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Manual for psimpoll and pscomb
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Six basic analyses are available:
- calculation of mean, standard deviation, skewness, and kurtosis
for the values presented for each pollen type, with results written
to the data analysis file (menu Ec).
Values of skewness and kurtosis significantly different from
zero (the value for a perfect normal distribution) are marked;
- calculation of a weighted average, or `optimum' location of each pollen
type in time (or depth), together with a standard deviation, or
`tolerance'. This is a measure that combines the extent of
occurrence of a taxon over time, weighted by its abundance.
It is included here, experimentally, as a potentially better
statistic for the location of a taxon in a sequence than
such subjective measures as `rational' or `empirical' limits etc.
The idea is borrowed from the statistics used to define optima
of diatoms along pH gradients: I have substituted time (depth)
for the environmental gradient
(Birks et al. 1990).
Output in the data analysis file gives, for each taxon, the optimum,
the tolerance, and the location (depth or age) of the
taxon's maximum value, and the value of that maximum;
- calculation of a `runs' test. If abundances of a pollen type along a
sequence were randomly distributed with time, then the length of `runs'
(series of samples all successively greater (or lower) than the previous
sample) will follow a predictable pattern. We can count the lengths of
observed runs (how many runs of a single sample, runs of two samples,
etc), and compare the resulting distribution with the distribution
for random samples. The result is a runs test, and gives a measure
of whether the overall pattern of change is, or is not, significantly
different from random. The output gives the runs statistic, udr,
and the goodness-of-fit, q. q greater than 0.05 indicates that the
sequence of runs for the taxon is not significantly different from
random.
- calculation of a Linear Correlation Coefficient. This is a statistic
that can be
used for detecting trends in the values for taxa.
If a taxon's values
increase continuously along the sequence, its correlation coefficient (r)
will be high and significant. If there are no trends
in the data, r will be low (near zero). The sign of
r indicates the direction of the trend. In the
normal situation where depth (time) values increase numerically down
a sequence, r will be positive for taxa whose values are
highest towards the base (i.e., decrease upwards). Conversely, r
will be negative for taxa whose values increase up the
sequence. Results (in the data analysis file) include for each taxon
r, the
significance level for the difference between r and zero,
and Fisher's z, which can be used further to investigate
differences between values of r. For 95% confidence
values, look for values of 'signif' that are less than 0.05.
See Press et al. (1992) for further details.
- calculation of Spearman's Rank Correlation Coefficient for each taxon.
This is a non-parametric statistic, making no assumptions about the
underlying distribution of the data.
It is a means of detecting 'trend' in the dataset. The coefficient
is based on the rank order of the values for the taxon concerned and
assessing the degree to which the rank order is the same as the
ordering of the samples (by depth or time). If the taxon values
increase continuously along the sequence, the correlation
coefficient will be high and significant. If there are no trends
in the data, the coefficient will be low (near zero). The sign of the
correlation coefficient indicates the direction of the trend. In the
normal situation where depth (time) values increase numerically down
a sequence, the coefficient will be positive for taxa whose values are
highest towards the base (i.e., decrease upwards). Conversely, the
coefficient will be negative for taxa whose values increase up the
sequence. Results (in the data analysis file) include for each taxon
the Correlation Coefficient 'r(s)', its significance 'signif.',
the sum-squared difference of ranks 'D', the number of standard
deviations by which D differs from zero 'num of sd', and the
significance level for the difference from zero. For 95% confidence
values, look for values of 'signif' that are less than 0.05.
See Press et al. (1992) for further details,
and Gauthier (2001) for
some simple examples of use in environmental research.
- calculation of Kendall's Tau. This is another statistic that can be
used for detecting trends in the values for taxa. It is even more
non-parametric than Spearman's, being based only on the relative
ordering of values: higher, lower, or the same.
If the taxon values
increase continuously along the sequence, Tau
will be high and significant. If there are no trends
in the data, Tau will be low (near zero). The sign of
Tau indicates the direction of the trend. In the
normal situation where depth (time) values increase numerically down
a sequence, Tau will be positive for taxa whose values are
highest towards the base (i.e., decrease upwards). Conversely, Tau
will be negative for taxa whose values increase up the
sequence. Results (in the data analysis file) include for each taxon
Kendall's Tau, the number of standard
deviations by which Tau differs from zero 'num of sd', and the
significance level for the difference from zero. For 95% confidence
values, look for values of 'signif' that are less than 0.05.
See Press et al. (1992) for further details.
Output from all three analyses is sent to the data analysis file
(selected from menu Ec);
This option toggles `on' and `off'.
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Copyright © 1995-2007 K.D. Bennett
Archaeology and Palaeoecology | 42 Fitzwilliam St | Belfast BT9 6AX | Northern Ireland | tel +44 28 90 97 5136
Archaeology and Palaeoecology | The 14Chrono Centre | URL http://www.qub.ac.uk/arcpal/ |
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