|
Tool |
Advantages |
Drawbacks |
Suitability in EIF |
|
Chemical analyses |
|
|
|
|
LSC (Limit of Significant Contamination) |
Calculates specific value for contamination limits. |
Dependent of the selection of stations included in the
calculation. Does not give the status for the biological
condition. |
Unsuitable alone |
|
Univariate methods |
|
|
|
|
Shannon-Wiener H’ |
Internationally well-known and used statistic. Calculates a
specific value relating to disturbance. |
Not accepted as a measurement of effects of pollution. |
Unsuitable alone |
|
Hurlbert’s ES100 |
Internationally well-known and used statistic. Calculates a
specific value relating to disturbance. |
As above. |
Unsuitable alone |
|
Pielou’s J |
Internationally well-known and used statistic. Calculates a
specific value relating to disturbance. |
As above. |
Unsuitable alone |
|
Graphical/distributional methods |
|
|
|
|
Log-normal plots |
Internationally well-known and used statistic. |
Might indicate disturbance, but needs detailed information
on dominant species. Difficult to quantify. |
Unsuitable alone |
|
Multivariate methods |
|
|
|
|
Cluster analysis |
An internationally well-known and well-used method for many
years. |
Shows faunal differences between stations, but gives no
information on why such differences occur and what the
differences are. |
Unsuitable alone. Could possibly be used together with other
methods. |
|
MDS |
An internationally well-known and well-used method for many
years. |
As for the cluster analysis. However, combined with the
results from other analyses the reason for the gradient can
be identified. The scale of the method is relative, which
makes it difficult to assess the significance of the
observed differences between samples in the plot. |
Unsuitable alone. Could possibly be used together with other
methods |
|
CA |
An internationally known and used method. |
As for the Cluster analysis and MDS. |
Unsuitable alone |
|
CDI |
Combines biological and environmental variables. Calculates
a specific value relating to disturbance. |
The method has until recently not been available. Not
peer-reviewed nor internationally known or used. |
Best developed for EIF so far. Needs further evaluation and
practical use by external groups |
|
ANOSIM |
Calculates whether group of samples are significantly
different from each other. |
Based on relative differences between samples, as MDS. |
Unsuitable alone |
|
Relationship between biological and environmental
variables |
|
|
|
|
CCA |
Combines biological and environmental variables and shows
the correlations between significant environmental factors
and the faunal distribution. Internationally well-known and
used.
|
Does not have a scale relating to disturbance. |
Could possibly be used. Needs further development |
|
BIO-ENV |
Combines biological and environmental variables.
Internationally well-known and used. |
Does not have a scale relating to disturbance. Does not
indicate how particular stations or species are related to
disturbance. |
Could possibly be used. Needs further development |
|
Qualitative methods |
|
|
|
|
Top ten and indicator species |
Gives specific information on the dominant species. Can be
quantified. |
Has not been scaled earlier. Needs to be adjusted for each
specific field. |
Unsuitable alone. Could possibly be used together with other
methods. |
|
Faunal groups |
Evaluate the results from all analyses carried out (univariate-,
multivariate- and correlation analyses). Can be quantified.
|
Subjective and dependent on the person/institution carrying
out the evaluation. |
Unsuitable alone. Could possibly be used together with other
methods. |