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Development and evaluation of teak (tectona grandis l f ) taper equations in northern thailand

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Tiêu đề Development and Evaluation of Teak (Tectona Grandis L.f.) Taper Equations in Northern Thailand
Tác giả Andrew J. Warner, Monton Jamroenprucksa, Ladawan Puangchit
Trường học Kasetsart University
Chuyên ngành Silviculture / Forestry
Thể loại Research article
Năm xuất bản 2016
Thành phố Bangkok
Định dạng
Số trang 19
Dung lượng 653,49 KB

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Development and evaluation of teak (Tectona grandis L f ) taper equations in northern Thailand Accepted Manuscript Development and evaluation of teak (Tectona grandis L f ) taper equations in northern[.]

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Development and evaluation of teak (Tectona grandis L.f.) taper equations in northern

Thailand

Andrew J Warner, Monton Jamroenprucksa, Ladawan Puangchit

PII: S2452-316X(16)30245-9

DOI: 10.1016/j.anres.2016.04.005

Reference: ANRES 57

To appear in: Agriculture and Natural Resources

Received Date: 25 January 2016

Accepted Date: 12 April 2016

Please cite this article as: Warner AJ, Jamroenprucksa M, Puangchit L, Development and evaluation

of teak (Tectona grandis L.f.) taper equations in northern Thailand, Agriculture and Natural Resources

(2017), doi: 10.1016/j.anres.2016.04.005.

This is a PDF file of an unedited manuscript that has been accepted for publication As a service to our customers we are providing this early version of the manuscript The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.

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Development and evaluation of teak (Tectona grandis L.f.) taper equations in northern

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Thailand

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Andrew J Warner*, Monton Jamroenprucksa, Ladawan Puangchit

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Department of Silviculture, Faculty of Forestry, Kasetsart University, Bangkhen, Bangkok

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10900, Thailand

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Article history:

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Received 25 January 2016

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Accepted 12 April 2016

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Keywords:

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Northern Thailand,

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Taper equation,

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Teak,

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Tectona grandis L.f

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*Corresponding author

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E-mail address: andywarnertas@gmail.com

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Abstract

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Taper refers to the general decrease in the regular outline of a solid body from its base

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to its tip Taper models are used to estimate the volume and value of wood products from

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harvesting trees Teak (Tectona grandis L.f.) is highly valued as one of the world’s most

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preferred timbers and a teak taper equation is required to inform optimal harvesting strategies

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given the limited plantation resource available in Thailand Teak taper equations were

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developed and evaluated based on 331 sample trees collected in 2014 from eight plantations

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in northern Thailand aged from 10 to 46 yr using two taper model formulations—the Kozak

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variable-exponent taper model and the Goodwin cubic polynomial model comprising

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hyperbolic and parabolic terms Variants based on both model types were fitted using

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nonlinear regression analysis with diameter at breast height, total tree height and height of

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girth measurement as the independent variables to estimate diameter underbark at the

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nominated height Goodness-of-fit and leave-one-out cross validation with lack-of-fit

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statistical testing combined with extensive graphical analysis of residuals were used to select

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the best model A Goodwin model variant (named FIO-teak1 as the first plantation teak taper

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model known to be published in Thailand) provided the best estimates of volume and

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diameter underbark A simple case study confirmed that FIO-teak1 in combination with the

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Farm Forestry Toolbox software package could assist teak plantation managers in decision

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making associated with optimizing log grade value based on standing tree inventory data

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Introduction

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Taper refers to the general decrease in the regular outline of a solid body from its base

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to its tip (Schreuder et al., 1993) Tree taper equations are important because reliable

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estimates of wood products and their value are essential to quantify expected commercial

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harvest returns (Salam and Pelkonen, 2012) Teak (Tectona grandis L.f.) is highly valued as

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one of the world’s most preferred timbers (Thaiutsa, 2008; Ladrach, 2009)

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Taper equations have been described for many species in almost every country where

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forest management has been administered, for example: more than 230 equations covering 50

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species in Europe (Zianis et al., 2005); 25 species of eucalypts in Australia (Bi, 2000); 11

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conifer species in the eastern USA and Canada (Li et al., 2012); 7 pine species in Swaziland

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(Crous et al., 2009); willow in Finland (Salam and Pelkonen, 2012), poplar in Sweden

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(Hjelm, 2013); radiata pine in Australia and New Zealand (Bi and Long, 2001; Goodwin,

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2009); and Styrax sp in Lao PDR (Ounekham, 2009) Many taper model forms and types

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have been developed and described; in addition to those above, see also Rojo et al (2005),

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Hart (2009), Westfall and Scott (2010), Fonweban et al (2011) and de-Miguel et al (2012),

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as all these studies and their associated references provide extensive detail on taper model

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options and such discussion is beyond the scope of this paper

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The Forest Industry Organization (FIO) is a Thai government State enterprise whose

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role today includes managing more than 74,000 ha of government-owned, commercial, teak

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plantations throughout extensive areas of central and northern Thailand (Forest Industry

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Organization, 2014) with more than 80% located in northern Thailand (Thaiutsa, 2008)

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There are no reports known of estate-level, teak taper equations available for use in

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Thailand, except for a simple trial example initiated by the first author and included in the

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Farm Forestry Toolbox (Goodwin, 2007; Warner, 2007) Therefore, the aim of the study was

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to develop a teak taper equation based on data collected from sample trees in available FIO

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plantations in northern Thailand

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Materials and Methods

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Standard tree measuring equipment was used to collect sample tree data and consisted

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of: 1) a good quality fiberglass girth/diameter tape; 2) a fiberglass 25 m or 50 m length tape;

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3) an altimeter (Haga Company; Nuremburg, Germany) for estimating the pre-felled, total

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tree height of each tree, in case the upper crown was destroyed during felling; 4) spray paint

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and chalk to mark reference details on each tree; 5) a hammer and chisel to extract bark chips

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and two small steel rulers with a scale in millimeters to measure the thickness of the bark;

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and 6) a global positioning unit to determine the easting and northing of each tree to facilitate

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any revisiting for data clarification Chainsaw felling of each sample tree was carried out by

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FIO personnel Field data were recorded on a customized paper sheet

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The dataset was stored in a customized Access database and some preliminary

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analysis and data checking used Excel, with both these software packages being components

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of the Office software package (2007; Microsoft Corp.; Redmond, WA, USA) The main data

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analysis was carried out using the R language and environment for statistical computing (R

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Core Team, 2015) linked with the RStudio software (version 0.98.1062; www.rstudio.com)

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Sample tree selection, measurement and taper modeling

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Stands in eight FIO plantations in four northern Thai provinces were sampled (see

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Table 1 for statistics) A sampling procedure selecting sample trees based on area stratified

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by age using a specially designed recording sheet was developed, then tested and revised with

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the FIO data measurement teams, emphasizing strict procedural consistency and accuracy

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Additional field checks of the teams and some data checking were undertaken during the

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sample tree measurement phase (January–May, 2014)

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Accurate modeling of taper to determine different high-value products was required in

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the lower bole, so girth measurements were taken above ground level at 0.3 m, 0.5 m, 0.8 m

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and breast height (1.3 m above ground on the uphill side of the tree) to also provide sufficient

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detail to allow sectional area to be corrected if necessary for pronounced buttressing in the

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lower bole Digital photographs of chainsawn cross sections including a metric scale measure

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were taken at these lower sampling heights where there appeared to be buttressing, so that

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image analysis could be carried out post sampling if required Sampling occurred usually at 2

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m intervals above breast height at a representative point (no obvious defect or exceptional

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girth) until the main stem was no longer apparent Total height (to the nearest centimeter) was

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measured to the tallest green shoot At each representative sample point, measurements were

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recorded of the overbark circumference (recorded as the girth to the nearest millimeter) and

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of bark thickness (to the nearest millimeter, in the holes formed by the removal of bark chips

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down to the cambium at three equidistant points around the girth at each measurement height,

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to derive an average bark thickness) and height from the ground (to the nearest centimeter,

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based on the reference line marked at breast height before felling)

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Two taper model formulations were chosen based on a literature review and also on

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their different approaches, so that they could be tested for their suitability to model teak taper

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as described below Variants of both models were appraised by removing terms

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Kozak’s variable-exponent taper model was chosen as it has been successfully applied

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to many species globally including in North America, Europe, Scandinavia and Asia (Kozak,

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2004; Heidarsson and Pukkala, 2011; Fonweban et al., 2012) Model “02” was the last in a

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series of models developed by Kozak and associated researchers; this model was chosen

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because it was reported to be consistently the best for estimating diameter underbark and tree

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and log volumes (Kozak, 2004) Notably, it includes an implied taper and bark thickness

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model because the diameter at breast height overbark is an input (Equation 1):

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where  = ℎ ⁄ + 1 ⁄ ⁄ ! + ".+ 1 ⁄  + $ %+ &

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 = 1 − ℎ ⁄  " ⁄ !/1 − 1.3 ⁄  " ⁄ !

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* = 1 − ℎ ⁄  " ⁄ !

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and a 0 , a 1 , a 2 , b 1 , b 2 , b 3 , b 4 , b 5 and b 6 are coefficients, d ub is the diameter underbark

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(centimeters), measured at height h (meters) above ground, D ob is the diameter overbark

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(centimeters) at breast height and H is the total tree height (meters)

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The second taper model tested was described by Goodwin (2009) as a cubic

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polynomial comprising hyperbolic and parabolic terms It has been generally used in

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Australia where Wang and Baker (2005) found it to be better than the Kozak model for

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plantation Eucalyptus globulus in Victoria Second-stage models (β1, β2 andβ3) suggested by

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Goodwin (2007, 2009) as applicable to many species were used to develop the starting point

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in the current study (Equation 2):

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 =  − ℎ+ + ,"ℎ − ℎ + ⁄- − ℎ. (2)

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where + = ,,ℎ− ℎ/-1 + ,ℎ1 + ,ℎ1 + , 

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,= /+ / + / + /"⁄ 10 

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, = +  + ⁄

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," = 1+ 1 + 1⁄ + 1 "⁄  + 110 ⁄ 10 

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and c 0 , c 1 , c 2 , c 3 , d 0 , d 1 , d 2 , f 0 , f 1 , f 2 , f 3 and f 4 are second stage candidate coefficients, d ub is the

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diameter underbark (centimeters), measured at height h (meters) above ground, Dub is the

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diameter underbark (centimeters) at breast height (h1, meters) and H is total tree height

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(meters)

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Statistical analysis

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Taper models were developed using nonlinear regression (using the nls and nlme

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modules in R) with extensive use made of graphical analysis, several goodness-of-fit (GOF)

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statistics and an index derived from lack-of-fit (LOF) analysis statistics based on cross

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validation to provide comparative information regarding models based on the same dataset

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While mixed effects models containing both fixed and random model parameters that can be

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estimated simultaneously have been reported to improve the precision of taper functions,

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Fonweban et al (2012) also noted that the improved performance from mixed-effects models

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over fixed-effects models was dependent on additional measurements or observations, while

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de-Miguel et al (2012) considered that fixed-effects models are more accurate when the aim

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is prediction, as in the current study Thus, mixed effects were not considered in this study

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but deserve future investigation Preliminary modeling with both model types found no

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benefit from applying weights, which was consistent with the approach reported by Goodwin

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(2009) and Kozak (2004) in their major studies of their respective models

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Recognizing the potential correlation among data points taken from the same tree, the

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model analyses avoided using any confidence limits or hypothesis tests even though the

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predictive effect of a model would be unaffected as the estimates of the regression

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coefficients are still unbiased (see for example, West et al., 1984; Tasissa and Burkhart, 1998;

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Kozak, 2004; Rojo et al., 2005)

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The residual standard error (the square root of the sum of squares divided by the

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respective degrees of freedom), the adjusted coefficient of determination (R345) and the

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Bayesian information criterion (BIC) were used for GOF analysis to select the better models

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for further LOF analysis and validation testing These statistics have been widely reported as

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suitable for comparison between models based on the same dataset, for example, by Ritz and

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Streibig (2008), Maindonald and Braun (2010), Fonweban et al (2011) and Tahar et al

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(2012), from which Equations 3 and 4 were sourced:

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R345 = 1 − 67 ∑ 9<:= : 79;:

67> ∑ 9 < :79?

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where @A, @;A and @? are the measured, predicted and average values of the dependent variable,

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respectively, n is the total number of observations used to fit the model and p is the number of

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model parameters

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BIC = -2(maximized log likelihood) + ln(n)(number of parameters) (4)

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where n is the number of observations and the BIC tends to penalize more complex models,

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with lower values usually resulting for simpler models (Hastie et al., 2013) and was

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considered suitable for GOF appraisal (Shmeuli, 2010)

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The best of both the Goodwin and Kozak model variants based on their GOF statistics

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were then chosen for further analysis using LOF procedures

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The best test of an equation to indicate how well it predicts is to consider the accuracy

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of its predictions which can be done using cross validation—testing the model on data not

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used in the model fitting—and evaluating LOF statistics (Maindonald and Braun, 2010)

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Leave one out (LOO) cross validation is a well known statistical approach (Venables and

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Ripley, 2002; Maindonald and Braun, 2010; Hastie et al., 2013) that has been used in forestry

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and reported to be reliable in the evaluation of the predictive performance of models (for

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example, Tarp-Johansen et al., 1997; Bi and Long, 2001; Kozak and Kozak, 2003; Rojo et al.,

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2005) LOO cross validation was applied to each of the 331 trees in turn to produce estimates

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for each excluded tree based on the model fit using the remaining 330 trees These data were

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then subjected to LOF analysis, using the percentage error (̅%) as a measure of the overall

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prediction accuracy and also to indicate positive and negative bias (Fonweban et al., 2011)

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and the relative error in prediction (RE%) to indicate the precision of the estimates (Huang et

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al., 2003); these terms are defined in Equations 5 and 6:

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̅% = 100 × ∑ @6 A− @GF

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JK% = 100 × L∑ @6 A− @GF 

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where @A is an observed value and @GF is its predicted value, n is the number of observations, @?

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is the mean of the observed values and the closer the terms are to zero, the better

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LOF analysis investigated three different aspects of the models using the LOO

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procedure: 1) prediction of d ub given h; 2) prediction of h given d ub; and 3) prediction of the

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volume underbark of a log in each sample tree with the upper and lower log heights selected

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at random The sample tree measurements were divided into roughly equal classes so that the

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LOF could be appraised at different diameter and relative height ranges in the sample trees

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The results were combined into an unweighted index using the LOF statistics from the three

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tests with the lowest combined index determining the best model (Oswalt and Saunders,

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2006; Goodwin, 2009; de-Miguel et al., 2012) The records for h = 1.3 m were omitted in the

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LOF analysis, as the residuals for such records were already constrained to zero by the

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Goodwin model formulation Furthermore, to reduce potential correlation between

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measurements in the same tree, only one randomly chosen value from each tree in each

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subclass of the tree stem was used in each of the LOF procedures

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In the LOF comparisons, Dob was converted to Dub for input to the Goodwin model

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using a bark thickness model derived from the sample tree data to ensure a fair comparison

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with the Kozak model, since the Kozak taper model (using Dob as an input) also included an

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implied bark thickness model The Kozak models using Dub as an input were also compared

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with the Goodwin models using Dub to remove any confounding effect of bark thickness

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Results and Discussion

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Measurements from 331 sample trees were checked and compiled in a database

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(Figure 1 and Table 1 present some of the data) Some dub data affected by pronounced

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buttressing (defined here as a difference between inferred tape sectional area and actual cross

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sectional area of greater than 3%) in the lower bole of larger trees were adjusted using cross

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sectional area analysis from the digital images

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Figure 1 Sample tree height and diameter at breast height overbark (D ob) by plantation

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Table 1 Summary statistics for the 331 teak sample trees by plantation location

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Tree count (total = 331)

Diameter at breast height overbark (cm)

Total height (m)

Tree age (yr)

Number of record heights per tree

* = Phrae province (KMK = Kunmaekammee; WGC = Wangchin; MMS = Maesaroi); Lampang province

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(MMJ = Maejang; MMM = Maemai; TGK = Tungkwean); Chiang Mai province (MHP = Maehopha); Lamphun

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province (MML = Maelee)

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Twenty-six models (18 Goodwin and 8 Kozak variants) were fitted using unweighted

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nonlinear regression and evaluated in the first instance with the GOF statistics

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Of the 26 models tested, Table 2 summarizes the GOF results for the

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performing models that were then subjected to LOF analysis The high adjusted R2 values

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(0.9825–0.9848) indicated that these models provided a good fit to the data The original

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formulation (Kozak 02) was the best of the Kozak models for both D ob and D ub as input; the

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b 5 term was significant, in contrast to the results reported by Rojo et al (2005) Generally, it

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... , a 2 , b 1 , b 2 , b 3 , b 4 , b 5 and b 6 are coefficients, d ub is...

subclass of the tree stem was used in each of the LOF procedures

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In the LOF comparisons, Dob was converted to Dub for input to the Goodwin model

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67> ∑ 9 < :79?

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where @A, @;A and @? are the

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