From d66bd4aa0bf9c4d9b8793a4e308c9e80691b440f Mon Sep 17 00:00:00 2001 From: Johannes Ranke Date: Sun, 12 Nov 2023 21:40:01 +0100 Subject: Enable links to source, upgrade to bootstrap 5 --- docs/reference/PEC_sw_exposit_drainage.html | 345 ++++++++++++---------------- 1 file changed, 144 insertions(+), 201 deletions(-) (limited to 'docs/reference/PEC_sw_exposit_drainage.html') diff --git a/docs/reference/PEC_sw_exposit_drainage.html b/docs/reference/PEC_sw_exposit_drainage.html index 5bd1d80..74f1b60 100644 --- a/docs/reference/PEC_sw_exposit_drainage.html +++ b/docs/reference/PEC_sw_exposit_drainage.html @@ -1,117 +1,60 @@ - - - - - - - -Calculate PEC surface water due to drainage as in Exposit 3 — PEC_sw_exposit_drainage • pfm - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -Calculate PEC surface water due to drainage as in Exposit 3 — PEC_sw_exposit_drainage • pfm + Skip to contents + +
+
+
-
+

This is a reimplementation of the calculation described in the Exposit 3.02 spreadsheet file, in the worksheet "Konzept Drainage". Although there are four groups of compounds ("Gefährdungsgruppen"), only one distinction is made in the @@ -121,123 +64,123 @@ the group is derived only from the Koc, if not given explicitly. For details, see the discussion of the function arguments below.

-
PEC_sw_exposit_drainage(
-  rate,
-  interception = 0,
-  Koc = NA,
-  mobility = c(NA, "low", "high"),
-  DT50 = Inf,
-  t_drainage = 3,
-  V_ditch = 30,
-  V_drainage = c(spring = 10, autumn = 100),
-  dilution = 2
-)
- -

Arguments

- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -
rate

The application rate in g/ha

interception

The fraction intercepted by the crop

Koc

The sorption coefficient to soil organic carbon used to determine the mobility. A trigger -value of 550 L/kg is used in order to decide if Koc >> 500.

mobility

Overrides what is determined from the Koc.

DT50

The soil half-life in days

t_drainage

The time between application and the drainage event, where degradation occurs, in days

V_ditch

The volume of the ditch is assumed to be 1 m * 100 m * 30 cm = 30 m3

V_drainage

The drainage volume, equivalent to 1 mm precipitation on 1 ha for spring/summer or 10 mm for -autumn/winter/early spring.

dilution

The dilution factor

- -

Source

+
+

Usage

+
PEC_sw_exposit_drainage(
+  rate,
+  interception = 0,
+  Koc = NA,
+  mobility = c(NA, "low", "high"),
+  DT50 = Inf,
+  t_drainage = 3,
+  V_ditch = 30,
+  V_drainage = c(spring = 10, autumn = 100),
+  dilution = 2
+)
+
+ +
+

Arguments

+
rate
+

The application rate in g/ha

+ + +
interception
+

The fraction intercepted by the crop

+ + +
Koc
+

The sorption coefficient to soil organic carbon used to determine the mobility. A trigger +value of 550 L/kg is used in order to decide if Koc >> 500.

+ + +
mobility
+

Overrides what is determined from the Koc.

+ + +
DT50
+

The soil half-life in days

+ + +
t_drainage
+

The time between application and the drainage event, where degradation occurs, in days

+ + +
V_ditch
+

The volume of the ditch is assumed to be 1 m * 100 m * 30 cm = 30 m3

-

A list containing the following components

-
perc_runoff

The runoff percentages for dissolved and bound substance

-
runoff

A matrix containing dissolved and bound input for the different distances

-
PEC_sw_runoff

A matrix containing PEC values for dissolved and bound substance + +

V_drainage
+

The drainage volume, equivalent to 1 mm precipitation on 1 ha for spring/summer or 10 mm for +autumn/winter/early spring.

+ + +
dilution
+

The dilution factor

+ +
+
+

Value

+ + +

A list containing the following components

+

+
perc_runoff
+

The runoff percentages for dissolved and bound substance

+ +
runoff
+

A matrix containing dissolved and bound input for the different distances

+ +
PEC_sw_runoff
+

A matrix containing PEC values for dissolved and bound substance for the different distances. If the rate was given in g/ha, the PECsw are in microg/L.

+ -
- -

See also

- -

perc_runoff_exposit for runoff loss percentages and perc_runoff_reduction_exposit for runoff reduction percentages used

- -

Examples

-
PEC_sw_exposit_drainage(500, Koc = 150)
#> $perc_drainage_total -#> spring autumn -#> 0.2 1.0 -#> -#> $perc_peak -#> spring autumn -#> 12.5 25.0 -#> -#> $PEC_sw_drainage -#> spring autumn -#> 1.562500 4.807692 -#>
-
- +
+

See also

+

perc_runoff_exposit for runoff loss percentages and perc_runoff_reduction_exposit for runoff reduction percentages used

+
-
-
+
+

Examples

+
  PEC_sw_exposit_drainage(500, Koc = 150)
+#> $perc_drainage_total
+#> spring autumn 
+#>    0.2    1.0 
+#> 
+#> $perc_peak
+#> spring autumn 
+#>   12.5   25.0 
+#> 
+#> $PEC_sw_drainage
+#>   spring   autumn 
+#> 1.562500 4.807692 
+#> 
+
+
+
- + - - - + -- cgit v1.2.3 From 4079a2c496aa4e8c6dc2a93afedcbedbf7a852b5 Mon Sep 17 00:00:00 2001 From: Johannes Ranke Date: Sun, 12 Nov 2023 21:59:34 +0100 Subject: Enable markdown and rebuild docs --- DESCRIPTION | 1 + docs/pkgdown.yml | 2 +- docs/reference/EFSA_washoff_2017.html | 8 ++-- docs/reference/FOCUS_GW_scenarios_2012.html | 12 +++--- docs/reference/FOCUS_Step_12_scenarios.html | 6 +-- docs/reference/FOMC_actual_twa.html | 4 +- docs/reference/GUS.html | 6 +-- docs/reference/PEC_soil.html | 40 +++++++++--------- docs/reference/PEC_sw_drainage_UK.html | 10 ++--- docs/reference/PEC_sw_drift.html | 2 +- docs/reference/PEC_sw_exposit_drainage.html | 14 +++---- docs/reference/PEC_sw_exposit_runoff.html | 14 +++---- docs/reference/PEC_sw_focus.html | 28 ++++++------- docs/reference/SFO_actual_twa.html | 4 +- docs/reference/SSLRC_mobility_classification.html | 12 +++--- docs/reference/TOXSWA_cwa.html | 32 +++++++++++++-- docs/reference/TSCF-1.png | Bin 27659 -> 40587 bytes docs/reference/TSCF.html | 6 +-- docs/reference/endpoint.html | 12 +++--- docs/reference/max_twa.html | 8 ++-- docs/reference/perc_runoff_exposit.html | 14 +++---- docs/reference/perc_runoff_reduction_exposit.html | 8 ++-- docs/reference/soil_scenario_data_EFSA_2015.html | 26 ++++++------ docs/reference/soil_scenario_data_EFSA_2017.html | 26 ++++++------ docs/search.json | 2 +- man/EFSA_washoff_2017.Rd | 8 ++-- man/FOCUS_GW_scenarios_2012.Rd | 8 ++-- man/FOCUS_Step_12_scenarios.Rd | 6 +-- man/FOMC_actual_twa.Rd | 4 +- man/GUS.Rd | 6 +-- man/PEC_soil.Rd | 48 +++++++++++----------- man/PEC_sw_drainage_UK.Rd | 12 +++--- man/PEC_sw_drift.Rd | 2 +- man/PEC_sw_exposit_drainage.Rd | 14 +++---- man/PEC_sw_exposit_runoff.Rd | 14 +++---- man/PEC_sw_focus.Rd | 28 ++++++------- man/SFO_actual_twa.Rd | 4 +- man/SSLRC_mobility_classification.Rd | 14 +++---- man/TOXSWA_cwa.Rd | 6 +-- man/TSCF.Rd | 2 +- man/endpoint.Rd | 12 +++--- man/max_twa.Rd | 8 ++-- man/perc_runoff_exposit.Rd | 18 ++++---- man/perc_runoff_reduction_exposit.Rd | 14 +++---- man/soil_scenario_data_EFSA_2015.Rd | 18 ++++---- man/soil_scenario_data_EFSA_2017.Rd | 18 ++++---- 46 files changed, 290 insertions(+), 271 deletions(-) (limited to 'docs/reference/PEC_sw_exposit_drainage.html') diff --git a/DESCRIPTION b/DESCRIPTION index a12f90b..a159c56 100644 --- a/DESCRIPTION +++ b/DESCRIPTION @@ -27,4 +27,5 @@ LazyLoad: yes LazyData: yes Encoding: UTF-8 URL: https://pkgdown.jrwb.de/pfm, https://github.com/jranke/pfm +Roxygen: list(markdown = TRUE, r6 = TRUE) RoxygenNote: 7.2.3 diff --git a/docs/pkgdown.yml b/docs/pkgdown.yml index eeed6da..6571239 100644 --- a/docs/pkgdown.yml +++ b/docs/pkgdown.yml @@ -2,7 +2,7 @@ pandoc: 2.17.1.1 pkgdown: 2.0.7 pkgdown_sha: ~ articles: {} -last_built: 2023-11-12T20:34Z +last_built: 2023-11-12T20:59Z urls: reference: https://pkgdown.jrwb.de/pfm/reference article: https://pkgdown.jrwb.de/pfm/articles diff --git a/docs/reference/EFSA_washoff_2017.html b/docs/reference/EFSA_washoff_2017.html index 1e292af..b424de9 100644 --- a/docs/reference/EFSA_washoff_2017.html +++ b/docs/reference/EFSA_washoff_2017.html @@ -54,10 +54,10 @@

Source

European Food Safety Authority (2017) EFSA guidance document for - predicting environmental concentrations of active substances of plant - protection products and transformation products of these active substances - in soil. EFSA Journal 15(10) 4982 - doi:10.2903/j.efsa.2017.4982

+predicting environmental concentrations of active substances of plant +protection products and transformation products of these active substances +in soil. EFSA Journal 15(10) 4982 +doi:10.2903/j.efsa.2017.4982

diff --git a/docs/reference/FOCUS_GW_scenarios_2012.html b/docs/reference/FOCUS_GW_scenarios_2012.html index 84c2fac..2e9982b 100644 --- a/docs/reference/FOCUS_GW_scenarios_2012.html +++ b/docs/reference/FOCUS_GW_scenarios_2012.html @@ -1,6 +1,6 @@ -A very small subset of the FOCUS Groundwater scenario definitions — FOCUS_GW_scenarios_2012 • pfmA very small subset of the FOCUS Groundwater scenario definitions — FOCUS_GW_scenarios_2012 • pfmProperties of the predefined scenarios from the EFSA guidance from 2015 — soil_scenario_data_EFSA_2015 • pfmProperties of the predefined scenarios from the EFSA guidance from 2017 — soil_scenario_data_EFSA_2017 • pfmProperties of the predefined scenarios from the EFSA guidance from 2017 — soil_scenario_data_EFSA_2017 • pfm