--- title: "Chapter 4 -- Linear models -- anything goes -- Exercise solutions and Code Boxes" author: "David Warton" date: "2022-08-24" output: rmarkdown::html_vignette vignette: > %\VignetteIndexEntry{Chapter 4 -- Linear models -- anything goes -- Exercise solutions and Code Boxes} %\VignetteEngine{knitr::rmarkdown} %\VignetteEncoding{UTF-8} --- ## Exercise 4.1: Ravens and gunshots We assume: * that we have a random sample of paired differences (most importantly, paired differences are independent of each other) * the paired differences are approixmately normal. ```r library(ecostats) data(ravens) qqenvelope(ravens$delta[ravens$treatment==1]) ``` ![plot of chunk ex4.1ravenscheck](../man/figures/ex4.1ravenscheck-1.png) This looks OK, there is no evidence against normality here ## Code Box 4.1: Paired t-test for the ravens data ```r data(ravens) crowGun = ravens[ravens$treatment == 1,] t.test(crowGun$Before, crowGun$After, paired=TRUE, alternative="less") #> #> Paired t-test #> #> data: crowGun$Before and crowGun$After #> t = -2.6, df = 11, p-value = 0.01235 #> alternative hypothesis: true mean difference is less than 0 #> 95 percent confidence interval: #> -Inf -0.335048 #> sample estimates: #> mean difference #> -1.083333 ``` There is some evidence that ravens fly towards the sound of gunshots. ## Exercise 4.2: Ravens, guns and air horns *Is there evidence that the response to gunshot different to response to other treatments?* We will use a linear model, with `location` included as a blocking factor to control for differences in raven abundance from one place to another, see Code Box 4.3. ## Code Box 4.2: Paired t-test for the ravens data via a linear model ```r library(reshape2) crowLong = melt(crowGun,measure.vars = c("Before","After"), variable.name="time",value.name="ravens") head(crowLong) #> delta site treatment trees time ravens #> 1 2 pilgrim 1 1 Before 0 #> 2 1 pacific 1 1 Before 0 #> 3 4 uhl hil 1 1 Before 0 #> 4 1 wolff r 1 1 Before 0 #> 5 0 teton p 1 1 Before 0 #> 6 3 glacier 1 1 Before 2 ravenlm = lm(ravens~site+time,data=crowLong) anova(ravenlm) #> Analysis of Variance Table #> #> Response: ravens #> Df Sum Sq Mean Sq F value Pr(>F) #> site 11 55.458 5.0417 4.84 0.007294 ** #> time 1 7.042 7.0417 6.76 0.024694 * #> Residuals 11 11.458 1.0417 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Code Box 4.3: A linear model for the blocked design given by the raven counts in Exercise 4.2 To analyse, we first subset to the three treatments of interest (1=gunshot, 2=airhorn, 3=whistle): ```r crowAfter = ravens[ravens$treatment <=3,] ft_crowAfter = lm(After~site+treatment,data=crowAfter) anova(ft_crowAfter) #> Analysis of Variance Table #> #> Response: After #> Df Sum Sq Mean Sq F value Pr(>F) #> site 11 28.667 2.6061 0.9269 0.5327 #> treatment 1 2.667 2.6667 0.9485 0.3402 #> Residuals 23 64.667 2.8116 ``` To check assumptions we could look at diagnostic plots: ```r par(mfrow=c(1,2),mar=c(3,3,1,1),mgp=c(1.75,0.75,0)) plotenvelope(ft_crowAfter) ``` ![plot of chunk box4.3ravensblockassumptions](../man/figures/box4.3ravensblockassumptions-1.png) The residual vs fits plot has a fan-shaped pattern, suggesting that transformation might be a good idea here! ## Exercise 4.3: Seaweed, snails and seaweed mass *Is there an effect of distance of isolation after controlling for wet mass?* *Q's* -- this is a hypothesis test, for an effect on `Total` of `Dist` after controlling for `Wmass`. *P's* We have three variables of interest: * `Total` is the quantitative response * `Dist` is a factor (0, 2 or 10) * `Wmass` is a quantitative variable, to be use as a covariate We can get all three variables onto the same graph using a scatterplot, with different colours for different treatment levels, as in Code Box 4.4. ## Code Box 4.4: Scatterplot of data from Exercise 4.3. ```r data(seaweed) seaweed$Dist = factor(seaweed$Dist) plot(Total~Wmass, data=seaweed, col=Dist, xlab="Wet Mass [log scale]",ylab="Density (per gram) [log scale]") legend("topright",levels(seaweed$Dist),col=1:3,pch=1) ``` ![plot of chunk box4.4seaweedplot](../man/figures/box4.4seaweedplot-1.png) ## Code Box 4.5: Analysis of covariance for the seaweed data of Exercise 4.3. ```r seaweed$logTot = log(seaweed$Total) seaweed$logWmass = log(seaweed$Wmass) lmMassDist=lm(logTot~logWmass+Dist,data=seaweed) anova(lmMassDist) #> Analysis of Variance Table #> #> Response: logTot #> Df Sum Sq Mean Sq F value Pr(>F) #> logWmass 1 7.7216 7.7216 35.7165 1.975e-07 *** #> Dist 2 2.1415 1.0708 4.9528 0.01067 * #> Residuals 53 11.4582 0.2162 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Exercise 4.4: Checking ANCOVA assumptions *Independence* can be guaranteed by randomly allocating `Dist` treatments to plots. Remaining assumptions can be checked using diagnostic plots. ```r par(mfrow=c(1,2),mar=c(3,3,1,1),mgp=c(1.75,0.75,0)) plotenvelope(lmMassDist, n.sim=99) ``` ![plot of chunk ex4.4seaweedplt](../man/figures/ex4.4seaweedplt-1.png) (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) * *normality* - normal quantile plot is close to a straight line so this is OK * *equal variance* - no fan shape on residual vs fits plot so this seems OK * *linearity* -- no U-shape on residual vs fits plot so this seems OK ## Code Box 4.6: ANCOVA with the order of terms switched. Notice that switching the order changes the results in the ANOVA table, and their interpretation. ```r lmDistMass=lm(logTot~Dist+logWmass,data=seaweed) anova(lmDistMass) #> Analysis of Variance Table #> #> Response: logTot #> Df Sum Sq Mean Sq F value Pr(>F) #> Dist 2 4.8786 2.4393 11.283 8.273e-05 *** #> logWmass 1 4.9845 4.9845 23.056 1.329e-05 *** #> Residuals 53 11.4582 0.2162 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Exercise 4.5: Order of terms in writing out a model for snails and seaweed. The correct model is `...logWmass+Dist` so we can look for an effect of `Dist` after controlling for `logWmass`. ## Code Box 4.7: "Type II sums of squares" for the ANCOVA of snails and seaweed. ```r drop1(lmMassDist,test="F") #> Single term deletions #> #> Model: #> logTot ~ logWmass + Dist #> Df Sum of Sq RSS AIC F value Pr(>F) #> 11.458 -83.448 #> logWmass 1 4.9845 16.443 -64.861 23.0561 1.329e-05 *** #> Dist 2 2.1415 13.600 -77.681 4.9528 0.01067 * #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Exercise 4.6: Snails, isolation and time **Q's** -- here is the research question: *Does invertebrate density change with isolation? Does the isolation effect vary with time period?* We want to test a specific hypothesis (no effect of `Dist`, no interaction of `Dist` with `Time`). **P's** There are three variables involved in this research question: * `Total` is invertebrate density (quantitative) * `Dist` is a factor (0, 2 or 10) * `Time` is also a factor (5 or 10 weeks) Given previous information we could also add `logWmass` as another covariate... Comparative boxplots would be a good way to start, as in Code Box 4.8. ## Code Box 4.8: A comparative boxplot of snail density at each of the six possible combinations of sampling time and distance of isolation. ```r plot(Total ~ interaction(Dist,Time), data=seaweed, log="y") ## and as usual use xlabel, ylabel to name axes ``` ![plot of chunk box4.8seaweedcompBox](../man/figures/box4.8seaweedcompBox-1.png) ## Exercise 4.7: Factorial ANOVA assumptions ```r par(mfrow=c(1,2),mar=c(3,3,1,1),mgp=c(1.75,0.75,0)) ft_seaweedFact=lm(logTot~Time*Dist, data=seaweed) plotenvelope(ft_seaweedFact, n.sim=99) ``` ![plot of chunk ex4.7seaweedfact](../man/figures/ex4.7seaweedfact-1.png) (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) * *independence*: if plots were randomly allocated to treatments then this will be satisfied * *normality*: the normal quantile plot is close to a straight line so this looks OK * *equal variance*: no fan-shape on the residual vs fits plot so this looks OK There is no linearity/additivity assumption in a factorial ANOVA ## Code Box 4.9: Factorial ANOVA of Snails, Isolation, and Time ```r ft_seaweedFact = lm(logTot~Time*Dist,data=seaweed) anova(ft_seaweedFact) #> Analysis of Variance Table #> #> Response: logTot #> Df Sum Sq Mean Sq F value Pr(>F) #> Time 1 0.2433 0.24333 0.8512 0.3605470 #> Dist 2 5.0323 2.51613 8.8023 0.0005201 *** #> Time:Dist 2 1.4673 0.73367 2.5666 0.0866804 . #> Residuals 51 14.5784 0.28585 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` There is marginal evidence of an interaction and strong evidence of a `Dist` main effect. So there is an effect of `Dist` and it could potentially vary with `Time`. Note we used `Time*Dist` because `Time` is not the variable of primary interest, it is `Dist`, and we only include `Time` to control for sampling time effects ## Code Box 4.10: R code for the interaction plot in Figure 4.1. ```r library(dplyr) seaweed$Time = as.factor(seaweed$Time) by_DistTime = group_by(seaweed,Dist,Time) distTimeMeans = summarise(by_DistTime, logTotal=mean(log(Total))) #> `summarise()` has grouped output by 'Dist'. You can override using the `.groups` argument. distTimeMeans #> # A tibble: 6 × 3 #> # Groups: Dist [3] #> Dist Time logTotal #> #> 1 0 5 1.58 #> 2 0 10 1.31 #> 3 2 5 2.01 #> 4 2 10 2.36 #> 5 10 5 1.68 #> 6 10 10 2.13 library(ggplot2) library(ggthemes) #loads special themes ggplot(seaweed, aes(x = factor(Dist), y = Total, colour = Time)) + geom_point() + geom_line(data = distTimeMeans, aes(y = exp(logTotal), group = Time)) + theme_few() + xlab("Distance of Isolation") + ylab("Total abundance [log scale]") + scale_y_log10(breaks=c(2,5,10,20)) ``` ![plot of chunk box4.10seaweedinterplot](../man/figures/box4.10seaweedinterplot-1.png) Alternatively, for a simpler plot without the data points on it, try: ```r interaction.plot(seaweed$Dist, seaweed$Time, ft_seaweedFact$fitted, xlab="Isolation of patch", ylab="Total density [log]", trace.label="Time") ``` ![plot of chunk box4.10seaweedinterplot2](../man/figures/box4.10seaweedinterplot2-1.png) ## Code Box 4.11: Uh oh... `anova` gone wrong ```r data(seaweed) ft_nofactor=lm(log(Total)~Time*Dist,data=seaweed) anova(ft_nofactor) #> Analysis of Variance Table #> #> Response: log(Total) #> Df Sum Sq Mean Sq F value Pr(>F) #> Time 1 0.2433 0.24333 0.6671 0.41771 #> Dist 1 0.7164 0.71635 1.9640 0.16691 #> Time:Dist 1 1.0303 1.03031 2.8248 0.09871 . #> Residuals 53 19.3313 0.36474 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Code Box 4.12: Tukey's comparisons don't work for main e ects in an orthogonal design, as seen for Exercise 4.9: ```r seaweed$Dist = factor(seaweed$Dist) seaweed$Time = factor(seaweed$Time) seaweed$logTot = log(seaweed$Total) ft_seaweedFact = lm(logTot~Time*Dist, data=seaweed) library(multcomp) contFact = mcp(Dist="Tukey") # telling R to compare on the Dist factor compFact = glht(ft_seaweedFact, linfct=contFact) # run multiple comparisions #> Warning in mcp2matrix(model, linfct = linfct): covariate interactions found -- default #> contrast might be inappropriate ``` ## Code Box 4.13: Tukey's comparisons for a main e ect of Dist for Exercise 4.6, assuming no interaction. ```r ft_seaweedMain=lm(logTot~Time+Dist,data=seaweed) # note it is + not * contrast = mcp(Dist="Tukey") # telling R to compare on the Dist factor compDistMain = glht(ft_seaweedMain, linfct=contrast) confint(compDistMain) #> #> Simultaneous Confidence Intervals #> #> Multiple Comparisons of Means: Tukey Contrasts #> #> #> Fit: lm(formula = logTot ~ Time + Dist, data = seaweed) #> #> Quantile = 2.4107 #> 95% family-wise confidence level #> #> #> Linear Hypotheses: #> Estimate lwr upr #> 2 - 0 == 0 0.72650 0.28783 1.16516 #> 10 - 0 == 0 0.45838 0.03893 0.87783 #> 10 - 2 == 0 -0.26812 -0.70678 0.17055 ``` ## Code Box 4.14: Tukey's comparisons for all possible treatment combinations for Exercise 4.6. This approach is wasteful as it compares some pairs we are not interested in (e.g. 2.10 vs 0.5). ```r td = interaction(seaweed$Dist,seaweed$Time) ft_seaweedInt=lm(logTot~td,data=seaweed) # Time*Dist as a single term contInt = mcp(td="Tukey") # telling R to compare on all Time*Dist levels compDistInt = glht(ft_seaweedInt, linfct=contInt) summary(compDistInt) #> #> Simultaneous Tests for General Linear Hypotheses #> #> Multiple Comparisons of Means: Tukey Contrasts #> #> #> Fit: lm(formula = logTot ~ td, data = seaweed) #> #> Linear Hypotheses: #> Estimate Std. Error t value Pr(>|t|) #> 2.5 - 0.5 == 0 0.4356 0.2391 1.822 0.46054 #> 10.5 - 0.5 == 0 0.1013 0.2391 0.424 0.99815 #> 0.10 - 0.5 == 0 -0.2643 0.2391 -1.105 0.87656 #> 2.10 - 0.5 == 0 0.7852 0.2635 2.980 0.04749 * #> 10.10 - 0.5 == 0 0.5512 0.2391 2.305 0.21028 #> 10.5 - 2.5 == 0 -0.3343 0.2391 -1.398 0.72723 #> 0.10 - 2.5 == 0 -0.6999 0.2391 -2.927 0.05396 . #> 2.10 - 2.5 == 0 0.3496 0.2635 1.327 0.76838 #> 10.10 - 2.5 == 0 0.1156 0.2391 0.483 0.99654 #> 0.10 - 10.5 == 0 -0.3656 0.2391 -1.529 0.64681 #> 2.10 - 10.5 == 0 0.6839 0.2635 2.596 0.11661 #> 10.10 - 10.5 == 0 0.4499 0.2391 1.882 0.42417 #> 2.10 - 0.10 == 0 1.0495 0.2635 3.983 0.00279 ** #> 10.10 - 0.10 == 0 0.8155 0.2391 3.411 0.01532 * #> 10.10 - 2.10 == 0 -0.2340 0.2635 -0.888 0.94749 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 #> (Adjusted p values reported -- single-step method) ``` ## Code Box 4.15: Tukey's comparisons for Dist within each sampling time, for Exercise 4.6. This is the best approach to use if you think there is an interaction and are primarily interested in Dist. ```r levels(seaweed$Time) = c("five","ten") #need non-numbers for mcp to work levels(seaweed$Dist) = c("Zero","Two","Ten") td = interaction(seaweed$Dist,seaweed$Time) ft_seaweedInt=lm(log(Total)~td,data=seaweed) # Time*Dist as a single term contDistinTime = mcp(td = c("Two.five - Zero.five = 0", "Ten.five - Zero.five = 0", "Ten.five - Two.five = 0", "Two.ten - Zero.ten = 0", "Ten.ten - Zero.ten = 0", "Ten.ten - Two.ten = 0")) compDistinTime = glht(ft_seaweedInt, linfct=contDistinTime) summary(compDistinTime) #> #> Simultaneous Tests for General Linear Hypotheses #> #> Multiple Comparisons of Means: User-defined Contrasts #> #> #> Fit: lm(formula = log(Total) ~ td, data = seaweed) #> #> Linear Hypotheses: #> Estimate Std. Error t value Pr(>|t|) #> Two.five - Zero.five == 0 0.4356 0.2391 1.822 0.31175 #> Ten.five - Zero.five == 0 0.1013 0.2391 0.424 0.99083 #> Ten.five - Two.five == 0 -0.3343 0.2391 -1.398 0.57118 #> Two.ten - Zero.ten == 0 1.0495 0.2635 3.983 0.00125 ** #> Ten.ten - Zero.ten == 0 0.8155 0.2391 3.411 0.00710 ** #> Ten.ten - Two.ten == 0 -0.2340 0.2635 -0.888 0.87446 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 #> (Adjusted p values reported -- single-step method) ``` ## Code Box 4.16: Testing for an interaction in an ANCOVA for density of epifauna as a function of Dist and algal wet mass. ```r lmMassDistInter=lm(logTot~log(Wmass)*Dist,data=seaweed) anova(lmMassDistInter) #> Analysis of Variance Table #> #> Response: logTot #> Df Sum Sq Mean Sq F value Pr(>F) #> log(Wmass) 1 7.7216 7.7216 35.3587 2.489e-07 *** #> Dist 2 2.1415 1.0708 4.9032 0.01128 * #> log(Wmass):Dist 2 0.3208 0.1604 0.7345 0.48475 #> Residuals 51 11.1374 0.2184 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` ## Exercise 4.8: Global plant height *Do the effects on plant height of latitude and rainfall interact?* We need an interaction term in the model, but because `lat` and `rain` are both quantitative, this is a quadratic term and other quadratic terms should enter the model too, as in Code Box 4.17. ## Code Box 4.17: Using R to fit a quadratic model to the plant height data of Exercise 3.1. ```r ft_latRain2 = lm(log(height)~poly(rain,lat,degree=2),data=globalPlants) summary(ft_latRain2) #> #> Call: #> lm(formula = log(height) ~ poly(rain, lat, degree = 2), data = globalPlants) #> #> Residuals: #> Min 1Q Median 3Q Max #> -3.3656 -0.9546 -0.0749 0.9775 3.1311 #> #> Coefficients: #> Estimate Std. Error t value Pr(>|t|) #> (Intercept) 1.1675 0.2094 5.577 1.44e-07 *** #> poly(rain, lat, degree = 2)1.0 5.7178 2.3419 2.441 0.01603 * #> poly(rain, lat, degree = 2)2.0 -1.1417 2.0304 -0.562 0.57493 #> poly(rain, lat, degree = 2)0.1 -5.0623 1.8212 -2.780 0.00628 ** #> poly(rain, lat, degree = 2)1.1 -6.1984 38.1037 -0.163 0.87104 #> poly(rain, lat, degree = 2)0.2 -2.3615 2.5031 -0.943 0.34729 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 #> #> Residual standard error: 1.441 on 125 degrees of freedom #> Multiple R-squared: 0.2706, Adjusted R-squared: 0.2415 #> F-statistic: 9.277 on 5 and 125 DF, p-value: 1.558e-07 ``` ## Exercise 4.9: Snowmelt and time to flowering *Does time from snowmelt to flowering vary with snowmelt date, beyond that explained by elevation? If so, how does it vary?* The data are available as snowmelt in the ecostats package, averaged over measurements taken at three sampling times. Answer the research questions using the appropriate linear model, being sure to check your assumptions. ```r data(snowmelt) plot(flow~snow,data=snowmelt) ``` ![plot of chunk ex4.9snowmelt](../man/figures/ex4.9snowmelt-1.png) ```r snowReduced = na.omit(snowmelt[,c("flow","snow","elev")]) #this line not normally needed, lm can handle NA's, but seems needed because of a weird conflict with MCMCglmm ft_snow = lm(flow~elev+snow, data=snowReduced) plotenvelope(ft_snow, n.sim=99) ``` ![plot of chunk ex4.9snowmelt](../man/figures/ex4.9snowmelt-2.png)![plot of chunk ex4.9snowmelt](../man/figures/ex4.9snowmelt-3.png) (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) This doesn't look great, there is the occasional large value for flowering time, and a suggestion of non-linearity (note from the scatterplot that at early snowmelt dates there is a strong decreasing relationship, but it can't continue to increase at the same rate because then flowering time would become negative). Try log-transforming flowering time... ```r plot(flow~snow,data=snowmelt,log="y") #> Warning in xy.coords(x, y, xlabel, ylabel, log): 1 y value <= 0 omitted from logarithmic plot ``` ![plot of chunk ex4.9snowmeltlog](../man/figures/ex4.9snowmeltlog-1.png) ```r snowReduced$logFlow = log(snowReduced$flow) snowReduced2 = snowReduced[snowReduced$logFlow>-Inf,] # look it's a bit naughty, removing the infinite value, but no biggie as only one value ft_logsnow = lm(logFlow~elev+snow, data=snowReduced2) plotenvelope(ft_logsnow, n.sim=99) ``` ![plot of chunk ex4.9snowmeltlog](../man/figures/ex4.9snowmeltlog-2.png)![plot of chunk ex4.9snowmeltlog](../man/figures/ex4.9snowmeltlog-3.png) ```r summary(ft_logsnow) #> #> Call: #> lm(formula = logFlow ~ elev + snow, data = snowReduced2) #> #> Residuals: #> Min 1Q Median 3Q Max #> -0.90161 -0.15794 0.02338 0.15834 1.08662 #> #> Coefficients: #> Estimate Std. Error t value Pr(>|t|) #> (Intercept) 3.8805208 0.3193019 12.153 < 2e-16 *** #> elev 0.0003357 0.0001226 2.739 0.00651 ** #> snow -0.0103172 0.0007551 -13.663 < 2e-16 *** #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 #> #> Residual standard error: 0.2909 on 316 degrees of freedom #> Multiple R-squared: 0.3774, Adjusted R-squared: 0.3735 #> F-statistic: 95.78 on 2 and 316 DF, p-value: < 2.2e-16 confint(ft_logsnow) #> 2.5 % 97.5 % #> (Intercept) 3.252294e+00 4.5087472418 #> elev 9.457986e-05 0.0005768232 #> snow -1.180299e-02 -0.0088315037 ``` (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) So as snowmelt date increases by 10 days, log(flowering time) decreases by between 0.12 and 0.09 (meaning about a 9-12% decrease). (Aside: Strictly speaking, `snow` should not be treated as a linear variable because it is a time-of-year variable, so is a cyclical variable with a period of 365. But in this case the values are all focussed over a few months towards the middle of the year so a linear approximation is OK.) ## Exercise 4.10: Bird exclusion and biological control *Is there an effect of the netting treatment on changes in aphid numbers across the sampling times?* ```r data(aphidsBACI) str(aphidsBACI) #> 'data.frame': 16 obs. of 5 variables: #> $ Plot : Factor w/ 8 levels "1","2","3","4",..: 1 2 3 4 5 6 7 8 1 2 ... #> $ Treatment: Factor w/ 2 levels "excluded","present": 2 2 2 2 1 1 1 1 2 2 ... #> $ Time : Factor w/ 2 levels "X18.06.","X15.07.": 1 1 1 1 1 1 1 1 2 2 ... #> $ counts : int 78 71 122 271 119 152 120 202 60 48 ... #> $ logcount : num 4.37 4.28 4.81 5.61 4.79 ... plot(logcount~interaction(Time,Treatment),data=aphidsBACI) ``` ![plot of chunk ex4.10aphidnetting](../man/figures/ex4.10aphidnetting-1.png) OK log(count) looks fine, different treatments have similar variation. Eyeballing the data it looks like there is a treatment effect, with many less aphids in the excluded group than in the control... When building a model, we need to take into account the pairing of the data -- Ingo and friends took repeated measures in each plot, so we include `Plot` as a blocking variable to account for this. This in turn means there is no need for a `Treatment` main effect, because different plots received different treatments. ```r par(mfrow=c(1,3),mar=c(3,3,1,1),mgp=c(1.75,0.75,0)) lm_aphids = lm(logcount~Plot+Time+Treatment:Time,data=aphidsBACI) plotenvelope(lm_aphids,which=1:3, n.sim=99) ``` ![plot of chunk ex4.10aphidlm](../man/figures/ex4.10aphidlm-1.png) (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) This all looks fine to me. The term if interest is `Treatment:Time`, which tells us if changes in aphids over time varied due to the bird exclusion treatment: ```r anova(lm_aphids) #> Analysis of Variance Table #> #> Response: logcount #> Df Sum Sq Mean Sq F value Pr(>F) #> Plot 7 0.8986 0.1284 0.4603 0.833357 #> Time 1 5.4675 5.4675 19.6038 0.004434 ** #> Time:Treatment 1 0.7397 0.7397 2.6522 0.154527 #> Residuals 6 1.6734 0.2789 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` There is no evidence of an interaction, meaning there is no evidence of an effect of bird exclusion on aphid numbers. Oh :( I guess the reason for this is that the levels of replication were low -- there were only eight plots, four in each treatment, so an effect would have to be very strong to be statistically significant. ## Exercise 4.11: Seaweed, snails and three factors ```r data(seaweed) str(seaweed) #> 'data.frame': 57 obs. of 22 variables: #> $ Size : chr "SMALL" "SMALL" "SMALL" "SMALL" ... #> $ Dist : int 0 0 0 0 0 2 2 2 2 2 ... #> $ Time : int 5 5 5 5 5 5 5 5 5 5 ... #> $ Rep : int 1 2 3 4 5 1 2 3 4 5 ... #> $ Wmass : num 15.8 13.1 25.1 29.7 17.4 13.3 4.7 6.8 7.7 14.3 ... #> $ Amph : num 75 16 14 21 55 17 9 11 28 37 ... #> $ Cope : num 0 7 37 37 0 14 6 29 21 83 ... #> $ Poly : num 17 8 2 5 1 2 1 3 6 10 ... #> $ Anem : num 2 0 0 0 0 0 0 1 0 0 ... #> $ Iso : num 0 2 1 1 15 0 12 51 19 56 ... #> $ Bival : num 3 2 1 0 0 2 0 4 3 0 ... #> $ Gast : num 6 18 33 9 9 1 10 7 4 15 ... #> $ Turb : num 1 0 0 0 0 0 0 0 0 0 ... #> $ Prawn : num 0 0 0 0 5 1 0 0 0 1 ... #> $ Urchin: num 0 0 0 0 0 0 0 0 0 0 ... #> $ Fish : num 0 0 0 0 1 0 0 0 0 0 ... #> $ Crab : num 0 1 1 0 0 0 0 1 0 0 ... #> $ Caddis: num 0 0 0 0 1 0 0 0 0 0 ... #> $ Opi : num 0 1 0 1 0 0 0 0 0 0 ... #> $ Ost : num 0 0 6 3 0 0 1 1 0 11 ... #> $ Bstar : num 0 0 0 0 0 0 0 0 0 1 ... #> $ Total : num 6.58 4.2 3.78 2.59 5 ... seaweed$logTot = log(seaweed$Total) seaweed$Dist = factor(seaweed$Dist) par(mar=c(4,7,1,1)) plot(logTot~interaction(Dist,Size,Time),data=seaweed,xlab="",ylab="Total abundance [log scale]",horizontal=TRUE,col=2:4,las=1) legend("topleft",legend=paste0("Dist=",levels(seaweed$Dist)),pch=15,col=2:4,pt.cex=2) ``` ![plot of chunk ex4.11seaweed3](../man/figures/ex4.11seaweed3-1.png) All good so far, no obvious trend, except that `Dist=0` seems to have lower total abundance at most times/sizes. Will analyse as a three-way ANOVA ```r par(mfrow=c(1,3),mar=c(3,3,1,1),mgp=c(1.75,0.75,0)) ft_seaweed3 = lm(log(Total)~Size*Time*Dist,data=seaweed) plotenvelope(ft_seaweed3,which=1:3, n.sim=99) ``` ![plot of chunk ex4.11seaweedanova3](../man/figures/ex4.11seaweedanova3-1.png) ```r anova(ft_seaweed3) #> Analysis of Variance Table #> #> Response: log(Total) #> Df Sum Sq Mean Sq F value Pr(>F) #> Size 1 0.9940 0.99399 3.5849 0.0647472 . #> Time 1 0.1923 0.19234 0.6937 0.4093064 #> Dist 2 4.7737 2.38686 8.6084 0.0006829 *** #> Size:Time 1 0.0605 0.06055 0.2184 0.6425429 #> Size:Dist 2 0.1800 0.09000 0.3246 0.7244968 #> Time:Dist 2 1.4117 0.70583 2.5456 0.0896686 . #> Size:Time:Dist 2 1.2318 0.61592 2.2214 0.1202189 #> Residuals 45 12.4772 0.27727 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` (Note that `plotenvelope` was run with just `99` iterations, to speed up computation time.) From the plots, we can't see any problems with assumptions. The ANOVA suggests a main effect of `Dist`, with marginal evidence of an interaction with `Time` (judging from the boxplots, this is probably because of the larger values for `logTot` at `Time=5` in large plots). We could reanalyse the data including `Wmass` as a covariate, for a three-factor ANCOVA: ```r ft_seaweedW3 = lm(logTot~Wmass*Size*Time*Dist,data=seaweed) anova(ft_seaweedW3) #> Analysis of Variance Table #> #> Response: logTot #> Df Sum Sq Mean Sq F value Pr(>F) #> Wmass 1 6.7793 6.7793 28.2266 7.328e-06 *** #> Size 1 0.7106 0.7106 2.9585 0.094792 . #> Time 1 0.0747 0.0747 0.3109 0.580899 #> Dist 2 2.8114 1.4057 5.8529 0.006675 ** #> Wmass:Size 1 0.0941 0.0941 0.3917 0.535700 #> Wmass:Time 1 0.0233 0.0233 0.0970 0.757459 #> Size:Time 1 0.3501 0.3501 1.4579 0.235849 #> Wmass:Dist 2 0.1979 0.0990 0.4121 0.665636 #> Size:Dist 2 0.0886 0.0443 0.1844 0.832475 #> Time:Dist 2 1.3263 0.6631 2.7611 0.077848 . #> Wmass:Size:Time 1 0.0081 0.0081 0.0337 0.855482 #> Wmass:Size:Dist 2 0.1404 0.0702 0.2924 0.748389 #> Wmass:Time:Dist 2 0.2767 0.1384 0.5761 0.567645 #> Size:Time:Dist 2 0.3440 0.1720 0.7162 0.496020 #> Wmass:Size:Time:Dist 2 0.1701 0.0850 0.3540 0.704475 #> Residuals 33 7.9257 0.2402 #> --- #> Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1 ``` We get pretty much the same results. `Wmass` seems to be an important covariate, but after controlling for it, there is still a strong `Dist` main effect and not much else happening.