DOUGLAS FIR BEETLE TRAP-SUPPRESSION STUDY STATISTICAL REPORT

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DOUGLAS FIR BEETLE TRAP-SUPPRESSION STUDY STATISTICAL REPORT Prepared for Dr. Robert Progar U.S. Forest Service Forest Sciences Laboratory Corvallis, Oregon January 2005 By Greg Brenner Pacific Analytics PO Box 219 Albany, OR 97321 (541) 926-0117

Prepared by: Pacific Analytics, L.L.C. Post Office Box 219 Albany, Oregon 97321 Tel. (541) 926-0117 mail@statpros.com www.statpros.com Gregory Brenner Senior Associate / Project Manager The pictures contained in this report are for the exclusive use by Pacific Analytics, L.L.C and its clients. All photographs are copyrighted by Pacific Analytics, L.L.C. and may not be reproduced or used without the express written permission of Pacific Analytics, L.L.C.

Table of Contents I. TABLE OF CONTENTS I. Table of Contents... 1 II. Executive Summary... 2 III. Introduction... 3 IV. Statistical Procedures... 6 V. Pre-Treatment ANOVA... 8 VI. Post-Treatment ANOVA... 9 VII. Literature Cited... 16 Pacific Analytics,L.L.C. Page 1

Executive Summary II. EXECUTIVE SUMMARY This is a report of the results of statistical analysis of Beetle Suppression data. Questions of interest are defined. The report includes a summary of the project, discussion of the structure of the data and explanatory and response variables, and the statistical procedures employed in the analysis. The data used was provided by Dr. Rob Progar, USDA Forest Service PNW Research Station, Corvallis, Oregon. Results are reported in two chapters, Pre-Treatment and Post-Treatment analyses. A list of Literature Cited is included in the last chapter. S-Plus commands and bench notes are included on the enclosed CD for further information and clarification of the analyses. Excel data and table files are also provided on the enclosed CD. This work is in partial fulfillment of USDA Purchase Order Number 43-04R4-4-0058. Pacific Analytics,L.L.C. Page 2

Introduction III. INTRODUCTION Summary of the experiment and objectives In 2004 an experiment was conducted to determine if reducing the number of Douglas Fir beetles in stands by trapping would reduce the number of trees killed by the beetles. In forests at each of two localities in Montana (Phillipsburg and Wisdom) six 2-acre plots were established to monitor tree mortality due to beetle attack. Treatments were assigned at random to the plots. On the perimeter of the three of the treatment plots at each locality, nine traps were established (in groups of three). No traps were set at the control plots. Traps were opened over the course of one field season, and the number of trees on each plot were classified into one of six status-categories. Pacific Analytics received the raw data in Excel spreadsheets during an initial consultation with the client in December 2004. The primary assigned tasks were to compile the data for evaluation, and to estimate the effects of beetle suppression on tree mortality. The structure of this study is a completely randomized design. The experimental units for testing Treatment level effects are the plots on which measurements were made. Pacific Analytics,L.L.C. Page 3

Introduction Primary Questions of Interest 1. Does trapping reduce the proportion of available trees that die (Code 2 trees) due to beetle attack? 2. Does trapping reduce the proportion of available trees attacked by beetles (Code 2 and Code 5 trees)? 3. Is there a relationship between the number of Douglas Fir Beetles and the number of red-legged Clarid beetles? 4. Is there a relationship between the number of Douglas Fir Beetles and the proportion of available trees attacked by beetles (Code 2 and Code 5 trees)? 5. Is there a relationship between the number of Douglas Fir Beetles and the proportion of available trees that die due to beetle attack (Code 2 trees)? Population of Interest The proportion of available trees on two-acre plots that died from beetle attack (Code 2 trees). The proportion of available trees on two-acre plots that were attacked by beetles (Code 2 and Code 5 trees). The number of red-legged Clarid beetles per treatment plot The number of Douglas Fir beetles per treatment plot Structure of the Experiment Experimental Units Experimental units are 2-acre plots at each locality. Response variables The proportion of trees on two-acre plots that died from beetle attack. Pacific Analytics,L.L.C. Page 4

Introduction ANOVA Tables Without Covariates Source of Variation Degrees of Freedom Locality 1 Site 4 Treatments 1 Experimental Error 5 With Covariates Source of Variation Degrees of Freedom Locality 1 Site 4 Covariate 1 1 Covariate 2 1 Treatments 1 Experimental Error 3 Pacific Analytics,L.L.C. Page 5

Statistical Procedures IV. Statistical Procedures Data Compilation Data compilation was conducted using Excel spreadsheet commands. The proportion for each category of Tree Code (0 5) were calculated based on the number of trees in that Code Class divided by the number of available trees (Code 0 + Code 2 + Code 5 trees). Proportion data were transformed using the arc sin square root transformation before analysis with ANOVA (Sokal and Rohlf 1981). Analysis of Variance Analysis of Variance is a statistical method used to analyze independent samples from three or more treatment groups. The method uses the F-test to answer the question Are all of the treatment group means equal? The F-test is based on residuals, the difference between the hypothesized value and the observed value. Residuals represent the variability in the observations unexplained by a model. The F-test compares the sum of squared residuals from a reduced (equal means) model to the sum of squared residuals from a full (separate means) model. The reduced model residuals were derived by subtracting the observed (measured) values from the grand mean for all observations. These residuals are squared and summed to obtain the sum of squared residuals (reduced). This value is also known as the Total variation or error. The full model residuals are derived by subtracting the observed (measured) values from mean of the treatment group to which it was assigned. These residuals are squared Pacific Analytics,L.L.C. Page 6

Statistical Procedures and summed to obtain the sum of squared residuals (full). This value is also known as the Within Groups variation. The difference between the sum of squared residuals (reduced) and the sum of squared residuals (full) is called the extra sum of squares, also known as the Between Groups variation. The F-statistic is the ratio of the average Between Groups variation (extra sum of squares divided by the degrees of freedom) and the Total variation. This ratio has an F-distribution that depends on two known parameters, the numerator degrees of freedom and the denominator degrees of freedom. The p-value obtained represents the strength of the evidence against the equal means model and in favor of the model with separate means. The assumptions of ANOVA are the same as those for many of the other standard statistical methods. Analysis of Variance is based on the normal (Gaussian) probability distribution, although this assumption is not critical unless the distributions of the data are extremely long-tailed and sample sizes are unequal. The method strictly relies on the assumption of independence of the observations, and random assignment of sampling units to treatment groups. The assumption of equal variance between groups is crucial, but ANOVA is robust to departures of variance equality when sample sizes are equal. Finally, outliers in the data can influence the results of ANOVA. Software used for all statistical analyses was S-Plus 2000 (MathSoft 1988-1999). Pacific Analytics,L.L.C. Page 7

Pretreatment ANOVA V. PRETREATMENT ANOVA NUMBER OF TREES PER PLOT Analysis of Variance (ANOVA) was used to test for pretreatment differences in the number of trees per 2-acre plot between treatments and control plots. Site and Locality were used as a blocking factors. ANOVA Table SOV DF Sum of Squares Mean Squares F Values P-Values Locality 1 109634.1 109634.1 9.942075 0.0253 Site 4 121115.7 30278.9 2.745818 0.1488 Treatment 1 12224.1 12224.1 1.108531 0.3406 Error 5 55136.4 11027.3 Statistical Inference There is no evidence of a difference in the number of trees per 2-acre plot between treatment and control plots (p-value = 0.3406). The control plots averaged 233 (±38.2) trees per 2-acre plot and the treatment plots averaged 297 (±89.8) trees per 2-acre plot. There is evidence that the Phillipsburg locality had a higher number of trees per 2-acre plot than Wisdom locality (p-value = 0.0253). The 2-acre plots in Phillipsburg had a average of 361 (±77.3) trees per 2-acre plot and the Wisdom plots had an average of 170 (±17.5) trees per 2-acre plot. Pacific Analytics,L.L.C. Page 8

Post-Treatment Analysis VI. POST-TREATMENT ANALYSIS CODE 2 TREES Analysis of Variance was used to test for a difference in the proportion of Code 2 trees per 2-acre plot between treatment and control plots. An arcsin square root transformation was applied to the proportion data for the analysis. Locality and site were used as blocking factors. ANOVA Table SOV DF Sum of Squares Mean Squares F Values P-Values Locality 1 0.04826496 0.04826496 2.571812 0.1697 Site 4 0.09622009 0.02405502 1.281779 0.3881 Treatment 1 0.00760855 0.00760855 0.405424 0.5523 Error 5 0.09383454 0.01876691 Statistical Inference There is no evidence of a difference in the median proportion of Code 2 trees per 2-acre plot between treatment and control plots (p-value = 0.5523). The median proportion of Code 2 trees on control plots was 0.08 (±0.001) trees per 2-acre plot and the median proportion of Code 2 trees on treatment plots was 0.11 (±0.007) trees per 2-acre plot. Pacific Analytics,L.L.C. Page 9

Post-Treatment Analysis CODE 2 TREES WITH COVARIATES Analysis of Variance was used to test for a difference in the proportion of Code 2 trees per 2-acre plot between treatment and control plots. An arcsin square root transformation was applied to the proportion data for the analysis. Locality and site were used as blocking factors. The proportion of Code 0 and Code 3 trees (arcsin square root transformed) were used as covariates in the ANOVA models. The covariates were placed in the model after accounting first for Locality and Site variations but before accounting for Treatment variation. ANOVA Table SOV DF Sum of Squares Mean Squares F Values P- Values Locality 1 0.04826496 0.04826496 27.42496 0.0136 Site 4 0.09622009 0.02405502 13.66847 0.0287 Code 0 1 0.08446699 0.08446699 47.99556 0.0062 Code 3 1 0.0000032 0.0000032 0.00182 0.9687 Treatment 1 0.01169322 0.01169322 6.64428 0.0819 Error 3 0.00527967 0.00175989 Statistical Inference There is suggestive evidence of a difference in the median proportion of Code 2 trees per 2-acre plot between treatment and control plots after accounting for the proportions of Code 0 and Code 3 trees per plot (p-value = 0.0819). The median proportion of Code 2 trees on control plots was 0.08 (±0.001) trees per 2-acre plot and the median proportion of Code 2 trees on treatment plots was 0.11 (±0.007) trees per 2-acre plot. Pacific Analytics,L.L.C. Page 10

Post-Treatment Analysis CODE 3 TREES Analysis of Variance was used to test for a difference in the proportion of Code 3 trees per 2-acre plot between treatment and control plots. An arcsin square root transformation was applied to the proportion data for the analysis. Locality and site were used as blocking factors. ANOVA Table SOV DF Sum of Squares Mean Squares F Values P-Values Locality 1 0.00609746 0.00609746 0.625542 0.4648 Site 4 0.03930021 0.00982505 1.007958 0.4825 Treatment 1 0.02534639 0.02534639 2.600302 0.1678 Error 5 0.04873739 0.00974748 Statistical Inference There is no evidence of a difference in the median proportion of Code 3 trees per 2-acre plot between treatment and control plots (p-value = 0.1678). The median proportion of Code 3 trees on control plots was 0.10 (±0.002) trees per 2-acre plot and the median proportion of Code 3 trees on treatment plots was 0.05 (±0.001) trees per 2-acre plot. Pacific Analytics,L.L.C. Page 11

Post-Treatment Analysis CODE 2 and 5 TREES Analysis of Variance was used to test for a difference in the combined proportion of Code 2 and Code 5 trees per 2-acre plot between treatment and control plots. An arcsin square root transformation was applied to the proportion data for the analysis. Locality and site were used as blocking factors. ANOVA Table SOV DF Sum of Squares Mean Squares F Values P-Values Locality 1 0.0925948 0.09259483 3.291138 0.1294 Site 4 0.1424617 0.03561541 1.265894 0.3929 Treatment 1 0.060232 0.060232 2.140852 0.2033 Error 5 0.140673 0.02813459 Statistical Inference There is no evidence of a difference in the median combined proportion of Code 2 and Code 5 trees per 2-acre plot between treatment and control plots (p-value = 0.2033). The median combined proportion of Code 2 and Code 5 trees on control plots was 0.11 (±0.002) trees per 2-acre plot and the median proportion of Code 3 trees on treatment plots was 0.22 (±0.01) trees per 2-acre plot. Pacific Analytics,L.L.C. Page 12

Post-Treatment Analysis NUMBER OF BEETLES AND TREES ATTACKED Regression was used to test for a significant relationship between the proportion of Code 2 trees per 2-acre plot and the number of Douglas Fir beetles captured on treatment plots. An arcsin square root transformation was applied to the proportion data for the analysis. The beetle count data were transformed using a natural logarithm transformation. Locality was used as blocking factor. Regression Table SOV Coefficient Standard Error t-value P-value Intercept 1.59 3.8958 0.4073 0.7111 Locality -0.33 0.2201-1.4848 0.2343 Beetles -0.09 0.3066-0.2867 0.7930 Statistical Inference There is no evidence of a relationship between the median proportion of Code 2 trees per 2-acre plot and the median number of beetles captured per plot (pvalue = 0.7930). Pacific Analytics,L.L.C. Page 13

Post-Treatment Analysis NUMBER OF BEETLES AND TREES ATTACKED Regression was used to test for a significant relationship between the combined proportion of Code 2 and Code 5 trees per 2-acre plot and the number of Douglas Fir beetles captured on treatment plots. An arcsin square root transformation was applied to the proportion data for the analysis. The beetle count data were transformed using a natural logarithm transformation. Locality was used as blocking factor. Regression Table SOV Coefficient Standard Error t-value P-value Intercept 5.03 3.7076 1.3578 0.2676 Locality -0.55 0.2095-2.6366 0.0779 Beetles -0.34 0.2918-1.179 0.3234 Statistical Inference There is no evidence of a relationship between the median combined proportion of Code 2 and Code 5 trees per 2-acre plot and the median number of beetles captured per plot (p-value = 0.3234). Pacific Analytics,L.L.C. Page 14

Post-Treatment Analysis NUMBER OF DOUGLAS FIR BEETLES AND RED-LEGGED CLARID BEETLES Regression was used to test for a significant relationship between the number of red-legged Clarid beetles and the number of Douglas Fir beetles captured on treatment plots. The beetle count data were transformed using a natural logarithm transformation. Locality was used as blocking factor. Regression Table SOV Coefficient Standard Error t-value P-value Intercept 8.38 12.6321 0.6636 0.5544 Locality -0.03 0.7138-0.0466 0.9658 Beetles 0.03 0.9943 0.0323 0.9763 Statistical Inference There is no evidence of a relationship between the median number of red-legged Clarid beetles and the median number of beetles captured per plot (p-value = 0.9763). Pacific Analytics,L.L.C. Page 15

Literature Cited VII. LITERATURE CITED Sokal, R.R. and F.J. Rohlf. 1981. Biometry, Second Edition. W.H. Freeman and Company, New York. 859 pp. S-Plus 2000. 1988-1999. Data Analysis Products Division, MathSoft, Seattle, WA. Pacific Analytics,L.L.C. Page 16