	100	0	.	447	70	758	47	311	62	0	.	0	.	124	100	0	.	0	.	255	100	0	.	343	58	0	.	0	.	0	.	0	.	0	.	0	.	0	.	1354	29	0	.	1347	36	178	100	234	74	1010	36	76	100	205	72	1498	32	0	.	0	.	1	100	948	54	0	.	113	100	0	.	308	72	0	.	0	.	0	.	0	.	82	73	0	.	0	.	0	.	220	60	278	90	284	71	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	103	71	92	100	0	.	237	70	138	100	33	100	6	100	0	.	0	.	0	.	209	100	0	.	0	.	0	.	0	.	0	.	145	59	542	52	547	57	179	100	35	100	0	.	0	.	13018	11
	total	81	83	95	61	242	63	1007	42	496	71	698	52	184	100	2283	28	1414	32	1841	27	14	100	0	.	124	100	0	.	272	75	654	57	655	61	1013	43	0	.	75	92	0	.	0	.	0	.	0	.	0	.	5047	18	234	100	1621	33	178	100	633	49	1776	27	794	38	913	35	2472	23	0	.	0	.	1	100	1471	39	0	.	296	68	196	100	308	72	334	71	0	.	203	98	0	.	82	73	0	.	264	73	28	100	409	52	481	61	642	47	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	0	.	41	71	0	.	0	.	105	100	0	.	1100	34	243	60	492	45	1034	29	628	48	587	38	556	51	47	100	266	58	155	100	419	71	0	.	0	.	250	74	291	72	0	.	159	54	543	52	547	57	179	100	175	83	165	82	0	.	37512	6
broadleaf roundwood	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	.
	public	1394	24	1058	36	889	30	1111	25	84	54	262	59	904	31	1018	26	3266	17	3004	16	706	40	894	34	1633	31	0	.	335	59	591	41	740	31	327	55	146	60	1036	27	393	37	732	28	323	35	1383	22	186	44	3048	17	669	36	442	49	91	43	249	41	191	40	284	38	238	47	196	36	347	56	69	40	1215	31	519	45	512	51	964	30	1267	38	533	43	1921	22	1098	31	1121	27	1038	31	980	29	688	35	275	80	702	41	294	46	430	45	994	46	142	45	801	27	222	47	1082	25	559	34	589	36	1618	22	1011	26	996	28	238	43	128	59	155	64	649	42	435	57	397	47	172	57	84	56	926	31	324	69	185	44	300	34	579	31	916	34	434	43	437	48	142	50	272	51	205	88	197	40	128	35	1071	22	248	56	800	35	395	39	192	50	650	38	587	37	617	40	739	32	0	.	62414	3
	private	906	39	391	47	0	.	1146	43	204	58	775	38	3165	22	2608	20	2517	19	660	34	166	96	253	95	572	50	0	.	103	88	749	45	708	42	1108	33	299	79	654	41	428	56	294	55	293	59	223	61	181	57	1665	27	1311	41	677	35	1454	26	354	64	189	47	45	73	99	70	244	49	586	43	0	.	220	56	703	43	1056	44	594	43	363	46	2037	24	352	54	408	63	95	.	278	74	700	41	355	57	165	54	425	53	973	34	764	47	659	34	39	91	0	.	150	100	242	60	1465	26	2292	19	365	61	377	45	1275	30	666	46	94	96	86	77	303	53	349	53	186	45	641	53	114	71	365	48	162	76	0	.	29	60	156	64	347	54	349	64	398	54	346	74	0	.	285	70	381	50	292	35	673	38	282	57	171	65	273	44	1253	28	615	36	448	59	299	69	87	73	0	.	51030	4
	total	2300	21	1449	29	889	30	2256	25	288	44	1037	32	4069	18	3626	16	5783	12	3664	14	872	37	1147	34	2205	27	0	.	438	49	1340	31	1448	26	1435	28	445	56	1690	23	822	34	1026	25	617	33	1606	21	368	36	4713	14	1980	30	1119	28	1546	25	603	41	380	30	329	34	337	39	440	31	933	34	69	40	1435	28	1222	31	1568	34	1557	24	1630	31	2570	21	2273	20	1506	28	1216	26	1316	29	1680	24	1043	30	440	54	1126	32	1266	28	1194	34	1653	31	182	40	801	27	372	49	1325	23	2024	21	2882	16	1983	21	1389	22	2270	21	904	36	222	53	240	50	952	33	784	40	583	35	812	43	197	47	1291	26	487	52	185	44	329	32	736	28	1263	28	783	37	835	36	488	54	272	51	489	55	578	36	420	26	1744	20	531	40	970	31	668	29	1445	25	1264	26	1035	33	916	35	826	29	0	.	113443	2
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	.
	public	1954	24	1674	28	1805	26	3436	21	1388	38	1893	36	5401	19	4606	19	6799	14	7461	14	757	39	1317	34	2284	29	180	.	1092	38	2145	29	2832	24	2046	30	225	63	4825	20	5025	16	4582	18	4927	18	12154	10	10249	10	7715	14	1590	28	1978	33	1283	33	935	40	993	38	1057	36	952	36	1315	30	1265	37	1573	30	3019	21	1279	36	1619	32	3234	22	2866	28	1758	35	3722	19	2304	26	2003	26	1514	29	1525	28	3191	24	1931	28	2099	29	584	46	1005	38	1855	34	1274	29	3358	20	2427	25	1429	22	580	34	643	35	3195	16	1638	23	1904	23	1197	38	779	42	2025	30	1719	30	1927	29	1008	44	732	45	250	61	2710	24	584	61	782	36	1962	22	1478	29	2143	25	1830	29	977	43	772	39	741	54	422	70	6567	12	5248	15	8154	13	943	36	1487	32	979	34	601	48	1251	34	1028	37	1246	34	1483	29	0	.	216696	2
	private	1228	34	475	44	0	.	1471	38	1697	39	2933	28	16171	11	10540	13	8647	14	2374	27	206	81	291	91	827	45	0	.	258	74	2241	31	2655	33	1913	27	335	76	1038	38	2601	24	1116	37	2357	25	1502	30	587	43	3148	22	3204	26	3998	21	6340	19	602	51	1430	32	250	73	304	71	1742	30	1265	34	176	.	1158	48	1936	34	1613	37	1349	34	1200	45	5655	21	617	47	511	59	95	.	335	72	879	39	628	45	1099	39	908	41	1939	29	1500	38	1583	29	177	71	0	.	346	61	242	60	1495	26	2352	19	375	61	377	45	1275	30	1040	40	877	50	289	68	739	43	828	43	1729	36	974	51	284	60	593	42	255	71	0	.	499	43	302	62	380	55	631	50	443	54	525	71	0	.	596	58	3024	24	1956	23	1856	27	801	57	709	53	778	38	2918	23	2206	27	906	46	431	59	260	71	0	.	142393	3
	total	3183	19	2150	24	1805	26	4906	18	3085	27	4826	22	21571	9	15146	10	15446	10	9835	12	963	35	1608	32	3111	24	180	.	1350	34	4387	21	5486	20	3959	20	560	52	5862	18	7627	13	5698	16	7284	14	13656	10	10836	10	10863	12	4794	19	5976	18	7622	16	1536	31	2424	24	1307	32	1256	32	3057	21	2530	25	1749	29	4177	20	3215	25	3232	24	4583	18	4066	24	7413	18	4339	18	2815	24	2098	25	1849	27	2404	23	3819	21	3030	23	3007	24	2523	25	2506	27	3438	22	1451	26	3358	20	2773	23	1671	21	2075	21	2995	16	3570	16	2016	20	3179	18	2236	27	1656	33	2314	27	2458	24	2755	24	2737	28	1706	35	534	43	3303	21	838	47	782	36	2460	20	1780	26	2524	22	2462	25	1420	34	1297	37	741	54	1018	45	9591	11	7204	13	10010	12	1744	32	2195	27	1757	25	3519	21	3456	21	1935	29	1678	30	1742	26	0	.	359089	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. 2290383. Birmensdorf, Swiss Federal Research Institute WSL

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