This function provides a way of showing the differences in concentrations between two time periods as a polar plot. There are several uses of this function, but the most common will be to see how source(s) may have changed between two periods.
polarDiff(
before,
after,
pollutant = "nox",
x = "ws",
limits = NULL,
plot = TRUE,
...
)
an openair plot.
A data frame that represents the "before" case. See
polarPlot()
for details of different input requirements.
A data frame that represents the "after" case. See polarPlot()
for details of different input requirements.
Mandatory. A pollutant name corresponding to a variable in a
data frame should be supplied e.g. pollutant = "nox"
. There can also
be more than one pollutant specified e.g. pollutant = c("nox",
"no2")
. The main use of using two or more pollutants is for model
evaluation where two species would be expected to have similar
concentrations. This saves the user stacking the data and it is possible to
work with columns of data directly. A typical use would be pollutant
= c("obs", "mod")
to compare two columns “obs” (the observations)
and “mod” (modelled values). When pair-wise statistics such as
Pearson correlation and regression techniques are to be plotted,
pollutant
takes two elements too. For example, pollutant =
c("bc", "pm25")
where "bc"
is a function of "pm25"
.
Name of variable to plot against wind direction in polar coordinates, the default is wind speed, “ws”.
The function does its best to choose sensible limits
automatically. However, there are circumstances when the user will wish to
set different ones. An example would be a series of plots showing each year
of data separately. The limits are set in the form c(lower, upper)
,
so limits = c(0, 100)
would force the plot limits to span 0-100.
Should a plot be produced? FALSE
can be useful when
analysing data to extract plot components and plotting them in other ways.
Arguments passed on to polarPlot
mydata
A data frame minimally containing wd
, another variable
to plot in polar coordinates (the default is a column “ws” --- wind
speed) and a pollutant. Should also contain date
if plots by time
period are required.
wd
Name of wind direction field.
type
type
determines how the data are split i.e. conditioned,
and then plotted. The default is will produce a single plot using the
entire data. Type can be one of the built-in types as detailed in
cutData
e.g. “season”, “year”, “weekday” and so
on. For example, type = "season"
will produce four plots --- one for
each season.
It is also possible to choose type
as another variable in the data
frame. If that variable is numeric, then the data will be split into four
quantiles (if possible) and labelled accordingly. If type is an existing
character or factor variable, then those categories/levels will be used
directly. This offers great flexibility for understanding the variation of
different variables and how they depend on one another.
Type can be up length two e.g. type = c("season", "weekday")
will
produce a 2x2 plot split by season and day of the week. Note, when two
types are provided the first forms the columns and the second the rows.
statistic
The statistic that should be applied to each wind
speed/direction bin. Because of the smoothing involved, the colour scale
for some of these statistics is only to provide an indication of overall
pattern and should not be interpreted in concentration units e.g. for
statistic = "weighted.mean"
where the bin mean is multiplied by the
bin frequency and divided by the total frequency. In many cases using
polarFreq
will be better. Setting statistic = "weighted.mean"
can be useful because it provides an indication of the concentration *
frequency of occurrence and will highlight the wind speed/direction
conditions that dominate the overall mean.Can be:
“mean” (default), “median”, “max” (maximum), “frequency”. “stdev” (standard deviation), “weighted.mean”.
statistic = "nwr"
Implements the Non-parametric Wind
Regression approach of Henry et al. (2009) that uses kernel smoothers. The
openair
implementation is not identical because Gaussian kernels are
used for both wind direction and speed. The smoothing is controlled by
ws_spread
and wd_spread
.
statistic = "cpf"
the conditional probability function (CPF)
is plotted and a single (usually high) percentile level is supplied. The
CPF is defined as CPF = my/ny, where my is the number of samples in the y
bin (by default a wind direction, wind speed interval) with mixing ratios
greater than the overall percentile concentration, and ny is the
total number of samples in the same wind sector (see Ashbaugh et al.,
1985). Note that percentile intervals can also be considered; see
percentile
for details.
When statistic = "r"
or statistic = "Pearson"
, the
Pearson correlation coefficient is calculated for two pollutants.
The calculation involves a weighted Pearson correlation coefficient, which
is weighted by Gaussian kernels for wind direction an the radial variable
(by default wind speed). More weight is assigned to values close to a wind
speed-direction interval. Kernel weighting is used to ensure that all data
are used rather than relying on the potentially small number of values in a
wind speed-direction interval.
When statistic = "Spearman"
, the Spearman correlation
coefficient is calculated for two pollutants. The calculation
involves a weighted Spearman correlation coefficient, which is weighted by
Gaussian kernels for wind direction an the radial variable (by default wind
speed). More weight is assigned to values close to a wind speed-direction
interval. Kernel weighting is used to ensure that all data are used rather
than relying on the potentially small number of values in a wind
speed-direction interval.
"robust_slope"
is another option for pair-wise statistics and
"quantile.slope"
, which uses quantile regression to estimate the
slope for a particular quantile level (see also tau
for setting the
quantile level).
"york_slope"
is another option for pair-wise statistics which
uses the York regression method to estimate the slope. In this
method the uncertainties in x
and y
are used in the
determination of the slope. The uncertainties are provided by
x_error
and y_error
--- see below.
exclude.missing
Setting this option to TRUE
(the default)
removes points from the plot that are too far from the original data. The
smoothing routines will produce predictions at points where no data exist
i.e. they predict. By removing the points too far from the original data
produces a plot where it is clear where the original data lie. If set to
FALSE
missing data will be interpolated.
uncertainty
Should the uncertainty in the calculated surface be shown?
If TRUE
three plots are produced on the same scale showing the
predicted surface together with the estimated lower and upper uncertainties
at the 95% confidence interval. Calculating the uncertainties is useful to
understand whether features are real or not. For example, at high wind
speeds where there are few data there is greater uncertainty over the
predicted values. The uncertainties are calculated using the GAM and
weighting is done by the frequency of measurements in each wind
speed-direction bin. Note that if uncertainties are calculated then the
type is set to "default".
percentile
If statistic = "percentile"
then percentile
is used, expressed from 0 to 100. Note that the percentile value is
calculated in the wind speed, wind direction ‘bins’. For this reason
it can also be useful to set min.bin
to ensure there are a
sufficient number of points available to estimate a percentile. See
quantile
for more details of how percentiles are calculated.
percentile
is also used for the Conditional Probability Function
(CPF) plots. percentile
can be of length two, in which case the
percentile interval is considered for use with CPF. For example,
percentile = c(90, 100)
will plot the CPF for concentrations between
the 90 and 100th percentiles. Percentile intervals can be useful for
identifying specific sources. In addition, percentile
can also be of
length 3. The third value is the ‘trim’ value to be applied. When
calculating percentile intervals many can cover very low values where there
is no useful information. The trim value ensures that values greater than
or equal to the trim * mean value are considered before the
percentile intervals are calculated. The effect is to extract more detail
from many source signatures. See the manual for examples. Finally, if the
trim value is less than zero the percentile range is interpreted as
absolute concentration values and subsetting is carried out directly.
cols
Colours to be used for plotting. Options include
“default”, “increment”, “heat”, “jet” and
RColorBrewer
colours --- see the openair
openColours
function for more details. For user defined the user can supply a list of
colour names recognised by R (type colours()
to see the full list).
An example would be cols = c("yellow", "green", "blue")
. cols
can also take the values "viridis"
, "magma"
,
"inferno"
, or "plasma"
which are the viridis colour maps
ported from Python's Matplotlib library.
weights
At the edges of the plot there may only be a few data points
in each wind speed-direction interval, which could in some situations
distort the plot if the concentrations are high. weights
applies a
weighting to reduce their influence. For example and by default if only a
single data point exists then the weighting factor is 0.25 and for two
points 0.5. To not apply any weighting and use the data as is, use
weights = c(1, 1, 1)
.
An alternative to down-weighting these points they can be removed
altogether using min.bin
.
min.bin
The minimum number of points allowed in a wind speed/wind
direction bin. The default is 1. A value of two requires at least 2 valid
records in each bin an so on; bins with less than 2 valid records are set
to NA. Care should be taken when using a value > 1 because of the risk of
removing real data points. It is recommended to consider your data with
care. Also, the polarFreq
function can be of use in such
circumstances.
mis.col
When min.bin
is > 1 it can be useful to show where data
are removed on the plots. This is done by shading the missing data in
mis.col
. To not highlight missing data when min.bin
> 1
choose mis.col = "transparent"
.
alpha
The alpha transparency to use for the plotting surface (a value
between 0 and 1 with zero being fully transparent and 1 fully opaque).
Setting a value below 1 can be useful when plotting surfaces on a map using
the package openairmaps
.
upper
This sets the upper limit wind speed to be used. Often there are only a relatively few data points at very high wind speeds and plotting all of them can reduce the useful information in the plot.
angle.scale
Sometimes the placement of the scale may interfere with an
interesting feature. The user can therefore set angle.scale
to any
value between 0 and 360 degrees to mitigate such problems. For example
angle.scale = 45
will draw the scale heading in a NE direction.
units
The units shown on the polar axis scale.
force.positive
The default is TRUE
. Sometimes if smoothing data
with steep gradients it is possible for predicted values to be negative.
force.positive = TRUE
ensures that predictions remain positive. This
is useful for several reasons. First, with lots of missing data more
interpolation is needed and this can result in artefacts because the
predictions are too far from the original data. Second, if it is known
beforehand that the data are all positive, then this option carries that
assumption through to the prediction. The only likely time where setting
force.positive = FALSE
would be if background concentrations were
first subtracted resulting in data that is legitimately negative. For the
vast majority of situations it is expected that the user will not need to
alter the default option.
k
This is the smoothing parameter used by the gam
function in
package mgcv
. Typically, value of around 100 (the default) seems to
be suitable and will resolve important features in the plot. The most
appropriate choice of k
is problem-dependent; but extensive testing
of polar plots for many different problems suggests a value of k
of
about 100 is suitable. Setting k
to higher values will not tend to
affect the surface predictions by much but will add to the computation
time. Lower values of k
will increase smoothing. Sometimes with few
data to plot polarPlot
will fail. Under these circumstances it can
be worth lowering the value of k
.
normalise
If TRUE
concentrations are normalised by dividing by
their mean value. This is done after fitting the smooth surface.
This option is particularly useful if one is interested in the patterns of
concentrations for several pollutants on different scales e.g. NOx and CO.
Often useful if more than one pollutant
is chosen.
key.header
Adds additional text/labels to the scale key. For example,
passing the options key.header = "header", key.footer = "footer1"
adds addition text above and below the scale key. These arguments are
passed to drawOpenKey
via quickText
, applying the
auto.text
argument, to handle formatting.
key.footer
see key.footer
.
key.position
Location where the scale key is to plotted. Allowed
arguments currently include "top"
, "right"
, "bottom"
and "left"
.
key
Fine control of the scale key via drawOpenKey
. See
drawOpenKey
for further details.
auto.text
Either TRUE
(default) or FALSE
. If TRUE
titles and axis labels will automatically try and format pollutant names
and units properly e.g. by subscripting the `2' in NO2.
ws_spread
The value of sigma used for Gaussian kernel weighting of
wind speed when statistic = "nwr"
or when correlation and regression
statistics are used such as r. Default is 0.5
.
wd_spread
The value of sigma used for Gaussian kernel weighting of
wind direction when statistic = "nwr"
or when correlation and
regression statistics are used such as r. Default is 4
.
x_error
The x
error / uncertainty used when statistic =
"york_slope"
.
y_error
The y
error / uncertainty used when statistic =
"york_slope"
.
kernel
Type of kernel used for the weighting procedure for when
correlation or regression techniques are used. Only "gaussian"
is
supported but this may be enhanced in the future.
formula.label
When pair-wise statistics such as regression slopes are calculated and plotted, should a formula label be displayed?
tau
The quantile to be estimated when statistic
is set to
"quantile.slope"
. Default is 0.5
which is equal to the median
and will be ignored if "quantile.slope"
is not used.
While the function is primarily intended to compare two time periods at the same location, it can be used for any two data sets that contain the same pollutant. For example, data from two sites that are close to one another, or two co-located instruments.
The analysis works by calculating the polar plot surface for the
before
and after
periods and then subtracting the before
surface from the after
surface.
Other polar directional analysis functions:
percentileRose()
,
polarAnnulus()
,
polarCluster()
,
polarFreq()
,
polarPlot()
,
pollutionRose()
,
windRose()
if (FALSE) {
before_data <- selectByDate(mydata, year = 2002)
after_data <- selectByDate(mydata, year = 2003)
polarDiff(before_data, after_data, pollutant = "no2")
# with some options
polarDiff(before_data, after_data, pollutant = "no2", cols = "RdYlBu", limits = c(-20, 20))
}
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