AN ASSESSMENT OF THE POINT-CENTRED QUARTER METHOD OF PLOTLESS SAMPLING IN SOME NEW ZEALAND FORESTS

Similar documents
Discussion of point sampling exercise

A Test of the Mean Distance Method for Forest Regeneration Assessment

GROWTH RATES IN SOUTH WESTLAND TERRACE RIMU FOREST 1. GROWING STOCK AND INCREMENT IN VIRGIN FOREST

Simulating and Sampling the Hardwood Compone11t of Loblolly Pine Plantations

Monitoring of the development of stands in uneven-aged beech and silver fir forest in Slovenia. D. Hladnik

Point Sampling Introduction BAF sq.ft./acre regardless of D. Plot Radius

Predicting productivity using combinations of LiDAR, satellite imagery and environmental data

Chapter 2 Timber Cruising

Attempt any FOUR questions. All questions are of equal marks.

COMPARISON OF COMPATIBLE POLYNOMIAL TAPER EQUATIONS

Using the tree-growth model MOSES to assess the impact of uneven-aged forest management

B. Statistical Considerations

Characterizing Stand Density for Stand Tending Strategies

PREDICTING DIAMETER AT BREAST HEIGHT FROM TOTAL HEIGHT AND CROWN LENGTH

VEGETATION PATTERNS IN A FOREST UNDERSTORY

Estimating individual tree growth with non-parametric. methods. Susanna Sironen U NIVERSITY OF JOENSUU FACULTY OF FORESTRY

FOR 274 Forest Measurements and Inventory. Written Take Home Exam

How would you measure shrub cover here? FOR 274: Forest Measurements and Inventory. Density: What is it?

Characterizing Stand Density for Stand Tending Strategies

Application of Non-Parametric Kernel Regression and Nearest-Neighbor Regression for Generalizing Sample Tree Information

Applicability of Four Regional Volume Tables for Estimating Growth Response to Thinning in Douglas-Fir

USING LIDAR AND RAPIDEYE TO PROVIDE

Overstory and Shrub Influences on Seedling Recruitment Patterns in an Old-growth Ponderosa Pine Stand

INDIAN AFFAIRS MANUAL. Chapter 8 Inventory and Monitoring Page 1

METHODS FOR ESTIMATING SPECIFIC GRAVITY OF LOGS

COMPARISON OF THE GROWTH OF VEGETATIVE PROPAGULES AND SEEDLINGS OF PINUS RADIATA

Overview of WSFG. Scott McPherson April 4, 2006 North Bay

NTFP Project 1 Supporting the sustainable use of Non-Timber Forest Products

2 Cruise Design. April 15, 2015 Amendment No

FOREST ACCURACY OF QUADRAT SAMPLING IN STUDYING REPRODUCTION ON CUT-OVER AREAS1

Tree Height Estimation in Redwood/Douglas-fir Stands in Mendocino County

INVENTORY? - MEASUREMENTS & - BASIC STATISTICS ARE IMPORTANT FOR PRUDENT FOREST MANAGEMENT

The Art of Timber Cruising Part II Fixed-Area Plots

12-1. TIMBER ESTIMATION 291

Point-3-P Alternative Timber Cruise Procedure Our goal. Our base theory.

Biology 317 Principles of Ecology October 19, 2017 Field Study of Plant Competition. Introduction. Observational Field Study

Hands on R Final Project Greg Pappas

Extension Bulletin E-1757, May "1984 " Cooperative Extension Service Michigan State University $1.00 AIDS TO PROFESSIONAL FORESTRY PRACTICE

Variable Method Source

WOOD BASIC DENSITY AND MOISTURE CONTENT OF YOUNG EUCALYPTUS REGNANS GROWN IN NEW ZEALAND

OPTIMAL STOCHASTIC DYNAMIC CONTROL OF SPATIALLY DISTRIBUTED INTERDEPENDENT PRODUCTION UNITS Version

NtreeSamplingBiblio.pdf

Upper Canopy module Fixed Area Plot Summary and beyond!

PNW-3 53 March 1980 ESTIMATING MERCHANTABLE VOLUMES OF SECOND GROWTH DOUGLAS-FIR STANDS FROM TOTAL CUBIC VOLUME AND ASSOCIATED STAND CHARACTERISTICS

INTERNAL REPORT 98 STAND STRUCTURE SIMULATION. Peter Farnum. University of Washington ABSTRACT

Growth of a 45-Year-Old Ponderosa Pine Plantation: An Arizona Case Study

Comparison of individual cow SCC estimates using an on-line SCC analyser and conventional herd tests

2015 AP Statistics Exam NAME

CRUISE DESIGN AND LAYOUT

Seed and Seedling Size Grading of Slash Pine Has Little Effect on Long-Term Growth of Trees

8.0 Forest Assessment Methods

Forest Thinning Scheduler. User s Guide

1. are generally independent of the volume of units produced and sold. a. Fixed costs b. Variable costs c. Profits d.

A jack pine bark factor equation for Michigan

Sampling vegetation is important for managing wildlife. Vegetation provides species

PROCEEDINGS OF THE TENTH NORTH AMERICAN FOREST BIOLOGY WORKSHOP

Section 12. Crowns: Measurements and Sampling

Evaluation of Using Systematic Random Sampling along with Forest Cruising Method in Caspian Forests-(Iran) (Case Study: Kheyrood-Kenar, Naushahr)

SLASH PINE SITE PREPARATION STUDY RESULTS AT AGE 11. Plantation Management Research Cooperative. Warnell School of Forest Resources

COMPOSITE TAPER EQUATIONS TO PREDICT OVER- AND UNDER-BARK DIAMETER AND VOLUME OF EUCALYPTUS PILULARIS, E. GLOBOIDEA, AND E. MUELLERIANA IN NEW ZEALAND

forests ISSN

SITE INDEX EQUATIONS FOR RADIATA PINE IN NEW ZEALAND

Forest Biodiversity in Sweden

TIMBER SALE PRESCRIPTION

STAT 2300: Unit 1 Learning Objectives Spring 2019

Summary of 2012 Fire Effects Monitoring for the Southern Blue Ridge Fire Learning Network 1. Peter Bates 2 December 21, 2012

REGENERATION AND SAPLING SURVEY

Potentially available LWD metrics for assessing riparian forest function

SOIL ACIDIFICATION BY ATMOSPHERIC POLLUTION ABSTRACT

VCS MODULE VMD0022 ESTIMATION OF CARBON STOCKS IN LIVING PLANT BIOMASS

Determining the Disturbance Effect on Forest Development for Use in Park Management Plans

ORGANON Calibration for Western Hemlock Project

A Statistical Comparison Of Accelerated Concrete Testing Methods

Equipment. Methods. 6. Pre-treatment monitoring will take place during the growing season.

Chapter 3 TIMBER SUPPLY ANALYSIS

LOBLOLLY PINE IMPROVED PLANTING STOCK-VEGETATION CONTROL STUDY-AGE 15 RESULTS

10.2 Correlation. Plotting paired data points leads to a scatterplot. Each data pair becomes one dot in the scatterplot.

Mountain Pine Bettle Infestation: Cycling and Succession in Lodgepole Pine Forest

Stand Density Management for Optimal Growth. Micky G. Allen II 12/07/2015

FWF Silviculture Lab Exercise 2018 Spring Semester. Comparison of Thinning Methods

2009 Council on Forest Engineering (COFE) Conference Proceedings: Environmentally Sound Forest Operations. Lake Tahoe, June 15-18, 2009

unit area = sample area

OPTIMAL PLOT SIZE FOR SAMPLING BIOMASS IN NATURAL AND LOGGED TROPICAL FORESTS

Lab 8 Community Ecology: Measuring Plant Species Diversity Please Read and Bring With You to Lab

Urban Tree Planting Quantification Guidance

Estimating Natural Regeneration Following Mountain Pine Beetle Attacks in British Columbia Using Nearest Neighbour Analyses

MORTALITY ESTIMATION IN FULLY-STOCKED STANDS OF YOUNG-GROWTH DOUGLAS-FIR

Improving Forest Inventory: Integrating Single Tree Sampling With Remote Sensing Technology

AP Statistics Scope & Sequence

Monitoring Silvicultural Operations

A Study of Tree Distribution in Diameter Classes in Natural Forests of Iran (Case Study: Liresara Forest)

Black Cherry Site Index Curves for the Allegheny Plateau

Community Properties. Describing Plant Communities. Different views of plant communities. Reading assignment: Chapter 9 in GSF

Figure 15 Periodic annual increment (PAI) and gross mean annual increment (MAI) in basal area per acre by treatments for (A) Skykomish treatments 1,

6 Stump Cruising. April 1,

Jeffrey Pine-Mixed Conifer Forests in Northwestern Mexico. Scott Stephens Department of Environmental Science, Policy, and Management UC Berkeley

Itasca State Park, Minnesota* Larry A. Drew. May, 1970

A New Algorithm for Stand Table Projection Models

Uneven-age Stand Management. a.k.a. Uneven-aged (Sized) Silviculture Walt Wintturi- Watershed to Wildlife

Supplemental Figure 1.

Transcription:

106 PROCEEDINGS OF THE NEW ZEALAND ECOLOGICAL SOCIETY, VOL 17, 1970 AN ASSESSMENT OF THE POINT-CENTRED QUARTER METHOD OF PLOTLESS SAMPLING IN SOME NEW ZEALAND FORESTS A F MARK Botany Department, University of Otago, Dunedin A E ESLER Botany Division, DSIR, Auckland SUMMARY: The point-centred quarter method of plotless sampling produces exaggerated values for mean ba5'alarea when used in most New Zealand forest types The error appears to be related to the rather wide range of size classes present in most forest stands and probably arises from the tendency for large,trees to be over-represented in samples INTRODUCTION In most fields of natural science, the density of individuals is usually determined from counts in defined areas of known dimensions When tree density is being measured, the delimitation of plots of up to a hectare or acre in area, presents some difficulties and is time-consuming Because of the reciprocal relationship between density and nearness of individuals to one another it is necessary to kuow only the distance between regularlyspaced individuals to be able to calculate density Each plant has available to it an area equal to the square of the between-plant distance If the individuals are distributed not regularly but at random, density may still be determined from the spacing, since between-plant distances will vary at random from the mean distance In most if not all, natural communities there is a departure from randomness ie individuals tend to be aggregated to some degree (Greig- Smith, 1964) For most forest sampling methods this non~randomness has usually been considered to be insufficient to affect the results seriously Mean distances may be determined by methods based on between-plant distances or, as in the point-centred quarter method, on point-to-plant distances Since being described by Cottam and Curtis (1956), the point-centred quarter method has become accepted, along with other methods of plotless sampling, as one of the most efficient for obtaining quantitative data on forest trees In this method the points are usually located systematically at fixed ;ntervals along a traverse Around each point four quarters or quadrants are delimited and the distance is measured from the point to the centre of the nearest individual stem in each quadrant The species and diameter of this stem are also recorded These values enable both total and relative densities and basal areas to be determined The number of points required to sample a forest stand adequately, varies Cottam and Curtis claimed that only 10 points, ie 40 distance measurements, provided an adequate sample for density in three different forest types They also indicated that a sample which is adequate for density will usually be adequate for basal area; but in a stand with a wide range of size classes many more measurements are required for an adequate sample of basal area than in an even-aged stand Only recently has the accuracy of the quarter method for determining basal areas of forest stands in New Zealand been questioned (Franklin, et al" 1965; Franklin, 1967) Franklin showed that the method consistently produced a serious over-estimation of basal area From four different forest stands, all with a wide range of diameter size classes, he found the quarter method to underestimate the percentage of trees in the smaller size classes and over-estimate the percentage of larger trees This distortion resulted in values for meau basal areas using the quarter method, that were 30~50% higher than those obtained from full tallies Recently we have examined the accuracy of the point-centred quarter method in different forest

MARK AND ELSER: THE POINT-CENTRED QUARTER METHOD OF PLOTLESS SAMPLING 107 types on seven sites: three beech (NothoflJgu~) forests in Fiordland (Norton and Mark, 1967), three in western Otago (Westerskov and Mark, 1968), and a Beilscl/lniedia tawa stand near Palmerston North At each site complete tallies of tree stems (> 4 in diam breast height) were made in one acre (5 x 2 chain) plots In addition, pointcentred quarter data were obtained from 50 points placed systematically within each plot (25 in the three western Otago stands) Distances were measured to the nearest inch and diameters to 01 inch RESULTS AND DISCUSSION The estimates of density and basal area obtained with the point-centred quarter method deviate widely from actual census values in many instances (Table I, Fig I) Most estimated density values are too low, but variation occurs on SIZE CLASS DISTRIBUTION - INCHES FIGURE l Comparison of diameter size class distribution from one-acre plots (solid lines) with values obtained by point-centred quarter samples within the same plots (broken lines) DaJa are for all trees from three beech forest stands in the Routeburn Valley, Western Otago (a--<:), three near Lake Monowai, Fiordland (d-f), and a rawa stand near Palmerston North (g) either side of the true values Mean basal area estimates are consistently high (by 7-46%) with the point-centred quarter method; and estimated total basal areas, being (he product Of Ihese two values, vary accordingly, with a maximum overestimation of 11% The point-centred quarter method apparently does not yield unbiased samples, ie each individual does not have an equal and independent chance of occurring in the sample The method commonly under-estimates the number of small individuals and over-estimates those in the larger size classes In the two stands, where small trees ( < 10 in dbh) are less than 45% of the stems, the deviation is particularly serious (Fig I b and f) The inaccuracies of the point-centred quarter method give cause to examine the underlying theory The method is theoretically most accurate when used in randomly-distributed populations and it is probable that the bias which occurs is in some way related to the structure of the stands examined In most forests, departures from random distribution are the rule and non-randomness occurs at various intensities and scales (Greig-Smith, 1964) In some forests large trees tend to exclude smaller ones from their sphere of influence Thus, the small members of a tree species may occur at some distance from the larger trees but in closer proximity to others of about the same size In this situation the nearest approach to randomness is likely to be displayed by the canopy trees whereas the greatest degree of aggregation would be among the small individuals This is usually evident where regeneration of the dominant species occurs around the margins of large canopies Thus, a single species may displav at least two different scales of pattern Possibly these account for the disproportionate sampling of large and small individuals when the point-centred quarter method is used The tendency towards over-representing large stems and under-representing the small ones implies a relationship between stem diameter and probability of inclusion in a sample Spatial relationships among individuals are involved in the concept of "area potentially available" (apa), put forward by Brown (1965) This is the area around each tree delimited by

108 PROCEEDINGS OF THE NEW ZEALAND ECOLOGICAL SOCiETY, VOL 17, 1970 TABLE 1 Comparison of values from one-acre plots withestimatiol1s based on the point:centred quarter method of plotless sumpling (PCQ) Deviation is expressed as percentage departure Irom the plot values A, MONOWAI, FIORDLAND Mountain beech stand Mtn-Si/ver beech stand Silver beech stalld Plot PcQ % Dev Plot P,CQ % Dev Plot P,CQ %Dev Tclal density (stems/acre) 252 282 +12 t79 208 +16 217 204-6 Mean basal area (sqftjtree)' 102 112 +10 147 157 + 7 168 229 +36 Total basal area (sqftjacre) 256 ' 317 +24 264 327 +24 364 468 +29 B ROUTEBURN VALLEY WESTERN OTAGO Red beech stand Mountain beech stand Silver beech stalld Plot PcQ % Dev Plot PcQ, % Dev Plot PcQ, % Dev ' Total density (stems/acre) 195 142-27 '226 232 h + 3 3t8 298 '- 6 Mean basal area (sqjt/tree) 164 239 ' +46 130 178 +37 075 0,81 + 8' Total basal area (sqft/acre) 320 339 + 6 294 4t4 +41 240 24t 0 C PALMERSTON NORTH Tawa stand Plot PcQ % Dcv TNal density (stems/acre) 382 323-15 Mean basal arc3 (sqft/tree) 051 066 +29 Total basal area (sqftjacre) 197 213 + 8 the perpendicular bisectors' of the straight lines joining it with each of its neighbours In terms of the point-centred quarter method it also represents the area in which the tree ilicontains will be the closest one to any sample point located within that area Thus the concept of apa is appropriate here since it is a measure of the ability of a particular tree to "catch" the points used in the quarter method Franklin (1967) attempting to explain the inaccuracy of the point-centred' quarter method in determining basal areas, suggested that randomly-located points in a stand', which has a wide range of size classes have a greater chance of falling within the' apa: of the larger' trees because they have greater i'1!pa values than smaner trees: There appears to, be 'no published information on apa for any NeW"Zealand indigenous forest nor, so far' as we k'rio"w, for any natural forest stands Brown'B'jl'formation, which Franklin applied came from a planted stand of Pinu,: ratula at Rotoehu Forest in the North Island However, the mapping of permanent 'quadrats on each of three one-acre plots in the Routeburn Valley (Westersk(wand Mark ]968) allowed apa values to be' determined, by the method " described by Brown (1965), for the 739 trees present (Fig 2) Calculations of the linear regression of tree diameter on apa for each of the three plots, individually and jointly (Fig 3) gave significant regression coefficients This direct relationship between apa and tree diameter, by increasing the chances of sampling the larger trees, could explain the consistently high estimates of mean basal area (7-46% in excess of the true value) obtained with the pointcentred quarter method If this relationship between apa and tree diameter is causal in the over~estimation of basal area, then combined with this effect should be another: the under-estimation of density This should ensue from Ihe values for mean distance being too large The results (Table I) however, are iljl'onclusiveon this aspect Total density was in fact under-estimated in only four of the,seven stands analysed No explanation of ; this apparent anomaly can be offered, The' error in estimating - total basal area may be reduced or even nullilied by a low estimation of density, but when density is also over-estimated as occurred in three of the, seven stands, then the error in assessing total basal area:-~may be much greater ' "', '-

MARK AND ELSER: THE POINT-CENTRED QUARTER METHOD OF PLOTLESS SAMPLING 109 Nolhofagus'menziesii Hoherio globrota figure 2 Part of the one-acre permanent quadrat in silver beech forest from the Routeburn Valley shc)w;ng tree taction and,diameter (inches) plus the "area potentially'avdllable'" around each tree " CONCLUSIONS In most types of New Zealand forest, the point-centred quarter method of plotless sampling produces values for mean basal areas that are erroneous and unacceptably large, exceeding the true value by up to 46% Total density estimations may also be seriously but not consistently in error Predictably, density values should be too low Values for total basal area, being the product of mean basal area and density, are therefore usually in error also This error may be reduced or even cancelled out by a low estimation of density compensating for the overestimation of mean basal area The reasons for the shortcomings of the method are not altogether obvious, but appear to be related to the rather wide range of size classes that occur in most New Zealand forests We have established for three beech forest stands that the area potentially available to a tree (which measures its ability to "catch" the point-centred sample points) tends to increase with the diameter of the tree The probability of large trees being included in a point-quarter sample would therefore be increased Values for mean basal area from all seven stands measured, substantiate this We cannot justify continued use of the pointcentred quarter method of obtaining absolute

110 PROCEEDINGS OF THE NEW ZEALAND ECOLOGICAL SOCIETY, VOl 17, 1970 values could be seriously in error' in stands with a wide range of size classes where individual species span only a part of the total range However, in the light of these results, we recommend further field testing of the method both in New Zealand forests and abroad, as wen as in other types of vegetation for which it has been used ACKNOWLEDGMENTS We wish to thank Dr G A M Scott, Botany Depart ment, University of Otago, for assistance with the statistical analyses and Mr T G Robertson, Mathematics Department, for discussion on mathematical aspects REFERENCES FIGURE 3 linear regression of tree diameter on "area potentially available" for 739 trees from three one-acre plot:,' in the Routeburn Valley values of basal area and density, at least in types of forest similar to those which we have exam ined It has been claimed that relative values of these two criteria, obtained with the point-centred quarter method, are valid regardless of distribution patterns (Greig-Smith 1964; p 52) But such BROWN,G S 1965 Point density For ReL Note 38, in stems per acre NZ COTIAM, G, and CURTIS,J T 1956 The use of distance measures in phytosociological sampling Ecology 37: 45t-460 FRANKLIN, D A 1967 Basal areas as determined by the point-centred quarter method NZ J Bot 5: 168-169 FRANKLIN, D A, MARK,A F and SCOTT,G A M 1965 Quantitative data on forest composition NZ J Bot 3: t68-t69 GREIG-SMITH, P 1964 Quantitative plant ecology But~ terv'orths 2nd Ed NORTON,R H, and MARK,A F 1967 An assessment of the point-centred quarter method for forest sampling Sci Record t 7: 44-47 WESTERSKOV,K and MARK,A F 1%8 Beech forests of the upper Routeburn Valley Part t Permanent quadrats and plotless sampling in the three major communities Sci Record 18: 16-52