Here we step through the Isopod Example using the script version of MixSIAR. For a demonstration using the GUI version, see the MixSIAR Manual. For a thorough walkthrough of how to use MixSIAR in a script, see the Wolves Example, which provides more commentary and explanation.
For a clean, runnable .R
script, look at
mixsiar_script_isopod.R
in the example_scripts
folder of the MixSIAR package install:
You can run the isopod example script directly with:
The Isopod Example is from Galloway et al. 2014 and demonstrates MixSIAR applied to an 8-dimensional fatty acid dataset. Here the mixture data are isopod polyunsaturated fatty acid (PUFA) profiles, with 5 replicates at each of 6 sites in Puget Sound, WA:
Here we treat Site as a random effect. This makes sense if we are interested in the overall population and think of Site as a nuisance factor. Fitting Site as a fixed effect would make more sense if we were interested specifically in the diet at each Site, as opposed to the overall population diet and variability between Sites. This differs from the analysis in Galloway et al. 2014.
Fatty acid data greatly increase the number of biotracers beyond the typical 2 stable isotopes, d13C and d15N, which gives the mixing model power to resolve more sources. We caution, however, that using fatty acid data is not a panacea for the “underdetermined” problem (# sources > # biotracers + 1). As the number of sources increases, the “uninformative” prior (α = 1) has greater influence, even if there are many more biotracers than sources. See the Cladocera Example prior with 7 sources and 22 biotracers.
See ?load_mix_data for details.
The isopod consumer data has 1 covariate
(factors="Site"
), which we fit as a random effect
(fac_random=TRUE
). “Site” is not nested within another
factor (fac_nested=FALSE
). There are no continuous effects
(cont_effects=NULL
).
# Replace the system.file call with the path to your file
mix.filename <- system.file("extdata", "isopod_consumer.csv", package = "MixSIAR")
mix <- load_mix_data(filename=mix.filename,
iso_names=c("c16.4w3","c18.2w6","c18.3w3","c18.4w3","c20.4w6","c20.5w3","c22.5w3","c22.6w3"),
factors="Site",
fac_random=TRUE,
fac_nested=FALSE,
cont_effects=NULL)
See ?load_source_data for details.
We do not have any fixed/random/continuous effects or concentration
dependence in the source data (source_factors=NULL
,
conc_dep=FALSE
). We only have source means, SD, and sample
size—not the original “raw” data (data_type="means"
).
See ?load_discr_data for details.
Note that Galloway et
al. 2014 conducted feeding trials to create a “resource library”. In
the mixing model, the sources are actually consumers fed exclusively
each of the sources. This allowed them to set the discrimination = 0
(see isopod_discrimination.csv
).
This is your chance to check:
When there are more than 2 biotracers, MixSIAR currently plots every pairwise combination. Here, that means ${8 \choose 2} = 28$ plots are produced. In the future, MixSIAR will offer non-metric multidimensional scaling (NMDS) plots for these cases.
Define your prior, and then plot using “plot_prior”
In the Isopod Example we demo the “Residual only” error option. The differences between “Residual * Process”, “Residual only”, and “Process only” are explained in Stock and Semmens (2016).
First use run = "test"
to check if 1) the data are
loaded correctly and 2) the model is specified correctly:
After a test run works, increase the MCMC run to a value that may converge:
See ?output_JAGS for details.
Since we fit Site as a random effect, we can make inference on diet
at the overall population level (p.global
, posterior
plot) as well as at individual sites (Site CP, posterior
plot).