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source/rmarkdown/analyses_diversity/test_breakaway_diversity.Rmd
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--- | ||
title: "Comparison of diversity among land-use types and depths using approach from R package `breakaway`" | ||
author: "Hans Van Calster" | ||
date: '`r Sys.Date()`' | ||
output: | ||
bookdown::html_document2: | ||
toc: true | ||
toc_float: true | ||
code_folding: hide | ||
editor_options: | ||
markdown: | ||
wrap: sentence | ||
--- | ||
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```{r setup, include=FALSE} | ||
library(knitr) | ||
opts_chunk$set(echo = TRUE) | ||
library(here) | ||
opts_chunk$set(echo = TRUE, error = TRUE, out.width = "100%") | ||
opts_knit$set(root.dir = here::here()) | ||
library(ggplot2) | ||
library(dplyr) | ||
library(tidyr) | ||
library(purrr) | ||
mbag_bodem_folder <- "G:/Gedeelde drives/PRJ_MBAG/4c_bodembiodiversiteit" # nolint | ||
library(breakaway) | ||
``` | ||
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# Inlezen data | ||
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```{r inlezen} | ||
metadata <- readr::read_csv( | ||
file.path( | ||
mbag_bodem_folder, | ||
"data", | ||
"Stratificatie_MBAG_plots", | ||
"MBAG_stratfile_v2_cleaned_13.csv") | ||
) %>% | ||
janitor::clean_names() %>% | ||
rename( | ||
ph_kcl = p_h_k_cl, | ||
swc_grav = sw_cgrav, | ||
swc_vol = sw_cvol, | ||
cn_stockbased = c_n_stockbased, | ||
c_density = cdensity, | ||
n_density = ndensity | ||
) %>% | ||
mutate( | ||
landgebruik = factor( | ||
landgebruik_mbag, | ||
levels = c( | ||
"Akker", "Tijdelijk grasland", "Blijvend grasland", | ||
"Residentieel grasland", "Natuurgrasland", "Heide", "Moeras") | ||
), | ||
diepte = gsub("_|/", "-", diepte) |> factor() | ||
) | ||
load( | ||
file.path( | ||
mbag_bodem_folder, | ||
"data", "statistiek", "Annelida", "phyloseq", | ||
"physeq_Olig01_Annelida_species.Rdata" | ||
) | ||
) | ||
physeq_Olig01_Annelida_species <- physeq_Olig01_Annelida_species |> | ||
phyloseq::subset_samples( | ||
!Landgebruik_MBAG %in% c("Moeras", "Heide") | ||
) | ||
``` | ||
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```{r} | ||
br <- breakaway(physeq_Olig01_Annelida_species) | ||
br_tbl <- summary(br) | ||
``` | ||
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```{r} | ||
br_tbl | ||
``` | ||
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```{r} | ||
combined <- br_tbl |> | ||
inner_join(metadata, by = join_by(sample_names == sample)) |> | ||
filter( | ||
!landgebruik_mbag %in% c("Moeras", "Heide") | ||
) |> | ||
mutate( | ||
landgebruik_mbag = factor( | ||
landgebruik_mbag, | ||
levels = c("Akker", "Tijdelijk grasland", "Blijvend grasland", | ||
"Residentieel grasland", "Natuurgrasland") | ||
) | ||
) | ||
``` | ||
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```{r} | ||
combined |> | ||
filter(error < 1e-7 ) %>% | ||
count(landgebruik_mbag) | ||
``` | ||
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Perform meta-analysis: | ||
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The `breakaway::betta` function seems too limited in scope as it only allows formulas of the form `y ~ x|group`. | ||
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```{r} | ||
ma <- betta( | ||
formula = estimate ~ landgebruik_mbag, | ||
ses = error, | ||
data = combined | ||
) | ||
ma$table | ||
``` | ||
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Instead, using meta-analytic capabilities of brms package: | ||
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```{r} | ||
library(brms) | ||
# adding a small value to error to avoid problems with error == 0 | ||
ma_brms <- brm( | ||
estimate | se(error + 0.01, sigma = TRUE) ~ | ||
landgebruik_mbag * diepte + (1 | cmon_plot_id), | ||
data = combined, | ||
family = "skew_normal", | ||
backend = "cmdstanr", | ||
cores = 4 | ||
# , | ||
# algorithm = "pathfinder", | ||
# history_size = 100, | ||
# psis_resample = TRUE | ||
) | ||
``` | ||
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```{r} | ||
summary(ma_brms) | ||
``` | ||
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```{r} | ||
conditional_effects( | ||
ma_brms, | ||
"landgebruik_mbag:diepte" | ||
) | ||
``` | ||
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The result is very much comparable to what we obtained via glmmTMB with an offset term - so probably not much added value. |
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