Package 'tidywater'

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

Help Index


Add Na, K, Cl, or SO4 to balance overall charge in a water

Description

This function takes a water defined by define_water and balances charge.

Usage

balance_ions(water)

Arguments

water

Water created with define_water, which may have some ions set to 0 when unknown

Details

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.

Value

A water class object with updated ions to balance water charge.

Examples

water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>%
  balance_ions()

Apply 'balance_ions' within a dataframe and output a column of 'water' class to be chained to other tidywater functions

Description

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.

Usage

balance_ions_chain(
  df,
  input_water = "defined_water",
  output_water = "balanced_water"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain

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".

Details

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.

Value

A data frame containing a water class column with updated ions to balance water charge.

See Also

balance_ions

Examples

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)

Apply 'balance_ions' function and output a dataframe

Description

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.

Usage

balance_ions_once(df, input_water = "defined_water")

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain

input_water

name of the column of water class data to be used as the input for this function. Default is "defined_water".

Details

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.

Value

A dataframe with updated ions to balance water charge

See Also

balance_ions

Examples

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)

Determine TOC removal from biofiltration using Terry & Summers BDOC model

Description

This function applies the Terry model to a water created by define_water to determine biofiltered DOC (mg/L).

Usage

biofilter_toc(water, ebct, ozonated = TRUE)

Arguments

water

Source water object of class "water" created by define_water.

ebct

The empty bed contact time (min) used for the biofilter

ozonated

Logical; TRUE if the water is ozonated (default), FALSE otherwise

Value

A water class object with modeled DOC removal from biofiltration.

Source

Terry and Summers 2018

Examples

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)

Determine blended water quality from multiple waters based on mass balance and acid/base equilibrium

Description

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.

Usage

blend_waters(waters, ratios)

Arguments

waters

Vector of source waters created by define_water

ratios

Vector of ratios in the same order as waters. (Blend ratios must sum to 1)

Value

A water class object with blended water quality parameters.

See Also

define_water

Examples

water1 <- define_water(7, 20, 50)
water2 <- define_water(7.5, 20, 100, tot_nh3 = 2)
blend_waters(c(water1, water2), c(.4, .6))

Apply 'blend_waters' within a dataframe and output a column of 'water' class to be chained to other tidywater functions

Description

This function allows blend_waters to be added to a piped data frame.

Usage

blend_waters_chain(df, waters, ratios, output_water = "blended_water")

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain,

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".

Details

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.

Value

A data frame with a water class column containing updated ions and pH.

See Also

blend_waters

Examples

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)

Apply 'blend_waters' to a dataframe and output 'water' slots as a dataframe

Description

This function allows blend_waters to be added to a piped data frame.

Usage

blend_waters_once(df, waters, ratios)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain

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)

Details

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.

Value

A data frame with blended water quality parameters.

See Also

blend_waters

Examples

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)

Data frame of bromate coefficients for predicting bromate formation during ozonation

Description

A dataset containing coefficients for calculating ozone formation

Usage

bromatecoeffs

Format

A dataframe with 30 rows and 10 columns

model

First author of source model

ammonia

Either T or F, depending on whether the model applies to waters with ammonia present.

A

First coefficient in bromate model

a

Exponent in bromate model, associated with Br-

b

Exponent in bromate model, associated with DOC

c

Exponent in bromate model, associated with UVA

d

Exponent in bromate model, associated with pH

e

Exponent in bromate model, associated with Alkalinity

f

Exponent in bromate model, associated with ozone dose

g

Exponent in bromate model, associated with reaction time

h

Exponent in bromate model, associated with ammonia (NH4+)

i

Exponent in bromate model, associated with temperature

I

Coefficient in bromate model, associated with temperature in the exponent. Either i or I are used, not both.

Source

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 six corrosion and scaling indices (AI, RI, LSI, LI, CSMR, CCPP)

Description

calculate_corrosion takes an object of class "water" created by define_water and calculates corrosion and scaling indices.

Usage

calculate_corrosion(
  water,
  index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"),
  form = "calcite"
)

Arguments

water

Source water of class "water" created by define_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"

Details

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.

Value

A water class object with updated corrosion and scaling index slots.

Source

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

See Also

define_water

Examples

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"))

Apply 'calculate_corrosion' to a dataframe and output a column of 'water' class to be chained to other tidywater functions.

Description

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).

Usage

calculate_corrosion_chain(
  df,
  input_water = "defined_water",
  output_water = "corrosion_indices",
  index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"),
  form = "calcite"
)

Arguments

df

a data frame containing a column, defined_water, which has already been computed using define_water, and a column named for each of the chemicals being dosed

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"

Details

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.

Value

A data frame containing a water class column with updated corrosion and scaling index slots.

See Also

calculate_corrosion

Examples

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)

Apply 'calculate_corrosion' to a dataframe and create new columns with up to 6 corrosion indices

Description

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).

Usage

calculate_corrosion_once(
  df,
  input_water = "defined_water",
  index = c("aggressive", "ryznar", "langelier", "ccpp", "larsonskold", "csmr"),
  form = "calcite"
)

Arguments

df

a data frame containing a water class column, created using define_water

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"

Details

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.

Value

A data frame containing specified corrosion and scaling indices.

See Also

calculate_corrosion

Examples

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)

Calculate dissolved inorganic carbon (DIC) from total carbonate

Description

This function takes a water class object defined by define_water and outputs a DIC (mg/L).

Usage

calculate_dic(water)

Arguments

water

a water class object containing columns with all the parameters listed in define_water

Value

A numeric value for the calculated DIC.

See Also

define_water

Examples

example_dic <- define_water(8, 15, 200) %>%
  calculate_dic()

Calculate hardness from calcium and magnesium

Description

This function takes Ca and Mg in mg/L and returns hardness in mg/L as CaCO3

Usage

calculate_hardness(ca, mg, type = "total", startunit = "mg/L")

Arguments

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

Value

A numeric value for the total hardness in mg/L as CaCO3.

Examples

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")

Determine disinfection credit from chlorine.

Description

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').

Usage

chemdose_ct(water, time, residual, baffle)

Arguments

water

Source water object of class "water" created by define_water. Water must include ph and temp

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.

Details

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.

Value

A data frame of the required CT, actual CT, and giardia log removal.

Source

Smith et al. (1995)

USEPA (2020)

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

See Also

define_water

Examples

example_ct <- define_water(ph = 7.5, temp = 25) %>%
  chemdose_ct(time = 30, residual = 1, baffle = 0.7)

Calculate DBP formation

Description

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.

Usage

chemdose_dbp(
  water,
  cl2,
  time,
  treatment = "raw",
  cl_type = "chorine",
  location = "plant"
)

Arguments

water

Source water object of class "water" created by define_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 distributions system, "ds".

Details

The function will calculate haloacetic acids (HAA) as HAA5, and total trihalomethanes (TTHM). Use summarise_wq to quickly tabulate the results.

Value

A water class object with predicted DBP concentrations.

Source

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

Examples

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")

Apply 'chemdose_dbp' within a data frame and output a column of 'water' class to be chained to other tidywater functions

Description

DBP = disinfection byproduct

Usage

chemdose_dbp_chain(
  df,
  input_water = "defined_water",
  output_water = "disinfected_water",
  cl2 = 0,
  time = 0,
  treatment = "raw",
  cl_type = "chlorine",
  location = "plant"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include a column named for the applied chlorine dose (cl2), and a column for time.

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".

Details

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.

Value

A data frame containing a water class column with predicted DBP concentrations.

See Also

chemdose_dbp

Examples

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)

Apply 'chemdose_dbp'function within a data frame and output a data frame

Description

DBP = disinfection byproduct

Usage

chemdose_dbp_once(
  df,
  input_water = "defined_water",
  cl2 = 0,
  time = 0,
  treatment = "raw",
  cl_type = "chlorine",
  location = "plant"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_once. The df may include a column named for the applied chlorine dose (cl2), and a column for time.

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".

Details

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.

Value

A data frame with predicted DBP concentrations.

See Also

chemdose_dbp

Examples

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)

Calculate new fluoride concentration after dosing alum.

Description

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).

Usage

chemdose_f(water, alum, coeff = c(1.11, 0.628, -2.07, 0.861))

Arguments

water

Source water object of class "water" created by define_water

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.

Value

A water class object with an updated fluoride concentration.

Examples

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")

Calculate new pH and ion balance after chemical addition

Description

chemdose_ph calculates the new pH, alkalinity, and ion balance of a water based on different chemical additions.

Usage

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
)

Arguments

water

Source water object of class "water" created by define_water

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

Details

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.

Value

A water class object with updated pH, alkalinity, and ions post-chemical addition.

See Also

define_water, convert_units

Examples

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

Apply 'chemdose_ph' within a dataframe and output a column of 'water' class to be chained to other tidywater functions

Description

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.

Usage

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
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include columns named for the chemical(s) being dosed.

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

Details

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.

Value

A data frame containing a water class column with updated pH, alkalinity, and ions post-chemical addition.

See Also

chemdose_ph

Examples

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)

Apply 'chemdose_ph' function and output a dataframe

Description

This function allows chemdose_ph to be added to a piped data frame. Its output is a data frame with updated ions and pH.

Usage

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
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include columns named for the chemical(s) being dosed.

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

Details

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.

Value

A data frame with updated pH, alkalinity, and ions post-chemical addition.

See Also

chemdose_ph

Examples

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)

Determine TOC removal from coagulation

Description

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.

Usage

chemdose_toc(
  water,
  alum = 0,
  ferricchloride = 0,
  ferricsulfate = 0,
  coeff = "Alum"
)

Arguments

water

Source water object of class "water" created by define_water. Water must include ph, doc, and uv254

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

Value

A water class object with an updated DOC, TOC, and UV254 concentration.

Source

Edwards (1997)

U.S. EPA (2001)

See reference list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

See Also

chemdose_ph

Examples

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
  ))

Apply 'chemdose_toc' within a dataframe and output a column of 'water' class to be chained to other tidywater functions

Description

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.

Usage

chemdose_toc_chain(
  df,
  input_water = "defined_water",
  output_water = "coagulated_water",
  alum = 0,
  ferricchloride = 0,
  ferricsulfate = 0,
  coeff = "Alum"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include a column named for the coagulant being dosed, and a column named for the set of coefficients to use.

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

Details

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.

Value

A data frame containing a water class column with updated DOC, TOC, and UV254 concentrations.

See Also

chemdose_toc

Examples

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)

Apply 'chemdose_toc' function and output a data frame

Description

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.

Usage

chemdose_toc_once(
  df,
  input_water = "defined_water",
  alum = 0,
  ferricchloride = 0,
  ferricsulfate = 0,
  coeff = "Alum"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include a column named for the coagulant being dosed, and a column named for the set of coefficients to use.

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

Details

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.

Value

A data frame with an updated DOC, TOC, and UV254 concentration.

See Also

chemdose_toc

Examples

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)

Data frame of conversion factors for estimating DBP formation from chloramines

Description

A dataset containing conversion factors for calculating DBP formation

Usage

chloramine_conv

Format

A dataframe with 17 rows and 3 columns

ID

abbreviation of dbp species

alias

full name of dbp species

percent

specifies the percent of DBP formation predicted from chloramines compared to chlorine, assuming the same chlorine dose applied

Source

U.S. EPA (2001), Table 5-10

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References


Calculate unit conversions for common compounds

Description

This function takes a value and converts units based on compound name.

Usage

convert_units(value, formula, startunit = "mg/L", endunit = "M")

Arguments

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

Value

A numeric value for the converted parameter.

Examples

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 'water' class object to a dataframe

Description

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.

Usage

convert_water(water)

Arguments

water

A water class object

Value

A data frame containing columns for all non-NA water slots.

See Also

define_water

Examples

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)

Convert a 'water' class object to a dataframe with ions in mg/L or ug/L

Description

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.

Usage

convert_watermg(water)

Arguments

water

A water class object

Value

A data frame containing columns for all non-NA water slots with ions in mg/L.

Examples

water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1) %>%
  convert_watermg()

Data frame of correction factors for estimating DBP formation as a function of location

Description

A dataset containing correction factors for calculating DBP formation

Usage

dbp_correction

Format

A dataframe with 17 rows and 4 columns

ID

abbreviation of dbp species

alias

full name of dbp species

plant

specifies the correction factor for modelling DBP formation within a treatment plant

ds

specifies the correction factor for modelling DBP formation within the distribution system

Source

U.S. EPA (2001), Table 5-7

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References


Data frame of DBP coefficients for predicting DBP formation

Description

A dataset containing coefficients for calculating DBP formation

Usage

dbpcoeffs

Format

A dataframe with 30 rows and 10 columns

ID

abbreviation of dbp species

alias

full name of dbp species

water_type

specifies which model the constants apply to, either treated or untreated water

A

First coefficient in DBP model

a

Second coefficient in DBP model, associated with TOC or DOC

b

Third coefficient in DBP model, associated with Cl2

c

Fourth coefficient in DBP model, associated with Br-

d

Fifth coefficient in DBP model, associated with temperature

e

Sixth coefficient in DBP model, associated with pH

f

Seventh coefficient in DBP model, associated with reaction time

Source

U.S. EPA (2001)

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References


Create a water class object given water quality parameters

Description

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.

Usage

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
)

Arguments

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+

Details

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.

Value

A water class object where slots are filled or calculated based on input parameters.

Examples

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)

Apply 'define_water' within a dataframe and output a column of 'water' class to be chained to other tidywater functions

Description

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.

Usage

define_water_chain(df, output_water = "defined_water")

Arguments

df

a data frame containing columns with all the parameters listed in define_water

output_water

name of the output column storing updated parameters with the class, water. Default is "defined_water".

Details

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.

Value

A data frame containing a water class column.

See Also

define_water

Examples

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)

Apply 'define_water' and output a dataframe

Description

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.

Usage

define_water_once(df)

Arguments

df

a data frame containing columns with all the parameters listed in define_water

Details

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.

Value

A data frame containing columns that were filled or calculated based on define_water.

See Also

define_water

Examples

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)

Dissociation constants and standard enthalpy for weak acids/bases

Description

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.

Usage

discons

Format

A dataframe with 8 rows and 3 columns

ID

Coefficient type

k

Equilibrium constant

deltah

Standard enthalpy in J/mol

Source

Benjamin (2015) Appendix A.1 and A.2.

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References


Simulate contributions of various lead solids to total soluble lead

Description

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"

Usage

dissolve_pb(
  water,
  hydroxypyromorphite = "Schock",
  pyromorphite = "Topolska",
  laurionite = "Nasanen"
)

Arguments

water

Source water object of class "water" created by define_water. Water must include alk and is. If po4, cl, and so4 are known, those should also be included.

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".

Details

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.

Value

A data frame containing only the controlling lead solid and modeled dissolved lead concentration.

Source

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

See Also

define_water

Examples

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")

Apply 'dissolve_pb' to a dataframe and create a new column with numeric dose

Description

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).

Usage

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
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain

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.

Details

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.

Value

A data frame containing the controlling lead solid and modeled dissolved lead concentration as new columns.

See Also

dissolve_pb

Examples

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)

Data frame of Edwards model coefficients

Description

A dataset containing coefficients from the Edwards (1997) model for coagulation TOC removal.

Usage

edwardscoeff

Format

A dataframe with 5 rows and 7 columns:

ID

Coefficient type

x3

x3 parameter

x2

x2 parameter

x1

x1 parameter

k1

k1 parameter

k2

k2 parameter

b

b parameter

Source

Edwards (1997) Table 2.

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References


Data frame of equilibrium constants for lead and copper solubility

Description

A dataset containing equilibrium constants for lead solubility

Usage

leadsol_constants

Format

A dataframe with 38 rows and 3 columns

Solids:

species_name

Name of lead solid or complex with possible _letter to cite different references

constant_name

Reference ID for constants

log_value

Equilibrium constant log value

source

Source for equilibrium constant value

Source

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


Molar weights of relevant compounds

Description

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,

Usage

mweights

Format

A dataframe with one row and one column per compound


Calculate bromate formation

Description

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.)

Usage

ozonate_bromate(water, dose, time, model = "Ozekin")

Arguments

water

Source water object of class "water" created by define_water

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")

Value

A water class object with calculated bromate (ug/L).

Source

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

Examples

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")

Determine disinfection credit from ozone.

Description

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

Usage

ozonate_ct(water, time, dose, kd, baffle)

Arguments

water

Source water object of class "water" created by define_water. Water must include ph and temp

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.

Details

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.

Value

A data frame containing actual CT, giardia log removal, virus log removal, and crypto log removal.

Source

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

See Also

define_water

Examples

# 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)

Calculate DOC Concentration in PAC system

Description

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.

Usage

pac_toc(water, dose, time, type = "bituminous")

Arguments

water

Source water object of class "water" created by define_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".

Details

The function will calculate DOC concentration by PAC adsorption in drinking water treatment. UV254 concentrations are predicted based on a linear relationship with DOC.

Value

A water class object with post-PAC predicted DOC and UV254.

Source

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

CHO(2007)

Examples

water <- define_water(toc = 2.5, uv254 = .05, doc = 1.5) %>%
  pac_toc(dose = 15, time = 50, type = "wood")

Apply 'pac_toc' within a data frame and output a column of 'water' class to be chained to other tidywater functions PAC = powdered activated carbon

Description

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.

Usage

pac_toc_chain(
  df,
  input_water = "defined_water",
  output_water = "pac_water",
  dose = 0,
  time = 0,
  type = "bituminous"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include columns named for the dose, time, and type

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".

Details

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.

Value

A data frame containing a water class column with updated DOC, TOC, and UV254 concentrations.

Source

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

CHO(2007)

See Also

pac_toc

Examples

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)

Apply 'pac_toc'function within a data frame and output a data frame

Description

PAC = powdered activated carbon

Usage

pac_toc_once(
  df,
  input_water = "defined_water",
  dose = 0,
  time = 0,
  type = "bituminous"
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include columns named for the dose, time, and type

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".

Details

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.

Value

A data frame with an updated DOC, TOC, and UV254 concentration.

Source

See references list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

CHO(2007)

See Also

pac_toc

Examples

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)

Create summary plot of ions from water class

Description

This function takes a water data frame defined by define_water and outputs an ion balance plot.

Usage

plot_ions(water)

Arguments

water

Source water vector created by link function here

Value

A ggplot object displaying the water's ion balance.

Examples

water_defined <- define_water(7, 20, 50, 100, 80, 10, 10, 10, 10, tot_po4 = 1)
plot_ions(water_defined)

Pluck out a single parameter from a 'water' class object

Description

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.

Usage

pluck_water(df, input_waters = c("defined_water"), parameter)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water

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

Value

A data frame containing columns of selected parameters from a list of water class objects.

See Also

convert_water

Examples

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)

Determine chemical cost

Description

This function takes a chemical dose in mg/L, plant flow, chemical strength, and $/lb and calculates cost.

Usage

solvecost_chem(dose, flow, strength = 100, cost, time = "day")

Arguments

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".

Value

A numeric value for chemical cost, $/time.

Examples

alum_cost <- solvecost_chem(dose = 20, flow = 10, strength = 49, cost = .22)

Determine labor cost

Description

This function takes number of FTE and annual $/FTE and determines labor cost

Usage

solvecost_labor(fte, cost, time = "day")

Arguments

fte

Number of FTEs. Can be decimal.

cost

$/year per FTE

time

Desired output units, one of c("day", "month", "year"). Defaults to "day".

Value

A numeric value for labor $/time.

Examples

laborcost <- solvecost_labor(1.5, 50000)

Determine power cost

Description

This function takes kW,

Usage

solvecost_power(power, utilization = 100, cost, time = "day")

Arguments

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".

Value

A numeric value for power, $/time.

Examples

powercost <- solvecost_power(50, 100, .08)

Determine solids disposal cost

Description

This function takes coagulant doses in mg/L as chemical, removed turbidity, and cost ($/lb) to determine disposal cost.

Usage

solvecost_solids(
  alum = 0,
  ferricchloride = 0,
  ferricsulfate = 0,
  flow,
  turb,
  b = 1.5,
  cost,
  time = "day"
)

Arguments

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".

Value

A numeric value for disposal costs, $/time.

Source

https://water.mecc.edu/courses/ENV295Residuals/lesson3b.htm#:~:text=From

Examples

alum_solidscost <- solvecost_solids(alum = 50, flow = 10, turb = 2, cost = 0.05)

Calculate a desired chemical dose for a target alkalinity

Description

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.

Usage

solvedose_alk(water, target_alk, chemical)

Arguments

water

Source water of class "water" created by define_water

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"

Value

A numeric value for the required chemical dose.

See Also

define_water

Examples

dose_required <- define_water(ph = 7.9, temp = 22, alk = 100, 80, 50) %>%
  solvedose_alk(target_alk = 150, "naoh")

Apply 'solvedose_alk' to a dataframe and create a new column with numeric dose

Description

This function allows solvedose_alk to be added to a piped data frame. Its output is a chemical dose in mg/L.

Usage

solvedose_alk_once(
  df,
  input_water = "defined_water",
  output_column = "dose_required",
  target_alk = NULL,
  chemical = NULL
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include a column with names for each of the chemicals being dosed.

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

Details

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.

Value

A data frame containing the original data frame and columns for target alkalinity, chemical dosed, and required chemical dose.

See Also

solvedose_alk

Examples

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)

Calculate a desired chemical dose for a target pH

Description

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.

Usage

solvedose_ph(water, target_ph, chemical)

Arguments

water

Source water of class "water" created by define_water

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"

Value

A numeric value for the required chemical dose.

See Also

define_water, chemdose_ph

Examples

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")

Apply 'solvedose_ph' to a dataframe and create a new column with numeric dose

Description

This function allows solvedose_ph to be added to a piped data frame. Its output is a chemical dose in mg/L.

Usage

solvedose_ph_once(
  df,
  input_water = "defined_water",
  output_column = "dose_required",
  target_ph = NULL,
  chemical = NULL
)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain. The df may include a column with names for each of the chemicals being dosed.

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

Details

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.

Value

A data frame containing the original data frame and columns for target pH, chemical dosed, and required chemical dose.

See Also

solvedose_ph

Examples

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)

Convert mg/L of chemical to lb/day

Description

This function takes a chemical dose in mg/L, plant flow, and chemical strength and calculates lb/day of product

Usage

solvemass_chem(dose, flow, strength = 100)

Arguments

dose

Chemical dose in mg/L as chemical

flow

Plant flow in MGD

strength

Chemical product strength in percent. Defaults to 100 percent.

Value

A numeric value for the chemical mass in lb/day.

Examples

alum_mass <- solvemass_chem(dose = 20, flow = 10, strength = 49)

Determine ozone decay

Description

This function applies the ozone decay model to a water created by define_water from U.S. EPA (2001) equation 5-128.

Usage

solveresid_o3(water, dose, time)

Arguments

water

Source water object of class "water" created by define_water.

dose

Applied ozone dose in mg/L

time

Ozone contact time in minutes

Value

A numeric value for the resiudal ozone.

Source

U.S. EPA (2001)

See reference list at: https://github.com/BrownandCaldwell-Public/tidywater/wiki/References

Examples

ozone_resid <- define_water(7, 20, 100, doc = 2, toc = 2.2, uv254 = .02, br = 50) %>%
  solveresid_o3(dose = 2, time = 10)

Apply 'solveresid_o3' to a data frame and create a new column with residual ozone dose

Description

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)

Usage

solveresid_o3_once(df, input_water = "defined_water", dose = 0, time = 0)

Arguments

df

a data frame containing a water class column, which has already been computed using define_water_chain

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

Details

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.

Value

A data frame containing the original data frame and columns for ozone dosed, time, and ozone residual.

Examples

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()

Create summary table from water class

Description

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.

Usage

summarize_wq(water, params = c("general"))

summarise_wq(water, params = c("general"))

Arguments

water

Source water vector created by define_water.

params

List of water quality parameters to be summarized. Options include "general", "ions", "corrosion", and "dbps". Defaults to "general" only.

Details

Use calculate_corrosion for corrosivity indicators and chemdose_dbp for modeled DBP concentrations.

Value

A knitr_kable table of specified water quality parameters.

Examples

# 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"))

Data frame of water quality parameters

Description

A dataset containing fabricated water quality to use as tidywater inputs. Parameters are set to reasonable water quality ranges. Parameters are as follows:

Usage

water_df

Format

A dataframe with 12 rows and 11 columns:

ph

pH in standard units (SU)

temp

Temperature in degree C

alk

Alkalinity in mg/L as CaCO3

tot_hard

Total hardness in mg/L as CaCO3

ca_hard

Calcium hardness in mg/L as CaCO3

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

Total chlorine in mg/L as Cl2

tot_po4

Total phosphate in mg/L as PO42-

Source

Fabricated for use in examples.