Comments on a recent post in the UK Hoverflies Facebook page
raise some important questions about the practice of retaining specimens. I
hope the following will help to set some perspective.
The dataset held by the HRS comprises a mixture of field
observations and preserved specimens. There would be very few records prior to
1976 without the collections of long-dead entomologists. Indeed, this is true
for most datasets involving invertebrates. The one problem with museum
collections is that they tend to be dominated (proportionally) by 'scarcer'
species and by species that are tricky to identify. This creates an unhelpful
imbalance that means that pre-1976 data are not ideal in presenting an image of
what the hoverfly fauna looked like in the past. The one thing we do know is
that certain species were regarded as 'prizes' (e.g. Volucella zonaria). Some data from this period are definitely
helpful in reconstructing our knowledge of particular species. Anybody wanting
to see this in action should look at two papers Stuart and I published on Volucella inanis and V. zonaria.
http://www.bacoastal.co.uk/Entomology/2004-Volucella-zonaria.pdf
http://www.bacoastal.co.uk/Entomology/2003-Volucella-inanis.pdf
Many of the species that were most prized were big and bold
(e.g. Callicera aurata). It is now
possible to read the accounts of field trips by one of the early Dipterists and
then actually hold the specimen the describe taking - which is an amazing link
back in history.
Evolution of the dataset
Fast speed forward to 1976. Between 1976 and around 2009 the
data held by the HRS was primarily supplied by people who at least partially
retained specimens. Over 50% of the data were supplied by around 20 people.
Those people generally record all taxa - in other words they tackle difficult
genera such as Cheilosia and Pipiza. Having voucher specimens is
essential if there are questions about a species' identity or if there is a
split. Even experienced recorders make mistakes and being able to check is
helpful. Only yesterday I spent the afternoon checking the IDs of specimens
forwarded for verification. Not all were right, even from very experienced
recorders. So, we must assume there are dodgy records in the dataset (some mine
I expect).
The degree to which records are dodgy is often difficult to
tell, but I have four species in mind where I think the maps definitely include
significant misinformation: Lejogaster
tarsata, Platycheirus immarginatus,
P. nielseni and possibly Eristalinus aeneus. In the case of the Platycheirus I think we will have to
restrict maps to cases where males have been recorded - females are too readily
confused with others. This means that we will only get a realistic picture from
specimens.
That leaves another 50% of data. What I have found is that
there is a strong separation between the records of the nucleus who retain
specimens and the remainder of the data, with far fewer records of tricky
species/genera, and far more of species that can to a greater or lesser degree
be identified from photographs or in the wild. Of course, we do get small
blocks of data from people who work all taxa but do relatively little
recording, so the data are not simply dominated by recorders who don't tackle
tricky species. These data exclude lists where I take one look and say
'Chinnery' - there are ways of telling how recorders behave and the sources
they use. They also exclude lists where it seems to me that the author has not
used the key or bothered to check on a species' distribution - the presence of
Scottish or coastal species in a list for a dry southern grassland is a fair
indication!
So, moving on to the era where the mantra is: take nothing but photos and leave nothing
but footprints. I am just finalising an analysis of species covered by
photographs over 2014. That highlights just over 130 species (I have excluded a
few photos of rare animals that were posted because I know they will arrive via
lists supplied by the author). I also have an analysis of what has not been
identified - no great surprises - dominated by Cheilosia, Pipiza, Platycheirus, but also including lots of
Syrphus and Eristalis. So, bearing in mind this dataset comprises over 10,000
records (all records extracted from internet sources in 2014), there is a new
influence on the dataset that will have to be taken into account when data are
analysed for trends.
Based on past analysis of photographic records, I reckon
that maybe 150 species will be recorded in this way, but that no more than 10
species will dominate the data, and no more than 35-40 will occur in sufficient
numbers to perform any year-on-year analysis. Whether numbers will be
sufficiently big to undertake latitudinal analysis remains to be seen, but I
suspect the list will be depleted further.
Should specimens be retained?
We therefore hit the point where one must ask the question 'is
it necessary to retain specimens?' If one wants to understand what is going on
in the natural environment there is a need for quantitative data. In broad
terms, that means trapping (and killing). But, trapping is fairly indiscriminate
and does not necessarily cover all taxa. Also, trapping can kill large numbers
of 'rare' species before this is detected. In the case of poorly known taxa
this may never be detected. So, although trapping has its place, it has many
drawbacks. If trapping is used to sample a narrow spectrum of animals then what
happens to the by-catch? Bearing in mind this can be voluminous, the chances of
it being tackled by a specialist are small. BUT, the data are quantitative and
can probably be repeated at suitable intervals, thus forming a long
time-series. One of the best examples of this is the Rothampstead moth survey.
Jenny Owen's malaise trap also produced a really valuable time-series from her
Leicester garden. These are rare, but valuable resources, and anything
Government funded is under threat, so may not be available in future.
The Rothampstead programme has already been cut. Its loss
would be catastrophic because it has highlighted a terrible decline in moth
populations. Those changes are not down to retaining specimens - they are a
mixture of climatic factors and anthropogenic changes to the countryside.
Similar declines can be detect for many other taxa, including hoverflies. About
40% of our hoverfly fauna is in decline. We know this from the HRS dataset,
which is supplied by a mixture of lethal and non-lethal sources, collected
largely in an ad-hoc manner. These data are not ideal, but they are the best we
have.
So, we now return to the question of retaining specimens in
this modern World. A relatively small number of people retain specimens and
many of them contribute extensive lists to the HRS. My guess is that around 150
people across Britain retain any level of specimens, and most retain very
little. The contribution they make to the dataset is considerable, however.
Perhaps not every specimen needs to be retained, but overall the impact of
specimen retention is negligible. Conversely, the impact of the contribution to
the dataset is considerable. Like it or not, we actually need people who are
prepared to retain specimens and are driven by this interest. If we rely on
non-lethal techniques then we will see a diminution in the value of the
dataset.
It is therefore important to put specimen retention into
context. Anybody who has watched social wasps hunting will know that they are
voracious killers. A single nest may kill many tens of thousands of insects.
Stuart and I did a bit of work in a small wood in Northamptonshire a few years
ago that showed there was a strong probability of about 1 wasp's nest for every
1.5 ha of woodland. (i.e. around 40 nests in 60ha). That mounts up to a huge
volume of invertebrate biomass. So social wasps are clearly important
regulators of invertebrates. They happily munch hoverflies and if they have the
same abilities of Anthrenus (museum
beetle) my bet is that they take rare species disproportionately. So, our
active Dipterist, working over the year, probably equates in impact to little
more than a few workers within a social wasp nest, spread over a much larger
area.
Ah, I hear you say, but if the 'collector' did not collect,
then there would be more insects. TRUE! FRACTIONALLY! But also there would be CONSIDERABLY
less data.
A further moral dilemma
So let us move on to the take nothing but footprints
argument. No hoverflies were killed in the making of this day out? Well, maybe.
But if you drive to your venue that may not be so. We know that huge volumes of
insects are killed in collision with cars. So, those who choose not to take
specimens but enjoy watching wildlife in special places are also taking an
informed decision to kill. It is just that they do so indiscriminately and with
little knowledge of what they are doing.
I have had this debate with several proponents of this
philosophy and am amazed by the answers they give - very largely about the fact
that this improves their quality of life and the death of the insects they kill
on the road is not intentional. How can this be? After all, they know that cars
kill insects and will be irritated by the splat marks on the windscreen when
they impair visibility. So, I fear, anybody who uses powered transport to
conduct their hobby is having a negative impact on insects. Who knows if their
victims are common or rare? The result is the same, but there is a difference
between this approach and that of the entomologist who retains specimens. One
generates partial data and the other more comprehensive data. Maybe this is a
broad generalisation, but I think the key philosophical question relates to the
contribution the deaths of insects make to our knowledge of insect ecology.
I therefore hold the view that the immoral issue is not
about whether or not specimens are retained; it is about the degree to which we
pursue our interests without making a contribution back to the wildlife we
love. Detailed recording at whatever level can make a difference in
highlighting the plight of wildlife. At least with robust data there is
something to influence politicians and decision-makers. The biggest threat to
wildlife is arguably the loss of taxonomically competent recorders whose
contributions are essential if we are to track the trajectory of wildlife
abundance.