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CALCULATION SYSTEM FOR LARGE-SCALE FOREST INVENTORY

KariT.

Korhonen

Metsäntutkimuslaitoksen

tiedonantoja

505

(2)
(3)

CALCULATION SYSTEM FOR LARGE-SCALE FOREST INVENTORY

Kari T. Korhonen

Metsäntutkimuslaitoksen

tiedonantoja

505

(4)

tiedonantoja

Calculationsystem for

large-scale

forest

inventory

Kari T. Korhonen

Joensuu 1994

(5)

Korhonen, system

large-scale inventory.

Metsäntutkimuslaitoksen

tiedonantoja

505. The Finnish Forest Research Institute, Research Papers505.36pp.ISBN951-40-1371-9,ISSN0358-4283.

Summary:

Thispaperdescribesa calculationsystem for

large-scale

forest

inventory.

National Forest

Inventory

datafromthe

Forestry

BoardDistrictofKainuuare usedfor

demonstrating

the calculationsystem. Mixedestimationis usedfor

estimating

localizedvolumes functionsfrom the

sample

tree data measuredinthe

inventory

anddatameasuredin a

previous inventory.

Ordinary

leastsquares

-technique

isusedfor

estimating growth

modelsandvolumefunctions

by

timber assortments. Estimated models and some basic statistics calculated for the testarea are

presented.

Keywords:

forest

inventory,

mixedestimation, models,volume,

growth

Author'saddress: Korhonen, KariT. TheFinnishForestResearch Institute, JoensuuResearch Station, P.0.80x 68, FIN-80101 Joensuu, Finland.

Publisher:TheFinnishForestResearchInstitute,

Department

ofForestResources,

project

3001.

Accepted by:

AameReunala,

professor,

24.5.1994

Distributor:TheFinnishForestResearch Institute, JoensuuResearch Station, P.0.80x 68, FIN -80101 Joensuu, Finland.

(6)

Data used in this

study

were collected

by

the fieldgroups of the

project

National Forest

Inventory

of Finland. Several persons

working

in the same

project

in the Finnish Forest ResearchInstitutehavedonevaluableworkinfurther

processing

oftheHelddata.

Especially

the workofMr.

Alpo

Aarnio,Mr.ArtoAhola,Mr.Matti

Kujala

andMs. HelenaMäkelähavemade it

possible

to carry out this

study.

Discussions with

people

mentionedaboveand with Ms.

HelenaHenttonen,Mr. AnttiIhalainen,Mr. Juha

Lappi,

Mr. SakariSalminenand Mr. Erkki

Tomppo

have

helped

in

solving

several

problems

meat

during

the research work. Mr. Juha

Lappi,

Mr.SakariSalminenandMr.Erkki

Tomppo

havereadthe

manuscript

and

given

valuable criticalcomments. Ms.Joannvon

Weissenberg

hasrevisedthe

English

text.Theauthorwishes

to thankallthese

people

for theirefforts.

Joensuu 1.6.1994 Kari T. Korhonen

(7)

1. BACKGROUND 8

2. MATERIAL AND METHODS 9

2.1

Study

material 9

2.2Methods 11

3. DESCRIPTIONOF SYSTEM 12

3.1

Processing sample

treedata 12

3.1.1Estimationofvolumes 12

3.1.2 Estimation of volume increment 13

3.2Estimationofvolumesandincrementfor

tally

trees 15

3.2.1 Volume functions 15

3.2.2 Growth models 18

3.3

Generating

reports 19

4. APPLICATION OF THE SYSTEM FOR KAINUU DISTRICT 22

4.1 Estimated models 22

4.2

Examples

ofcalculatedresultsforKainuudistrict 23

5. DISCUSSION 25

APPENDICES 29

(8)
(9)

Concepts

andNotation

The

following

concepts relatedtothe measurementsof thefielddataareusedinthispaper.

sample point

= a

point

wherea

relascope plot

is measured

relascope plot

= a set of concentric circles with each circle

having

a fixedradius for each

diameter

(the

radiusis afunctionofthecross sectional areaofthe

tree)

restricted

relascope plot

=a

relascope plot having

amaximumradius; treeswith distancefrom

the

sample point

greaterthanthemaximumradiusarenot tallied

plot

section=sectionofa

plot,

whenthe

plot

isnear aland-class

boundary

plot

factor=relativesize of a

plot;

whena

plot

is locatedneara land-class

boundary

and the

center

point

ofthe

plot

ison

forestry

land,the

plot

factorindicatesthe

proportion

ofthe whole

plot

circle made

by

the

plot

sectionon

forestry

land

plot

stand=stand

containing

trees talliedon a

relascope plot, usually

a

plot

containstrees from

only

onestand; delineationofstandsisbasedonthecharacteristics ofthesite andthe

growing

stock

tally

tree =a tree

belonging

to the

(restricted) relascope plot

sample

tree =a

tally

tree forwhichmore detailedmeasurements aretaken

(10)

timbertree =

tally

tree

containing high enough

timber

quality

foratleastone saw

log

non-timbertree =

tally

tree whose dimensionsand/or

quality

are not

enough

forany saw

logs

The

following

notationsforthemostcommon treeandstandvariablesare usedinthispaper.

(11)
(12)

1. BACKGROUND

In

large-scale

forestinventories

sampling

methodsare usedtoobtaina

representee sample

of

the

population.

Inmanycases it isnot

possible

orrationaltomeasure

directly

thosevariables

that we are interested in. Therefore, mathematicalmethods

(also

methodsotherthan

simple

summation)

are neededtoderivethestatisticsoffinalinterestfromthecharacteristicsmeasured

forthe sample.

A

complete

calculationsystem of

inventory

resultsshouldinclude

following

components:

1.

checking

offielddata,

2. derivationof volumes, volume

growth

etc. for

sample

trees

using existing

modelsand

measured data,

3.

generalization

ofvolumesandothercharacteristics for

tally

trees,

4. summationofstatistics for

any chosen calculationstratum,and

5. estimationof

reliability

oftheresults.

Theaimofthis

study

wasto

develop

a systemofcalculationfor theNationalForest

Inventory

ofFinland(NFI).Thesystem shouldbe basedontestedanddocumentedmethodsandshould

cover estimationof areas of different strata

(e.g.

forest

types),

mean volume,

growth

and

percentages oftimber assortments. Estimationsoffuture

growth

and

cutting possibilities

are, however,excludedfromthe system. Norare

procedures

for

detecting

errors inthe fielddatanor

estimationof

sampling

error withinthescope ofthis

study.

Thecalculationsystem is tested

using

Kainuudistrictasa

study

area.

(13)

2. MATERIAL AND METHODS

2.1Studymaterial

Datafromthe7thNationalForest

Inventory

ofFinland

(NFI7)

forthe wholecountryanddata

fromtheBth8thNationalForest

Inventory

ofFinland(NFI8) forKainuudistrict(see

Fig.

1) were

usedin this

study.

The NFI7wascarriedout

during

1977-1984

(Kuusela

& Salminen

1991).

The NFIB data for Kainuu district were measured in 1992.

In both inventoriesthe

sampling

methodwas

systematic

cluster

sampling.

In the NFI7 the

distance between clusters was 8 km andeach clusterconsistedof 21

relascope plots.

In the

NFIB in the Kainuu district the distance between clusters was 7 km and each cluster consisted

of15 restricted

relascope plots.

Figure

1. LocationofKainuudistrict.

(14)

Inbothinventories,severalvariables

describing

thesiteand

growing

stockofthe

plot

stand(s)

wererecorded. Talliedtreeswereselectedwitha

relascope.

Inthe NFI7a

relascope

withabasal

areafactorof2was used.IntheNFIBinKainuudistrictarestricted

relascope plot

withabasal

area factor of 1.5 and a maximum radius of 12.45 m was used. In both sets of data the

following

variableswererecorded foreverytalliedtree:

tree

species

diameter

quality

class

describing

the

quality

ofthestem,latercalled

'tally

tree

quality

class'

crown class.

IntheNFI7data,the

living

treesweredividedinto3

quality

classes: non-timbertrees

(based

on

the dimensionsofthe stem), non-timbertrees(basedondefectson thestem),and timbertrees.

In theNFIBdataamoredetailedclassificationwasused todescribe,e.g. whetheratimbertree

is of

good

orpoor

quality.

In theNFI7,

tally

treesmeasuredatfour

plots

ineveryclusterwere used as

sample

trees.Inthe NFIB every7thtalliedtree was measured as a

sample

tree. In bothsetsofdatathe

following

variableswere

registered

for

sample

trees:

height

-

age

length

andlocationofdifferenttimberassortments

(=saw log quality

classesA,B, andC;

pulp

wood;

cull)

diameterincrementfor thepast

5-year period

height

incrementforthepast

5-year period (only

forconifers).

Inadditiontoabovementionedvariables,diameteratsixmeters

height

andthicknessofbarkat

breast

height

were

registered

forall

sample

trees in the NFI7data andfor a

sub-sample

of

sample

treesin theNFIB data.

In the NFIB dataavariablecalled

'sample

tree

quality

class' was alsorecorded. This variable

describes the cruisers

opinion

ofthe

quality

ofthe stemaftermeasurementofthe

sample

tree.

The

'tally

tree

quality

class'describes thecruiser's

opinion

aboutthe

quality

beforethe

sample

tree was measured. The cruiser may

change

his

opinion

about the

quality during

detailed

(15)

examinationofthestem when

measuring

thecharacteristicsof the

sample

tree.

2.2 Methods

The first

phase

in the calculations is to derive volume,

growth

and percentages oftimber

assortments forevery

sample

tree measured.Thevolumesof thetrees were calculated

using

volumefunctionsofLaasasenaho

(1982).

Volumesoftimberassortments werecalculated

using

thetaper curve modelsofLaasasenaho

(1982)

asa functionofd,

d«,

andh.Volumeincrement

ofthe

sample

treeswas estimated

according

to themethodsdescribed

by

Salminen

(1978)

and

Kujala (1980).

Regression analysis (Ordinary

Least

Squares, OLS)

andmixedestimationwereusedtoestimate thevolumeandincrementof

tally

trees.Mixedestimationis

widely

usedin

problems requiring

combinationoftwoormoredatasets

(Teräsvirta 1981).

Korhonen

(1992, 1993)

hasshownthat

mixedestimationisefficientfor

combining sample

treedatafromtwo inventories.

SAS statistical software was usedfor

studying

the

relationships

betweendifferentmeasured

variables inorder to determinethe correct formof thenecessary models

(SAS

InstituteInc.

1989).Theparametersofthemodelswereestimatedwith

Fortran-programs

made

by

theauthor.

IMSL-routineswere usedfor matrix

operations (such

as

inversion)

in theseprograms

(IMSL

library...

1982). The reason for

selecting Fortran-programs

instead of available statistical software was that

Fortran-programs

makesit

possible

to simulate

sampling

andthus test the

methodsusedinthecalculationsystem.

Fortran-programs

werealso usedtoderivethevolumes ofdifferenttimberassortments for

sample

trees measured.

Volumeand

growth

of

tally

trees were estimatedwith

Fortran-programs developed by

the

author. The treewisecharacteristics were summed upinto statistics forthe wholecalculation

area with SAS statistical software.

(16)

3. DESCRIPTION OF THE SYSTEM

3.1

Processing sample

treedata

3.1.1 Estimation of volumes

IntheNFIB data,dandhwere measuredforevery

sample

tree.

Upper

diameter,

dg,

however,

was measured

only

fora

sub-sample

ofthe

sample

trees. The first

phase

inthecalculationof volumeswas toconstructmodelsfor

estimating

the upperdiameterofall

sample

trees

(higher

than8

meters).

Function

(1)

was

applied

asthe model

(Kolhonen 1992)

butwasusedinitsfull

form

only

for

pine

and spruce. For other

species, only

variables d2,

h

2, d/t, and were

significant

regressors; therest ofthe variableswereexcludedfromthemodel.

Theparametersofthemodel

(1)

foreach tree

species

wereestimated

using

mixedestimation.

In the first stage of theestimationprocess, first-levelestimates ofparameters were obtained

using

NFI7dataforthewholecountry.Inthesecondstage,second-levelestimatesofparameters

a,-aswereobtained

using

NFIBdatafromKainuudistrict(Korhonen

1992).

Parametersrelated

tothecoordinatesarenotestimetedinthesecondstagebecausethedatameasuredinthisstage

are

quite

few and

geographically

not

representative.

In

(dj

=ao+

a,*d

2+ a3*h2+ +a3*ln(d6L)+

a«*ln(G)

+a7

*YC+

a,*YC

2+

a,*XC

+alO

*XC2+

+

a„*YC*XC,

(1)

(17)

Whenall

sample

treeshavemeasuredvalues forvariablesdandh andalltrees

higher

than 8

meters haveameasuredorestimatedvalueforvariable thestemvolume

(from

theestimated

stump

height

to the top of the

tree)

can be estimated with the functions

presented by

Laasasenaho (1982).

Estimationoftimber assortments is based on thedimensionsof thestem

(d, d«, h)

andthe

measured

lengths

ofdifferent

quality

classes. Thesemeasurements wereusedtodividethestem

intosaw

logs

thatfulfilledthedimension

(top

diameterand

length) requirements.

Thestemwas

divided into saw

logs by maximizing

the value of the stem witha

'complete

enumeration' method.Inthismethod,all

possible

solutions

(combinations

ofsaw

logs

ofdifferent

lengths)

are testedandthe solutionthat

gives

thebestvalueischosen.Thistimber

ruling

wasmadewith

a

Fortran-program

in whichthedimension

requirements (minimum

andmaximum

lengths

and minimumdiameters)and relativevaluesofdifferentassortments are

optional

parameterssothat

they

can

easily

be

changed.

3.1.2 Estimation of volume increment

The

sample

treevariables thatarerelatedtotheestimationof

growth

arediameterand

height

increment

during

thepast

5-year period

and thickness ofthebark. Thebark is measured

only

forsome ofthe

sample

trees.Therefore,a

regression

modelwas constructedfor

estimating

the

thicknessofthebark.Function

(2)

was foundasa suitablemodelfor

pine.

where b = thickness of bark.

For other

species

a

logarithmic

model

(Function 3)

was foundto be necessary to solve the

problem

of

heteroscedasticity.

Fordecidioustreesheightincrementwas notmeasured.Therefore,this variable was estimated

b =&o+

a,*d

+

(2)

ln(b) =a„+

a,*ln(d)

+

(3)

(18)

using

thetablesofIlvessalo

(1948,

see

Kujala 1980),

in which

height,

age,andcrown classof

the treeare

independent

variables.

Whenthebark modelsare estimated,each

sample

tree havemeasuredorestimatedvaluesfor variablesrelatedtovolume

growth:

diameterand

height

incrementandthicknessofthebark.No characteristics aremeasuredto

directly

describe the

changes

in stem formand inthicknessof

thebark

during

thepast

5-year period.

When

calculating

thevolumeincrementthese

changes

can betakenintoaccountwiththe method

presented by

Salminen

(1978)

and

Kujala (1980).

In this methodit is assumed thatthe

change

in

v/gj (ratio

ofvolumeand cross sectional

area)

during

thepast

5-year period

canbeestimatedwith

help

ofafunction

(v/g,=f(h))

estimatedfrom

thepresentv,g(

andhofthe trees.

Todescribe themethodofSalminen

(1978)

and

Kujala (1980),

letus note that:

r(h)

=afunctionthatestimatesr asa functionof

height,

(Vuistheunitvolumeofa

sample

tree=volumeofthetreedivided

by

itscross sectionalarea), and

(SVu

is 'seedvolume'ofa

relascope

tree =the volumeofthe tree 5 years agodivided

by

its

presentcross sectional

area)

r

=v/g„

(4)

Vu =

v/g (5)

SVu= Vj/g (6)

(19)

Formula (6) for SVu can befurtherwrittenas follows:

Using

notationVufor

v/g,

r(h) forestimated

v/g„

and

f(h

s

)

forestimated Function (7)can be written:

Afterthe 'seedvolume' ofatreeisestimated

using

Function

(8)

andareasin cross sectionand

heights

now and5 years ago are measured, the volume5 years agocan be calculated with

Formula (9):

3.2 Estimationofvolumesandincrement for tallytrees

3.2.1 Volume functions

Functionsfor

estimating

thevolumeof the wholestem fromstumptothe topof thetreewere

constructed

using sample

trees measured in the NFI7 and the NFIB. The two data were

combined

using

mixedestimation

(Korhonen 1993).

Atthefirststageoftheconstructionofthe

volume functions, NFI7 data were used for

determining

the form of the models andfor

obtaining

first-levelestimatesoftheparameters. Ina

previous study (Korhonen 1993)

Function 10was shown to workwellfor

pine.

SVu =gis

/g

*

(vj/g

i3)

<=>

SVu =gi3

/g

*

(v/gi

-

(y/g-,

-

v,/g

i

5))

<=>

SVu = *

v/g,

- gis

/g

*

(V/&

-

Vj/g

i

5)

<=>

SVu =gis

/g

*

(g/g,

*

v/g

-

(v/g,

-

Vj/gi,)) (7)

SVu =

gis

/g

*

(g/

gi *Vu -

(f(h)

-

?(h

5

)). (8)

v 5 =

g * SVu

(9)

(20)

whereRDIST=relativedistancefromthe seacoast

(see 'Concepts

and

Notation').

Function

(10)

was alsofoundtobe

satisfactory

forspruce andbirches. Forother

species,

the variable RDIST was excluded from the model.

Atthesecondstage intheconstructionofthevolumefunctions,mixedestimationwas usedfor

obtaining

second-level estimates of the parameters

(Korhonen 1993). Only

data from the calculationarea

(typically

onedistrictoftheCentralBoardof

Forestry

in

Finland)

wereusedfor

there-estimation.Becausethe numberof

sample

treesmeasuredwas

quite high

for

pine,

spruce

and birches, modelswereestimated

separately

foreachsiteclass.

Only

constant andparameters

ofvariablesd, d

2,and

ln(G)

wereestimatedatthe second stage;forothervariables, first-level estimates were used (Korhonen 1993).

Regression

models were also constructed for

estimating

the volumes of different timber

assortments: timberandcull.Thevolumeof

pulp

wood

quality

wasestimated

by subtracting

the estimatedvolumesoftimberandcull fromtheestimatedstemvolume.Afunctionwithaform

of

Equation (11)

was foundtobesuitable.

BecausetheformoftheFunction

(11)

fortimberassortmentwisevolumesdiffers

markedly

from

theFunction

(10)

forwhole-stemvolume,itwasalso necessarytoestimateamodelofaform

similarto

Equation

(11)forstemvolume.Otherwise,allerrors duetothe formofthefunctions

wouldhavebeensummedupin thevolumeestimatefor

pulp

wood.In somecases thiscould

evenhaveledto

negative

estimates for

pulp

wood.Finalestimates for,e.g. thesaw

log

volume ofa

tally

treewerethenobtainedwithformula

(12).

v/d2=ao+ a l

*d+

a^d

2+ a3*RDIST+

04*111(0

+

a,*YC

+

a^YC

2+

a,*XC

+

a^XC

2+

a,*YC*XC, (10)

vt/d

2

=a„+

a,*ln(d)

+ (11)

(21)

Because

logging

ruleshave

changed

since theNFI7,itwas not

possible

touse theNFI7dataas

prior

information.Timberassortmentwise modelswere estimated

using

OLS and

sample

tree data measured from the calculation area.

Naturally,

the

proportions

of timberassortments vary

markedly by

tree class. Therefore, the

sample

treedatawere

grouped by

treeclasses asfollows.

1 = non-timber tree

2 =a

good

saw

log

tree

3 =apoor saw

log

tree.

As mentionedinSection 2.1, inthefieldmeasurements two differentcodesfor treeclass were

recorded forthe

sample

trees. The firstof these describes the

quality

'at first

glance',

which

refers tothe way itiscodedfor

tally

trees(later called

'tally

tree

quality

class'). The second

one is coded

according

to moredetailed

sample

tree measurements

(later

called

'sample

tree

quality class'). Usually,

thecodes match,butinsomecases thecruiser

may

change

the

quality

code when

taking sample

tree measurements. Thus,a

sample

tree with

tally

tree class code

'non-timbertree' can includesaw

log quality,

and viceversa.

Only

trees with the

sample

tree

quality

class code

'good

saw

log

tree'or

'poor

saw

log

tree'

were usedin

estimating

theabove mentioned

regression

modelsfortimberassortment volume.

Atthe

application

stage

tally

treeswere

grouped

intothe

respective quality

classes

according

to

the

tally

tree

quality

class. To avoid

possible

bias caused

by

differencesin thetwo

quality

classifications an

adjustment

was made as follows. For all

sample

trees the mean of the

measuredtimbervolumeand the meanoftheestimatedtimbervolumewere calculated

by

tree

species.

Thetimbervolumeestimateof a

single

tree was then

multiplied by

theratio ofthese V,=

v/v

2

*

v, ,

(12)

where v,=finalestimateforv„

vt=estimateforv,obtainedwiththe modelfortheformof

Equation (11)

v, =estimatefor vobtainedwiththe modelforthe formof

Equation (10),

and

v2

=estimatefor vobtainedwiththe modelfortheformof

Equation

(11).

(22)

two means. Asimilar

adjustment

wasmadefortheestimatesofcull volume.

3.2.2 Growth models

Model

(13)

was selectedas a basic modelfor

estimating

thevolumeincrementofthepast5-

year

period.

For some

species

notallthe variablesinthe

equation

were

significant

rcgressors.

Inthesecases,

only significant

variableswere used

(see

Section

4.1).

whereSI, S2,

S 3 are dummy

variablesfordifferentsiteclasses, andSOILis a

dummy

variable

to separatemineralsoils form

peatlands.

When the

growth

models were estimated, trees

growing

on

poorly productive

land were

separated

fromtrees

growing

on forestlandfortwo reasons:

1. the

growth

of trees

growing

on

poorly productive

landis

markedly

different from the

growth

oftrees onforestland,and

2. mostofthevariables

describing

the

growing

stockare not measuredon

poorly productive

land.

Equation (14)

was usedasa

growth

modelfortreeson

poorly productive

land.

The natural

logarithm

of

i^d

2is usedas an

dependent

variable inmodels

(13)

and

(14).

In

applications,

unbiasedestimatesfor

i^d

2 inthearithmetic scale are needed.Themostcommon

way tocorrectthebiasduetothenon-lineartransformationistoaddtheterm 1/2*MSEtothe

logarithmic

estimate. This correction is based on the

assumption

that theresiduals of the

logarithmic

modelare

normally

distributed.Ifthisdoesnot holdtrue,

following

estimatorcan

be

justified according

toSnowdon

(1991):

ln(iyd

2) =a<>+

a,*d

+

aj*ln(d)

+

aj*G

+

a^*DD

+ + +

a,*S2

+

ag*S3

+

a,»SOIL

(13)

ln(i/d

2

)

=a,,+

a,*d

+

a2*ln(d) (14)

(23)

y, =measuredvalueforobservationi,and

ft

=estimated

logarithmic

valueforobservationi.

Estimator

(15)

wasusedinthis

study

to correctthebias duetothenon-lineartransformationin

growth

models.

3.3

Generating

reports

Using

the modelsdescribedinSection3.3, theHelddataare transformedintoa file, which is suitableforfurther

processing

with SASstatistical

package.

Inthisfile,each

plot

standhasone

recordforcharacteristics

describing

the locationofthe

plot

andsiteandthe

growing

stock of

the stand; and one record for each measured

tally

tree. The recordof a

tally

tree contains

following

data:

- tree

species

-

tally

tree

quality

class -d

- v/d2

-tyd

2

-OJd

2

-

U

2

.

(Volumes

andand

growth

are divided

by d 2 before they

are stored in the file in order to decreasethe errorsdueto

rounding off).

Whenareaestimatesare calculatedfordifferentstrata,e.g. site classes, the

sample point

isused

asone observation.AreaestimatesareobtainedwithFormula(17)(Salminen1993).

ft

=

c*exp(p

i

), (15)

2y.

where c= ,

S exp(pi)

(24)

Volume sum and mean statistics for a calculation area or different strata of the area are

compiled by summing

thevolumesand

plot

factorsofthe

plots

overthestratain

question.

The

meanvolumeis calculated

by dividing

thevolumesum

by

thesumofthe

plot

factors.Nomean volumesfor

single

standsof a

relascope plot

are needed.Infact, itis

impossible

tocalculate

suchmeanvolumesin theNFIdatafor standsthatdonot coverthewhole

relascope plot.

In the case of a restricted

relascope plot

with maximumradius of 12.45 m (as inNFIB in

Kainuudistrict) thevolumesumofa

plot

(section)iscalculatedasfollows.

It should be noted, that Formula

(17)

does not differentiatebetween whole

plots

and

plots

sections. Thesizeof a

plot

is takenintoaccount laterwhenthemeans or sums are calculated

for the calculation strata.

Afterthe volumesums arecalculatedforeachpart

plot,

mean volumeestimates fordifferent

strata ofa

inventory

areaare obtainedwithFormula

(18).

Äj

=

m/M

* AREA,

(16)

V=

X

n, V,,

(17)

(25)

IV,

Vi

= ,

(18)

iFi

(26)

4.APPLICATION OF THE SYSTEMFORKAINUU DISTRICT

4.1 Estimated models

Theupperdiameterfunctionsestimated

using sample

treesfromKainuudistrictarein

Appendix

2.

Separate

modelswereestimatedfor

following species: pine

(Pinus

sylvestris),

spruce

(Picea

abies),

whitebirch

(Betula pendula),

silverbirch

(B. pubescens),

aspen

(Populus tremuloides),

alder (Alnus incanaand A.

glutinosa).

As described earlier, NFI7 data were used as

prior

informationforsomeoftheparameters and

only

asinformationforotherparameters

(Korhonen

1992).

Thebark modelsfor

sample

trees of Kainuudistrictare in

Appendix

3.

Separate

modelsfor

pine,

birches

(no

differencebetweenwhiteand silver

birch),

aspenandalderwereused. The modelswere estimated

using

NFI7 andNFIB

sample

tree datafromKainuudistrict.

Volumefunctionsestimatedfordifferent

species

forKainuudistrictarein

Appendix

4.For

pine,

spruce and birches the final

parameterestimates were calculated

separately

for 4 site class

groups.For aspen,alderandthe groupofother

species

the

sample

tree datawere too few to

distinguish

betweensiteclasses.Themodels

presented

in

Appendix

4are not

logical

forsmall sized trees.Therefore,generalvolumefunctionswere usedfor treeswithd <3 cm.

The

regression

modelsfor timberassortmentwise volumesare

presented

in

Appendix

5. The

datafor

pine

andspruceweredividedintotwosite classgroups.

Separate

modelsfortimberand

cull volume modelswereestimatedforthe two groups.Thedataforbirches were too few to

makeadistinctionbetweensiteclasses. For aspen

only

few

sample

trees were codedas timber

quality

trees,andthereforenomodelfortimbervolumewereestimated.Atthe

application

stage, timbervolumemodelofbirches were usedfor thoseaspens thatwere codedas timber

quality

trees.For other

species,

no timbertreeswere measured;modelswere estimated

only

for cull volume.The correctionfactorsfortimberassortmentwisevolumes

(see

Section

3.2.1)

are also

given

in

Appendix

5.

Theestimatedmodelsfor thepast

5-year

volume

growth

ofdifferent

species

are in

Appendix

6.

Separate

modelsfortrees

growing

atforestlandand

poorly productive

landwereestimated.

For forest land separate models for

pine,

spruce,birches and aspenwere used. For

poorly

(27)

productive

landbirchesandaspenwere combinedtothegroupofother

species.

Thecorrection

terms

(see Equation (16))

are also

given

in

Appendix

6.

4.2

Examples

ofcalculatedstatistics forKainuudistrict

According

to thestatisticsoftheNationalBoardof

Survey,

thetotallandareaofKainuudistrict is2 156690ha. Estimatedareaof forestlandis 1 664015ha.

Figures

2and 3present two

examples

ofestimatedpercentages ofdifferent strata.In

Figure

2 is thedistributionofforest

land

by

dominant

species. Figure

3 presents the age class distributionon the forestland in

Kainuu district.

Theestimatedmeanandtotalvolumesandtimberassortmentwise meanand totalvolumes

by

species

onforestlandand

poorly productive

land are

given

in Table1. The

growth

statistics obtained

using

thecalculationsystem are

presented

inTable2.

Figure

2.Dominanceoftree

species

onforestland.

(28)

Figure

3.

Age

structure on forestland

Table 1.Meanandtotalvaluesofstemvolumeand timberassortmentwisevolumes

by species

for forestand

poorly productive

land.

Table2.Meanandtotalvalueestimates for

growth by species

forforestand

poorly productive

land.

Meanvolumes, m 3

/ha Totalvolumes, 1000m

3

saw

log pulp

total saw

log pulp

total

Pine 13.3 21.9 37.7 25089 41288 71062

Spruce

6.1 9.8 16.9 11427 18427 31947

Birches 0.2 6.2 8.7 414 11763 16382

Others 0.0 0.7 1.1 29 1273 2009

All 19.8 44.8 64.4 36959 72750 121401

Pine

Spruce

Birches Others All

m

3/ha 1.35 0.41 0.38 0.06 2.20

1000m

3 2552 782 715 104 4153

(29)

5. DISCUSSION

Thesystemofcalculation

presented

inthispaperdiffersfromthepresentcalculationsystemfor

NFIin the

following

ways:

1. Stemvolumeandthe timberassortmentwise volumesare

generalized

for

tally

trees

using

regression

modelsinsteadofclasswise meanvalues.

2. Growthestimatesarecalculatedfor

tally

trees withamethodsimilarto thatfor

estimating

the timber assortmentwise volumes. In the

present calculation

system

growth

is not

generalized

for

tally

trees

(growth

isestimated

using growth

percentagesestimatedfromthe

sample

treedataanddiameterdistributionsestimatedfromthe

tally

tree

data).

Theabove-mentionedsolutionsmakethe system flexible.Area,volumeand

growth

estimates

can

easily

becalculatedforanysub-classofthedata.Plotwisevolumeand

growth

estimatescan

easily

beusedasa

'ground

truth' for

processing

satellite

images (Tomppo 1992).

Charactericsof'final

interest',

suchastimberassortmentwisevolumesandvolume

growth,

were

usedas

dependent

variableswhenthemodelswereestimatedfromthe

sample

treedata.Another

possibility

wouldhavebeento use variables

describing

thedimensions

(d,

h,b, id,

ij

and

quality (lengths

ofdifferent

quality

classes) as

independent

variables.The modelswouldthen

give

estimatesofall

sample

treevariablesforevery

tally

tree.Theseestimatescouldbe usedas

independent

variables for further estimations, e.g. of the volume or

growth

of

tally

trees.

Variousmodificationsofthismethoddescribed

by

Kilkki (1979)are

widely

usedin

inventory

systems. The method hasone serious drawback, however: residual varianceof thedifferent

models mustbe taken into account when, e.g.,

using

estimatedh,

i,,,

and ih as

independent

variablesin

estimating

volumeincrement

(Kilkki 1979).

The

joint

distributionsoftheerrorsof

(30)

the different models are difficulttoestimate. Therefore, aftersome trials this

approach

was

rejected.

As stated, in this system ofcalculation

sample

treevariables such as

height

and age are not

generalized

for

tally

trees.

Therefore,

thedata

generated

for

tally

treescannotbeused to

predict

the future

development

of forests with simulation systems like the Finnish

Mela-system

(Siitonen 1983).

Furtherstudiesareneeded

if,

for

example,

the

grid

method

(Holm

etal.

1979)

is

applicaple

for

generalizing

the

sample

treecharacteristicsfor

tally

treesinsuch awaythatthe

results can be used as a basis both for

calculating

unbiased

inventory

statistics and for

simulating

thefuture

development

ofthetrees.

(31)

LITERATURE

Holm,S.,

Hägglund,

B.&Märtensson,A.Amethodfor

generalization

of

sample

treedatafrom the Swedish National Forest

Survey.

Swedish

University

of

Agricultural

Sciences.

Department

of Forest

Survey. Report

25. 94pp.

IMSL

library

reference manual.Edition9. 1982.IMSLInc. Houston,Texas.

Kilkki, P. 1979. Outline for a data

processing

system in forestmensuration. SilvaFennica

13(4):368-384.

Korhonen,K.T. 1993.Mixedestimationincalibrationofvolumefunctionsof Scots

pine.

Silva Fennica 27(4):269-276.

Korhonen,K.T. 1992.Calibrationofupperdiametermodelsin

large-scale

forest

inventory.

Silva Fennica 26(4) :23 1-239.

Kujala,

M. 1980.

Runkopuun

kuorellisen tilavuuskasvun laskentamenetelmä.

Summary:

A calculation method for

measuring

the volume

growth

over bark of stemwood. Folia Forestalia441. 18pp.

Kuusela,K.& Salminen,S. 1991.Suomenmetsävarat 1977-1984

ja

niiden

kehittyminen

1952- 1980.Forestresources ofFinlandin 1977-1984and their

development

in 1952-1980.Acta ForestaliaFennica220.84pp.

Laasasenaho, J. 1982.

Taper

curve and volume functions for

pine,

spruce and birch.

CommunicationesInstitutiForestalisFenniae 108.74pp.

Salminen,S. 1993.EteläisimmänSuomenmetsävarat1986-1988.

Summary:

Forestresourcesof SouthernmostFinland.FoliaForestalia825. 11l pp.

Salminen,S. 1978. Incrementcalculationsonthe basis of

relascope sampling

in theFinnish NationalForest

Inventory. Paper presented

in lUFRO

Meeting

of June 18-25, 1978 in Bucharest, Romania.

Subject Group

54.02. 7 p. The Finnish Forest Research Institute.

Helsinki, Finland.

SASInstituteInc.,SAS/STATUser's

quide,

Version6,FourthEdition, Volumes1and2,

Cary,

NC: SAS Institute Inc., 1989.

Siitonen,

M. 1983.A

long

term

forestry planning

systembasedondatafromtheNationalForest

Inventory

ofFinland. In:Forest

inventory

for

improved

management.

Proceedings

ofthe lUFRO

Subject Group

4.02

Meeting

in Finland,

September

5-9, 1983.

University

of Helsinki.

Department

ofForestMensurationand

Management.

ResearchNotes 17:195-207.

Snowdon, P. 1991. Aratio estimatorforbias correction in

logarithmic regression.

Canadian JournalofForestResearch 21(5):720-724.

Teräsvirta,T. 1981.Someresultson

improving

the leastsquaresestimationoflinearmodels

by

mixed estimation. Scandinavian Journal of Statistics 8:33-38.

(32)

Tomppo,

E. 1992. Multi-source NationalForest

Inventory

of Finland. In:

Proceedings

of Ilvessalo

Symposium

on National Forest Inventories. Finland 17-21

August

1992.

Nyyssönen,

A.,Poso,S.&Rautala, J.(ed.).TheFinnishForestResearchInstitute.Research

Papers

444:52-59.

Valtakunnanmetsien 8. inventointi.

Kenttätyöohjeet,

Kainuun

ja Pohjois-Pohjanmaan

veriso.

1992.

[Field

instructionsforthe fieldworkof the8"NationalForest

Inventory

ofFinland

atKainuuand

Pohjois-Pohjanmaa

districts. InFinnish.]

Manuscript

67 pp +

appendices.

TheFinnishForestResearchInstitute. Helsinki, Finland.

Valtakunnanmetsieninventoinnin

kenttätyöohjeet

VMI7. 1978.

[Field

instructionsforthefield work of the 7th NationalForest

Inventory

of Finland. In

Finnish.] Manuscript.

59 pp +

appendices.

The FinnishForestResearchInstitute.Helsinki, Finland.

(33)

Appendix

1. for ratio of volume over bark and cross sectional area inside bark (r = v/gj (Kujala 1980)

.

r(h) = 0.39 +

0.39* h +

2/(h.l-3) +

o.77*V(h-1.3)

r(h) = 0.44 +

0.355* h +

2/(h.l-3) +

o.6s*V(h-1.3)

r(h) = 0.48 + 0.48* h + 3.5/(h.l-3)

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