When out walking I make a serious effort to
record the insects that I come across. Obviously most, but not all,
are hoverflies. On several occasions I have
seen relatively uncommon saproxylic species well away from woodland.
Two species immediately come to mind: Myolepta dubia, which I
found in several places last year, and Mallota cimbiciformis
which I found once in a tree-lined avenue. I recall, however,
recording Mallota at
Thrislington Plantation (an open grassland) a decade or more ago. At
the time I thought it odd because there were no decent-sized trees
for at least a mile in any direction.
Casting
the mind wider, last year I found the snipe fly Chrysopilus
erythrophthalmus ovipositing on
an isolated Black Poplar where it had been felled and in the same
area found the cranefly Gnophomyia viridipennis.
Both species breed in decaying sap, a highly transient habitat. They must have arrived within a year of the tree being felled: so where did they come from?
Do we need to develop a register of mobility attributes?
Once
one starts to think about insect mobility, the question then arises: do we
actually know much about the mobility of insects of conservation
interest? I think we are just starting to scrape the surface. Work on
the Aspen Hoverfly Hammerschmidtia ferruginea
has shown that it is actually comparatively mobile. Again, I have encountered this species substantial distances away from potential breeding sites. By inference, I think we
can also assume that Callicera rufa
is very mobile, given that it is now cropping up at a wide variety of English localities.
Conversely,
there are other species that appear to be anything but mobile, or
they are so specialised that those individuals that stray never find
suitable habitat? Examples that come immediately to mind include
Caliprobola speciosa
that is seemingly confined to the New Forest and Windsor Great Park,
and the Pine Hoverfly Blera fallax
that is restricted to two closely approximated localities in
Speyside.
Where
are, and which are the intermediates?
Relevance to conservation management
When
I worked in the Invertebrate Site Register Team back in the 1980s,
the thinking was that saproxylic species were relatively immobile.
After all, if they flew too far, they would end up in a wilderness of
open countryside! That approach was clearly wrong! Or at least was
it? It seems to me that we need to think in much more detail about
insect mobility from a conservation management perspective. Many invertebrates utilise micro-features that are transient to some extent and so they must move as the situation demands. The crucial point is that the landscape needs to support sufficient of these micro-features as a constant asset, even if the individual features appear and disappear.
There
are of course the flagships for meta-populations such as Marsh
Fritillary Butterfly. But, who is thinking about strategic
distribution of micro-habitats for other invertebrates? Conservation
strategies tend to focus on big projects – major site developments. Perhaps one of the most useful programmes might be to work on
relatively small features that are important and distinct
micro-habitats? For many years I have felt that there was a case for
locilised reduction in grazing pressure over base-rich seepage lines.
Perhaps too, there is a case for developing a strategic vision of a
landscape that will eventually be richer in veteran trees with
associated micro-habitats?
I also wonder if there is a need to develop projects that investigate the
availability of important invertebrate micro-habitats. Not
large-scale mapping of macro-features, but a log of important
micro-features such as trees with different types of rot and their
distribution across the landscape. Can we make any correlation between densities of such attributes and the distribution of important saproxylic assemblages? If there is a link (and I'm sure there is one) then the best way to improve the overall resource of saproxylic species is strategic planting to secure veteran trees across hitherto uninhabited landscapes.
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