#' Calculate equilibrium solubility in the presence of humic acid
#'
#' @description Compute equilibrium solubility in the presence of humic acid, using the
#' Windermere Humic Acid Model (WHAM), due to Tipping and Hurley (see `phreeqc::Tipping_Hurley.dat`,
#' \url{https://doi.org/10.1016/0016-7037(92)90158-F}, and
#' \url{https://water.usgs.gov/water-resources/software/PHREEQC/documentation/phreeqc3-html/phreeqc3.htm}).
#' This function works like `eq_sol_fixed()`.
#'
#' @param ph pH
#' @param dic Dissolved inorganic carbon, in mg C/L.
#' @param phosphate Orthophosphate, in mg P/L.
#' @param phase Equilibrium phase.
#' @param element An element to return the equilibrium concentration of.
#' @param mass_ha Mass of humic acid in grams dissolved organic carbon.
#' @param mu_is An initial guess for the ionic strength, used to estimate the specific surface
#' area of the humic acid molecules.
#' @param phase_quantity Moles of equilibrium phase initially present.
#' @param pe Set the pe of the solution.
#' @param eq_phase_components Additional equilibrium phase components, passed to
#' `tidyphreeqc::phr_input_section` as a list.
#' @param surface_components Additional surface components, passed to
#' `tidyphreeqc::phr_input_section` as a list.
#' @param new_phase Define phases not included in the database.
#' @param phase_out Add an equilibrium phase to the output. Default is the pseudophase "Fix_pH".
#' @param new_species Define solution species not included in the database.
#' @param output_components Additional output components, passed to
#' `tidyphreeqc::phr_input_section` as a list.
#' @param buffer Substance added or subtracted from the solution to yield the desired pH.
#' @param db The database to use for equilibrium solubility computations. The default is
#' `leadsol`
#' @param max_iter Maximum iterations allowed for convergence of ionic strength.
#' @param print Choose whether to print the input file ("input"), the full output ("output"), or the selected output.
#' Default is the latter.
#' @param ... Arguments passed on to `tidyphreeqc::phr_input_section()` as solution phase
#' components. Concentrations should be expressed in mmol/kgw.
#'
#' @return A tibble with columns representing equilibrium phase, pH, dissolved inorganic carbon,
#' orthophosphate (as P), pe, ionic strength (mu), total concentration of element in solution, and moles of the equilibrium phase
#' dissolved.
#' @importFrom dplyr %>%
#' @importFrom rlang :=
#' @importFrom rlang .data
#' @export
#'
#' @examples
#' eq_sol_wham(element = "Pb", ph = 7.5, dic = 50, phase = "Cerussite", Na = 10, mass_ha = 3.5e-3)
eq_sol_wham <- function(
ph,
dic,
phosphate = 0,
phase,
mass_ha = 0,
element,
mu_is = .003,
phase_quantity = 1,
pe = 4,
eq_phase_components = list(),
new_phase = list(),
phase_out = "Fix_pH",
new_species = list(),
surface_components = list(),
output_components = list(),
buffer = "NaOH",
db = pbcu2sol,
max_iter = 3,
print = NULL,
...
) {
if(!is.null(print)) if(!print %in% c("input", "output"))
stop("Valid entries for print are NULL, 'input', or 'output'")
output_components <- if(length(output_components) == 0) {
list("-totals" = c("P", "C", element))
} else output_components
# data from WHAM:
surface_master_species <- phreeqc::Tipping_Hurley.dat[3168:3175]
surface_species <- phreeqc::Tipping_Hurley.dat[3176:3351]
# charge on 4 nHA sites:
nHA_4 <- 2.84 / 4 * mass_ha / 1e3 # (eq)
# charge on 12 diprotic sites:
diprotic <- 2.84 / 12 * mass_ha / 1e3
# solution:
solution_components <- list(...)
add_species <- tidyphreeqc::phr_input_section(
type = "SOLUTION_SPECIES",
components = new_species
)
soln <- tidyphreeqc::phr_input_section(
type = "SOLUTION",
number = 1,
name = "water",
components = list(
"pH" = ph,
"C(4)" = if(is.numeric(dic)) dic / chemr::mass("C") else dic,
"P" = phosphate / chemr::mass("P"),
"pe" = pe,
"temp" = 25,
"redox" = "pe",
"units" = "mmol/kgw",
"density" = 1,
"-water" = 1
) %>% c(solution_components)
)
# phases:
pH_def <- tidyphreeqc::phr_pH_fix_definition()
pe_def <- tidyphreeqc::phr_pe_fix_definition()
add_phase <- tidyphreeqc::phr_input_section(
type = "PHASES",
components = new_phase
)
eq_phase <- tidyphreeqc::phr_input_section(
type = "EQUILIBRIUM_PHASES",
number = 1,
name = "Solid",
components = list(
"phase" = c(0, phase_quantity),
"Fix_pH" = c(-ph, buffer, 1e6),
"Fix_pe" = c(-pe, "O2", 1e6)
) %>%
rlang::set_names(c(phase, "Fix_pH", "Fix_pe")) %>%
c(eq_phase_components)
)
# output
out <- tidyphreeqc::phr_input_section(
type = "SELECTED_OUTPUT",
number = 1,
components = list(
"-equilibrium_phases" = paste(names(eq_phase$components), collapse = " "),
"-state" = "true",
"-mu" = "true",
"-pH" = "true",
"-pe" = "true"
) %>% c(output_components)
)
# humic acid surface:
# For Psi vs I (= ionic strength) dependence, adapt specific surface area in PHRC:
# SS = 159300 - 220800/(I)^0.09 + 91260/(I)^0.18
# Example: SS = 46514 m2/g for I = 0.003 mol/l
pb_sol_wham_iter <- function(mu_guess, output_type = NULL) {
ssa <- 159300 - 220800/ mu_guess ^ 0.09 + 91260 / mu_guess ^ 0.18
surface <- tidyphreeqc::phr_input_section(
type = "SURFACE",
components = list(
# from example 19 ("Modeling Cd +2 Sorption With Linear, Freundlich, and Langmuir Isotherms, and
# With a Deterministic Distribution of Sorption Sites for Organic Matter, Clay Minerals, and Iron Oxyhydroxides")
# 3.5 mg OC, 0.025 meq total charge, distributed over the sites:
# charge on 4 nHA sites: -2.84 / 4 * 3.5e-3 / 1e3 (eq)
"H_a" = c(nHA_4, ssa, mass_ha),
"H_b" = nHA_4,
"H_c" = nHA_4,
"H_d" = nHA_4,
# charge on 4 nHB sites: 0.5 * charge on nHA sites
"H_e" = 0.5 * nHA_4,
"H_f" = 0.5 * nHA_4,
"H_g" = 0.5 * nHA_4,
"H_h" = 0.5 * nHA_4,
# charge on 12 diprotic sites: -2.84 / 12 * 3.5e-3 / 1e3
"H_ab" = diprotic,
"H_ad" = diprotic,
"H_af" = diprotic,
"H_ah" = diprotic,
"H_bc" = diprotic,
"H_be" = diprotic,
"H_bg" = diprotic,
"H_cd" = diprotic,
"H_cf" = diprotic,
"H_ch" = diprotic,
"H_de" = diprotic,
"H_dg" = diprotic,
"-Donnan",
"-equilibrate" = 1
) %>%
c(surface_components)
)
surface <- if(mass_ha == 0) NULL else surface
run <- tidyphreeqc::phr_input(
surface_master_species, surface_species,
pH_def, pe_def, add_phase, add_species, surface,
soln, eq_phase, out, tidyphreeqc::phr_end()
)
tidyphreeqc::phr_use_db(db)
if(is.null(output_type)) {
tidyphreeqc::phr_run(run) %>%
tibble::as_tibble() %>%
dplyr::filter(.data$state == "react") %>%
dplyr::transmute(
phase,
pH = .data$pH,
dic_ppm = 1e3 * .data$`C(mol/kgw)` * chemr::mass("C"),
p_ppm = 1e3 * .data$`P(mol/kgw)` * chemr::mass("P"),
pe = .data$pe,
mu = .data$mu,
!!paste0(stringr::str_to_lower(element), "_ppb") := 1e6 * .data[[paste0(element, "(mol/kgw)")]] * chemr::mass(element),
!!paste0("mol_", phase) := -.data[[paste0("d_", phase)]],
!!paste0("mol_", phase_out) := -.data[[paste0("d_", phase_out)]]
)
} else
if(output_type == "input") run else
if(output_type == "output") {
# full output:
tidyphreeqc::phr_run(run) %>%
tidyphreeqc::phr_print_output()
}
}
# an initial guess for mu is required to estimate the specific surface area of the humic molecules;
# if it's wrong, repeat the calculation using the updated value for mu until mu converges
# or max_iter is reached:
next_iter <- pb_sol_wham_iter(mu_guess = mu_is)
mu_old <- mu_is
mu_new <- next_iter$mu
print_is_null <- if(mu_new - mu_old < 1e-5 | mass_ha == 0) next_iter else{
counter <- 1
while(mu_new - mu_old > 1e-5 & counter <= max_iter) {
counter <- counter + 1 # add one to iteration counter
next_iter <- pb_sol_wham_iter(mu_guess = mu_new) # use updated mu to run calculation
mu_old <- mu_new # updated mu becomes old mu
mu_new <- next_iter$mu # update mu
}
next_iter
}
if(is.null(print)) print_is_null else
pb_sol_wham_iter(mu_guess = mu_new, output_type = print)
}
#' @describeIn eq_sol_wham Shorthand for `eq_sol_wham()` with `element = "Pb"`. For backwards compatibility.
#' @export
pb_sol_wham <- function(element = "Pb", ...) {
eq_sol_wham(element = element, ...)
}
#' @describeIn eq_sol_wham Shorthand for `eq_sol_wham()` with `element = "Cu"`. For backwards compatibility.
#' @export
cu_sol_wham <- function(element = "Cu", ...) {
eq_sol_wham(element = element, ...)
}
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