Introduction to the guidance manual
14. Species assemblages
14.1 What is an assemblage ?
ASSIs/SSSIs, SPAs and Ramsar sites may each be notified
because of the presence of important assemblages of species. This
might seem straightforward, but in the context of species features
two situations can be envisaged:
- A colony of different species all occurring / living together,
where the total number of individuals is the key aspect of the
interest on the site (e.g. more than 20,000 seabirds on a SPA
site).
- A number of characteristic species which together form the
feature and usually share similar ecological or habitat
requirements (e.g. the co-occurrence of woodland or upland bird
species, or heathland invertebrates).
The term 'assemblage' can also be used in a third, functional,
way; when there are a number of features which co-exist, yet are
individually notified (i.e. they are features in their own
right). While it may be possible to assess them using the
same or very similar attributes, these species must be assessed as
individual features independently of any assemblage of which they
may also form a part (e.g. under scenario 1).
14.2 Scoring systems
For some taxonomic groups, the selection of SSSIs for species
assemblages is based on a simple scoring system with
clearly-defined thresholds for sites considered to be of SSSI
quality (e.g. vascular plants, breeding birds, amphibians and
dragonflies). Quantitative thresholds are also used to identify
SPAs and Ramsar sites for waterfowl assemblages, and SPAs for
seabird assemblages. In other cases (e.g. most invertebrate
assemblages), SSSI selection guidelines are less clearly
defined.
There are several possible approaches to monitoring species
assemblages. Where there are quantitative selection thresholds an
acceptable approach might be to evaluate the assemblage against the
selection criteria. For example, by recording presence/absence of
the constituent species and comparing the scores with the SSSI
selection guidelines and/or the assessment at the time of
notification. However, it needs to be recognised that not all
species may be recorded during one site visit, while the original
selection of the feature may have been made after several visits
using a compilation of data. It may be sensible, therefore, to set
a favourable condition threshold which takes account of such
circumstances. Recording relative abundance of the components of
the assemblage on a scale of common to rare, could provide
additional information for subsequent comparisons.
14.3 Indicator species
An alternative approach is to use indicator species to assess
the condition of the whole assemblage. Suitable indicators would
typically include species characteristic of a range of different
micro-habitats, and, if possible, conspicuous species that could be
recorded by a non-specialist. Both approaches should usually be
complemented by setting target values for habitat attributes which
relate to the features required for the maintenance of the
assemblage.