Title: | Water Quality Models for Drinking Water Treatment Processes |
---|---|
Description: | Provides multiple water chemistry-based models and published empirical models in one standard format. Functions can be chained together to model a complete treatment process and are designed to work in a 'tidyverse' workflow. Models are primarily based on these sources: Benjamin, M. M. (2002, ISBN:147862308X), Crittenden, J. C., Trussell, R., Hand, D., Howe, J. K., & Tchobanoglous, G., Borchardt, J. H. (2012, ISBN:9781118131473), USEPA. (2001) <https://www.epa.gov/sites/default/files/2017-03/documents/wtp_model_v._2.0_manual_508.pdf>. |
Authors: | Sierra Johnson [aut, cre], Libby McKenna [aut], Riley Mulhern [aut] , Chris Corwin [aut] , Rachel Merrifield [ctb], Mayuri Namasivayam [ctb], USEPA [cph] (Copyright holder of included TELSS fragments (dissolve_pb function)), Brown and Caldwell [fnd, cph] |
Maintainer: | Sierra Johnson <[email protected]> |
License: | Apache License (>= 2) | MIT + file LICENSE |
Version: | 0.6.2 |
Built: | 2024-11-06 09:42:03 UTC |
Source: | CRAN |
This function takes a water defined by define_water
and balances charge.
balance_ions(water)
balance_ions(water)
water |
Water created with define_water, which may have some ions set to 0 when unknown |
If more cations are needed, sodium will be added, unless a number for sodium is already provided and potassium is 0, then it will add potassium. Similarly,
anions are added using chloride, unless sulfate is 0. If calcium and magnesium are not specified when defining a water with
define_water
, they will default to 0 and not be changed by this function. This function is purely mathematical.
User should always check the outputs to make sure values are reasonable for the input source water.
A water class object with updated ions to balance water charge.
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>% balance_ions()
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>% balance_ions()
This function allows balance_ions
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be used with "downstream" tidywater functions.
balance_ions_chain( df, input_water = "defined_water", output_water = "balanced_water" )
balance_ions_chain( df, input_water = "defined_water", output_water = "balanced_water" )
df |
a data frame containing a water class column, which has already been computed using |
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
output_water |
name of the output column storing updated parameters with the class, water. Default is "balanced_water". |
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with updated ions to balance water charge.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain(output_water = "balanced ions, balanced life") %>% chemdose_ph_chain(input_water = "balanced ions, balanced life", naoh = 5) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain(output_water = "balanced ions, balanced life") %>% chemdose_ph_chain(input_water = "balanced ions, balanced life", naoh = 5) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
This function allows balance_ions
to be added to a piped data frame.
tidywater functions cannot be added after this function because they require a 'water' class input.
balance_ions_once(df, input_water = "defined_water")
balance_ions_once(df, input_water = "defined_water")
df |
a data frame containing a water class column, which has already been computed using |
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A dataframe with updated ions to balance water charge
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_once() example_df <- water_df %>% define_water_chain(output_water = "Different_defined_water_column") %>% balance_ions_once(input_water = "Different_defined_water_column") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_once() # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_once() example_df <- water_df %>% define_water_chain(output_water = "Different_defined_water_column") %>% balance_ions_once(input_water = "Different_defined_water_column") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_once() # Optional: explicitly close multisession processing plan(sequential)
This function applies the Terry model to a water created by define_water
to determine biofiltered
DOC (mg/L).
biofilter_toc(water, ebct, ozonated = TRUE)
biofilter_toc(water, ebct, ozonated = TRUE)
water |
Source water object of class "water" created by |
ebct |
The empty bed contact time (min) used for the biofilter |
ozonated |
Logical; TRUE if the water is ozonated (default), FALSE otherwise |
A water class object with modeled DOC removal from biofiltration.
Terry and Summers 2018
library(tidywater) water <- define_water(ph = 7, temp = 25, alk = 100, toc = 5.0, doc = 4.0, uv254 = .1) %>% biofilter_toc(ebct = 10, ozonated = FALSE)
library(tidywater) water <- define_water(ph = 7, temp = 25, alk = 100, toc = 5.0, doc = 4.0, uv254 = .1) %>% biofilter_toc(ebct = 10, ozonated = FALSE)
This function takes a vector of waters defined by define_water
and a vector of ratios and outputs a new water object with updated ions and pH.
blend_waters(waters, ratios)
blend_waters(waters, ratios)
waters |
Vector of source waters created by |
ratios |
Vector of ratios in the same order as waters. (Blend ratios must sum to 1) |
A water class object with blended water quality parameters.
water1 <- define_water(7, 20, 50) water2 <- define_water(7.5, 20, 100, tot_nh3 = 2) blend_waters(c(water1, water2), c(.4, .6))
water1 <- define_water(7, 20, 50) water2 <- define_water(7.5, 20, 100, tot_nh3 = 2) blend_waters(c(water1, water2), c(.4, .6))
This function allows blend_waters
to be added to a piped data frame.
blend_waters_chain(df, waters, ratios, output_water = "blended_water")
blend_waters_chain(df, waters, ratios, output_water = "blended_water")
df |
a data frame containing a water class column, which has already
been computed using |
waters |
List of column names containing a water class to be blended |
ratios |
List of column names or vector of blend ratios in the same order as waters. (Blend ratios must sum to 1) |
output_water |
name of output column storing updated parameters with the class, water. Default is "blended_water". |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
The 'water' class columns to use in the function are specified as function arguments. Ratios may be input
as columns with varied ratios (in this case, input column names in the function arguments), OR input as numbers directly.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with a water class column containing updated ions and pH.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22) %>% mutate( ratios1 = .4, ratios2 = .6 ) %>% blend_waters_chain( waters = c("defined_water", "dosed_chem_water"), ratios = c("ratios1", "ratios2"), output_water = "Blending_after_chemicals" ) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_chain(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_chain(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22) %>% mutate( ratios1 = .4, ratios2 = .6 ) %>% blend_waters_chain( waters = c("defined_water", "dosed_chem_water"), ratios = c("ratios1", "ratios2"), output_water = "Blending_after_chemicals" ) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_chain(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_chain(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Optional: explicitly close multisession processing plan(sequential)
This function allows blend_waters
to be added to a piped data frame.
blend_waters_once(df, waters, ratios)
blend_waters_once(df, waters, ratios)
df |
a data frame containing a water class column, which has already been computed using
|
waters |
List of column names containing a water class to be blended |
ratios |
List of column names or vector of blend ratios in the same order as waters. (Blend ratios must sum to 1) |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
The 'water' class columns to use in the function are specified as function arguments. Ratios may be input
as columns with varied ratios (in this case, input column names in the function arguments), OR input as numbers directly.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with blended water quality parameters.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% mutate( ratios1 = .4, ratios2 = .6 ) %>% blend_waters_once(waters = c("defined_water", "dosed"), ratios = c("ratios1", "ratios2")) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_once(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_once(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% mutate( ratios1 = .4, ratios2 = .6 ) %>% blend_waters_once(waters = c("defined_water", "dosed"), ratios = c("ratios1", "ratios2")) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_once(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(naoh = 22, output_water = "dosed") %>% blend_waters_once(waters = c("defined_water", "dosed", "balanced_water"), ratios = c(.2, .3, .5)) # Optional: explicitly close multisession processing plan(sequential)
A dataset containing coefficients for calculating ozone formation
bromatecoeffs
bromatecoeffs
A dataframe with 30 rows and 10 columns
First author of source model
Either T or F, depending on whether the model applies to waters with ammonia present.
First coefficient in bromate model
Exponent in bromate model, associated with Br-
Exponent in bromate model, associated with DOC
Exponent in bromate model, associated with UVA
Exponent in bromate model, associated with pH
Exponent in bromate model, associated with Alkalinity
Exponent in bromate model, associated with ozone dose
Exponent in bromate model, associated with reaction time
Exponent in bromate model, associated with ammonia (NH4+)
Exponent in bromate model, associated with temperature
Coefficient in bromate model, associated with temperature in the exponent. Either i or I are used, not both.
Ozekin (1994), Sohn et al (2004), Song et al (1996), Galey et al (1997), Siddiqui et al (1994)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
calculate_corrosion
takes an object of class "water" created by define_water
and calculates
corrosion and scaling indices.
calculate_corrosion( water, index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
calculate_corrosion( water, index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
water |
Source water of class "water" created by |
index |
The indices to be calculated. Default calculates all six indices: "aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr" CCPP may not be able to be calculated sometimes, so it may be advantageous to leave this out of the function to avoid errors |
form |
Form of calcium carbonate mineral to use for modelling solubility: "calcite" (default), "aragonite", or "vaterite" |
Aggressiveness Index (AI), unitless - the corrosive tendency of water and its effect on asbestos cement pipe.
Ryznar Index (RI), unitless - a measure of scaling potential.
Langelier Saturation Index (LSI), unitless - describes the potential for calcium carbonate scale formation. Equations use empirical calcium carbonate solubilities from Plummer and Busenberg (1982) and Crittenden et al. (2012) rather than calculated from the concentrations of calcium and carbonate in the water.
Larson-skold Index (LI), unitless - describes the corrosivity towards mild steel.
Chloride-to-sulfate mass ratio (CSMR), mg Cl/mg SO4 - indicator of galvanic corrosion for lead solder pipe joints.
Calcium carbonate precipitation potential (CCPP), mg/L as CaCO3 - a prediction of the mass of calcium carbonate that will precipitate at equilibrium. A positive CCPP value indicates the amount of CaCO3 (mg/L as CaCO3) that will precipitate. A negative CCPP indicates how much CaCO3 can be dissolved in the water.
A water class object with updated corrosion and scaling index slots.
AWWA (1977)
Crittenden et al. (2012)
Langelier (1936)
Larson and Skold (1958)
Merrill and Sanks (1977a)
Merrill and Sanks (1977b)
Merrill and Sanks (1978)
Nguyen et al. (2011)
Plummer and Busenberg (1982)
Ryznar (1946)
Schock (1984)
Trussell (1998)
U.S. EPA (1980)
See reference list at https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
water <- define_water( ph = 8, temp = 25, alk = 200, tot_hard = 200, tds = 576, cl = 150, so4 = 200 ) %>% calculate_corrosion() water <- define_water(ph = 8, temp = 25, alk = 100, tot_hard = 50, tds = 200) %>% calculate_corrosion(index = c("aggressive", "ccpp"))
water <- define_water( ph = 8, temp = 25, alk = 200, tot_hard = 200, tds = 576, cl = 150, so4 = 200 ) %>% calculate_corrosion() water <- define_water(ph = 8, temp = 25, alk = 100, tot_hard = 50, tds = 200) %>% calculate_corrosion(index = c("aggressive", "ccpp"))
This function allows calculate_corrosion
to be added to a piped data frame.
Up to six additional columns will be added to the output 'water' class column depending on what corrosion/scaling
indices are selected: Aggressive index (AI), Ryznar index (RI), Langelier saturation index (LSI),
Larson-Skold index (LI), chloride-to-sulfate mass ratio (CSMR) & calcium carbonate precipitation potential (CCPP).
calculate_corrosion_chain( df, input_water = "defined_water", output_water = "corrosion_indices", index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
calculate_corrosion_chain( df, input_water = "defined_water", output_water = "corrosion_indices", index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
df |
a data frame containing a column, defined_water, which has already
been computed using |
input_water |
name of the column of water class data to be used as the input. Default is "defined_water". |
output_water |
name of output column storing updated indices with the class, water. Default is "corrosion_indices". |
index |
The indices to be calculated. Default calculates all six indices: "aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr" CCPP may not be able to be calculated sometimes, so it may be advantageous to leave this out of the function to avoid errors |
form |
Form of calcium carbonate mineral to use for modelling solubility: "calcite" (default), "aragonite", or "vaterite" |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
The 'water' class column to use in the function is specified in the 'input_water' argument (default input 'water' is "defined_water".
The name of the output 'water' class column defaults to "corrosion_indices", but may be altered using the 'output_water' argument.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with updated corrosion and scaling index slots.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_chain() example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_chain(index = c("aggressive", "ccpp")) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% calculate_corrosion_chain(index = c("aggressive", "ccpp")) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_chain() example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_chain(index = c("aggressive", "ccpp")) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% calculate_corrosion_chain(index = c("aggressive", "ccpp")) # Optional: explicitly close multisession processing plan(sequential)
This function allows calculate_corrosion
to be added to a piped data frame.
Up to six additional columns will be added to the dataframe depending on what corrosion/scaling
indices are selected: Aggressive index (AI), Ryznar index (RI), Langelier saturation index (LSI),
Larson-Skold index (LI), chloride-to-sulfate mass ratio (CSMR) & calcium carbonate precipitation potential (CCPP).
calculate_corrosion_once( df, input_water = "defined_water", index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
calculate_corrosion_once( df, input_water = "defined_water", index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"), form = "calcite" )
df |
a data frame containing a water class column, created using |
input_water |
name of the column of water class data to be used as the input. Default is "defined_water". |
index |
The indices to be calculated. Default calculates all six indices: "aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr". CCPP may not be able to be calculated sometimes, so it may be advantageous to leave this out of the function to avoid errors |
form |
Form of calcium carbonate mineral to use for modelling solubility: "calcite" (default), "aragonite", or "vaterite" |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing specified corrosion and scaling indices.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_once() example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_once(index = c("aggressive", "ccpp")) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% calculate_corrosion_once(index = c("aggressive", "ccpp")) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_once() example_df <- water_df %>% slice_head(n = 2) %>% # used to make example run faster define_water_chain() %>% calculate_corrosion_once(index = c("aggressive", "ccpp")) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% calculate_corrosion_once(index = c("aggressive", "ccpp")) # Optional: explicitly close multisession processing plan(sequential)
This function takes a water class object defined by define_water
and outputs a DIC (mg/L).
calculate_dic(water)
calculate_dic(water)
water |
a water class object containing columns with all the parameters listed in |
A numeric value for the calculated DIC.
example_dic <- define_water(8, 15, 200) %>% calculate_dic()
example_dic <- define_water(8, 15, 200) %>% calculate_dic()
This function takes Ca and Mg in mg/L and returns hardness in mg/L as CaCO3
calculate_hardness(ca, mg, type = "total", startunit = "mg/L")
calculate_hardness(ca, mg, type = "total", startunit = "mg/L")
ca |
Calcium concentration in mg/L as Ca |
mg |
Magnesium concentration in mg/L as Mg |
type |
"total" returns total hardness, "ca" returns calcium hardness. Defaults to "total" |
startunit |
Units of Ca and Mg. Defaults to mg/L |
A numeric value for the total hardness in mg/L as CaCO3.
calculate_hardness(50, 10) water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) calculate_hardness(water_defined@ca, water_defined@mg, "total", "M")
calculate_hardness(50, 10) water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) calculate_hardness(water_defined@ca, water_defined@mg, "total", "M")
This function takes a water defined by define_water
and other disinfection parameters
and outputs a data frame of the required CT ('ct_required'), actual CT ('ct_actual'), and giardia log removal ('glog_removal').
chemdose_ct(water, time, residual, baffle)
chemdose_ct(water, time, residual, baffle)
water |
Source water object of class "water" created by |
time |
Retention time of disinfection segment in minutes. |
residual |
Minimum chlorine residual in disinfection segment in mg/L as Cl2. |
baffle |
Baffle factor - unitless value between 0 and 1. |
CT actual is a function of time, chlorine residual, and baffle factor, whereas CT required is a function of pH, temperature, chlorine residual, and the standard 0.5 log removal of giardia requirement. CT required is an empirical regression equation developed by Smith et al. (1995) to provide conservative estimates for CT tables in USEPA Disinfection Profiling Guidance. Log removal is a rearrangement of the CT equations.
A data frame of the required CT, actual CT, and giardia log removal.
Smith et al. (1995)
USEPA (2020)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
example_ct <- define_water(ph = 7.5, temp = 25) %>% chemdose_ct(time = 30, residual = 1, baffle = 0.7)
example_ct <- define_water(ph = 7.5, temp = 25) %>% chemdose_ct(time = 30, residual = 1, baffle = 0.7)
chemdose_dbp
calculates disinfection byproduct (DBP) formation based on the U.S. EPA's
Water Treatment Plant Model (U.S. EPA, 2001). Required arguments include an object of class "water"
created by define_water
chlorine dose, type, reaction time, and treatment applied (if any).
The function also requires additional water quality parameters defined in define_water
including bromide, TOC, UV254, temperature, and pH.
chemdose_dbp( water, cl2, time, treatment = "raw", cl_type = "chorine", location = "plant" )
chemdose_dbp( water, cl2, time, treatment = "raw", cl_type = "chorine", location = "plant" )
water |
Source water object of class "water" created by |
cl2 |
Applied chlorine dose (mg/L as Cl2). Model results are valid for doses between 1.51 and 33.55 mg/L. |
time |
Reaction time (hours). Model results are valid for reaction times between 2 and 168 hours. |
treatment |
Type of treatment applied to the water. Options include "raw" for no treatment (default), "coag" for water that has been coagulated or softened, and "gac" for water that has been treated by granular activated carbon (GAC). GAC treatment has also been used for estimating formation after membrane treatment with good results. |
cl_type |
Type of chlorination applied, either "chlorine" (default) or "chloramine". |
location |
Location for DBP formation, either in the "plant" (default), or in the distributions system, "ds". |
The function will calculate haloacetic acids (HAA) as HAA5, and total trihalomethanes (TTHM).
Use summarise_wq
to quickly tabulate the results.
A water class object with predicted DBP concentrations.
TTHMs, raw: U.S. EPA (2001) equation 5-131
HAAs, raw: U.S. EPA (2001) equation 5-134
TTHMs, treated: U.S. EPA (2001) equation 5-139
HAAs, treated: U.S. EPA (2001) equation 5-142
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
example_dbp <- suppressWarnings(define_water(8, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% chemdose_dbp(cl2 = 2, time = 8) example_dbp <- suppressWarnings(define_water(7.5, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% chemdose_dbp(cl2 = 3, time = 168, treatment = "coag", location = "ds")
example_dbp <- suppressWarnings(define_water(8, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% chemdose_dbp(cl2 = 2, time = 8) example_dbp <- suppressWarnings(define_water(7.5, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% chemdose_dbp(cl2 = 3, time = 168, treatment = "coag", location = "ds")
DBP = disinfection byproduct
chemdose_dbp_chain( df, input_water = "defined_water", output_water = "disinfected_water", cl2 = 0, time = 0, treatment = "raw", cl_type = "chlorine", location = "plant" )
chemdose_dbp_chain( df, input_water = "defined_water", output_water = "disinfected_water", cl2 = 0, time = 0, treatment = "raw", cl_type = "chlorine", location = "plant" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
output_water |
name of the output column storing updated parameters with the class, water. Default is "disinfected_water". |
cl2 |
Applied chlorine dose (mg/L as Cl2). Model results are valid for doses between 1.51 and 33.55 mg/L. |
time |
Reaction time (hours). Model results are valid for reaction times between 2 and 168 hours. |
treatment |
Type of treatment applied to the water. Options include "raw" for no treatment (default), "coag" for water that has been coagulated or softened, and "gac" for water that has been treated by granular activated carbon (GAC). GAC treatment has also been used for estimating formation after membrane treatment with good results. |
cl_type |
Type of chlorination applied, either "chlorine" (default) or "chloramine". |
location |
Location for DBP formation, either in the "plant" (default), or in the distribution system, "ds". |
This function allows chemdose_dbp
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be used with "downstream" tidywater functions.
TTHM, HAA5, and individual DBP species will be updated based on the applied chlorine dose,
the reaction time, treatment type, chlorine type, and DBP formation location.
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a chlorine dose column (cl2) or time column (time), the function will use those columns. Note: The function can only take cl2 and time inputs as EITHER a column or from the function arguments, not both.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with predicted DBP concentrations.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_chain(input_water = "balanced_water", cl2 = 4, time = 8) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% mutate( cl2 = seq(2, 24, 2), time = 30 ) %>% chemdose_dbp_chain(input_water = "balanced_water") example_df <- water_df %>% mutate(br = 80) %>% define_water_chain() %>% balance_ions_chain() %>% mutate(time = 8) %>% chemdose_dbp_chain( input_water = "balanced_water", cl = 6, treatment = "coag", location = "ds", cl_type = "chloramine" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_chain(input_water = "balanced_water", cl2 = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_chain(input_water = "balanced_water", cl2 = 4, time = 8) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% mutate( cl2 = seq(2, 24, 2), time = 30 ) %>% chemdose_dbp_chain(input_water = "balanced_water") example_df <- water_df %>% mutate(br = 80) %>% define_water_chain() %>% balance_ions_chain() %>% mutate(time = 8) %>% chemdose_dbp_chain( input_water = "balanced_water", cl = 6, treatment = "coag", location = "ds", cl_type = "chloramine" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_chain(input_water = "balanced_water", cl2 = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
DBP = disinfection byproduct
chemdose_dbp_once( df, input_water = "defined_water", cl2 = 0, time = 0, treatment = "raw", cl_type = "chlorine", location = "plant" )
chemdose_dbp_once( df, input_water = "defined_water", cl2 = 0, time = 0, treatment = "raw", cl_type = "chlorine", location = "plant" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
cl2 |
Applied chlorine dose (mg/L as Cl2). Model results are valid for doses between 1.51 and 33.55 mg/L. |
time |
Reaction time (hours). Model results are valid for reaction times between 2 and 168 hours. |
treatment |
Type of treatment applied to the water. Options include "raw" for no treatment (default), "coag" for water that has been coagulated or softened, and "gac" for water that has been treated by granular activated carbon (GAC). GAC treatment has also been used for estimating formation after membrane treatment with good results. |
cl_type |
Type of chlorination applied, either "chlorine" (default) or "chloramine". |
location |
Location for DBP formation, either in the "plant" (default), or in the distribution system, "ds". |
This function allows chemdose_dbp
to be added to a piped data frame.
Its output is a data frame containing columns for TTHM, HAA5, and individual DBP species.
DBPs are estimated based on the applied chlorine dose, the reaction time, treatment type, chlorine type, and DBP formation location.
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a chlorine dose column (cl2) or time column (time), the function will use those columns. Note: The function can only take cl2 and time inputs as EITHER a column or from the function arguments, not both.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with predicted DBP concentrations.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_once(input_water = "balanced_water", cl2 = 4, time = 8) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% mutate( cl2 = seq(2, 24, 2), time = 30 ) %>% chemdose_dbp_once(input_water = "balanced_water") example_df <- water_df %>% mutate(br = 80) %>% define_water_chain() %>% balance_ions_chain() %>% mutate(time = 8) %>% chemdose_dbp_once( input_water = "balanced_water", cl = 6, treatment = "coag", location = "ds", cl_type = "chloramine" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_once(input_water = "balanced_water", cl2 = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_once(input_water = "balanced_water", cl2 = 4, time = 8) example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% mutate( cl2 = seq(2, 24, 2), time = 30 ) %>% chemdose_dbp_once(input_water = "balanced_water") example_df <- water_df %>% mutate(br = 80) %>% define_water_chain() %>% balance_ions_chain() %>% mutate(time = 8) %>% chemdose_dbp_once( input_water = "balanced_water", cl = 6, treatment = "coag", location = "ds", cl_type = "chloramine" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_dbp_once(input_water = "balanced_water", cl2 = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
Applies equation of the form: raw_f - A*alum^a*ph ^ b * raw_f^c. There is no published model, so it is recommended to fit the coefficients with experimental data. When fitting, the following units must be used: Alum in mg/L as chemical, Fluoride in mg/L, pH in SU. Default coefficients are fit from Sollo et al (1978). This function outputs a water class object with an updated fluoride concentration (which will be in M, per standard water units).
chemdose_f(water, alum, coeff = c(1.11, 0.628, -2.07, 0.861))
chemdose_f(water, alum, coeff = c(1.11, 0.628, -2.07, 0.861))
water |
Source water object of class "water" created by |
alum |
Amount of hydrated aluminum sulfate added in mg/L: Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
coeff |
Model coefficients to use as vector of numbers. |
A water class object with an updated fluoride concentration.
dosed_water <- define_water(ph = 7, temp = 25, alk = 50, f = 4) %>% chemdose_ph(alum = 50) %>% chemdose_f(alum = 50) convert_units(dosed_water@f, "f", "M", "mg/L")
dosed_water <- define_water(ph = 7, temp = 25, alk = 50, f = 4) %>% chemdose_ph(alum = 50) %>% chemdose_f(alum = 50) convert_units(dosed_water@f, "f", "M", "mg/L")
chemdose_ph
calculates the new pH, alkalinity, and ion balance of a water based on different chemical
additions.
chemdose_ph( water, hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, caoh2 = 0, mgoh2 = 0, na2co3 = 0, nahco3 = 0, caco3 = 0, cacl2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, softening_correction = FALSE )
chemdose_ph( water, hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, caoh2 = 0, mgoh2 = 0, na2co3 = 0, nahco3 = 0, caco3 = 0, cacl2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, softening_correction = FALSE )
water |
Source water object of class "water" created by |
hcl |
Amount of hydrochloric acid added in mg/L: HCl -> H + Cl |
h2so4 |
Amount of sulfuric acid added in mg/L: H2SO4 -> 2H + SO4 |
h3po4 |
Amount of phosphoric acid added in mg/L: H3PO4 -> 3H + PO4 |
co2 |
Amount of carbon dioxide added in mg/L: CO2 (gas) + H2O -> H2CO3* |
naoh |
Amount of caustic added in mg/L: NaOH -> Na + OH |
caoh2 |
Amount of lime added in mg/L: Ca(OH)2 -> Ca + 2OH |
mgoh2 |
Amount of magneisum hydroxide added in mg/L: Mg(OH)2 -> Mg + 2OH |
na2co3 |
Amount of soda ash added in mg/L: Na2CO3 -> 2Na + CO3 |
nahco3 |
Amount of sodium bicarbonate added in mg/L: NaHCO3 -> Na + H + CO3 |
caco3 |
Amount of calcium carbonate added (or removed) in mg/L: CaCO3 -> Ca + CO3 |
cacl2 |
Amount of calcium chloride added in mg/L: CaCl2 -> Ca2+ + 2Cl- |
cl2 |
Amount of chlorine gas added in mg/L as Cl2: Cl2(g) + H2O -> HOCl + H + Cl |
naocl |
Amount of sodium hypochlorite added in mg/L as Cl2: NaOCl -> Na + OCl |
nh4oh |
Amount of ammonium hydroxide added in mg/L as N: NH4OH -> NH4 + OH |
nh42so4 |
Amount of ammonium sulfate added in mg/L as N: (NH4)2SO4 -> 2NH4 + SO4 |
alum |
Amount of hydrated aluminum sulfate added in mg/L: Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Amount of ferric Chloride added in mg/L: FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
ach |
Amount of aluminum chlorohydrate added in mg/L: Al2(OH)5Cl*2H2O + HCO3 -> 2Al(OH)3(am) + Cl + 2H2O + CO2 |
softening_correction |
Set to TRUE to correct post-softening pH (caco3 must be < 0). Default is FALSE. Based on WTP model equation 5-62 |
The function takes an object of class "water" created by define_water
and user-specified
chemical additions and returns a new object of class "water" with updated water quality.
Units of all chemical additions are in mg/L as chemical (not as product).
chemdose_ph
works by evaluating all the user-specified chemical additions and solving for what the new pH
must be using uniroot
to satisfy the principle of electroneutrality in pure water while correcting for the existing alkalinity
of the water that the chemical is added to. Multiple chemicals can be added simultaneously or each addition can be
modeled independently through sequential doses.
A water class object with updated pH, alkalinity, and ions post-chemical addition.
water <- define_water(ph = 7, temp = 25, alk = 10) # Dose 1 mg/L of hydrochloric acid dosed_water <- chemdose_ph(water, hcl = 1) dosed_water@ph # Dose 1 mg/L of hydrochloric acid and 5 mg/L of alum simultaneously dosed_water <- chemdose_ph(water, hcl = 1, alum = 5) dosed_water@ph # Dose 1 mg/L of hydrochloric acid and 5 mg/L of alum sequentially dosed_water1 <- chemdose_ph(water, hcl = 1) dosed_water1@ph dosed_water2 <- chemdose_ph(dosed_water1, alum = 5) dosed_water2@ph # Softening: water2 <- define_water(ph = 7, temp = 25, alk = 100, tot_hard = 350) dosed_water1 <- chemdose_ph(water2, caco3 = -100) dosed_water1@ph dosed_water2 <- chemdose_ph(water2, caco3 = -100, softening_correction = TRUE) dosed_water2@ph
water <- define_water(ph = 7, temp = 25, alk = 10) # Dose 1 mg/L of hydrochloric acid dosed_water <- chemdose_ph(water, hcl = 1) dosed_water@ph # Dose 1 mg/L of hydrochloric acid and 5 mg/L of alum simultaneously dosed_water <- chemdose_ph(water, hcl = 1, alum = 5) dosed_water@ph # Dose 1 mg/L of hydrochloric acid and 5 mg/L of alum sequentially dosed_water1 <- chemdose_ph(water, hcl = 1) dosed_water1@ph dosed_water2 <- chemdose_ph(dosed_water1, alum = 5) dosed_water2@ph # Softening: water2 <- define_water(ph = 7, temp = 25, alk = 100, tot_hard = 350) dosed_water1 <- chemdose_ph(water2, caco3 = -100) dosed_water1@ph dosed_water2 <- chemdose_ph(water2, caco3 = -100, softening_correction = TRUE) dosed_water2@ph
This function allows chemdose_ph
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be used with "downstream" tidywater functions.
Ions and pH will be updated based on input chemical doses.
chemdose_ph_chain( df, input_water = "defined_water", output_water = "dosed_chem_water", hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, na2co3 = 0, nahco3 = 0, caoh2 = 0, mgoh2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, caco3 = 0 )
chemdose_ph_chain( df, input_water = "defined_water", output_water = "dosed_chem_water", hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, na2co3 = 0, nahco3 = 0, caoh2 = 0, mgoh2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, caco3 = 0 )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
output_water |
name of the output column storing updated parameters with the class, water. Default is "dosed_chem_water". |
hcl |
Hydrochloric acid: HCl -> H + Cl |
h2so4 |
Sulfuric acid: H2SO4 -> 2H + SO4 |
h3po4 |
Phosphoric acid: H3PO4 -> 3H + PO4 |
co2 |
Carbon Dioxide CO2 (gas) + H2O -> H2CO3* |
naoh |
Caustic: NaOH -> Na + OH |
na2co3 |
Soda ash: Na2CO3 -> 2Na + CO3 |
nahco3 |
Sodium bicarbonate: NaHCO3 -> Na + H + CO3 |
caoh2 |
Lime: Ca(OH)2 -> Ca + 2OH |
mgoh2 |
Magneisum hydroxide: Mg(OH)2 -> Mg + 2OH |
cl2 |
Chlorine gas: Cl2(g) + H2O -> HOCl + H + Cl |
naocl |
Sodium hypochlorite: NaOCl -> Na + OCl |
nh4oh |
Amount of ammonium hydroxide added in mg/L as N: NH4OH -> NH4 + OH |
nh42so4 |
Amount of ammonium sulfate added in mg/L as N: (NH4)2SO4 -> 2NH4 + SO4 |
alum |
Hydrated aluminum sulfate Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Ferric Chloride FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
ach |
Amount of aluminum chlorohydrate added in mg/L: Al2(OH)5Cl*2H2O + HCO3 -> 2Al(OH)3(am) + Cl + 2H2O + CO2 |
caco3 |
Amount of calcium carbonate added (or removed) in mg/L: CaCO3 -> Ca + CO3 |
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a column(s) name matching a valid chemical(s), the function will dose that chemical(s) in addition to the
ones specified in the function's arguments.
The column names must match the chemical names as displayed in chemdose_ph
.
To see which chemicals can be passed into the function, see chemdose_ph
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with updated pH, alkalinity, and ions post-chemical addition.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(input_water = "balanced_water", naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( hcl = seq(1, 12, 1), naoh = 20 ) %>% chemdose_ph_chain(input_water = "balanced_water", mgoh2 = 55, co2 = 4) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(input_water = "balanced_water", naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(input_water = "balanced_water", naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( hcl = seq(1, 12, 1), naoh = 20 ) %>% chemdose_ph_chain(input_water = "balanced_water", mgoh2 = 55, co2 = 4) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(input_water = "balanced_water", naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
This function allows chemdose_ph
to be added to a piped data frame.
Its output is a data frame with updated ions and pH.
chemdose_ph_once( df, input_water = "defined_water", hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, na2co3 = 0, nahco3 = 0, caoh2 = 0, mgoh2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, caco3 = 0 )
chemdose_ph_once( df, input_water = "defined_water", hcl = 0, h2so4 = 0, h3po4 = 0, co2 = 0, naoh = 0, na2co3 = 0, nahco3 = 0, caoh2 = 0, mgoh2 = 0, cl2 = 0, naocl = 0, nh4oh = 0, nh42so4 = 0, alum = 0, ferricchloride = 0, ferricsulfate = 0, ach = 0, caco3 = 0 )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
hcl |
Hydrochloric acid: HCl -> H + Cl |
h2so4 |
Sulfuric acid: H2SO4 -> 2H + SO4 |
h3po4 |
Phosphoric acid: H3PO4 -> 3H + PO4 |
co2 |
Carbon Dioxide CO2 (gas) + H2O -> H2CO3* |
naoh |
Caustic: NaOH -> Na + OH |
na2co3 |
Soda ash: Na2CO3 -> 2Na + CO3 |
nahco3 |
Sodium bicarbonate: NaHCO3 -> Na + H + CO3 |
caoh2 |
Lime: Ca(OH)2 -> Ca + 2OH |
mgoh2 |
Magneisum hydroxide: Mg(OH)2 -> Mg + 2OH |
cl2 |
Chlorine gas: Cl2(g) + H2O -> HOCl + H + Cl |
naocl |
Sodium hypochlorite: NaOCl -> Na + OCl |
nh4oh |
Amount of ammonium hydroxide added in mg/L as N: NH4OH -> NH4 + OH |
nh42so4 |
Amount of ammonium sulfate added in mg/L as N: (NH4)2SO4 -> 2NH4 + SO4 |
alum |
Hydrated aluminum sulfate Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Ferric Chloride FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
ach |
Amount of aluminum chlorohydrate added in mg/L: Al2(OH)5Cl*2H2O + HCO3 -> 2Al(OH)3(am) + Cl + 2H2O + CO2 |
caco3 |
Amount of calcium carbonate added (or removed) in mg/L: CaCO3 -> Ca + CO3 |
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a column(s) name matching a valid chemical(s), the function will dose that chemical(s) in addition to the
ones specified in the function's arguments.
The column names must match the chemical names as displayed in chemdose_ph
.
To see which chemicals can be passed into the function, see chemdose_ph
.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with updated pH, alkalinity, and ions post-chemical addition.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_once(input_water = "balanced_water", naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( hcl = seq(1, 12, 1), naoh = 20 ) %>% chemdose_ph_once(input_water = "balanced_water", mgoh2 = 55, co2 = 4) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_once(input_water = "balanced_water", naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_once(input_water = "balanced_water", naoh = 5) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( hcl = seq(1, 12, 1), naoh = 20 ) %>% chemdose_ph_once(input_water = "balanced_water", mgoh2 = 55, co2 = 4) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_once(input_water = "balanced_water", naoh = 5) # Optional: explicitly close multisession processing plan(sequential)
This function applies the Edwards (1997) model to a water created by define_water
to determine coagulated
DOC. Coagulated UVA is from U.S. EPA (2001) equation 5-80. Note that the models rely on pH of coagulation. If
only raw water pH is known, utilize chemdose_ph
first.
chemdose_toc( water, alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
chemdose_toc( water, alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
water |
Source water object of class "water" created by |
alum |
Amount of hydrated aluminum sulfate added in mg/L: Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Amount of ferric chloride added in mg/L: FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
coeff |
String specifying the Edwards coefficients to be used from "Alum", "Ferric", "General Alum", "General Ferric", or "Low DOC" or named vector of coefficients, which must include: k1, k2, x1, x2, x3, b |
A water class object with an updated DOC, TOC, and UV254 concentration.
Edwards (1997)
U.S. EPA (2001)
See reference list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
water <- define_water(ph = 7, temp = 25, alk = 100, toc = 3.7, doc = 3.5, uv254 = .1) dosed_water <- chemdose_ph(water, alum = 30) %>% chemdose_toc(alum = 30, coeff = "Alum") dosed_water <- chemdose_ph(water, ferricsulfate = 30) %>% chemdose_toc(ferricsulfate = 30, coeff = "Ferric") dosed_water <- chemdose_ph(water, alum = 10, h2so4 = 10) %>% chemdose_toc(alum = 10, coeff = c( "x1" = 280, "x2" = -73.9, "x3" = 4.96, "k1" = -0.028, "k2" = 0.23, "b" = 0.068 ))
water <- define_water(ph = 7, temp = 25, alk = 100, toc = 3.7, doc = 3.5, uv254 = .1) dosed_water <- chemdose_ph(water, alum = 30) %>% chemdose_toc(alum = 30, coeff = "Alum") dosed_water <- chemdose_ph(water, ferricsulfate = 30) %>% chemdose_toc(ferricsulfate = 30, coeff = "Ferric") dosed_water <- chemdose_ph(water, alum = 10, h2so4 = 10) %>% chemdose_toc(alum = 10, coeff = c( "x1" = 280, "x2" = -73.9, "x3" = 4.96, "k1" = -0.028, "k2" = 0.23, "b" = 0.068 ))
This function allows chemdose_toc
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be used with "downstream" tidywater functions.
TOC, DOC, and UV254 will be updated based on input chemical doses.
chemdose_toc_chain( df, input_water = "defined_water", output_water = "coagulated_water", alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
chemdose_toc_chain( df, input_water = "defined_water", output_water = "coagulated_water", alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of Water class data to be used as the input for this function. Default is "defined_water". |
output_water |
name of the output column storing updated parameters with the class, Water. Default is "coagulated_water". |
alum |
Hydrated aluminum sulfate Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Ferric Chloride FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
coeff |
String specifying the Edwards coefficients to be used from "Alum", "Ferric", "General Alum", "General Ferric", or "Low DOC" or named vector of coefficients, which must include: k1, k2, x1, x2, x3, b |
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a coagulant(s) name matching a valid coagulant(s), the function will dose that coagulant(s). Note: The function can only dose a coagulant either a column or from the function arguments, not both.
The column names must match the chemical names as displayed in chemdose_toc
.
To see which chemicals can be passed into the function, see chemdose_toc
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with updated DOC, TOC, and UV254 concentrations.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(alum = 30) %>% chemdose_toc_chain(input_water = "dosed_chem_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( ferricchloride = seq(1, 12, 1), coeff = "Ferric" ) %>% chemdose_toc_chain(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_toc_chain(input_water = "balanced_water", alum = 40, coeff = "General Alum") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate(ferricchloride = seq(1, 12, 1)) %>% chemdose_toc_chain(input_water = "balanced_water", coeff = "Ferric") # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(alum = 30) %>% chemdose_toc_chain(input_water = "dosed_chem_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( ferricchloride = seq(1, 12, 1), coeff = "Ferric" ) %>% chemdose_toc_chain(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_toc_chain(input_water = "balanced_water", alum = 40, coeff = "General Alum") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate(ferricchloride = seq(1, 12, 1)) %>% chemdose_toc_chain(input_water = "balanced_water", coeff = "Ferric") # Optional: explicitly close multisession processing plan(sequential)
This function allows chemdose_toc
to be added to a piped data frame.
Its output is a data frame with updated TOC, DOC, and UV254.
chemdose_toc_once( df, input_water = "defined_water", alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
chemdose_toc_once( df, input_water = "defined_water", alum = 0, ferricchloride = 0, ferricsulfate = 0, coeff = "Alum" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of Water class data to be used as the input for this function. Default is "defined_water". |
alum |
Hydrated aluminum sulfate Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Ferric Chloride FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
coeff |
String specifying the Edwards coefficients to be used from "Alum", "Ferric", "General Alum", "General Ferric", or "Low DOC" or named vector of coefficients, which must include: k1, k2, x1, x2, x3, b |
The data input comes from a 'water' class column, as initialized in define_water
or balance_ions
.
If the input data frame has a column(s) name matching a valid coagulant(s), the function will dose that coagulant(s). Note: The function can only dose a coagulant as either a column or from the function arguments, not both.
The column names must match the coagulant names as displayed in chemdose_toc
.
To see which coagulants can be passed into the function, see chemdose_toc
.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with an updated DOC, TOC, and UV254 concentration.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(alum = 30) %>% chemdose_toc_once(input_water = "dosed_chem_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( ferricchloride = seq(1, 12, 1), coeff = "Ferric" ) %>% chemdose_toc_once(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_toc_once(input_water = "balanced_water", alum = 40, coeff = "General Alum") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate(ferricchloride = seq(1, 12, 1)) %>% chemdose_toc_once(input_water = "balanced_water", coeff = "Ferric") # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_ph_chain(alum = 30) %>% chemdose_toc_once(input_water = "dosed_chem_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( ferricchloride = seq(1, 12, 1), coeff = "Ferric" ) %>% chemdose_toc_once(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% chemdose_toc_once(input_water = "balanced_water", alum = 40, coeff = "General Alum") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate(ferricchloride = seq(1, 12, 1)) %>% chemdose_toc_once(input_water = "balanced_water", coeff = "Ferric") # Optional: explicitly close multisession processing plan(sequential)
A dataset containing conversion factors for calculating DBP formation
chloramine_conv
chloramine_conv
A dataframe with 17 rows and 3 columns
abbreviation of dbp species
full name of dbp species
specifies the percent of DBP formation predicted from chloramines compared to chlorine, assuming the same chlorine dose applied
U.S. EPA (2001), Table 5-10
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
This function takes a value and converts units based on compound name.
convert_units(value, formula, startunit = "mg/L", endunit = "M")
convert_units(value, formula, startunit = "mg/L", endunit = "M")
value |
Value to be converted |
formula |
Chemical formula of compound. Accepts compounds in mweights for conversions between g and mol or eq |
startunit |
Units of current value, currently accepts g/L; g/L CaCO3; g/L N; M; eq/L; and the same units with "m", "u", "n" prefixes |
endunit |
Desired units, currently accepts same as start units |
A numeric value for the converted parameter.
convert_units(50, "ca") # converts from mg/L to M by default convert_units(50, "ca", "mg/L", "mg/L CaCO3") convert_units(50, "ca", startunit = "mg/L", endunit = "eq/L")
convert_units(50, "ca") # converts from mg/L to M by default convert_units(50, "ca", "mg/L", "mg/L CaCO3") convert_units(50, "ca", startunit = "mg/L", endunit = "eq/L")
This converts a 'water' class to a dataframe with individual columns for each slot (water quality parameter) in the 'water'. This is useful for one-off checks and is applied in all 'fn_once' tidywater functions. For typical applications, there may be a 'fn_once' tidywater function that provides a more efficient solution.
convert_water(water)
convert_water(water)
water |
A water class object |
A data frame containing columns for all non-NA water slots.
library(dplyr) library(tidyr) # Generates 1 row dataframe example_df <- define_water(ph = 7, temp = 20, alk = 100) %>% convert_water() example_df <- water_df %>% define_water_chain() %>% mutate(to_dataframe = map(defined_water, convert_water)) %>% unnest(to_dataframe) %>% select(-defined_water)
library(dplyr) library(tidyr) # Generates 1 row dataframe example_df <- define_water(ph = 7, temp = 20, alk = 100) %>% convert_water() example_df <- water_df %>% define_water_chain() %>% mutate(to_dataframe = map(defined_water, convert_water)) %>% unnest(to_dataframe) %>% select(-defined_water)
This function is the same as convert_water
except it converts the units of following slots from
M to mg/L: na, ca, mg, k, cl, so4, hco3, co3, h2po4, hpo4, po4, ocl, bro3, f, fe, al. These slots are converted to
ug/L: br, mn. All other values remain unchanged.
convert_watermg(water)
convert_watermg(water)
water |
A water class object |
A data frame containing columns for all non-NA water slots with ions in mg/L.
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>% convert_watermg()
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>% convert_watermg()
A dataset containing correction factors for calculating DBP formation
dbp_correction
dbp_correction
A dataframe with 17 rows and 4 columns
abbreviation of dbp species
full name of dbp species
specifies the correction factor for modelling DBP formation within a treatment plant
specifies the correction factor for modelling DBP formation within the distribution system
U.S. EPA (2001), Table 5-7
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
A dataset containing coefficients for calculating DBP formation
dbpcoeffs
dbpcoeffs
A dataframe with 30 rows and 10 columns
abbreviation of dbp species
full name of dbp species
specifies which model the constants apply to, either treated or untreated water
First coefficient in DBP model
Second coefficient in DBP model, associated with TOC or DOC
Third coefficient in DBP model, associated with Cl2
Fourth coefficient in DBP model, associated with Br-
Fifth coefficient in DBP model, associated with temperature
Sixth coefficient in DBP model, associated with pH
Seventh coefficient in DBP model, associated with reaction time
U.S. EPA (2001)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
This function takes user-defined water quality parameters and creates an S4 "water" class object that forms the input and output of all tidywater models.
define_water( ph, temp = 25, alk, tot_hard, ca, mg, na, k, cl, so4, tot_ocl = 0, tot_po4 = 0, tot_nh3 = 0, tds, cond, toc, doc, uv254, br, f, fe, al, mn )
define_water( ph, temp = 25, alk, tot_hard, ca, mg, na, k, cl, so4, tot_ocl = 0, tot_po4 = 0, tot_nh3 = 0, tds, cond, toc, doc, uv254, br, f, fe, al, mn )
ph |
water pH |
temp |
Temperature in degree C |
alk |
Alkalinity in mg/L as CaCO3 |
tot_hard |
Total hardness in mg/L as CaCO3 |
ca |
Calcium in mg/L Ca2+ |
mg |
Magnesium in mg/L Mg2+ |
na |
Sodium in mg/L Na+ |
k |
Potassium in mg/L K+ |
cl |
Chloride in mg/L Cl- |
so4 |
Sulfate in mg/L SO42- |
tot_ocl |
Chlorine in mg/L as Cl2. Used when a starting water has a chlorine residual. |
tot_po4 |
Phosphate in mg/L as PO4 3-. Used when a starting water has a phosphate residual. |
tot_nh3 |
Total ammonia in mg/L as N |
tds |
Total Dissolved Solids in mg/L (optional if ions are known) |
cond |
Electrical conductivity in uS/cm (optional if ions are known) |
toc |
Total organic carbon (TOC) in mg/L |
doc |
Dissolved organic carbon (DOC) in mg/L |
uv254 |
UV absorbance at 254 nm (cm-1) |
br |
Bromide in ug/L Br- |
f |
Fluoride in mg/L F- |
fe |
Iron in mg/L Fe3+ |
al |
Aluminum in mg/L Al3+ |
mn |
Manganese in ug/L Mn2+ |
Carbonate balance is calculated and units are converted to mol/L. Ionic strength is determined from ions, TDS, or conductivity. Missing values are handled by defaulting to 0 or NA. Calcium hardness defaults to 65 manually specify all ions in the define_water arguments. The following equations are used to determine ionic strength: Ionic strength (if TDS provided): Crittenden et al. (2012) equation 5-38 Ionic strength (if electrical conductivity provided): Snoeyink & Jenkins (1980) Ionic strength (from ion concentrations): Lewis and Randall (1921), Crittenden et al. (2012) equation 5-37 Temperature correction of dielectric constant (relative permittivity): Harned and Owen (1958), Crittenden et al. (2012) equation 5-45.
A water class object where slots are filled or calculated based on input parameters.
water_missingions <- define_water(ph = 7, temp = 15, alk = 100, tds = 10) water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1)
water_missingions <- define_water(ph = 7, temp = 15, alk = 100, tds = 10) water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1)
This function allows define_water
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be chained with "downstream" tidywater functions.
define_water_chain(df, output_water = "defined_water")
define_water_chain(df, output_water = "defined_water")
df |
a data frame containing columns with all the parameters listed in |
output_water |
name of the output column storing updated parameters with the class, water. Default is "defined_water". |
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_once() example_df <- water_df %>% define_water_chain(output_water = "This is a column of water") %>% balance_ions_once(input_water = "This is a column of water") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_once() #' #Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_once() example_df <- water_df %>% define_water_chain(output_water = "This is a column of water") %>% balance_ions_once(input_water = "This is a column of water") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% balance_ions_once() #' #Optional: explicitly close multisession processing plan(sequential)
This function allows define_water
to be added to a piped data frame.
It outputs all carbonate calculations and other parameters in a data frame.
tidywater functions cannot be added after this function because they require a 'water' class input.
define_water_once(df)
define_water_once(df)
df |
a data frame containing columns with all the parameters listed in |
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing columns that were filled or calculated based on define_water.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_once() # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_once() # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_once() # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_once() # Optional: explicitly close multisession processing plan(sequential)
Equilibrium constants (k) and corresponding standard enthalpy of reaction values (deltah) for significant acids in water influencing pH at equilibrium. Includes carbonate, sulfate, phosphate, and hypochlorite. Standard enthalpy of reaction is calculated by taking the sum of the enthalpy of formation of each individual component minus the enthalpy of formation of the final product. e.g., the standard enthalpy of reaction for water can be calculated as: deltah_h2o = deltah_f_oh + deltah_f_h - deltah_f_h2o = -230 + 0 - (-285.83) = 55.83 kJ/mol. See MWH (2012) example 5-5 and Benjamin (2002) eq. 2.96.
discons
discons
A dataframe with 8 rows and 3 columns
Coefficient type
Equilibrium constant
Standard enthalpy in J/mol
Benjamin (2015) Appendix A.1 and A.2.
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
This function takes a water data frame defined by define_water
and outputs a dataframe of the controlling lead solid and total lead solubility.
Lead solid solubility is calculated based on controlling solid.
Total dissolved lead species (tot_dissolved_pb, M) are calculated based on lead complex calculations.
Some lead solids have two k-constant options. The function will default to the EPA's default constants.
The user may change the constants to hydroxypyromorphite = "Zhu" or pyromorphite = "Xie" or laurionite = "Lothenbach"
dissolve_pb( water, hydroxypyromorphite = "Schock", pyromorphite = "Topolska", laurionite = "Nasanen" )
dissolve_pb( water, hydroxypyromorphite = "Schock", pyromorphite = "Topolska", laurionite = "Nasanen" )
water |
Source water object of class "water" created by |
hydroxypyromorphite |
defaults to "Schock", the constant, K, developed by Schock et al (1996). Can also use "Zhu". |
pyromorphite |
defaults to "Topolska", the constant, K, developed by Topolska et al (2016). Can also use "Xie". |
laurionite |
defaults to "Nasanen", the constant, K, developed by Nasanen & Lindell (1976). Can also use "Lothenbach". |
The solid with lowest solubility will form the lead scale (controlling lead solid).
Make sure that total dissolved solids, conductivity, or ca, na, cl, so4 are used in 'define_water' so that an ionic strength is calculated.
A data frame containing only the controlling lead solid and modeled dissolved lead concentration.
Code is from EPA's TELSS lead solubility dashboard https://github.com/USEPA/TELSS which is licensed under MIT License: Permission is hereby granted, free of charge, to any person obtaining a copy of this software and associated documentation files (the "Software"), to deal in the Software without restriction, including without limitation the rights to use, copy, modify, merge, publish, distribute, sublicense, and/or sell copies of the Software, and to permit persons to whom the Software is furnished to do so, subject to the following conditions: The above copyright notice and this permission notice shall be included in all copies or substantial portions of the Software.
Wahman et al. (2021)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
example_pb <- define_water( ph = 7.5, temp = 25, alk = 93, cl = 240, tot_po4 = 0, so4 = 150, tds = 200 ) %>% dissolve_pb() example_pb <- define_water( ph = 7.5, temp = 25, alk = 93, cl = 240, tot_po4 = 0, so4 = 150, tds = 200 ) %>% dissolve_pb(pyromorphite = "Xie")
example_pb <- define_water( ph = 7.5, temp = 25, alk = 93, cl = 240, tot_po4 = 0, so4 = 150, tds = 200 ) %>% dissolve_pb() example_pb <- define_water( ph = 7.5, temp = 25, alk = 93, cl = 240, tot_po4 = 0, so4 = 150, tds = 200 ) %>% dissolve_pb(pyromorphite = "Xie")
This function allows dissolve_pb
to be added to a piped data frame.
Two additional columns will be added to the dataframe; the name of the controlling lead solid, and total dissolved lead (M).
dissolve_pb_once( df, input_water = "defined_water", output_col_solid = "controlling_solid", output_col_result = "pb", hydroxypyromorphite = "Schock", pyromorphite = "Topolska", laurionite = "Nasanen", water_prefix = TRUE )
dissolve_pb_once( df, input_water = "defined_water", output_col_solid = "controlling_solid", output_col_result = "pb", hydroxypyromorphite = "Schock", pyromorphite = "Topolska", laurionite = "Nasanen", water_prefix = TRUE )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input. Default is "defined_water". |
output_col_solid |
name of the output column storing the controlling lead solid. Default is "controlling_solid". |
output_col_result |
name of the output column storing dissolved lead in M. Default is "pb". |
hydroxypyromorphite |
defaults to "Schock", the constant, K, developed by Schock et al (1996). Can also use "Zhu". |
pyromorphite |
defaults to "Topolska", the constant, K, developed by Topolska et al (2016). Can also use "Xie". |
laurionite |
defaults to "Nasanen", the constant, K, developed by Nasanen & Lindell (1976). Can also use "Lothenbach". |
water_prefix |
name of the input water used for the calculation, appended to the start of output columns. Default is TRUE. Chenge to FALSE to remove the water prefix from output column names. |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
Use the 'output_col_solid' and 'output_col_result' arguments to name the ouput columns for the controlling lead solid
and total dissolved lead, respectively. The input 'water' used for the calculation will be appended to the
start of these output columns. Omit the input 'water' in the output columns, set 'water_prefix' to FALSE (default is TRUE).
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing the controlling lead solid and modeled dissolved lead concentration as new columns.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% dissolve_pb_once(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% dissolve_pb_once(output_col_result = "dissolved_lead", pyromorphite = "Xie") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% dissolve_pb_once(output_col_result = "dissolved_lead", laurionite = "Lothenbach") # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% dissolve_pb_once(input_water = "balanced_water") example_df <- water_df %>% define_water_chain() %>% dissolve_pb_once(output_col_result = "dissolved_lead", pyromorphite = "Xie") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% dissolve_pb_once(output_col_result = "dissolved_lead", laurionite = "Lothenbach") # Optional: explicitly close multisession processing plan(sequential)
A dataset containing coefficients from the Edwards (1997) model for coagulation TOC removal.
edwardscoeff
edwardscoeff
A dataframe with 5 rows and 7 columns:
Coefficient type
x3 parameter
x2 parameter
x1 parameter
k1 parameter
k2 parameter
b parameter
Edwards (1997) Table 2.
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
A dataset containing equilibrium constants for lead solubility
leadsol_constants
leadsol_constants
A dataframe with 38 rows and 3 columns
Solids:
Name of lead solid or complex with possible _letter to cite different references
Reference ID for constants
Equilibrium constant log value
Source for equilibrium constant value
Benjamin (2010)
Lothenbach et al. (1999)
Nasanen & Lindell (1976)
Powell et al. (2009)
Powell et al. (2005)
Schock et al. (1996)
Topolska et al. (2016)
Xie & Giammar (2007)
Zhu et al. (2015)
Wahman et al. (2021)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
A dataset containing the molar weights of several compounds in g/mol. Column names are lowercase chemical formulas (with no charge), with the exception of the following coagulants: alum = Al2(SO4)3*14H2O, ferricchloride = FeCl3, ferricsulfate = Fe2(SO4)3*8.8H2O,
mweights
mweights
A dataframe with one row and one column per compound
Calculates bromate (BrO3-, ug/L) formation based on selected model. Required arguments include an object of class "water"
created by define_water
ozone dose, reaction time, and desired model.
The function also requires additional water quality parameters defined in define_water
including bromide, DOC or UV254 (depending on the model), pH, alkalinity (depending on the model), and
optionally, ammonia (added when defining water using the 'tot_nh3' argument.)
ozonate_bromate(water, dose, time, model = "Ozekin")
ozonate_bromate(water, dose, time, model = "Ozekin")
water |
Source water object of class "water" created by |
dose |
Applied ozone dose (mg/L as O3). Results typically valid for 1-10 mg/L, but varies depending on model. |
time |
Reaction time (minutes). Results typically valid for 1-120 minutes, but varies depending on model. |
model |
Model to apply. One of c("Ozekin", "Sohn", "Song", "Galey", "Siddiqui") |
A water class object with calculated bromate (ug/L).
Ozekin (1994), Sohn et al (2004), Song et al (1996), Galey et al (1997), Siddiqui et al (1994)
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
example_dbp <- suppressWarnings(define_water(8, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% ozonate_bromate(dose = 1.5, time = 5, model = "Ozekin") example_dbp <- suppressWarnings(define_water(7.5, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% ozonate_bromate(dose = 3, time = 15, model = "Sohn")
example_dbp <- suppressWarnings(define_water(8, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% ozonate_bromate(dose = 1.5, time = 5, model = "Ozekin") example_dbp <- suppressWarnings(define_water(7.5, 20, 66, toc = 4, uv254 = .2, br = 50)) %>% ozonate_bromate(dose = 3, time = 15, model = "Sohn")
This function takes a water defined by define_water
and the first order decay curve parameters
from an ozone dose and outputs a dataframe of acutal CT, and log removal for giardia, virus, and crypto
ozonate_ct(water, time, dose, kd, baffle)
ozonate_ct(water, time, dose, kd, baffle)
water |
Source water object of class "water" created by |
time |
Retention time of disinfection segment in minutes. |
dose |
Ozone dose in mg/L. This value can also be the y intercept of the decay curve (often slightly lower than ozone dose.) |
kd |
First order decay constant. This parameter is optional. If not specified, the default ozone decay equations will be used. |
baffle |
Baffle factor - unitless value between 0 and 1. |
First order decay curve for ozone has the form: 'residual = dose * exp(kd*time)'. kd should be a negative number. Actual CT is an integration of the first order curve. The first 30 seconds are removed from the integral to account for instantaneous demand.
A data frame containing actual CT, giardia log removal, virus log removal, and crypto log removal.
USEPA (2020) Equation 4-4 through 4-7 https://www.epa.gov/system/files/documents/2022-02/disprof_bench_3rules_final_508.pdf
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
# Use kd from experimental data (recommended): define_water(ph = 7.5, temp = 25) %>% ozonate_ct(time = 10, dose = 2, kd = -0.5, baffle = 0.9) define_water(ph = 7.5, alk = 100, doc = 2, uv254 = .02, br = 50) %>% ozonate_ct(time = 10, dose = 2, baffle = 0.5)
# Use kd from experimental data (recommended): define_water(ph = 7.5, temp = 25) %>% ozonate_ct(time = 10, dose = 2, kd = -0.5, baffle = 0.9) define_water(ph = 7.5, alk = 100, doc = 2, uv254 = .02, br = 50) %>% ozonate_ct(time = 10, dose = 2, baffle = 0.5)
Calculates DOC concentration multiple linear regression model found in 2-METHYLISOBORNEOL AND NATURAL ORGANIC MATTER
ADSORPTION BY POWDERED ACTIVATED CARBON by HYUKJIN CHO (2007)
Required arguments include an object of class "water"
created by define_water
initial DOC concentration, amount of PAC added to system, contact time with PAC, type of PAC
water must contain DOC or TOC value.
pac_toc(water, dose, time, type = "bituminous")
pac_toc(water, dose, time, type = "bituminous")
water |
Source water object of class "water" created by |
dose |
Applied PAC dose (mg/L). Model results are valid for doses concentrations between 5 and 30 mg/L. |
time |
Contact time (minutes). Model results are valid for reaction times between 10 and 1440 minutes |
type |
Type of PAC applied, either "bituminous", "lignite", "wood". |
The function will calculate DOC concentration by PAC adsorption in drinking water treatment. UV254 concentrations are predicted based on a linear relationship with DOC.
A water class object with post-PAC predicted DOC and UV254.
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
CHO(2007)
water <- define_water(toc = 2.5, uv254 = .05, doc = 1.5) %>% pac_toc(dose = 15, time = 50, type = "wood")
water <- define_water(toc = 2.5, uv254 = .05, doc = 1.5) %>% pac_toc(dose = 15, time = 50, type = "wood")
This function allows pac_toc
to be added to a piped data frame.
Its output is a 'water' class, and can therefore be used with "downstream" tidywater functions.
pac_toc_chain( df, input_water = "defined_water", output_water = "pac_water", dose = 0, time = 0, type = "bituminous" )
pac_toc_chain( df, input_water = "defined_water", output_water = "pac_water", dose = 0, time = 0, type = "bituminous" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
output_water |
name of the output column storing updated parameters with the class, water. Default is "disinfected_water". |
dose |
Applied PAC dose (mg/L). Model results are valid for doses concentrations between 5 and 30 mg/L. |
time |
Contact time (minutes). Model results are valid for reaction times between 10 and 1440 minutes |
type |
Type of PAC applied, either "bituminous", "lignite", "wood". |
The data input comes from a 'water' class column, as initialized in define_water
.
If the input data frame has a dose, time or type column, the function will use those columns. Note: The function can only take dose, time, and type inputs as EITHER a column or from the function arguments, not both.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing a water class column with updated DOC, TOC, and UV254 concentrations.
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
CHO(2007)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_chain(input_water = "raw", dose = 10, time = 20) example_df <- water_df %>% define_water_chain("raw") %>% mutate(dose = seq(11, 22, 1), time = 30) %>% pac_toc_chain(input_water = "raw") example_df <- water_df %>% define_water_chain("raw") %>% mutate(time = 8) %>% pac_toc_chain( input_water = "raw", dose = 6, type = "wood" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_chain(input_water = "raw", dose = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_chain(input_water = "raw", dose = 10, time = 20) example_df <- water_df %>% define_water_chain("raw") %>% mutate(dose = seq(11, 22, 1), time = 30) %>% pac_toc_chain(input_water = "raw") example_df <- water_df %>% define_water_chain("raw") %>% mutate(time = 8) %>% pac_toc_chain( input_water = "raw", dose = 6, type = "wood" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_chain(input_water = "raw", dose = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
PAC = powdered activated carbon
pac_toc_once( df, input_water = "defined_water", dose = 0, time = 0, type = "bituminous" )
pac_toc_once( df, input_water = "defined_water", dose = 0, time = 0, type = "bituminous" )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input for this function. Default is "defined_water". |
dose |
Applied PAC dose (mg/L). Model results are valid for doses concentrations between 5 and 30 mg/L. |
time |
Contact time (minutes). Model results are valid for reaction times between 10 and 1440 minutes |
type |
Type of PAC applied, either "bituminous", "lignite", "wood". |
This function allows pac_toc
to be added to a piped data frame.
Its output is a data frame containing a water with updated TOC, DOC, and UV254.
The data input comes from a 'water' class column, as initialized in define_water
.
If the input data frame has a dose, time or type column, the function will use those columns. Note: The function can only take dose, time, and type inputs as EITHER a column or from the function arguments, not both.
tidywater functions cannot be added after this function because they require a 'water' class input.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame with an updated DOC, TOC, and UV254 concentration.
See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
CHO(2007)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_once(input_water = "raw", dose = 10, time = 20) example_df <- water_df %>% define_water_chain("raw") %>% mutate(dose = seq(5, 60, 5), time = 30) %>% pac_toc_once(input_water = "raw") example_df <- water_df %>% define_water_chain("raw") %>% mutate(time = 8) %>% pac_toc_once( input_water = "raw", dose = 6, type = "wood" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_once(input_water = "raw", dose = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_once(input_water = "raw", dose = 10, time = 20) example_df <- water_df %>% define_water_chain("raw") %>% mutate(dose = seq(5, 60, 5), time = 30) %>% pac_toc_once(input_water = "raw") example_df <- water_df %>% define_water_chain("raw") %>% mutate(time = 8) %>% pac_toc_once( input_water = "raw", dose = 6, type = "wood" ) # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain("raw") %>% pac_toc_once(input_water = "raw", dose = 4, time = 8) # Optional: explicitly close multisession processing plan(sequential)
This function takes a water data frame defined by define_water
and outputs an ion balance plot.
plot_ions(water)
plot_ions(water)
water |
Source water vector created by link function here |
A ggplot object displaying the water's ion balance.
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) plot_ions(water_defined)
water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) plot_ions(water_defined)
This function plucks one or more selected parameters from selected columns of 'water' class objects.
The names of the output columns will follow the form 'water_parameter'
To view all slots as columns, please use one of the 'fn_once' functions or convert_water
.
pluck_water(df, input_waters = c("defined_water"), parameter)
pluck_water(df, input_waters = c("defined_water"), parameter)
df |
a data frame containing a water class column, which has already
been computed using |
input_waters |
vector of names of the columns of water class data to be used as the input for this function. |
parameter |
vector of water class parameters to view outside the water column |
A data frame containing columns of selected parameters from a list of water class objects.
library(dplyr) library(furrr) library(purrr) library(tidyr) pluck_example <- water_df %>% define_water_chain() %>% pluck_water(parameter = "tot_co3") pluck_example <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% pluck_water(input_waters = c("defined_water", "balanced_water"), parameter = c("na", "cl")) plan(multisession, workers = 2) # Remove the workers argument to use all available compute pluck_example <- water_df %>% define_water_chain() %>% pluck_water(parameter = c("ph", "alk")) # Optional: explicitly close multisession processing plan(sequential)
library(dplyr) library(furrr) library(purrr) library(tidyr) pluck_example <- water_df %>% define_water_chain() %>% pluck_water(parameter = "tot_co3") pluck_example <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% pluck_water(input_waters = c("defined_water", "balanced_water"), parameter = c("na", "cl")) plan(multisession, workers = 2) # Remove the workers argument to use all available compute pluck_example <- water_df %>% define_water_chain() %>% pluck_water(parameter = c("ph", "alk")) # Optional: explicitly close multisession processing plan(sequential)
This function takes a chemical dose in mg/L, plant flow, chemical strength, and $/lb and calculates cost.
solvecost_chem(dose, flow, strength = 100, cost, time = "day")
solvecost_chem(dose, flow, strength = 100, cost, time = "day")
dose |
Chemical dose in mg/L as chemical |
flow |
Plant flow in MGD |
strength |
Chemical product strength in percent. Defaults to 100 percent. |
cost |
Chemical product cost in $/lb |
time |
Desired output units, one of c("day", "month", "year"). Defaults to "day". |
A numeric value for chemical cost, $/time.
alum_cost <- solvecost_chem(dose = 20, flow = 10, strength = 49, cost = .22)
alum_cost <- solvecost_chem(dose = 20, flow = 10, strength = 49, cost = .22)
This function takes number of FTE and annual $/FTE and determines labor cost
solvecost_labor(fte, cost, time = "day")
solvecost_labor(fte, cost, time = "day")
fte |
Number of FTEs. Can be decimal. |
cost |
$/year per FTE |
time |
Desired output units, one of c("day", "month", "year"). Defaults to "day". |
A numeric value for labor $/time.
laborcost <- solvecost_labor(1.5, 50000)
laborcost <- solvecost_labor(1.5, 50000)
This function takes kW,
solvecost_power(power, utilization = 100, cost, time = "day")
solvecost_power(power, utilization = 100, cost, time = "day")
power |
Power consumed in kW |
utilization |
Amount of time equipment is running in percent. Defaults to continuous. |
cost |
Power cost in $/kWhr |
time |
Desired output units, one of c("day", "month", "year"). Defaults to "day". |
A numeric value for power, $/time.
powercost <- solvecost_power(50, 100, .08)
powercost <- solvecost_power(50, 100, .08)
This function takes coagulant doses in mg/L as chemical, removed turbidity, and cost ($/lb) to determine disposal cost.
solvecost_solids( alum = 0, ferricchloride = 0, ferricsulfate = 0, flow, turb, b = 1.5, cost, time = "day" )
solvecost_solids( alum = 0, ferricchloride = 0, ferricsulfate = 0, flow, turb, b = 1.5, cost, time = "day" )
alum |
Hydrated aluminum sulfate Al2(SO4)3*14H2O + 6HCO3 -> 2Al(OH)3(am) +3SO4 + 14H2O + 6CO2 |
ferricchloride |
Ferric Chloride FeCl3 + 3HCO3 -> Fe(OH)3(am) + 3Cl + 3CO2 |
ferricsulfate |
Amount of ferric sulfate added in mg/L: Fe2(SO4)3*8.8H2O + 6HCO3 -> 2Fe(OH)3(am) + 3SO4 + 8.8H2O + 6CO2 |
flow |
Plant flow in MGD |
turb |
Turbidity removed in NTU |
b |
Correlation factor from turbidity to suspended solids. Defaults to 1.5. |
cost |
Disposal cost in $/lb |
time |
Desired output units, one of c("day", "month", "year"). Defaults to "day". |
A numeric value for disposal costs, $/time.
https://water.mecc.edu/courses/ENV295Residuals/lesson3b.htm#:~:text=From
alum_solidscost <- solvecost_solids(alum = 50, flow = 10, turb = 2, cost = 0.05)
alum_solidscost <- solvecost_solids(alum = 50, flow = 10, turb = 2, cost = 0.05)
This function calculates the required amount of a chemical to dose based on a target alkalinity and existing water quality. Returns numeric value for dose in mg/L. Uses uniroot on the chemdose_ph function.
solvedose_alk(water, target_alk, chemical)
solvedose_alk(water, target_alk, chemical)
water |
Source water of class "water" created by |
target_alk |
The final alkalinity in mg/L as CaCO3 to be achieved after the specified chemical is added. |
chemical |
The chemical to be added. Current supported chemicals include: acids: "hcl", "h2so4", "h3po4", "co2", bases: "naoh", "na2co3", "nahco3", "caoh2", "mgoh2" |
A numeric value for the required chemical dose.
dose_required <- define_water(ph = 7.9, temp = 22, alk = 100, 80, 50) %>% solvedose_alk(target_alk = 150, "naoh")
dose_required <- define_water(ph = 7.9, temp = 22, alk = 100, 80, 50) %>% solvedose_alk(target_alk = 150, "naoh")
This function allows solvedose_alk
to be added to a piped data frame.
Its output is a chemical dose in mg/L.
solvedose_alk_once( df, input_water = "defined_water", output_column = "dose_required", target_alk = NULL, chemical = NULL )
solvedose_alk_once( df, input_water = "defined_water", output_column = "dose_required", target_alk = NULL, chemical = NULL )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input. Default is "defined_water". |
output_column |
name of the output column storing doses in mg/L. Default is "dose_required". |
target_alk |
set a goal for alkalinity using the function argument or a data frame column |
chemical |
select the chemical to be used to reach the desired alkalinity using function argument or data frame column |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
If the input data frame has column(s) named "target_alk" or "chemical", the function will use the column(s)
as function argument(s). If these columns aren't present, specify "target_alk" or "chemical" as function arguments.
The chemical names must match the chemical names as displayed in solvedose_alk
.
To see which chemicals can be dosed, see solvedose_alk
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing the original data frame and columns for target alkalinity, chemical dosed, and required chemical dose.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( target_alk = 300, chemical = rep(c("naoh", "na2co3"), 6) ) %>% solvedose_alk_once() # When the selected chemical can't raise the alkalinity, the dose_required will be NA # Eg,soda ash can't bring the alkalinity to 100 when the water's alkalinity is already at 200. example_df <- water_df %>% define_water_chain() %>% solvedose_alk_once(input_water = "defined_water", target_alk = 100, chemical = "na2co3") example_df <- water_df %>% define_water_chain() %>% mutate(target_alk = seq(100, 210, 10)) %>% solvedose_alk_once(chemical = "na2co3") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% mutate(target_alk = seq(100, 210, 10)) %>% solvedose_alk_once(chemical = "na2co3") # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% balance_ions_chain() %>% mutate( target_alk = 300, chemical = rep(c("naoh", "na2co3"), 6) ) %>% solvedose_alk_once() # When the selected chemical can't raise the alkalinity, the dose_required will be NA # Eg,soda ash can't bring the alkalinity to 100 when the water's alkalinity is already at 200. example_df <- water_df %>% define_water_chain() %>% solvedose_alk_once(input_water = "defined_water", target_alk = 100, chemical = "na2co3") example_df <- water_df %>% define_water_chain() %>% mutate(target_alk = seq(100, 210, 10)) %>% solvedose_alk_once(chemical = "na2co3") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% mutate(target_alk = seq(100, 210, 10)) %>% solvedose_alk_once(chemical = "na2co3") # Optional: explicitly close multisession processing plan(sequential)
solvedose_ph
calculates the required amount of a chemical to dose based on a target pH and existing water quality.
The function takes an object of class "water" created by define_water
, and user-specified chemical and target pH
and returns a numeric value for the required dose in mg/L.
solvedose_ph
uses uniroot
on chemdose_ph
to match the required dose for the requested pH target.
solvedose_ph(water, target_ph, chemical)
solvedose_ph(water, target_ph, chemical)
water |
Source water of class "water" created by |
target_ph |
The final pH to be achieved after the specified chemical is added. |
chemical |
The chemical to be added. Current supported chemicals include: acids: "hcl", "h2so4", "h3po4", "co2"; bases: "naoh", "na2co3", "nahco3", "caoh2", "mgoh2" |
A numeric value for the required chemical dose.
water <- define_water(ph = 7, temp = 25, alk = 10) # Calculate required dose of lime to reach pH 8 solvedose_ph(water, target_ph = 8, chemical = "caoh2")
water <- define_water(ph = 7, temp = 25, alk = 10) # Calculate required dose of lime to reach pH 8 solvedose_ph(water, target_ph = 8, chemical = "caoh2")
This function allows solvedose_ph
to be added to a piped data frame.
Its output is a chemical dose in mg/L.
solvedose_ph_once( df, input_water = "defined_water", output_column = "dose_required", target_ph = NULL, chemical = NULL )
solvedose_ph_once( df, input_water = "defined_water", output_column = "dose_required", target_ph = NULL, chemical = NULL )
df |
a data frame containing a water class column, which has already been computed using
|
input_water |
name of the column of water class data to be used as the input. Default is "defined_water". |
output_column |
name of the output column storing doses in mg/L. Default is "dose_required". |
target_ph |
set a goal for pH using the function argument or a data frame column |
chemical |
select the chemical to be used to reach the desired pH using function argument or data frame column |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
If the input data frame has column(s) named "target_ph" or "chemical", the function will use the column(s)
as function argument(s). If these columns aren't present, specify "target_ph" or "chemical" as function arguments.
The chemical names must match the chemical names as displayed in solvedose_ph
.
To see which chemicals can be dosed, see solvedose_ph
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing the original data frame and columns for target pH, chemical dosed, and required chemical dose.
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% mutate( target_ph = 10, chemical = rep(c("naoh", "mgoh2"), 6) ) %>% solvedose_ph_once(input_water = "defined_water") example_df <- water_df %>% define_water_chain() %>% solvedose_ph_once(input_water = "defined_water", target_ph = 8.8, chemical = "naoh") example_df <- water_df %>% define_water_chain() %>% mutate(target_ph = seq(9, 10.1, .1)) %>% solvedose_ph_once(chemical = "naoh") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% mutate(target_ph = seq(9, 10.1, .1)) %>% solvedose_ph_once(chemical = "naoh") # Optional: explicitly close multisession processing plan(sequential)
library(purrr) library(furrr) library(tidyr) library(dplyr) example_df <- water_df %>% define_water_chain() %>% mutate( target_ph = 10, chemical = rep(c("naoh", "mgoh2"), 6) ) %>% solvedose_ph_once(input_water = "defined_water") example_df <- water_df %>% define_water_chain() %>% solvedose_ph_once(input_water = "defined_water", target_ph = 8.8, chemical = "naoh") example_df <- water_df %>% define_water_chain() %>% mutate(target_ph = seq(9, 10.1, .1)) %>% solvedose_ph_once(chemical = "naoh") # Initialize parallel processing plan(multisession, workers = 2) # Remove the workers argument to use all available compute example_df <- water_df %>% define_water_chain() %>% mutate(target_ph = seq(9, 10.1, .1)) %>% solvedose_ph_once(chemical = "naoh") # Optional: explicitly close multisession processing plan(sequential)
This function takes a chemical dose in mg/L, plant flow, and chemical strength and calculates lb/day of product
solvemass_chem(dose, flow, strength = 100)
solvemass_chem(dose, flow, strength = 100)
dose |
Chemical dose in mg/L as chemical |
flow |
Plant flow in MGD |
strength |
Chemical product strength in percent. Defaults to 100 percent. |
A numeric value for the chemical mass in lb/day.
alum_mass <- solvemass_chem(dose = 20, flow = 10, strength = 49)
alum_mass <- solvemass_chem(dose = 20, flow = 10, strength = 49)
This function applies the ozone decay model to a water created by define_water
from U.S. EPA (2001) equation 5-128.
solveresid_o3(water, dose, time)
solveresid_o3(water, dose, time)
water |
Source water object of class "water" created by |
dose |
Applied ozone dose in mg/L |
time |
Ozone contact time in minutes |
A numeric value for the resiudal ozone.
U.S. EPA (2001)
See reference list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References
ozone_resid <- define_water(7, 20, 100, doc = 2, toc = 2.2, uv254 = .02, br = 50) %>% solveresid_o3(dose = 2, time = 10)
ozone_resid <- define_water(7, 20, 100, doc = 2, toc = 2.2, uv254 = .02, br = 50) %>% solveresid_o3(dose = 2, time = 10)
This function allows solveresid_o3
to be added to a piped data frame.
Once additional column will be added to the data frame; the residual ozone dose (mg/L)
solveresid_o3_once(df, input_water = "defined_water", dose = 0, time = 0)
solveresid_o3_once(df, input_water = "defined_water", dose = 0, time = 0)
df |
a data frame containing a water class column, which has already been computed using |
input_water |
name of the column of Water class data to be used as the input for this function. Default is "defined_water". |
dose |
Applied ozone dose in mg/L |
time |
Ozone contact time in minutes |
The data input comes from a 'water' class column, initialized in define_water
or balance_ions
.
For large datasets, using 'fn_once' or 'fn_chain' may take many minutes to run. These types of functions use the furrr package for the option to use parallel processing and speed things up. To initialize parallel processing, use 'plan(multisession)' or 'plan(multicore)' (depending on your operating system) prior to your piped code with the 'fn_once' or 'fn_chain' functions. Note, parallel processing is best used when your code block takes more than a minute to run, shorter run times will not benefit from parallel processing.
A data frame containing the original data frame and columns for ozone dosed, time, and ozone residual.
library(dplyr) ozone_resid <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% solveresid_o3_once(dose = 2, time = 10) ozone_resid <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% mutate( dose = seq(1, 12, 1), time = seq(2, 24, 2) ) %>% solveresid_o3_once()
library(dplyr) ozone_resid <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% solveresid_o3_once(dose = 2, time = 10) ozone_resid <- water_df %>% mutate(br = 50) %>% define_water_chain() %>% mutate( dose = seq(1, 12, 1), time = seq(2, 24, 2) ) %>% solveresid_o3_once()
This function takes a water data frame defined by define_water
and outputs a formatted summary table of
specified water quality parameters.
summarise_wq()
and summarize_wq()
are synonyms.
summarize_wq(water, params = c("general")) summarise_wq(water, params = c("general"))
summarize_wq(water, params = c("general")) summarise_wq(water, params = c("general"))
water |
Source water vector created by |
params |
List of water quality parameters to be summarized. Options include "general", "ions", "corrosion", and "dbps". Defaults to "general" only. |
Use calculate_corrosion
for corrosivity indicators and chemdose_dbp
for modeled DBP concentrations.
A knitr_kable table of specified water quality parameters.
# Summarize general parameters water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) summarize_wq(water_defined) # Summarize major cations and anions summarize_wq(water_defined, params = list("ions"))
# Summarize general parameters water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) summarize_wq(water_defined) # Summarize major cations and anions summarize_wq(water_defined, params = list("ions"))
A dataset containing fabricated water quality to use as tidywater inputs. Parameters are set to reasonable water quality ranges. Parameters are as follows:
water_df
water_df
A dataframe with 12 rows and 11 columns:
pH in standard units (SU)
Temperature in degree C
Alkalinity in mg/L as CaCO3
Total hardness in mg/L as CaCO3
Calcium hardness in mg/L as CaCO3
Sodium in mg/L Na+
Potassium in mg/L K+
Chloride in mg/L Cl-
Sulfate in mg/L SO42-
Total chlorine in mg/L as Cl2
Total phosphate in mg/L as PO42-
Fabricated for use in examples.