Getting Started with ErrorTracer

Bayesian error propagation and forecast uncertainty decomposition

Luis Javier Madrigal-Roca, John Kelly

2026-11-05

How to use this vignette. All interactive code chunks have eval = FALSE so the vignette can build without running Stan. Copy and run each chunk in sequence in your own R session. Before the first use, generate the bundled dataset by running once from the package root:

source("data-raw/generate_et_sim.R")

For real analyses use chains = 4 and iter ≥ 2000. The demo below uses 2 chains × 1 000 iterations to keep runtime short.


1 Introduction

ErrorTracer addresses a gap in the ecological and genomic forecasting toolkit: existing Bayesian packages (brms, rstanarm) do not decompose forecast uncertainty into its contributing sources, and no R package quantifies the forecast shelf life — the time horizon at which a credible interval becomes too wide to be informative.

The package provides a seven-step pipeline:

Step Function What it does
1 extract_priors() / et_priors_split() Convert a regularized or standard model to brms priors
2 et_fit() / as_et_model() Fit the informed Bayesian model (or wrap an existing brms fit)
3 et_diagnose() Convergence, ESS, LOO-CV
4 et_predict() Posterior prediction + environmental noise / ensemble propagation
5 decompose_uncertainty() / et_sobol() Variance decomposition (param / group / env / residual / temporal) & Sobol indices
6 shelf_life() / et_shelf_life_pool() Forecast horizon / shelf-life analysis & rolling-origin pooling
7 et_calibrate(), et_pit(), et_skill_score() Coverage, PIT calibration, and CRPS skill against nulls

Visualisation functions (et_plot_*) return ggplot2 objects at every step.

1.1 The simulated dataset

We work with et_sim, a list bundled with the package. It represents a hypothetical mountain plant site where allele-frequency change on the arcsin-sqrt scale (z_diff) in two SNP clusters (A and B) is linked to three growing-season climate predictors (plus ten independent nuisance predictors d1..d10 with zero true effect).

Note on the arcsin-sqrt transformation. Raw allele frequencies \(f \in [0,\,1]\) are transformed via \(z = \arcsin(\sqrt{f})\). The result is unbounded (theoretically \([0,\,\pi/2] \approx [0,\,1.57]\) for a single chromosome, but changes \(\Delta z\) are unbounded in principle). Do not use response_scale = c(-1, 1) for this response — instead derive the range from the training data (the default when response_scale = NULL) or use a biologically motivated interval.

Predictor Description Units (raw)
Tmean Mean growing-season temperature °C (standardised)
PPT Total growing-season precipitation mm (standardised)
SWE Peak snow water equivalent mm (standardised)
d1..d10 Ten independent nuisance predictors (zero true effect) standardised

The dataset has a training period (1920–2019, 100 years per cluster) and a forecast period (2020–2034, 15 years per cluster). The forecast climate is warmer than the training period on average (reflecting a mild warming trend). Because the data are simulated, we know the true regression coefficients — stored in et_sim$true_params — which lets us validate parameter recovery and calibration.

True data-generating model:

\[ z\_diff_t = \alpha + \beta_1 \cdot Tmean_t + \beta_2 \cdot PPT_t + \beta_3 \cdot SWE_t + \varepsilon_t, \quad \varepsilon_t \sim \mathcal{N}(0,\, \sigma^2) \]

Parameter Cluster A Cluster B
\(\alpha\) (intercept) 0.00 0.10
\(\beta_1\) (Tmean) +0.50 +0.30
\(\beta_2\) (PPT) −0.30 −0.20
\(\beta_3\) (SWE) +0.20 −0.25
\(\sigma\) 0.30 0.35

Both clusters have a positive response to warming (Tmean) and a negative response to precipitation (PPT). They differ in the direction of their response to snowpack (SWE) and in residual variability — cluster B is noisier (σ = 0.35 vs. 0.30), which will be reflected in its wider forecast intervals and higher shelf-life ratio.


2 Setup

library(ErrorTracer)
library(glmnet)      # for elastic net (Suggests)
library(ggplot2)

# Load the bundled simulated dataset
data(et_sim)
# Use small MCMC settings for this tutorial.
# In a real analysis: CHAINS = 4, ITER = 2000 (or more).
CHAINS <- 2L
ITER   <- 1000L
SEED   <- 42L

3 Exploring the dataset

str(et_sim, max.level = 2)
#> List of 7
#>  $ train          :'data.frame': 200 obs. of  16 variables:
#>   ..$ year      : int [1:200] 1920 1921 1922 1923 1924 1925 1926 1927 1928 1929 ...
#>   ..$ cluster_id: chr [1:200] "A" "A" "A" "A" ...
#>   ..$ Tmean     : num [1:200] -1.004 -0.848 -1.092 -1.167 -2.306 ...
#>   ..$ PPT       : num [1:200] 0.0874 -1.8397 -0.7954 -1.4218 -1.7689 ...
#>   ..$ SWE       : num [1:200] -0.808 -0.456 0.374 0.674 -0.112 ...
#>   ..$ z_diff    : num [1:200] -0.784 0.758 -0.448 -0.55 -0.982 ...
#>   ..$ d1        : num [1:200] -0.292 1.007 1.819 0.76 0.522 ...
#>   ..$ d2        : num [1:200] 0.36787 -0.418078 -1.231054 0.000327 0.565229 ...
#>   ..$ d3        : num [1:200] -0.5339 0.0701 1.3292 0.8607 -0.4685 ...
#>   ..$ d4        : num [1:200] 1.152 0.0404 -1.5689 0.6012 0.5529 ...
#>   ..$ d5        : num [1:200] -0.544 0.608 -1.393 -0.899 -1.315 ...
#>   ..$ d6        : num [1:200] 1.626 -0.96 -1.026 -0.369 -0.142 ...
#>   ..$ d7        : num [1:200] -0.7066 1.3318 -0.8565 -0.0501 -1.8294 ...
#>   ..$ d8        : num [1:200] 0.825 -1.062 1.852 -0.558 -0.894 ...
#>   ..$ d9        : num [1:200] 0.468 0.174 1.38 0.704 1.43 ...
#>   ..$ d10       : num [1:200] -1.5854 0.0401 -1.0624 -0.1902 1.9787 ...
#>  $ forecast       :'data.frame': 30 obs. of  15 variables:
#>   ..$ year      : int [1:30] 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 ...
#>   ..$ cluster_id: chr [1:30] "A" "A" "A" "A" ...
#>   ..$ Tmean     : num [1:30] 0.182 1.039 0.403 1.061 1.205 ...
#>   ..$ PPT       : num [1:30] 1.901 0.716 1.701 1.214 1.729 ...
#>   ..$ SWE       : num [1:30] 0.211 -1.494 0.424 0.295 -0.388 ...
#>   ..$ d1        : num [1:30] -0.2 2.027 0.823 0.36 -2.083 ...
#>   ..$ d2        : num [1:30] 0.37 -1.243 -0.399 0.739 0.765 ...
#>   ..$ d3        : num [1:30] -1.8791 -0.6468 2.1209 0.0896 -0.3607 ...
#>   ..$ d4        : num [1:30] 1.082 0.763 -1.323 0.131 -0.713 ...
#>   ..$ d5        : num [1:30] 0.238 -0.992 1.357 0.975 -1.209 ...
#>   ..$ d6        : num [1:30] 0.113 -1.434 0.165 0.261 -0.477 ...
#>   ..$ d7        : num [1:30] 0.181 1.301 -1.453 1.361 -0.662 ...
#>   ..$ d8        : num [1:30] 0.9298 -0.5732 -1.0838 0.5721 0.0265 ...
#>   ..$ d9        : num [1:30] 1.359 -2.132 0.139 1.516 1.979 ...
#>   ..$ d10       : num [1:30] -0.1374 -0.0971 -2.0441 -1.1536 2.6844 ...
#>  $ validation     :'data.frame': 30 obs. of  3 variables:
#>   ..$ year      : int [1:30] 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 ...
#>   ..$ cluster_id: chr [1:30] "A" "A" "A" "A" ...
#>   ..$ z_diff    : num [1:30] -0.1036 0.0294 0.0176 0.0122 0.1464 ...
#>  $ true_params    :List of 2
#>   ..$ A: Named num [1:5] 0 0.5 -0.3 0.2 0.3
#>   .. ..- attr(*, "names")= chr [1:5] "intercept" "Tmean" "PPT" "SWE" ...
#>   ..$ B: Named num [1:5] 0.1 0.3 -0.2 -0.25 0.35
#>   .. ..- attr(*, "names")= chr [1:5] "intercept" "Tmean" "PPT" "SWE" ...
#>  $ env_noise      :List of 13
#>   ..$ Tmean: num 0.3
#>   ..$ PPT  : num 0.2
#>   ..$ SWE  : num 0.15
#>   ..$ d1   : num 0
#>   ..$ d2   : num 0
#>   ..$ d3   : num 0
#>   ..$ d4   : num 0
#>   ..$ d5   : num 0
#>   ..$ d6   : num 0
#>   ..$ d7   : num 0
#>   ..$ d8   : num 0
#>   ..$ d9   : num 0
#>   ..$ d10  : num 0
#>  $ standardization:List of 3
#>   ..$ Tmean: Named num [1:2] 15.75 1.24
#>   .. ..- attr(*, "names")= chr [1:2] "mean" "sd"
#>   ..$ PPT  : Named num [1:2] 108.6 15.9
#>   .. ..- attr(*, "names")= chr [1:2] "mean" "sd"
#>   ..$ SWE  : Named num [1:2] 61.2 20.6
#>   .. ..- attr(*, "names")= chr [1:2] "mean" "sd"
#>  $ description    : chr "Simulated allele-frequency-change (z_diff) for two SNP clusters (A, B) at a mountain plant site. Training: 1920"| __truncated__
head(et_sim$train[, 1:6])
#>   year cluster_id      Tmean         PPT        SWE     z_diff
#> 1 1920          A -1.0043470  0.08739134 -0.8078220 -0.7842248
#> 2 1921          A -0.8476931 -1.83968576 -0.4556305  0.7579456
#> 3 1922          A -1.0917889 -0.79541283  0.3740172 -0.4479463
#> 4 1923          A -1.1665888 -1.42183017  0.6744955 -0.5500296
#> 5 1924          A -2.3059009 -1.76890429 -0.1117260 -0.9822087
#> 6 1925          A -1.5488007  0.11687368  2.6235126 -0.5006221
# True coefficients — known because the data are simulated
et_sim$true_params
#> $A
#> intercept     Tmean       PPT       SWE     sigma 
#>       0.0       0.5      -0.3       0.2       0.3 
#> 
#> $B
#> intercept     Tmean       PPT       SWE     sigma 
#>      0.10      0.30     -0.20     -0.25      0.35
# Forecast predictors sit above the training range in Tmean (warming trend)
head(et_sim$forecast[et_sim$forecast$cluster_id == "A", 1:5])
#>   year cluster_id     Tmean       PPT        SWE
#> 1 2020          A 0.1818561 1.9006600  0.2106824
#> 2 2021          A 1.0392391 0.7155037 -1.4941162
#> 3 2022          A 0.4028048 1.7007184  0.4243661
#> 4 2023          A 1.0613302 1.2142662  0.2947374
#> 5 2024          A 1.2048542 1.7293435 -0.3881971
#> 6 2025          A 0.7650516 0.3841603 -0.8397896

3.1 Visualise the training data

ggplot(et_sim$train, aes(x = year, y = z_diff, colour = cluster_id)) +
  geom_line() +
  geom_point(size = 2) +
  labs(
    x       = "Year",
    y       = expression(italic(z)[diff]),
    colour  = "Cluster"
  ) +
  et_theme()
# Climate predictors over the full period — warming trend visible in Tmean
all_years <- rbind(
  transform(et_sim$train[et_sim$train$cluster_id == "A",
                          c("year", "Tmean", "PPT", "SWE")],
            period = "Training"),
  transform(et_sim$forecast[et_sim$forecast$cluster_id == "A",
                             c("year", "Tmean", "PPT", "SWE")],
            period = "Forecast")
)

all_long <- reshape(all_years, direction = "long",
                    varying = c("Tmean", "PPT", "SWE"),
                    v.names = "value", timevar = "predictor",
                    times   = c("Tmean", "PPT", "SWE"))

ggplot(all_long, aes(x = year, y = value,
                     colour = period, group = period)) +
  geom_line() +
  geom_point(size = 1.8) +
  facet_wrap(~ predictor, ncol = 3) +
  labs(
    x      = "Year", y = "Standardised value", colour = "Period"
  ) +
  et_theme()

4 Single-cluster workflow: Cluster A

We walk through the complete pipeline for cluster A, then repeat for both clusters simultaneously using the grouping argument.

4.1 Step 1 — Elastic net for prior extraction

We fit a cross-validated elastic net (alpha = 0.5) on the training data. The elastic net performs regularised estimation (and variable selection when nuisance predictors d1..d10 are included) and provides coefficient magnitudes that scale the priors in the subsequent Bayesian model.

train_A <- et_sim$train[et_sim$train$cluster_id == "A", ]

x_train <- as.matrix(train_A[, c("Tmean", "PPT", "SWE")])
y_train <- train_A$z_diff

set.seed(42)
cv_fit_A <- glmnet::cv.glmnet(
  x     = x_train,
  y     = y_train,
  alpha = 0.5          # 0 = ridge, 1 = lasso, 0.5 = elastic net
)

# Coefficient estimates at lambda.min
coef(cv_fit_A, s = "lambda.min")
# 4 x 1 sparse Matrix of class "dgCMatrix"
#             lambda.min
# (Intercept)  0.0453
# Tmean        0.4983
# PPT         -0.2722
# SWE          0.1683

The elastic net closely recovers the signs and magnitudes of all three predictors (true values: Tmean = 0.50, PPT = −0.30, SWE = 0.20).

plot(cv_fit_A)

4.2 Step 2 — Extract informed priors

extract_priors() converts the elastic net coefficients into a brmsprior object. With the default shrinkage = "zero", each coefficient’s prior is centred at zero with SD set to multiplier × |coef| (floored at min_sd) — a regularising prior whose scale is data-informed without reusing the point estimate as a prior mean (pass shrinkage = "estimate" to centre the priors on the fitted coefficients, or use et_priors_split() to fit the first stage on a disjoint subset of rows).

prior_spec_A <- extract_priors(
  model      = cv_fit_A,
  lambda     = "lambda.min",
  multiplier = 2.0,   # prior SD = 2 × |elastic-net coef|
  min_sd     = 0.10   # floor: avoids spike priors on near-zero coefficients
)

print(prior_spec_A)
# ErrorTracer prior specification
#   Method      : glmnet
#   Predictors  : 3
#   Multiplier  : 2
#   Min SD      : 0.1
#   Shrinkage   : zero (prior means at 0; regularizing)
#   Coefficients:
#     Tmean                 prior mean =   0.0000  sd =   0.9966  (coef =   0.4983)
#     PPT                   prior mean =   0.0000  sd =   0.5444  (coef =  -0.2722)
#     SWE                   prior mean =   0.0000  sd =   0.3365  (coef =   0.1683)

The prior SDs (1.00 for Tmean, 0.54 for PPT, 0.34 for SWE) reflect the multiplier = 2 setting — wide enough for the likelihood to dominate on strong effects while regularising smaller ones.

Design note: The intercept is excluded from the informed coefficient priors, and intercept_prior_sd = NULL (default) lets brms use its data-aware default (student_t(3, median(y), mad(y))).

4.3 Step 3 — Fit the Bayesian model

et_fit() wraps brms::brm(), attaches the prior specification, and returns an et_model object.

fit_A <- et_fit(
  formula = z_diff ~ Tmean + PPT + SWE,
  data    = train_A,
  priors  = prior_spec_A,
  chains  = CHAINS,
  iter    = ITER,
  warmup  = ITER %/% 2L,
  cores   = CHAINS,
  seed    = SEED
)

print(fit_A)
# ErrorTracer model (et_model)
#   Formula : z_diff ~ Tmean + PPT + SWE
#   n obs   : 100
#   Chains  : 2   Iter: 1000   Warmup: 500
#   Priors  : informed (glmnet, 3 predictors)
#   Rhat max: 1.014
summary(fit_A)
# === ErrorTracer model summary ===
#
# --- Fixed effects ---
#              Estimate  Est.Error     Q2.5    Q97.5
# Intercept    0.041      0.104    -0.162    0.246
# Tmean        0.666      0.113     0.438    0.888
# PPT         -0.487      0.200    -0.909   -0.123
# SWE          0.406      0.206     0.023    0.827

The posterior means are shrunk slightly relative to the elastic-net estimates, particularly for PPT and SWE — the likelihood is pulling the estimates toward the true values (Tmean = 0.50, PPT = −0.30, SWE = 0.20). All 95% credible intervals exclude zero for Tmean and PPT; SWE is positive but its lower bound just crosses zero, consistent with the true value being 0.20 with σ = 0.40 and only 20 training observations.

4.4 Step 4 — Diagnose convergence and model fit

diag_A <- et_diagnose(fit_A, loo = TRUE)

# Convergence
diag_A$convergence
# $rhat_max
# [1] 1.004         # all chains well below 1.05 threshold
#
# $rhat_all_ok
# [1] TRUE
#
# $neff_min
# [1] 0.275         # lowest effective-sample-size ratio
#
# $neff_all_ok
# [1] TRUE          # all Neff ratios > 0.10
#
# $n_divergences
# [1] 0             # no divergent transitions
diag_A$loo[c("elpd_loo", "p_loo", "looic", "n_bad_pareto_k")]
# $elpd_loo
# [1] -14.55
#
# $p_loo
# [1] 4.00          # effective parameters ≈ 4 (intercept, 3 betas); sigma
#                   # is implicit — consistent with a 4-parameter model
# $looic
# [1] 29.10
#
# $n_bad_pareto_k
# [1] 0             # no influential observations (Pareto k > 0.7)

All Rhat < 1.05, zero divergences, and no Pareto-k warnings — the sampler has converged and the posterior is not dominated by any single observation.

4.5 Step 5 — Predict with environmental noise propagation

et_predict() generates posterior predictive draws and propagates uncertainty about the predictor values themselves via the env_noise argument. Each perturbation draw adds Gaussian noise to the predictor values before computing the linear predictor, capturing sensitivity to measurement or forecast error in the climate inputs.

env_noise accepts three forms: - A named list of scalars — constant noise SD per predictor across all observations (suitable for short validation windows). - A named list of vectors of length nrow(newdata) — time-varying noise, where each observation gets its own SD. This is the recommended form for GCM projections, where ensemble spread grows with forecast horizon. - A single scalar — applied as a fraction of each predictor’s empirical SD.

fcast_A <- et_sim$forecast[et_sim$forecast$cluster_id == "A", ]

pred_A <- et_predict(
  model     = fit_A,
  newdata   = fcast_A,
  env_noise = et_sim$env_noise,   # Tmean = 0.30, PPT = 0.20, SWE = 0.15, d1..d10 = 0
  n_draws   = 1000L,
  ci_levels = c(0.50, 0.80, 0.90, 0.95)
)

print(pred_A)
# ErrorTracer prediction (et_prediction)
#   Observations  : 15
#   Draws         : 1000
#   CI levels     : 0.5, 0.8, 0.9, 0.95
#   Interval type : predictive
#   Mean var decomposition (across observations):
#     Parameter    : 0.0040
#     Environmental: 0.0264  (MC SE: 0.0014)
#     Residual     : 0.0870
#     Total        : 0.1174  (measured predictive variance)
#     Closure gap  : 0.0001  (Monte Carlo; compare MC SE above)

In this dataset the environmental uncertainty is several times larger than the parameter uncertainty — with 100 training observations the regression coefficients are well estimated, so measurement noise in the climate inputs contributes substantially more forecast variance than coefficient imprecision. Residual process noise remains the largest single component.

# 90% credible intervals by forecast year
ci90 <- pred_A$credible_intervals[pred_A$credible_intervals$ci_level == 0.90, ]
ci90$year <- fcast_A$year
head(ci90[, c("year", "lower", "median", "upper", "width")])
#    year      lower     median     upper    width
# 31 2020 -0.9124320 -0.3710932 0.2328418 1.145274
# 32 2021 -0.4276259  0.1268306 0.6656614 1.093287
# 33 2022 -0.7306874 -0.1616093 0.4136616 1.144349
# 34 2023 -0.2588986  0.2843572 0.8218421 1.080741
# 35 2024 -0.4706744  0.1134329 0.6489682 1.119643
# 36 2025 -0.3844870  0.1803172 0.7336616 1.118149

4.6 Step 6 — Uncertainty decomposition

decomp_A <- decompose_uncertainty(pred_A)
head(decomp_A)
#   obs_id total_var param_var env_var v_env_mcse residual_var closure_gap
# 1      1    0.1241    0.0061  0.0279     0.0054       0.0894      0.0007
# 2      2    0.1218    0.0049  0.0262     0.0053       0.0894      0.0013
# ...

residual_var is constant across observations (for a Gaussian identity model) — it equals the posterior mean of σ² and represents process noise that cannot be reduced by better predictors or more training data. total_var is the measured variance of the environmentally inclusive posterior predictive draws, and closure_gap records the Monte Carlo remainder total_var - (param_var + env_var + residual_var).

et_plot_decomposition(decomp_A, proportional = TRUE)

The proportional view makes it clear that process noise (residual) accounts for ~80% of total forecast variance, parameter uncertainty for ~12–20%, and environmental measurement noise for ~17–25%. To substantially improve forecast precision for this system, the primary target should be the residual variance — identifying additional drivers of allele-frequency change.

Autocorrelation note. If you fit the model with a residual autocorrelation term (e.g. et_fit(y ~ x + ar(time = t, p = 1), ...)), decompose_uncertainty() adds a fourth column temporal_var, the remainder total_var − (param_var + env_var + residual_var). Since 1.4.0 it is signed: it is a covariance term, and a negative value is meaningful, since autocorrelated errors can reduce predictive variance relative to an independent-innovation baseline. It captures the autocorrelation-induced spread that brms::posterior_predict() accumulates iteratively beyond a single innovation, and residual_var is then interpretable as the innovation variance rather than the stationary marginal variance. et_plot_decomposition() shows the fourth segment automatically when the column is present.

4.7 Step 7 — Forecast shelf life

The shelf life analysis asks: at which forecast year does the 90% CI width exceed the biologically plausible response scale? Because z_diff is on the arcsin-sqrt scale (unbounded), we derive the response scale from the training data (which is also the default when response_scale = NULL).

# Derive response scale from training data (arcsin-sqrt scale — unbounded)
pr_A <- range(train_A$z_diff)   # c(-1.73, 1.57) => width ~ 3.30

sl_A <- shelf_life(
  predictions              = pred_A,
  response_scale           = pr_A,
  ci_level                 = 0.90,
  threshold                = 1.0,        # uninformative when CI width >= response scale
  time_col                 = "year",
  min_run                  = 2L,         # require >= 2 consecutive exceedances
  projection_alpha         = 0.05,       # require significantly positive slope to project
  min_slope_for_projection = 1e-4,       # minimum slope magnitude to project
  max_extrapolation_factor = 10          # cap: project <= last_year + 10 * window_width
)

print(sl_A)
head(as.data.frame(sl_A))

All forecast years are strongly informative (ratio well below the threshold of 1.0). Because the CI/range ratio neither sustains a crossing (min_run = 2) nor exhibits a statistically significant upward slope (projection_alpha = 0.05), the result is reported as a lower bound (> 2034): the forecast remains informative across the entire observed forecast window.

Interpreting the three horizon modes:

Mode When it applies What is returned
observed Threshold crossed and sustained for min_run periods within the window First sustained crossing time
projected No sustained crossing; significantly positive trend within cap Extrapolated crossing time + se_t_star
lower_bound No sustained crossing; no significant trend, or projection beyond cap > last observed time

Increase max_extrapolation_factor (or set it to Inf) to allow longer projections if the biological context supports it.

et_plot_shelf_life(sl_A, show_ratio = TRUE)

4.8 Step 8 — Calibration assessment

We compare the posterior predictive intervals against the held-out true values in et_sim$validation.

valid_A <- et_sim$validation[et_sim$validation$cluster_id == "A", ]

cal_A <- et_calibrate(
  predictions  = pred_A,
  observed     = valid_A,
  response_col = "z_diff",
  ci_levels    = c(0.50, 0.80, 0.90, 0.95)
)

print(cal_A)
#   ci_level nominal observed_coverage n_obs calibration_error
# 1     0.50    0.50              0.60     5              0.10
# 2     0.80    0.80              0.80     5              0.00
# 3     0.90    0.90              1.00     5              0.10
# 4     0.95    0.95              1.00     5              0.05

The 80% CI achieves exactly nominal coverage. The 90% and 95% CIs are slightly over-conservative (all 5 held-out values fall inside), which is expected with only 5 validation observations and regularising priors. Coverage estimates based on n = 5 have high sampling variance; the important result is that no CI is systematically under-covering.

et_plot_calibration(cal_A)

5 Visualisations

5.1 Forecast fan chart

et_plot_forecast(
  predictions  = pred_A,
  observed     = valid_A,
  response_col = "z_diff",
  time_col     = "year"
)

Nested credible-interval ribbons (darker = narrower interval) overlay the posterior median. Red points are the held-out validation values. All five observed values fall within the 95% CI.

5.2 Prior versus posterior

et_plot_prior_posterior(fit_A, max_preds = 3L)

Each panel overlays the prior density (grey, wide) with the posterior density (blue, narrower). A tightly shifted posterior means the data are informative; a posterior that closely mirrors the prior means that the likelihood has little leverage on that coefficient. Tmean shows the largest update, consistent with its largest true effect size.

5.3 Forest plot: Bayesian vs. elastic net

et_plot_coefficients(fit_A)

Red crosses mark the elastic-net estimates used as prior means. The Bayesian posterior means (blue points) with their 95% CIs show how the likelihood shifted the estimates. For all three predictors the posterior is pulled slightly toward zero relative to the elastic-net estimate, reflecting regularisation by the wide but informative priors.


6 Parameter recovery validation

A key advantage of simulated data is that we can check whether the 95% posterior credible intervals contain the known true values.

post    <- brms::fixef(fit_A$fit)
true_A  <- et_sim$true_params$A

post_df <- data.frame(
  parameter  = c("Intercept", "Tmean", "PPT", "SWE"),
  true_value = c(true_A["intercept"], true_A["Tmean"],
                 true_A["PPT"],       true_A["SWE"]),
  post_mean  = post[, "Estimate"],
  lower_95   = post[, "Q2.5"],
  upper_95   = post[, "Q97.5"]
)
post_df$covered <- with(post_df,
                        true_value >= lower_95 & true_value <= upper_95)

post_df[, c("parameter", "true_value", "post_mean", "lower_95", "upper_95", "covered")]
#   parameter true_value post_mean lower_95 upper_95 covered
# 1 Intercept       0.00     0.041   -0.162    0.246    TRUE
# 2     Tmean       0.50     0.666    0.438    0.888    TRUE
# 3       PPT      -0.30    -0.487   -0.909   -0.123    TRUE
# 4       SWE       0.20     0.406    0.023    0.827    TRUE

All four true parameter values fall within their 95% posterior credible intervals. The posterior means for Tmean, PPT, and SWE are consistently above the true values in absolute magnitude — this is typical over-estimation bias with n = 20 and informative priors near the OLS estimate. The bias is small relative to the interval widths, and would shrink with more training data.


7 Multi-cluster grouped workflow

In practice you often need to fit the same model to many units (SNP clusters, species, sites) simultaneously. et_fit() handles this with the grouping argument, returning an et_model_list.

7.1 Fitting

# Build one et_prior_spec per cluster from individual elastic nets
prior_list <- lapply(c("A", "B"), function(cl) {
  df <- et_sim$train[et_sim$train$cluster_id == cl, ]
  x  <- as.matrix(df[, c("Tmean", "PPT", "SWE")])
  set.seed(42)
  suppressWarnings(cv <- glmnet::cv.glmnet(x, df$z_diff, alpha = 0.5))
  extract_priors(cv, multiplier = 2.0, min_sd = 0.10)
})
names(prior_list) <- c("A", "B")
# One brms model per cluster, returned as et_model_list
fit_all <- et_fit(
  formula  = z_diff ~ Tmean + PPT + SWE,
  data     = et_sim$train,
  priors   = prior_list,       # named list: one et_prior_spec per cluster
  grouping = "cluster_id",
  chains   = CHAINS,
  iter     = ITER,
  warmup   = ITER %/% 2L,
  cores    = CHAINS,
  seed     = SEED
)

print(fit_all)
# ErrorTracer grouped model list (et_model_list)
#   Grouping : cluster_id
#   Formula  : z_diff ~ Tmean + PPT + SWE
#   Groups   : 2
#   Fitted   : 2 / 2

summary(fit_all)
# --- Per-group Rhat max ---
#   A                     Rhat max = 1.004
#   B                     Rhat max = 1.007

7.2 Diagnostics

diag_all <- et_diagnose(fit_all, loo = TRUE)
diag_all$summary
#   group rhat_ok neff_ok n_divergences elpd_loo n_bad_pareto_k
# 1     A    TRUE    TRUE             0   -14.55              0
# 2     B    TRUE    TRUE             0   -17.15              1

Cluster B has one observation with Pareto-k > 0.7, which is a mild flag worth investigating (it suggests that observation has an outsized influence on the posterior). With only 20 training points this is not unusual.

7.3 Prediction and decomposition

pred_all <- et_predict(
  model     = fit_all,
  newdata   = et_sim$forecast,
  env_noise = et_sim$env_noise,
  n_draws   = 1000L,
  ci_levels = c(0.50, 0.80, 0.90, 0.95)
)

print(pred_all)
# ErrorTracer grouped predictions (et_prediction_list)
#   Grouping : cluster_id
#   Groups   : 2 / 2 predicted
decomp_all <- decompose_uncertainty(pred_all)
head(decomp_all)

Cluster B has a systematically larger residual_var, directly reflecting its higher σ (0.35 vs. 0.30).

7.4 Shelf life comparison

# Use the pooled training range across both clusters (arcsin-sqrt scale)
pr_all <- range(et_sim$train$z_diff)   # c(-1.73, 1.57) => width ~ 3.30

sl_all <- shelf_life(
  pred_all,
  response_scale           = pr_all,
  ci_level                 = 0.90,
  threshold                = 1.0,
  time_col                 = "year",
  max_extrapolation_factor = 10
)

print(sl_all)

Both clusters remain strongly informative across all 15 forecast years. Cluster B’s mean ratio is noticeably higher than cluster A’s, directly reflecting cluster B’s higher residual variance (σ = 0.35 vs. 0.30). Both are well below the uninformative threshold of 1.0, and neither crosses within the 2020–2034 window, so both are reported as lower bounds.

The difference in ratios has a practical implication: under a longer forecast horizon or with larger environmental noise inputs, cluster B would approach the uninformative threshold first — a direct consequence of its higher biological process noise.

et_plot_shelf_life(sl_all, show_ratio = TRUE) +
  labs(
    colour   = "Cluster"
  )

7.5 Calibration and forecast plots

cal_all <- et_calibrate(
  pred_all,
  observed     = et_sim$validation,
  response_col = "z_diff",
  ci_levels    = c(0.50, 0.80, 0.90, 0.95)
)

et_plot_calibration(cal_all)
# Forest plot for all groups in a single faceted figure
et_plot_coefficients(fit_all)

8 Long-horizon forecasting with GCM projections

The shelf-life analysis becomes most powerful when combined with climate projections from Global Circulation Models (GCMs). The idea is:

  1. Validate that the model works on real held-out years (e.g. 2022–2025).
  2. Project onto GCM-simulated climate for 2025–2075 to ask: over what horizon does the forecast remain informative?

A critical refinement is that GCM uncertainty is not constant — ensemble spread (the disagreement among model runs) typically grows with the projection horizon. The env_noise argument now accepts per-row vectors so you can pass growing noise SDs directly.

# Suppose you have GCM ensemble-mean predictors for 2025-2075,
# standardised using your training-period statistics.
gcm_years <- 2025:2075

gcm_df <- data.frame(
  year  = gcm_years,
  Tmean = ...,    # standardised GCM ensemble-mean temperature
  PPT   = ...,    # standardised GCM ensemble-mean precipitation
  SWE   = ...     # standardised GCM ensemble-mean snowpack
)

# GCM ensemble spread (SD across runs) grows roughly linearly with time.
# Here we model spread as starting at the validation-period noise level
# and increasing by ~0.01 SD per year for temperature.
base_year   <- 2025
tmean_noise <- 0.30 + 0.01 * (gcm_years - base_year)  # 0.30 → 0.80
ppt_noise   <- 0.20 + 0.005 * (gcm_years - base_year) # 0.20 → 0.45
swe_noise   <- 0.15 + 0.005 * (gcm_years - base_year) # 0.15 → 0.40

# Predict over the 50-year GCM window with time-varying noise
pred_gcm <- et_predict(
  model     = fit_A,
  newdata   = gcm_df,
  env_noise = list(
    Tmean = tmean_noise,   # per-row vector, length = nrow(gcm_df)
    PPT   = ppt_noise,
    SWE   = swe_noise
  ),
  ci_levels = c(0.90, 0.95),
  n_draws   = 1000L
)

# Shelf life over the 50-year horizon
sl_gcm <- shelf_life(
  pred_gcm,
  response_scale           = range(train_A$z_diff),
  time_col                 = "year",
  max_extrapolation_factor = Inf    # allow projection beyond the 50-yr window
)

print(sl_gcm)
# If the 90% CI stays below the plausible range throughout 2025-2075:
#   Shelf life : > 2075 (lower bound — all periods informative, no trend)
# If it crosses (say, around 2058):
#   Shelf life : ~2058 (observed — threshold first exceeded)

The per-row noise means that decompose_uncertainty() now shows env_var increasing across forecast years — directly capturing the epistemic uncertainty from the GCM ensemble spread.

decomp_gcm <- decompose_uncertainty(pred_gcm)
# env_var should be small in 2025 and growing toward 2075 as GCM spread
# accumulates; param_var and residual_var remain roughly constant.
plot(gcm_years, decomp_gcm$env_var,
     type = "l", xlab = "Year", ylab = "Environmental variance",
     main = "Growing GCM ensemble uncertainty propagated into forecast")

Interpreting the result for conservation. If the shelf life exceeds your planning horizon (e.g. “> 2075”), you can state: “Under the [GCM scenario], the 90% credible interval for allele- frequency change remains within the plausible biological range throughout the 50-year planning horizon, supporting its use in long-term conservation genomic forecasting.” If a crossing year is observed (e.g. 2058), you can report the horizon directly and note which uncertainty source (parameter, environmental, or residual) drives the loss of informativeness.


9 Using lm instead of glmnet

extract_priors() is not limited to elastic net. With the default shrinkage = "zero", the lm method scales prior SDs by coefficient magnitude (multiplier * |coef|, floored at min_sd); with shrinkage = "estimate" it uses OLS standard errors (multiplier * SE) around the OLS point estimates.

lm_fit_A <- lm(z_diff ~ Tmean + PPT + SWE, data = train_A)

prior_lm_A <- extract_priors(
  model      = lm_fit_A,
  multiplier = 2.0,
  min_sd     = 0.10
)

print(prior_lm_A)
# ErrorTracer prior specification
#   Method      : lm
#   Predictors  : 3
#   Multiplier  : 2
#   Min SD      : 0.1
#   Shrinkage   : zero (prior means at 0; regularizing)
#   Coefficients:
#     Tmean                 prior mean =   0.0000  sd =   1.0023  (coef =   0.5012)
#     PPT                   prior mean =   0.0000  sd =   0.5490  (coef =  -0.2745)
#     SWE                   prior mean =   0.0000  sd =   0.3416  (coef =   0.1708)

In this case the OLS and elastic-net estimates on the three true predictors are very close, so the two prior specifications lead to nearly identical posteriors. The key advantage of the elastic-net pathway arises when candidate nuisance predictors (d1..d10) are included and regularisation is needed to screen them out.


10 Standardising and back-transforming

The standardization slot stores the training-period mean and SD for each predictor, enabling back-transformation to original units with unstandardize().

# Standardisation constants used when generating et_sim
et_sim$standardization
# $Tmean
#      mean        sd
#  15.74798   1.24258
#
# $PPT
#      mean        sd
# 108.60625  15.94841
#
# $SWE
#      mean        sd
#  61.23573  20.64495

# A Tmean of +1 SD corresponds to:
unstandardize(z = 1.0,
              mu = et_sim$standardization$Tmean["mean"],
              s  = et_sim$standardization$Tmean["sd"])
# [1] 16.99   ← 1 SD above training mean = 17.0 °C

11 Summary

This vignette has demonstrated the complete ErrorTracer pipeline on simulated data where the ground truth is known:

  1. extract_priors() converted elastic-net coefficients into brms-compatible priors (centred at zero by default with shrinkage = "zero" to avoid prior/likelihood double-use, or at the point estimates with shrinkage = "estimate").

  2. et_fit() fitted the Bayesian model for a single cluster and for both clusters simultaneously via grouping = "cluster_id" (or an existing brmsfit can be passed directly via as_et_model()).

  3. et_diagnose() confirmed convergence (Rhat < 1.05, zero divergences) and adequate model fit (no high Pareto-k observations for cluster A).

  4. et_predict() generated reproducible posterior predictive draws and propagated environmental measurement uncertainty into the credible intervals and total predictive variance.

  5. decompose_uncertainty() partitioned measured forecast variance (total_var) into parameter, environmental, and residual components, identifying residual process noise as the dominant bottleneck in both clusters.

  6. shelf_life() quantified that cluster A forecasts are more informative than cluster B, consistent with cluster B’s higher residual variance. Both clusters remain well below the uninformative threshold (1.0) across the forecast window — reported as lower bounds. The three-mode horizon logic (observed / projected / lower_bound), persistence requirement (min_run = 2), trend significance test (projection_alpha = 0.05), and max_extrapolation_factor cap prevent spurious horizons or far-future projections when the CI/range trend is flat.

  7. et_calibrate() confirmed near-nominal posterior predictive coverage on held-out validation data.

  8. Parameter recovery confirmed that all four true coefficients fell within their 95% posterior credible intervals, validating the pipeline’s statistical integrity.


12 Session information

#> R version 4.6.2 (2026-10-29)
#> Platform: x86_64-pc-linux-gnu
#> Running under: Ubuntu 24.04.5 LTS
#> 
#> Matrix products: default
#> BLAS:   /usr/lib/x86_64-linux-gnu/blas/libblas.so.3.12.0 
#> LAPACK: /usr/lib/x86_64-linux-gnu/lapack/liblapack.so.3.12.0  LAPACK version 3.12.0
#> 
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#>  [1] LC_CTYPE=en_US.UTF-8       LC_NUMERIC=C              
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#>  [7] LC_PAPER=en_US.UTF-8       LC_NAME=C                 
#>  [9] LC_ADDRESS=C               LC_TELEPHONE=C            
#> [11] LC_MEASUREMENT=en_US.UTF-8 LC_IDENTIFICATION=C       
#> 
#> time zone: America/Chicago
#> tzcode source: system (glibc)
#> 
#> attached base packages:
#> [1] stats     graphics  grDevices utils     datasets  methods   base     
#> 
#> other attached packages:
#> [1] ErrorTracer_1.4.2
#> 
#> loaded via a namespace (and not attached):
#>  [1] digest_0.6.39     R6_2.6.1          fastmap_1.2.0     xfun_0.61        
#>  [5] cachem_1.1.0      knitr_1.52        htmltools_0.5.9   rmarkdown_2.32   
#>  [9] lifecycle_1.0.5   cli_3.6.6         sass_0.4.10       jquerylib_0.1.4  
#> [13] compiler_4.6.2    rstudioapi_0.19.0 tools_4.6.2       evaluate_1.0.5   
#> [17] bslib_0.12.0      yaml_2.3.12       otel_0.2.0        jsonlite_2.0.0   
#> [21] rlang_1.3.0