NFI13
NFI data
The sample plot data of the 13th national forest inventory (NFI13)
from the years 2019–2023 (Korhonen et al. 2024) were used in the calculations.
MELA data
The input data for MELA, based on the NFI13 field
measurements, covers the stands that include a NFI plot center and
are on forest land or on poorly productive forest lands. The total
number of calculation units in the input data is 51051.
The trees of input data were generated using a model-based
approach based on the measurements of stand-level
characteristics (the stratum-level basal-area, mean diameter
and mean height) and measured NFI sample trees.
The stratum-level measurements describe the growing stock of
the stand realistically, but the measurements are not fully
objective and therefore not unbiased. The tree-level
measurements from NFI plots are based on objective procedures
and yield unbiased estimates at area-level, but due to the
small sample size from only one location within the stand,
they include a large amount of random variability at stand
level. The model-based approach aims in such description that
is as close to the stratum-level measurements within stand as
possible, but also utilizes the measured sample trees
efficiently, and scales up at area-level to the
species-specific totals based on the sample trees.
The calculation included the following steps:
- The NFI sample trees were allocated to the strata
measured on the stand by utilizing information about
tree storeys, tree species and diameter of the trees
and strata. A tree could be allocated only in a
stratum that belongs to the same storey. If no
stratum was defined with the species of the tree as
the main tree species, the tree was allocated to a
stratum of other species. However, a conifer stratum
was priorized for conifer trees, a birch stratum for
birch trees and other broadleaved stratum for other
broadleaved trees.
Retention trees could be allocated only to a retention
tree stratum and retention tree stratum could include only
retention trees.
The allocations were utilized in
(1) estimating the diameter distributions of the
stratum, (2) estimatimg the height-diameter curve of
the stratum and (3) in estimating the tree species
proportions of the stratums by main tree species, as
described below. However, when estimating the diameter
distribution and height-diameter curve, only conifer
trees were used for conifer strata, only birches for
birch strata, and only other-broadleaved trees for
other broadleaved strata.
- Average species proportions were estimated for classes
determined by region and stratum main species based on
how much trees of different species were allocated to
strata of different main tree species. This way we
took into account that forests usually have small
proportion of such species that seldom are described
as main species of a stratum, and ensured that the
generated trees of the input data have similar species
distribution than the NFI sample trees have at regional
level.
- Correction factors of mean diameter and mean height
were defined by regions and tree species so that the
mean diameters and height at regional level matched
with values based on NFI sample trees by species and
regions.
- A two-parameter Weibull distribution was fitted for
every stratum so that the mean diameter matched by
the field-measured mean diameter of the stratum after
adjustment using the factor determined in step 3
above, the distribution fits to the sample trees of
the stratum, and that the diameter distribution at
regional level matches well to the diameter
distribution of the NFI sample trees. Trees were
generated from the estimated diameter distribution
according to the tree species proportions determined
in step 2. The total number of trees was proportional
to the basal area of the stratum so that the mean
number of generated trees was 33 trees per calculation
unit.
-
Such retention trees that were not allocated to any
retention tree stratum were added to the data as such
and the basal areas of trees of that stand were reduced
correspondingly.
-
The estimated number of stems for every generated
tree was adjusted so that the total basal areas
matched to the estimates based
on all NFI sample trees (i.e. also those from stands
without NFI plot center).
The adjustment was done by regions for retention trees and
by regions and species for other trees.
- The Height-Diameter models of Siipilehto and Kangas (2015) were
re-estimated to a dataset where the measured height sample trees
of NFI13 were added to the original model fitting data. The model
was used to predict heights to the generated trees of
the MELA input data. If there was one or more height
sample trees measured in a stratum, the model was
calibrated for the stratum using a random-effect
calibration approach, otherwise the fixed part of the
model was used in prediction.
A detailed description of the method is given in
Mehtätalo et al. (2026).
For strata with mean height below 1.3. meters, an approach
based on height distribution was used.
Forest management categories
The management units were classified into three categories according to sample plot
restrictions concerning wood production (see Table):
- no restrictions for wood production
- restrictions for wood production
- no wood production allowed
Table. Land areas and growing stock volumes (over bark) by management categories of
MELA data which were formed according
to the NFI field measurements for the whole country.
| Management category |
Area, million ha |
Proportion, % of total area |
| |
Forest land |
Scrub land |
Total |
|
| No restrictions for wood production |
17.14 |
- * |
17.14 |
74.9 |
| Restrictions for wood production |
1.16 |
0.98 |
2.14 |
9.3 |
| No wood production allowed |
2.01 |
1.61 |
3.62 |
15.8 |
| Total |
20.31 |
2.59 |
22.89 |
100.0 |
| |
Volume, million m3 |
Proportion, % of total volume |
| No restrictions for wood production |
2 059 |
- * |
2 059 |
80,7 |
| Restrictions for wood production |
165 |
29 |
194 |
7,6 |
| No wood production allowed |
255 |
45 |
299 |
11,7 |
| Total |
2 478 |
74 |
2 552 |
100,0 |
| * Scrub land (poorly productive forest land) belongs
either in the category "restrictions for wood production"
or in the category "no wood production allowed". However, in the calculation there were
no logging events on scrub land.
|