Dr. Salvador A. Gezan

a month agoThe fitting of a linear mixed model (LMM) can be divided into two steps. The first one is the estimation of the variance components. In ASReml and Genstat this is done using restricted (or residual) maximum likelihood based on a complex algorithm that uses the average information (AI) algorithm and sparse matrix operations. Once these variance components are estimated, we then go onto the second step, where these variances are used to obtain estimates of the fixed effects and predictions of random effects. This is where we need to differentiate between BLUEs and BLUPs. *But what are these*?

Best Linear Unbiased Estimates (BLUEs) are the solutions (or estimates) associated with the fixed effects and Best Linear Unbiased Predictions (BLUPs) are the solutions (but identified as predictions) associated with the random effects of a model. *But what does Best Linear Unbiased mean*?

Best | Among all possible unbiased linear estimators these solutions have minimum variance |

Linear | Solutions are formed from a linear combination of the observations |

Unbiased | Expectations of these solutions are equal to their true values |

The use of BLUPs to predict random effects was first described by C. R. Henderson. He developed the mixed model equations (MME, see equation [2]) for LMMs in order to calculate BLUPs of breeding values (or any random effect) and BLUEs of fixed effects.

Let’s have a look at how solutions are obtained from a linear mixed model. For this, we will consider the model written in matrix notation:

[1]

where , , , and are vectors of observations, fixed effects, random effects, and random residuals, respectively; and and are design matrices connecting the observations to the effects.

The above model is the basis for most genetic analyses with what is known as the *Animal Model*, that once fitted provides us with an estimation of the breeding values for each of the ‘animals’ (individuals) considered in the model.

Considering the Animal Model on its matrix notation of above, we have corresponding to a series of nuisance fixed effects, for example contemporary group, age or replicate. However, what is more interesting to us is , corresponding to the breeding values. As this factor is random, we have distributional assumptions, namely that ~ where the is the numerator relationship matrix that describes the additive genetic relationship between individuals, and is the additive variance.

As the error or residual term, , is also a random effect, we have their distributional assumptions of ~ , with an identity matrix and the residual variance (or mean square error).

As you can see, the central problem in predicting breeding values from observed phenotypic data is separating the genetic and environmental effects. This separation is clearly done by the Animal Model.

So, in order to get our solutions (i.e., BLUEs and BLUPs), we need to solve the following system of equations, known as Henderson’s MME:

[2]

All the elements we have previously defined, except for , which is formed from variance components estimated in the first step when fitting a LMM. This system can involve hundreds or even thousands of equations, requiring some intense computational calculations in order to estimate our solutions.

A different way to see the above equations is to express the formulae for BLUEs as:

[3]

and for the BLUPs (breeding values) as:

[4]

where

Interestingly, expression [3] is equivalent to the estimation of Weighted Least Squares (WLS) as described for linear regression or linear models. Here, the weights are defined as . This is relevant as the elements on (particularly the diagonals) will be associated with the amount of information, or weight, that each record has (in this case phenotypic response of an individual).

Also, the expression for the breeding values is extremely relevant. Note that [4] can be written as:

where is resembling the calculation of heritability with the genetic component in the numerator () and the phenotypic variance () in the denominator as an inverse. Also, , represents the phenotypic response ‘corrected’ for nuisance effects. Therefore, the above expression resembles the breeder’s equation:

where the index is used to identify the individual.

Therefore, fitting a LMM using an Animal Model is equivalent to that well-known expression, but in this case, the specification of matrices connecting pieces of data allows us to use *all* information and relationships between individuals and to have different weights for each of these pieces. Therefore, Henderson’s MME provide us with the best linear unbiased predictions of our breeding values!

Salvador Gezan is a statistician/quantitative geneticist with more than 20 years’ experience in breeding, statistical analysis and genetic improvement consulting. He currently works as a Statistical Consultant at VSN International, UK. Dr. Gezan started his career at Rothamsted Research as a biometrician, where he worked with Genstat and ASReml statistical software. Over the last 15 years he has taught ASReml workshops for companies and university researchers around the world.

Dr. Gezan has worked on agronomy, aquaculture, forestry, entomology, medical, biological modelling, and with many commercial breeding programs, applying traditional and molecular statistical tools. His research has led to more than 100 peer reviewed publications, and he is one of the co-authors of the textbook *Statistical Methods in Biology: Design and Analysis of Experiments and Regression*.

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The VSNi Team

7 months agoOutliers are sample observations that are either much larger or much smaller than the other observations in a dataset. Outliers can skew your dataset, so how should you deal with them?

Imagine Jane, the general manager of a chain of computer stores, has asked a statistician, Vanessa, to assist her with the analysis of data on the daily sales at the stores she manages. Vanessa takes a look at the data, and produces a boxplot for each of the stores as shown below.

Vanessa pointed out to Jane the presence of outliers in the data from Store 2 on days 10 and 22. Vanessa recommended that Jane checks the accuracy of the data. *Are the outliers due to recording or measurement error?* If the outliers can’t be attributed to errors in the data, Jane should investigate what might have caused the increased sales on these two particular days. Always investigate outliers - this will help you better understand the data, how it was generated and how to analyse it.

Vanessa explained to Jane that we should never drop a data value just because it is an outlier. The nature of the outlier should be investigated before deciding what to do.

Whenever there are outliers in the data, we should look for possible causes of error in the data. If you find an error but cannot recover the correct data value, then you should replace the incorrect data value with a missing value.

However, outliers can also be real observations, and sometimes these are the most interesting ones! If your outlier can’t be attributed to an error, you shouldn’t remove it from the dataset. Removing data values unnecessarily, just because they are outliers, introduces bias and may lead you to draw the wrong conclusions from your study.

- Transform the data: if the dataset is not normally distributed, we can try transforming the data to normalize it. For example, if the data set has some high-value outliers (i.e. is right skewed), the log transformation will “pull” the high values in. This often works well for count data.
- Try a different model/analysis: different analyses may make different distributional assumptions, and you should pick one that is appropriate for your data. For example, count data are generally assumed to follow a Poisson distribution. Alternatively, the outliers may be able to be modelled using an appropriate explanatory variable. For example, computer sales may increase as we approach the start of a new school year.

In our example, Vanessa suggested that since the mean for Store 2 is highly influenced by the outliers, the median, another measure of central tendency, seems more appropriate for summarizing the daily sales at each store. Using the statistical software Genstat, Vanessa can easily calculate both the mean and median number of sales per store for Jane.

Vanessa also analyses the data assuming the daily sales have Poisson distributions, by fitting a log-linear model.

Notice that Vanessa has included “Day” as a blocking factor in the model to allow for variability due to temporal effects.

From this analysis, Vanessa and Jane conclude that the means (of the Poisson distributions) differ between the stores (p-value < 0.001). Store 3, on average, has the most computer sales per day, whereas Stores 1 and 4, on average, have the least.

There are other statistical approaches Vanessa might have used to analyse Jane’s sales data, including a one-way ANOVA blocked by Day on the log-transformed sales data and Friedman’s non-parametric ANOVA. Both approaches are available in Genstat’s comprehensive menu system.

There are many ways to deal with outliers, but no single method will work in every situation. As we have learnt, we can remove an observation if we have evidence it is an error. But, if that is not the case, we can always use alternative summary statistics, or even different statistical approaches, that accommodate them.

Dr. John Rogers

9 months agoEarlier this year I had an enquiry from Carey Langley of VSNi as to why I had not renewed my Genstat licence. The truth was simple – I have decided to fully retire after 50 years as an agricultural entomologist / applied biologist / consultant. This prompted some reflections about the evolution of bioscience data analysis that I have experienced over that half century, a period during which most of my focus was the interaction between insects and their plant hosts; both how insect feeding impacts on plant growth and crop yield, and how plants impact on the development of the insects that feed on them and on their natural enemies.

My journey into bioscience data analysis started with undergraduate courses in biometry – yes, it was an agriculture faculty, so it was biometry not statistics. We started doing statistical analyses using full keyboard Monroe calculators (for those of you who don’t know what I am talking about, you can find them here). It was a simpler time and as undergraduates we thought it was hugely funny to divide 1 by 0 until the blue smoke came out…

After leaving university in the early 1970s, I started working for the Agriculture Department of an Australian state government, at a small country research station. Statistical analysis was rudimentary to say the least. If you were motivated, there was always the option of running analyses yourself by hand, given the appearance of the first scientific calculators in the early 1970s. If you wanted a formal statistical analysis of your data, you would mail off a paper copy of the raw data to Biometry Branch… and wait. Some months later, you would get back your ANOVA, regression, or whatever the biometrician thought appropriate to do, on paper with some indication of what treatments were different from what other treatments. Dose-mortality data was dealt with by manually plotting data onto probit paper.

In-house ANOVA programs running on central mainframes were a step forward some years later as it at least enabled us to run our own analyses, as long as you wanted to do an ANOVA…. However, it also required a 2 hours’ drive to the nearest card reader, with the actual computer a further 1000 kilometres away.… The first desktop computer I used for statistical analysis was in the early 1980s and was a CP/M machine with two 8-inch floppy discs with, I think, 256k of memory, and booting it required turning a key and pressing the blue button - yes, really! And about the same time, the local agricultural economist drove us crazy extolling the virtues of a program called Lotus 1-2-3!

Having been brought up on a solid diet of the classic texts such as Steele and Torrie, Cochran and Cox and Sokal and Rohlf, the primary frustration during this period was not having ready access to the statistical analyses you knew were appropriate for your data. Typical modes of operating for agricultural scientists in that era were randomised blocks of various degrees of complexity, thus the emphasis on ANOVA in the software that was available in-house. Those of us who also had less-structured ecological data were less well catered for.

My first access to a comprehensive statistics package was during the early to mid-1980s at one of the American Land Grant universities. It was a revelation to be able to run virtually whatever statistical test deemed necessary. Access to non-linear regression was a definite plus, given the non-linear nature of many biological responses. As well, being able to run a series of models to test specific hypotheses opened up new options for more elegant and insightful analyses. Looking back from 2021, such things look very trivial, but compared to where we came from in the 1970s, they were significant steps forward.

My first exposure to Genstat, VSNi’s stalwart statistical software package, was Genstat for Windows, Third Edition (1997). Simple things like the availability of residual plots made a difference for us entomologists, given that much of our data had non-normal errors; it took the guesswork out of whether and what transformations to use. The availability of regressions with grouped data also opened some previously closed doors.

After a deviation away from hands-on research, I came back to biological-data analysis in the mid-2000s and found myself working with repeated-measures and survival / mortality data, so ventured into repeated-measures restricted maximum likelihood analyses and generalised linear mixed models for the first time (with assistance from a couple of Roger Payne’s training courses in Hobart and Queenstown). Looking back, it is interesting how quickly I became blasé about such computationally intensive analyses that would run in seconds on my laptop or desktop, forgetting that I was doing ANOVAs by hand 40 years earlier when John Nelder was developing generalised linear models. How the world has changed!

Of importance to my Genstat experience was the level of support that was available to me as a Genstat licensee. Over the last 15 years or so, as I attempted some of these more complex analyses, my aspirations were somewhat ahead of my abilities, and it was always reassuring to know that Genstat Support was only ever an email away. A couple of examples will flesh this out.

Back in 2008, I was working on the relationship between insect-pest density and crop yield using R2LINES, but had extra linear X’s related to plant vigour in addition to the measure of pest infestation. A support-enquiry email produced an overnight response from Roger Payne that basically said, “Try this”. While I slept, Roger had written an extension to R2LINES to incorporate extra linear X’s. This was later incorporated into the regular releases of Genstat. This work led to the clearer specification of the pest densities that warranted chemical control in soybeans and dry beans (https://doi.org/10.1016/j.cropro.2009.08.016 and https://doi.org/10.1016/j.cropro.2009.08.015).

More recently, I was attempting to disentangle the effects on caterpillar mortality of the two Cry insecticidal proteins in transgenic cotton and, while I got close, I would not have got the analysis to run properly without Roger’s support. The data was scant in the bottom half of the overall dose-response curves for both Cry proteins, but it was possible to fit asymptotic exponentials that modelled the upper half of each curve. The final double-exponential response surface I fitted with Roger’s assistance showed clearly that the dose-mortality response was stronger for one of the Cry proteins than the other, and that there was no synergistic action between the two proteins (https://doi.org/10.1016/j.cropro.2015.10.013)

One thing that I especially appreciate about having access to a comprehensive statistics package such as Genstat is having the capacity to tease apart biological data to get at the underlying relationships. About 10 years ago, I was asked to look at some data on the impact of cold stress on the expression of the Cry2Ab insecticidal protein in transgenic cotton. The data set was seemingly simple - two years of pot-trial data where groups of pots were either left out overnight or protected from low overnight temperatures by being moved into a glasshouse, plus temperature data and Cry2Ab protein levels. A REML analysis, and some correlations and regressions enabled me to show that cold overnight temperatures did reduce Cry2Ab protein levels, that the effects occurred for up to 6 days after the cold period and that the threshold for these effects was approximately 14 Cº (https://doi.org/10.1603/EC09369). What I took from this piece of work is how powerful a comprehensive statistics package can be in teasing apart important biological insights from what was seemingly very simple data. Note that I did not use any statistics that were cutting edge, just a combination of REML, correlation and regression analyses, but used these techniques to guide the dissection of the relationships in the data to end up with an elegant and insightful outcome.

Looking back over 50 years of work, one thing stands out for me: the huge advances that have occurred in the statistical analysis of biological data has allowed much more insightful statistical analyses that has, in turn, allowed biological scientists to more elegantly pull apart the interactions between insects and their plant hosts.

For me, Genstat has played a pivotal role in that process. I shall miss it.

**Dr John Rogers**

Research Connections and Consulting

St Lucia, Queensland 4067, Australia

Phone/Fax: +61 (0)7 3720 9065

Mobile: 0409 200 701

Email: john.rogers@rcac.net.au

Alternate email: D.John.Rogers@gmail.com

Kanchana Punyawaew

9 months agoThis blog illustrates how to analyze data from a field experiment with a balanced lattice square design using linear mixed models. We’ll consider two models: the balanced lattice square model and a spatial model.

The example data are from a field experiment conducted at Slate Hall Farm, UK, in 1976 (Gilmour *et al*., 1995). The experiment was set up to compare the performance of 25 varieties of barley and was designed as a balanced lattice square with six replicates laid out in a 10 x 15 rectangular grid. Each replicate contained exactly one plot for every variety. The variety grown in each plot, and the coding of the replicates and lattice blocks, is shown in the field layout below:

There are seven columns in the data frame: five blocking factors (*Rep, RowRep, ColRep, Row, Column*), one treatment factor, *Variety*, and the response variate, *yield*.

The six replicates are numbered from 1 to 6 (*Rep*). The lattice block numbering is coded within replicates. That is, within each replicates the lattice rows (*RowRep*) and lattice columns (*ColRep*) are both numbered from 1 to 5. The *Row* and *Column* factors define the row and column positions within the field (rather than within each replicate).

To analyze the response variable, *yield*, we need to identify the two basic components of the experiment: the treatment structure and the blocking (or design) structure. The treatment structure consists of the set of treatments, or treatment combinations, selected to study or to compare. In our example, there is one treatment factor with 25 levels, *Variety* (i.e. the 25 different varieties of barley). The blocking structure of replicates (*Rep*), lattice rows within replicates (*Rep:RowRep*), and lattice columns within replicates (*Rep:ColRep*) reflects the balanced lattice square design. In a mixed model analysis, the treatment factors are (usually) fitted as fixed effects and the blocking factors as random.

The balanced lattice square model is fitted in ASReml-R4 using the following code:

```
> lattice.asr <- asreml(fixed = yield ~ Variety,
random = ~ Rep + Rep:RowRep + Rep:ColRep,
data=data1)
```

The REML log-likelihood is -707.786.

The model’s BIC is:

The estimated variance components are:

The table above contains the estimated variance components for all terms in the random model. The variance component measures the inherent variability of the term, over and above the variability of the sub-units of which it is composed. The variance components for *Rep*, *Rep:RowRep* and *Rep:ColRep* are estimated as 4263, 15596, and 14813, respectively. As is typical, the largest unit (replicate) is more variable than its sub-units (lattice rows and columns within replicates). The *"units!R"* component is the residual variance.

By default, fixed effects in ASReml-R4 are tested using sequential Wald tests:

In this example, there are two terms in the summary table: the overall mean, (*Intercept*), and *Variety*. As the tests are sequential, the effect of the *Variety* is assessed by calculating the change in sums of squares between the two models (*Intercept*)+*Variety* and (*Intercept*). The p-value (Pr(Chisq)) of < 2.2 x 10-16 indicates that *Variety* is a highly significant.

The predicted means for the *Variety* can be obtained using the predict() function. The standard error of the difference between any pair of variety means is 62. Note: all variety means have the same standard error as the design is balanced.

Note: the same analysis is obtained when the random model is redefined as replicates (*Rep*), rows within replicates (*Rep:Row*) and columns within replicates (*Rep:Column*).

As the plots are laid out in a grid, the data can also be analyzed using a spatial model. We’ll illustrate spatial analysis by fitting a model with a separable first order autoregressive process in the field row (*Row*) and field column (*Column*) directions. This is often a useful model to start the spatial modeling process.

The separable first order autoregressive spatial model is fitted in ASReml-R4 using the following code:

```
> spatial.asr <- asreml(fixed = yield ~ Variety,
residual = ~ar1(Row):ar1(Column),
data = data1)
```

The BIC for this spatial model is:

The estimated variance components and sequential Wald tests are:

The residual variance is 38713, the estimated row correlation is 0.458, and the estimated column correlation is 0.684. As for the balanced lattice square model, there is strong evidence of a *Variety* effect (p-value < 2.2 x 10-16).

A log-likelihood ratio test cannot be used to compare the balanced lattice square model with the spatial models, as the variance models are not nested. However, the two models can be compared using BIC. As the spatial model has a smaller BIC (1415) than the balanced lattice square model (1435), of the two models explored in this blog, it is chosen as the preferred model. However, selecting the optimal spatial model can be difficult. The current spatial model can be extended by including measurement error (or nugget effect) or revised by selecting a different variance model for the spatial effects.

Butler, D.G., Cullis, B.R., Gilmour, A. R., Gogel, B.G. and Thompson, R. (2017). *ASReml-R Reference Manual Version 4.* VSN International Ltd, Hemel Hempstead, HP2 4TP UK.

Gilmour, A. R., Anderson, R. D. and Rae, A. L. (1995). *The analysis of binomial data by a generalised linear mixed model*, Biometrika 72: 593-599..