Saving Wild Cats
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May 2015<br />
Issue 1<br />
All you need to<br />
know about<br />
butterfly<br />
colouration<br />
Inside:<br />
See Loch Lomond<br />
transformed with<br />
analogue.<br />
Vultures: What’s<br />
the situation<br />
now?<br />
<strong>Saving</strong> <strong>Wild</strong> <strong>Cats</strong><br />
Are breeding centres<br />
the answer?
Relax and<br />
enjoy our<br />
beautiful<br />
surroundings<br />
A note from the editor<br />
Welcome to the first issue of Nature’s Call, a monthly magazine dedicated<br />
to all things nature. You’ll find everything from wildlife to plants, insects to<br />
landscapes right here along with science and photography.<br />
This month the spotlight is on endangered species with two of our features<br />
on vulture populations and big cats. We look at how the vulture population<br />
is recovering from recent decline and also how breeding programmes in<br />
captivity may help to save endangered tigers and leopards in the future.<br />
In this issue you’ll also find regular features such as exhibition and<br />
product reviews, great tips on image analysis techniques and our day with a<br />
photographer. This month we stepped away from nature and biology to gain<br />
an insight into a day in the life of dance photographer, Ashley Holmes.<br />
I also took a trip to Scotland and visited beautiful Loch Lomond for some analogue photography. It was an<br />
amazing day with thick fog making the already breath taking scenery even more stunning. And of course<br />
developing film and seeing what you have when you get back is always exciting. The trip was definitely worth it and<br />
I hope you like the end result.<br />
Enjoy reading Nature’s Call!<br />
Page 18<br />
Debra McFarlane<br />
Editor<br />
Page 30<br />
3
Can the<br />
Contents<br />
Captive<br />
Animals in Captivity:<br />
Can the Captive Save the <strong>Wild</strong>?<br />
5<br />
A Day With a Photographer:<br />
Ashley Holmes<br />
Birds:<br />
Vultures, an endangered species<br />
Landscape: Analogue<br />
Photography Loch Lomond<br />
Exhibit Time:<br />
Unstable<br />
11<br />
12<br />
18<br />
24<br />
Fig 5: A captive<br />
Amur leopard<br />
(Panthera pardus<br />
orientalis)<br />
save the<br />
<strong>Wild</strong>?<br />
Fig 6: A captive<br />
Amur tiger<br />
(Panthera tigris<br />
altaica)<br />
Testing It Out:<br />
Intervalometer<br />
Photoshop Technique:<br />
Image Analysis<br />
Urban <strong>Wild</strong>life<br />
Small Worlds:<br />
A Closer Look at Colour<br />
25<br />
26<br />
28<br />
30<br />
Fig 7: A captive Amur<br />
leopard (Panthera pardus<br />
orientalis) feeding
Captivity<br />
In total, approximately 26 billion animals are kept in<br />
captivity whether in zoos, farms, breeding centres or<br />
research labs. There are arguments for and against keeping<br />
animals captive: from positive associations with education<br />
and conservation to concerns regarding animal welfare and<br />
cruelty.<br />
There are over 10,000 different species of captive animals<br />
and the way in which they react to captivity varies greatly.<br />
In general, captive animals live longer, healthier lives with<br />
greater breeding success than those in the wild. This is<br />
due to the fact that they are provided with food and water,<br />
protected from predators and have access to veterinary care<br />
when required. However, this is not the case for all animals; giraffes, African elephants and Asian elephants are<br />
examples of those that have shorter life spans in zoos than in the wild. The stresses induced by captivity itself may<br />
play a role in the negative effect on survival.<br />
Endangered <strong>Cats</strong> in Captivity<br />
There are approximately 11,000 tigers in captivity<br />
throughout the world. Only 1000 of these are kept in<br />
zoos with the remaining numbers being split almost<br />
equally between private ownership in North America<br />
and breeding centres, the majority of which are in<br />
China. In comparison to the 11,000 tigers in captivity, a<br />
mere 3000 are estimated to be present in the wild. This<br />
is a stark contrast to the 100,000 tigers that were living<br />
in the wild just a century ago, and human persecution is<br />
largely to blame for the population decline. Of the nine<br />
different tiger species that are known, three are already<br />
completely extinct. The territorial range occupied by<br />
tigers stretched from China to Turkey but this has also<br />
shrunk dramatically. Tigers now occupy only 7% of the<br />
area they used to.<br />
Tigers along with many other species of big cats, such<br />
as leopards and cheetahs, are classified as endangered<br />
and there are great fears that they may become extinct<br />
Fig 8: Giraffes<br />
(Giraffa<br />
camelopardalis)<br />
in captivity have a<br />
shorter lifespan<br />
in the wild. The African Lion (Panthera Leo) is<br />
considered vulnerable with population numbers having<br />
declined by 30% over the past 20 years leaving between<br />
30,000 and 35,000 individuals in the wild. Of the key<br />
populations, a number of which are in protected areas<br />
throughout Africa, 40% are in decline. The severest<br />
threat of extinction is that faced by the Amur leopard<br />
(Panthera pardus orientalis) with only around 70<br />
individuals left in the wild. Fifty of these inhabit an area<br />
in Russia’s Far-East and another small population can<br />
be found in China. Like tigers, the population of Amur<br />
leopards has suffered due to poaching and habitat loss.<br />
Amur leopards exist in zoos mainly in Europe, Russia<br />
and North America with a few also in Asian zoos.<br />
Their presence in zoos has contributed positively to<br />
their conservation in the wild through fundraising and<br />
increased public awareness. Research in zoos has also<br />
enabled essential data to be collated and for important<br />
genes to be maintained.<br />
Breeding & Genetics in Captivity<br />
Breeding programmes are one way in which zoos and<br />
breeding centres hope to increase population numbers<br />
with the possibility of eventually releasing individuals<br />
back into the wild.<br />
There are concerns over these breeding programmes<br />
as, with most endangered species, populations within<br />
captivity are relatively small. Even among small<br />
populations in the wild, breeding within these groups<br />
leads to a loss of genetic diversity as the gene pool<br />
is reduced. This can result in genetic mutations and<br />
reduces the chances of that population’s sustained<br />
survival. This is one problem incurred by the small<br />
numbers that make up the current wild Amur leopard<br />
population. In addition to this, captive animals also<br />
develop genetic adaptations in response to captivity<br />
through both natural and artificial selection.<br />
In order to minimise the chances of these genetic<br />
adaptations impacting a species’ chance for survival,<br />
measures are taken to control population growth and<br />
limit the number of generations reared in captivity. One<br />
way to do this is to delay reproduction by separating<br />
Fig 12: A captive<br />
Amur tiger<br />
(Panthera tigris<br />
altaica) grooming<br />
male and female members or by using reversible<br />
contraceptive methods. Separating males and females<br />
can lead to aggression and stress and so contraceptive<br />
methods may be better in terms of allowing social<br />
interactions to remain as natural as possible. The<br />
reversibility of these forms of contraception is vital<br />
especially when administered to individuals with strong<br />
genes and desirable traits.<br />
Contraceptive methods do have side effects however<br />
and these are shown to vary between species. The use<br />
of hormonal implants has been shown to result in a<br />
lower chance of successful reproduction in the Amur<br />
tiger (Panthera tigris altaica) whilst the African lion<br />
displays a loss of secondary sexual characteristics. Oral<br />
contraception leads to aggression in the Amur leopard<br />
and the African lion with the former also refusing food<br />
and the latter exhibiting weight loss and masculisation.<br />
In all three species, some forms of contraception also<br />
increase the likelihood of individuals contracting<br />
disease as a result of reproduction.<br />
Fig 9, 10 & 11: African Lion<br />
(Panthera Leo), Amur leopard<br />
(Panthera pardus orientalis)<br />
and Amur tiger (Panthera tigris<br />
altaica) in captivity<br />
7
Some conservation organisations are<br />
sceptical of breeding programmes and<br />
feel that efforts should be more focused<br />
on individuals that are already in the wild.<br />
They believe that animals such as tigers<br />
will naturally breed and recover population<br />
numbers successfully as long as measures are<br />
put in place to protect them from poachers.<br />
Although critically endangered, the Amur<br />
leopard population has grown from about<br />
35 individuals in 2007 to 70 at present.<br />
This is facilitated through conservation<br />
efforts to supplement feeding by increasing<br />
prey numbers, fighting against illegal<br />
poaching and protecting habitats. The fact<br />
that the ratio of male to females is 1:1 is an<br />
encouraging sign that this species could<br />
recover.<br />
For the regeneration of the Amur leopard,<br />
sourcing and releasing individuals from<br />
breeding populations may be the only<br />
viable option. Although the translocation<br />
of wild-caught individuals is preferable<br />
and also has a greater success rate over the<br />
release of captive-born animals in terms of<br />
reintroduction projects, this is not possible<br />
due to the small numbers that exist in the<br />
wild. Removing individuals and placing<br />
them elsewhere in an attempt to establish<br />
a new population would be detrimental to<br />
the survival of the already fragile species.<br />
Another option is to pair a captive-bred<br />
animal with a wild partner in order to<br />
facilitate learning. As Amur leopards are<br />
not social animals, this is again not a viable<br />
option.<br />
There are two programmes currently<br />
working towards the reintroduction of<br />
Amur leopards. As of 2008, the European<br />
Endangered species Programme (EEP) has<br />
130 leopards in Europe and Russia and the<br />
Population Management Program (PMP)<br />
has 97 leopards in North America. Leopards<br />
kept in zoos in Asia do not qualify for these<br />
breeding programmes due to issues with<br />
accessibility and genetics.<br />
A captive population are preferred to have<br />
90% of ‘wild’ genes present in their genetic<br />
make-up. The EEP population of leopards<br />
have just below that level at 88.9%. Members<br />
of the PMP population have no genetic lines<br />
that are not found in the EEP leopards. This<br />
limits the opportunity to increase genetic<br />
diversity through cross breeding between<br />
the two programmes. However, an attempt<br />
can be made to maintain desirable genes by<br />
pairing up individuals that are the strongest<br />
genetically. In the future it may be possible<br />
to artificially inseminate captive females<br />
with semen from wild males.<br />
All leopards must undergo health checks<br />
and screening before being considered for<br />
breeding programmes. This ensures that the<br />
individuals being used are genetically viable<br />
and will produce offspring that may have a<br />
chance of release into the wild.<br />
Fig 13: Captive animals like the Amur leopard (Panthera<br />
pardus orientalis) are provided with sufficient food
Fig 15: An image<br />
from Ashley’s<br />
banner.<br />
A Day with a Dance<br />
Photographer<br />
Before releasing captive animals into the wild, suitable<br />
areas must first be found. The requirements of these<br />
areas are generally that they are within a range historical<br />
to the species and that they are far enough away from<br />
the current wild population to avoid breeding between<br />
the two. It is believed that it is better to try to introduce<br />
a new population as apposed to building upon the<br />
existing one(s). This will prevent genes that have arisen<br />
due to captivity being passed on to the wild population<br />
and reduces the risk of potentially harming the fitness<br />
and chance of survival as a species.<br />
Other requirements would be adequate space and<br />
an abundance of prey. For tigers, the requirement is<br />
at least 100 km2 per tiger. Areas of this magnitude are<br />
not available in China and perhaps controversially, four<br />
Southern China Tigers (two males and two females)<br />
were released in South Africa in 2006 and 2007. This<br />
drew criticism due to the fact that tigers were never<br />
native to Africa and with only a 13% success rate of<br />
captive born species being reintroduced, many are of<br />
the opinion that money and efforts are best spent on<br />
conserving already wild populations. This low success<br />
rate can be attributed to a captive raised animal’s lack<br />
of experience in instinctive behaviours. These include<br />
hunting, exploring and avoidance of humans and<br />
predators. Captive animals are also more susceptible<br />
to disease and so this can also impede their chances of<br />
survival.<br />
Fig 14: A captive Amur<br />
leopard (Panthera pardus<br />
orientalis) leaping from a<br />
climbing structure<br />
Releasing Captive <strong>Cats</strong><br />
Projects such as the release of tigers in South Africa<br />
provide animals with live prey in order to help develop<br />
hunting skills. Few projects however ensure captive<br />
animals are not accustomed to humans. Given the<br />
degree of involvement humans have in caring for<br />
animals in captivity this would be difficult to enforce.<br />
However, releasing animals that do not view humans<br />
as a threat leaves them vulnerable at the hands of<br />
poachers. Ensuring that release areas are protected and<br />
are not within close proximity to areas where humans<br />
live is one way to eliminate this problem.<br />
Although animals may suffer stress as a result of<br />
captivity, many zoos demonstrate a high level of care<br />
for the animals they keep. Allowing people to visit<br />
zoos increases awareness of conservation projects<br />
and the vulnerability of endangered species. This in<br />
turn helps raise funds to facilitate projects and, using<br />
Amur leopards as an example, the majority of funds<br />
contributed to the conservation of wild animals are<br />
raised by zoos. Efforts are also being made to improve<br />
conditions and animal enclosures within zoos. Breeding<br />
programmes within zoos and specialised breeding<br />
centres serve as hope that more and more captive<br />
animals can be successfully released into the wild with<br />
the ultimate goal of regenerating population numbers<br />
and saving endangered species from extinction.<br />
Ashley Holmes (pictured<br />
top right) is a Leicester<br />
based photographer who,<br />
after a career in finance,<br />
began making a living from<br />
photography approximately<br />
four years ago. Starting out as an event photographer<br />
at sports games and tournaments, Ashley now focuses<br />
primarily on dance photography.<br />
I met Ashley for the first time at Groby Community<br />
College where the dance school, Dance Addict’s, were<br />
performing. This was their first show independent of the<br />
college and the dancers involved ranged from three year<br />
old beginners all the way to senior level dancers in their<br />
teens.<br />
Inside the college, the walls leading to the theatre are<br />
lined with photographs of past performances, displaying<br />
a sense of pride and documenting the history of the<br />
school and its students. As the photographer of these<br />
images, Ashley points out a few of his favourites and also<br />
shows me one that is of his own daughter.<br />
‘I fell into dance<br />
photography after<br />
photographing<br />
performances that my own<br />
daughters were part of ’ he<br />
explains. ‘I soon realised<br />
that outdoor photography<br />
in bad weather wasn’t<br />
something I enjoyed very<br />
much so I moved over to<br />
dance where performances<br />
take place inside’. Working<br />
mainly with local dance Fig 17: Ashley in action.<br />
schools, Ashley’s goal is to<br />
document the show and<br />
produce images that act as a lasting memory for both<br />
parents and the dancers themselves. As well as capturing<br />
all the action of the performances, Ashley also attends<br />
the dress rehearsal and at some shows even sets up a<br />
small studio where dancers can pose for portrait images.<br />
Watching the dancers perform can be quite an<br />
emotional experience especially when it involves the<br />
younger ones. You can therefore see the importance of<br />
Ashley’s work and the role he plays in encompassing<br />
that proud moment of a parent seeing their child on<br />
stage. For that reason he focuses on<br />
individuals rather than group shots.<br />
‘Parents don’t tend to want a group<br />
photograph. They prefer an<br />
image of their own child that<br />
they can display proudly in<br />
their home and look back on for years to come’.<br />
Ashley explains to me that when photographing a<br />
Fig 16: Ashley Holmes<br />
dance performance, lighting is the main challenge. As he<br />
has no control over the stage lights and is unable to use<br />
flash, he must do all that he can in camera to overcome<br />
the dark conditions, spot lights and multi-coloured<br />
lights that make up a dance show. Shooting without a<br />
tripod on a Canon 5D Mark II and almost always using<br />
a Canon 70-200mm f2.8 lens, Ashley uses high ISO,<br />
fast shutter speed and wide aperture. Each plays an<br />
important role in the final outcome of his images. High<br />
ISO accounts for the dark lighting whilst wide aperture<br />
allows as much light as possible to enter the camera. This<br />
then allows the use of a fast shutter speed, which freezes<br />
the movement of the dancer.<br />
Fig 18: The lighting<br />
at a dance show<br />
can prove tricky at<br />
times.<br />
After the show it’s time for a quick turn around in<br />
selecting the best images, editing if necessary and<br />
making them available for dancers, teachers, friends and<br />
family to view online. Ashley offers generous discounts<br />
for the purchase of multiple images and his website<br />
testimonials are filled with great reviews and people<br />
thanking him for extra images and excellent deals.<br />
So what does the future hold for Ashley? Continuing<br />
with dance photography whilst pursuing and expanding<br />
on his portrait photography are his main goals. ‘Anyone<br />
with a camera is a photographer. The main thing is<br />
to keep yourself motivated to get out there and do it<br />
professionally’.<br />
You can view Ashley’s images and find out more on his<br />
website at www.ashleyholmesphotography.co.uk<br />
11
Fig 19: The population of cinereous<br />
vultures (Aegypius monachus) came<br />
under threat in Asia.<br />
$6.9 million. In India, the health costs incurred as a<br />
result of fewer vultures is approximately $1.5 billion per<br />
year. This is due to an increase in the number of dogs<br />
feeding on carcasses and the presence of rabies.<br />
Despite the important role they play, little is<br />
being done to raise awareness and document the<br />
consequences of the population decline in recent years.<br />
Of the 23 vulture species present today, 14 or 61% of<br />
the world’s vulture species are in danger of becoming<br />
extinct. The most rapid declines have been seen in<br />
Africa, Asia and parts of Europe where poisoning of<br />
vultures, both intentionally and unintentionally, is<br />
thought to be a major cause. Poisoning is commonly<br />
carried out by poachers in a bid to disguise the locations<br />
of their activities and also as a result of poisoning<br />
carnivores that are predators of livestock. Other causes<br />
of population decline can be attributed to collisions with<br />
power lines and wind turbines, poaching for medicine<br />
and in revenge for the killing of new-born lambs<br />
Vultures have been targeted for centuries due to lack<br />
of education and ignorance with people believing that<br />
they were in fact responsible for filthy drinking water<br />
and the spread of anthrax. They are also connected to<br />
superstitious beliefs and in some cultures are believed to<br />
represent evil spirits.<br />
Why so vulnerable?<br />
Vulture populations are particularly vulnerable to<br />
extinction due to attributes such as delayed maturity,<br />
low reproductive rates and high adult longevity. Their<br />
reproductive rates are in fact the lowest among all<br />
birds. Coupled with the fact that vultures usually feed<br />
communally and large numbers can therefore be wiped<br />
out by feeding on a single carcass, their population<br />
numbers are extremely vulnerable to high mortality<br />
rates. The high longevity of vultures leaves them<br />
exposed to the bioaccumulation of toxins, the effects<br />
of which are sub lethal in terms of immune responses<br />
and reproductive success. The fact that they eat dead<br />
animals and waste products increases their exposure to<br />
contaminants.<br />
Vultures<br />
an endangered species<br />
An Overview<br />
With sharp eyesight and in some species, a keen sense<br />
of smell, vultures have established themselves as the<br />
most successful scavengers and the only known obligate<br />
scavengers on land. As vultures are amongst some of the<br />
largest flying birds,<br />
they are able to cover<br />
vast areas in search<br />
for food. Gliding<br />
allows them to make<br />
use of upward air<br />
movements and they<br />
therefore have the<br />
ability to cover long<br />
distances rapidly and<br />
Fig 20: Vultures cover vast areas<br />
and use their wings to glide.<br />
with relatively little<br />
energy expenditure.<br />
Their large size also enables them to consume a higher<br />
volume of food, store more for energy reserves and take<br />
precedence over smaller scavengers competing for the<br />
same food source.<br />
Although plagued with a generally negative<br />
perception, with Charles Darwin himself labelling<br />
them as ‘disgusting’, vultures contribute greatly to<br />
society in a number of ways. One of the most important<br />
ways is preventing the spread of disease through<br />
their scavenging behaviour and the decomposition of<br />
carcasses. Their digestive tracts are very acidic, with pH<br />
values of approximately 1-2. This plays an important<br />
role in destroying bacteria and limits the chances of<br />
vultures themselves spreading disease.<br />
They have also been shown to be of important<br />
economical value. Through scavenging, vultures in<br />
effect provide a free sanitation service and conservation<br />
efforts in Nepal have saved the country an estimated<br />
ASIA<br />
In India, vultures are relied upon heavily to feed on<br />
the carcasses of cattle, thus aiding in and speeding up<br />
the process of decomposition disposal, which in turn<br />
prevents the spread of disease.<br />
In the early nineties, vulture populations in India<br />
dropped to 1% of what they were. As a result of reduced<br />
vulture numbers, there was an increase in the number<br />
of disease-ridden species of feral dogs and rats feeding<br />
on carcasses. Cases of human anthrax also became more<br />
common as people were themselves handling infected<br />
carcasses in the absence of vultures.<br />
It took ten years to discover the cause however it was<br />
eventually linked to diclofenac, a veterinary drug used<br />
to treat livestock. It caused the population of Gyps<br />
vultures alone to drop by more than 95%. Vultures<br />
inadvertently ingested the drug and become poisoned<br />
when feeding upon the carcasses of livestock that had<br />
received diclofenac as a means of medication. This then<br />
lead to kidney failure in the vultures and consequently,<br />
their fatality.<br />
Studies show that the level of drugs present in dead<br />
livestock was indeed sufficient to cause the population<br />
decline in vultures. The drug was banned in India,<br />
Pakistan and Nepal in 2006 and later in Bangladesh<br />
in 2010. There is evidence to suggest that vulture<br />
populations have begun to recover as a result of<br />
this ban. Between 2007 and 2011, three species of<br />
India<br />
endangered Gyps vultures showed no population<br />
decline in India and the oriental white-backed vulture<br />
showed signs that their population numbers were<br />
beginning to increase in both India and Nepal. The<br />
resident species of Gyps vultures were the most severely<br />
affected populations and two of these (Gyps indicus and<br />
Gyps bengalensis) are classed as critically endangered<br />
on the IUCN Red List. Migratory species such as the<br />
cinereous vulture (Aegypius monachus) were also<br />
affected by the use of diclofenac but their presence in<br />
other areas such as Europe prevented them from being<br />
as badly affected as resident species.<br />
Full recovery will take time as well as continued efforts<br />
from both conservation organisations and governments.<br />
Overall however the rate at which population numbers<br />
are declining has slowed, implying that there is hope for<br />
the future of vultures in Asia.<br />
13
AFRICA<br />
Africa has seen a similar rate of population decline<br />
as India and other parts of Asia. The causes however<br />
are different and unlike in Asia, there has been little<br />
or no government support in vulture conservation.<br />
This may be due to the fact that in Asia, the cause of<br />
population decline can be put down to one specific<br />
reason. In Africa however there are multiple causes and<br />
these also vary from region to region. This may prevent<br />
governments from getting involved, as there is no clear<br />
focus or strategy to work from.<br />
Poisoning and poaching appear to be the main causes<br />
of the decline of vulture populations. In West Africa,<br />
the decrease in vulture numbers has been linked to<br />
poisoning and hunting for medicine and food. In<br />
Eastern Africa, studies in Kenya and Uganda suggest<br />
that poisoning through the use of Ferdan as an<br />
agricultural pesticide may be a major cause. Despite<br />
these findings and a plea to the Kenyan government<br />
to ban the sale of such pesticides no action has so far<br />
been taken. There have been dramatic decreases in<br />
population numbers of other species and so such a ban<br />
or at least stricter control is imperative for the sake of<br />
other wildlife as well as vultures. In Kenya, without<br />
vultures, the time taken for the decomposition of a<br />
carcass was shown to triple. The number of mammals,<br />
the time they spent at a carcass and the contact each had<br />
with other scavengers also increased. This suggests that<br />
a decreased vulture presence could result in diseases<br />
being transmitted between animals at carcasses.<br />
Another way that vultures play an important role in the<br />
environment is by indicating to predators the location<br />
of a potential food source through their scavenging<br />
behaviour. This has been shown to occur with hyenas<br />
and lions although vultures are at a distinct advantage<br />
given their aerial point of view and the ability to arrive<br />
at a food source rapidly and in larger numbers. This aid<br />
in detecting a food source however does encourage the<br />
flow of energy within the ecosystem.<br />
In some parts of Africa, certain species are considered<br />
to be extinct. In Morocco, the lappet faced vulture<br />
(Torgos tracheliotus) and the cinereous vulture are no<br />
longer present. Globally, they are classified as vulnerable<br />
and near threatened respectively. In Southern Africa,<br />
the Egyptian vulture (Neophron percriopterus) is<br />
now extinct as a breeding species and is considered<br />
endangered.<br />
Africa<br />
Fig 21 : The lappet faced vulture (Torgos<br />
tracheliotus) is extinct in parts of Africa.<br />
The lappet<br />
faced vulture<br />
is extinct in<br />
Morocco<br />
The Egyptian<br />
vulture is<br />
extinct in<br />
Southern<br />
Africa<br />
Fig 22 :The Egyptian vulture (Neophron<br />
percriopterus) is now classed as endangered.
The Future<br />
Spain<br />
EUROPE<br />
In Europe, deliberate poisoning of carnivores was a<br />
major threat to vultures that then fed on the carcasses<br />
of these animals. The introduction of strict regulations<br />
and penalties has reduced incidents of poisoning. In<br />
Spain, dogs are now trained to detect such poisons and<br />
the success rate is 70% higher than when humans work<br />
alone.<br />
Although the risk of poisoning has been reduced,<br />
vulture populations are still at risk of decline. In Spain,<br />
the closure of supplementary feeding stations due to<br />
concerns over bovine spongiform (more commonly<br />
known as mad cow disease) and the spread of infection<br />
as a result of cattle carcasses not only lead to a food<br />
shortage but also put birds at an increased risk of<br />
collision with wind turbines due to a change in foraging<br />
behaviour.<br />
Studies in Spain show that griffon vultures (Gyps<br />
fulvus) are the most commonly killed bird species<br />
and whilst these types of mortalities may not have a<br />
significant effect on all bird populations, they do appear<br />
to impact vulnerable species such as vultures.<br />
One suggestion as to why griffon vultures are more<br />
frequently killed by wind turbines than any other bird<br />
species is that their visual field contains large blind spots<br />
which in effect make them sightless in terms of the<br />
direction in which they are travelling.<br />
Wind turbines are positioned in windy regions in<br />
order to optimize the conditions and maximize the<br />
2005 - 2009:<br />
45% increase in<br />
the presence of<br />
wind farms in the<br />
European Union<br />
potential for energy production. Birds, likewise, use<br />
wind to their advantage to increase gliding efficiency<br />
and to conserve energy during flight. This increases the<br />
likelihood that wind farms will be in the flight path of a<br />
number of birds, especially raptors.<br />
A study in 2008 showed that selectively stopping<br />
wind turbines that were found to cause the majority of<br />
fatalities, significantly decreased the mortality rates of<br />
vultures. Calculations suggest that the stopping of wind<br />
turbines for that reason would result in only 0.07% less<br />
energy production per year. It therefore appears to be<br />
a viable option to prevent further decline of vultures in<br />
Europe.<br />
Fig 23 : Griffon vultures (Gyps fulvus) are vulnerable to<br />
collissions with wind turbines in Europe.<br />
Although many may find vultures vulgar and repulsive,<br />
there is no denying the fact that they play an integral<br />
role in the sanitary conditions of our environment.<br />
By aiding in the decomposition of carcasses vultures<br />
therefore prevent the spread of disease and deter the<br />
presence of disease-ridden animals such as rats and<br />
feral dogs. Continued efforts in Asia are vital to ensure<br />
the recovery of vulture populations after almost being<br />
wiped out through the use of diclofenac for livestock.<br />
Although efforts are being made by conservationists<br />
in Kenya and South Africa, more widespread action<br />
and support from governments both financially and to<br />
implement laws will be fundamental in the progress of<br />
protecting and saving vultures throughout the African<br />
continent.<br />
In Europe, reduced cases of poisoning has helped<br />
towards conserving vulture populations however<br />
increased use of wind farms appears to be posing a new<br />
threat specific to vultures. Care must therefore be taken<br />
in the positioning of new wind turbines to ensure they<br />
do not coincide with the flight path of vultures and<br />
Birds in<br />
Flight<br />
11:30am 2:00pm<br />
4:15pm<br />
other raptors. Breeding programmes are in place and<br />
the success of these in terms of releasing captive bred<br />
birds into the wild may be imperative to the recovery of<br />
vulture populations especially in Africa.<br />
Fig 24 : The claws of a of cinereous<br />
vulture (Aegypius monachus).<br />
Gloucester<br />
GL18 1JJ<br />
www.icbp.org<br />
17
Analogue<br />
Fig 25: The view from Loch Lomond captured using a medium format camera<br />
Photography
Loch Lomond<br />
Fig 27: The top of Ben Lomond on a misty day<br />
Loch Lomond and the Trossachs National Park<br />
comprises an area of 720 square miles including<br />
farmland, forest and moorland as well as 39 miles of<br />
coast line. With breath taking scenery and diverse<br />
landscapes the park is situated conveniently within a<br />
one-hour drive of half the Scottish population. It is also<br />
home to over 15,000 people and attracts tourists from<br />
all over the world who come to enjoy both land and<br />
water activities such as walking, climbing, canoeing and<br />
water skiing.<br />
The national park was officially opened by Princess<br />
Anne in July 2002 and is split up into four areas: Loch<br />
Lomond, Argyll Forest, The Trossachs and Breadalbane.<br />
Although classed as a living, working area, the park<br />
is also abundant in wildlife. It is one of the few places<br />
where red squirrels can still be spotted and also provides<br />
habitats to otters, water voles, black grouse and deer.<br />
There are a number of osprey breeding pairs that return<br />
to the park each spring to mate.<br />
The park consists of 22 large lochs, which make<br />
up 6.5% of the total area. Loch Lomond is the main<br />
attraction with respect to these lochs and is also the<br />
largest body of freshwater in Great Britain.<br />
On the East shore of Loch Lomond stands Ben<br />
Lomond, a mountain that is 3193 feet tall (974 metres).<br />
Ben Lomond is Scotland’s most southerly munro. A<br />
munro is a mountain that is 3000 feet or higher and<br />
within the national park, there are 23 of them.<br />
The majority of Ben Lomond is designated as a Site<br />
of Special Scientific Interest (SSSI) due to its range of<br />
upland habitats present at both low and high altitudes.<br />
It is also part of the National Trust for Scotland and is<br />
home to a national memorial for those who lost their<br />
lives at war. Being one of the most popular hill walks<br />
in Scotland, the trust must work hard to ensure the<br />
conservation of natural wildlife and their habitats.<br />
It also works in conjunction with tenanted farmers<br />
to ensure grazing activities by sheep and cattle are<br />
balanced with nature.<br />
Fig 26: A pier and hills in the distance at Loch Lomond
Digital vs<br />
Analogue<br />
Fig 28 & 29: Comparison of a view taken with a digital then<br />
medium format camera<br />
Photography has always been popular and, by the<br />
early 1970’s, a camera could be found in almost<br />
every household in the USA and Western Europe.<br />
The function of photography in analogue and digital<br />
processes has always been the same. The hierarchy of<br />
these functions however has changed as we have moved<br />
into the digital era. Analogue photography was a means<br />
of creating memories first and foremost and images<br />
were usually put together in photo albums or kept in<br />
shoeboxes. More often than not a date, location and<br />
the names of those in the photograph<br />
would be listed. This served primarily<br />
as a way of capturing and preserving<br />
memories and images would later be<br />
used to illustrate stories and to share or<br />
reminisce with others.<br />
In comparison to analogue<br />
photography, digital images are rarely<br />
transformed to hard copies and are<br />
instead posted on social media, blogs<br />
or sent to others electronically. Images<br />
are now shared as experiences rather<br />
than a physical, tangible object. Digital<br />
photography, especially with the<br />
introduction of smart phones, provides<br />
a real-time experience whereby a person<br />
can take, send, receive and even edit<br />
images in a matter of seconds. Due to<br />
the abundance and saturation of digital<br />
images, they are less frequently put<br />
together as a collection and although<br />
these images serve as memory also,<br />
the primary function has shifted to<br />
that of communication. Nowadays,<br />
images are so easily taken and shared<br />
online via social media or messaging<br />
services that it is use as a method<br />
of conversing. Whereas in the past<br />
photography was used as a means of<br />
capturing important, special or unique<br />
events, digital photography now allows<br />
people to capture everyday incidences such as a pretty<br />
sunset, delicious food or a new purchase. The younger<br />
generation more often than not regards their images<br />
as temporary reminders as apposed to a permanent<br />
record of their memories. Reminiscent of postcards as<br />
a snapshot of a person’s holiday, digital images are to be<br />
discarded. Especially for those documenting every day<br />
occurrences, they serve more as moment in time rather<br />
than mementoes over time.<br />
Digitisation of photography offers more control<br />
over the final outcome of our images, as we are able<br />
to process, edit and manipulate them with both ease<br />
and speed. Other than the initial cost of a camera,<br />
editing software and equipment, be it a laptop, smart<br />
phone or desktop computer, digital photography is a<br />
relatively inexpensive process. Compared with analogue<br />
photography where there are only a certain number of<br />
exposures per roll of film, digital photography offers an<br />
almost endless capacity for image capture. Along with<br />
the ability to review and delete images as you go, there<br />
is no real need to be selective with regards to where,<br />
when and how<br />
often you release<br />
the shutter. As<br />
mentioned before<br />
however, this<br />
saturation of<br />
images is what<br />
leads to them<br />
being overlooked,<br />
left aside and<br />
perhaps stored<br />
in a computer<br />
file never to be<br />
looked at again.<br />
With analogue<br />
photography<br />
more care and<br />
consideration<br />
is taken before<br />
taking a picture<br />
and there is<br />
a sense of<br />
anticipation<br />
and pride over<br />
what will be on<br />
the film when<br />
it is developed.<br />
The downside<br />
of analogue<br />
photography<br />
is that if an<br />
image goes<br />
wrong, it won’t be apparent until after its been taken<br />
and developed. With digital cameras, reviewing the<br />
image allows you to check the settings are correct and<br />
depending on the subject, enables you to take as many<br />
images as needed to get it right. This is a wonderful<br />
development as with analogue photography, a wasted<br />
film costs not only money but also time spent capturing<br />
and developing the images. Of course, things can go<br />
wrong with digital photography as well in the form of<br />
erased or faulty memory cards and depleted batteries.<br />
For professional photographers using digital SLRs,<br />
the ability to review images and make adjustments<br />
accordingly is of great benefit to their work. Likewise,<br />
the average person taking images of a special event such<br />
as a birthday celebration or a wedding will be safe in<br />
the knowledge that their photograph has turned out<br />
ok and the moment has been captured successfully.<br />
However, advances in photography have taken away<br />
the ability for one to take a picture and forget about<br />
it. Analogue photography allows you to appreciate<br />
your surroundings and to stay in the moment as once<br />
you have taken an<br />
image there is no<br />
Fig 30: A digitally coloured image of the view<br />
going back. With<br />
from Loch Lomond<br />
digital photography,<br />
there is a tendency<br />
to take a picture<br />
then scrutinize<br />
over it whilst<br />
simultaneously<br />
missing what is<br />
going on around<br />
you.<br />
Although unique<br />
entities, analogue<br />
and digital<br />
photography do<br />
not always need to<br />
be thought of as<br />
separate from one<br />
another. Advances<br />
in technology and<br />
image manipulation<br />
can be applied to<br />
analogue techniques<br />
also. The scanning<br />
of film allows us<br />
to convert our<br />
negatives into<br />
a digital image.<br />
An under or<br />
overexposed image<br />
may be salvaged through editing and adjustments to<br />
exposure, highlights and shadows. An image can be<br />
transformed from black and white to colour using<br />
colourisation techniques and images can be stored or<br />
shared without incurring the cost of printing.<br />
Even with such advances in technology, there is room<br />
for both digital and analogue photography. Digital<br />
brings with it fresh, modern images whereas analogue<br />
produces classic, timeless pieces that remind us of the<br />
history of photography.<br />
23
Review Corner<br />
Exhibit Time<br />
Review Corner<br />
Testing it Out<br />
This month we’re in Derby at the Format International<br />
Photography Festival. With multiple exhibitions featuring<br />
contemprary photography, we decided to check out<br />
Unstable, an exhibit that challenges the concept of<br />
photography as we know it.<br />
Unstable is an exhibition that makes<br />
up part of the Format Photography<br />
Festival in Derby. Featuring<br />
the work of five photographers,<br />
Unstable defies the concept of<br />
photography as a permanent record<br />
and challenges us to look beyond<br />
our initial perception of what we see<br />
and accept as reality.<br />
Each artist displays a body of<br />
work that has been developed using<br />
heat sensitive materials or that is<br />
left unfixed. As a result, the images<br />
displayed will change throughout<br />
the exhibition and will be destroyed<br />
by the very same thing that is<br />
required to create them – light.<br />
Regardless of whether or<br />
not you are interested in the<br />
Exhibition Highlight<br />
Anthony Carr’s exhibit<br />
entitled Lost Moon is the<br />
most interactive and perhaps<br />
most awe inspiring of the five<br />
exhibits. With an interesting<br />
story behind it, this exhibition<br />
is a combination of fact<br />
and imagination, depicting the<br />
whereabouts of the Apollo 13<br />
rocks distributed by the Nixon<br />
Administration in the 1970’s, a<br />
number of which were stolen or<br />
misplaced.<br />
Using thermochromic ink over<br />
black and white photograph<br />
we see what appears to be a<br />
solitary piece of rock on a black<br />
background.<br />
techniques behind these images, this<br />
exhibition provides an interactive<br />
and wondrous experience that<br />
people of all ages can appreciate and<br />
enjoy.<br />
The Space<br />
Photo Parlour is a small but open<br />
space tucked away on Monk Street,<br />
away from the main hub of venues<br />
playing host to Format Festival’s<br />
other offerings. Located above an<br />
old garage, you get a sense that you<br />
are entering an abandoned, arty<br />
warehouse. As Photo Parlour is a<br />
traditional dark room, it seems a<br />
Fig 32: One of Anthony Carr’s heat sensitive pieces.<br />
By heating the images using the<br />
hairdryer provided the blackness<br />
disappears to reveal a setting<br />
within which the rock is situated.<br />
At first glance you believe you<br />
are looking at something that is a<br />
part of a outer space. The reality<br />
of where the piece of rock actually<br />
is however, is quite different from<br />
the one that we perceive.<br />
Fig 31: Ky Lewis’ lumen prints<br />
entitled ‘Evanecent Growth’.<br />
particularly fitting venue for this<br />
exhibition.<br />
The Exhibits<br />
Unstable showcases a series of<br />
images that are not always what they<br />
seem, do not remain<br />
the same over time but<br />
still portray a sense of<br />
honesty and realness.<br />
Each exhibitor has<br />
contributed a unique<br />
diplay that enables the<br />
viewer to question the<br />
role of photography<br />
in both a comparative<br />
and contrasting way.<br />
From highlighting<br />
how history can<br />
be portrayed in an<br />
untrue manner to showing that<br />
without photography it can be<br />
forgotten completely, this exhibit<br />
leaves food for thoguht as to how<br />
essential it is that an image leaves<br />
behind a permanat record. In terms<br />
of preserving and documenting<br />
history it would seem yes, however<br />
in the eyes of an artist it may not<br />
always be necessary.<br />
What is an intervalometer?<br />
An intervalometer is a device<br />
that releases the camera shutter<br />
at specific intervals without you<br />
having to manually do so. It allows<br />
you to control how often your<br />
camera’s shutter opens, how many<br />
images to capture and even how<br />
long the shutter stays open for.<br />
When would I use an<br />
intervalometer?<br />
An intervalometer can be used to<br />
capture time-lapse sequences or as a<br />
remote shutter release.<br />
Using an intervalometer for time<br />
lapse means that you can set your<br />
camera up and leave it to capture<br />
images over a long period of time.<br />
It also eliminates camera shake<br />
caused by the vibration of manually<br />
pressing the shutter and ensures that<br />
the interval at which the images are<br />
taken is timed accurately.<br />
As a remote shutter realease, the<br />
cord allows you to stand a short<br />
distance from the camera providing<br />
a simple solution for problems such<br />
as you casting a shadow onto your<br />
subject.<br />
What I liked:<br />
The digital display counts down<br />
both the time until the next shutter<br />
release and the number of images<br />
Fig 35 - 38 time lapse<br />
sequence of a daffodil<br />
opening using an<br />
intervalometer set to<br />
capture an image every<br />
five minutes.<br />
left to capture. There are also<br />
warning lights – a green one to let<br />
you know the shutter is about to<br />
be released and a red one that stays<br />
on for the duration of the shutter<br />
being open. An optional ‘beep’ also<br />
sounds when the shutter is open.<br />
The hold button is useful when<br />
using it as a remote shutter as it<br />
prevents you from accidentally<br />
releasing the shutter too early.<br />
Running on two AAA batteries,<br />
the intervalometer does not appear<br />
to use up too much power so<br />
you shouldn’t need to replace the<br />
batteries too often.<br />
What would make it<br />
better?<br />
A keypad that allows you to punch<br />
in the digits to set time and number<br />
of images would be useful. The<br />
arrow keys function well however<br />
if you want to capture say 200<br />
images, that’s an awful lot of button<br />
pressing to set your target number.<br />
The alternative would be to set it<br />
at 399, by pressing the down arrow<br />
once from zero and manually stop it<br />
when ready.<br />
It takes a bit of getting used to in<br />
terms of what to press to confirm<br />
a selection, what to press to move<br />
to the next section etc. After a few<br />
MC-36B intervalometer<br />
Fig 33 & 34 (below):<br />
Intervalometer<br />
attempts however you will soon get<br />
the hang of it.<br />
After the first time using this<br />
intervalometer I can see that the<br />
ink on the digital display is faded<br />
at one point. I can only assume<br />
that this will deteriorate further<br />
with continued use. Overall<br />
though, this is a reasonably priced<br />
intervalometer that will do all most<br />
photographers will need it to.<br />
Key Features:<br />
• digital display<br />
• optional backlight display<br />
• optional warning<br />
sound<br />
• alert lights<br />
• shutter release<br />
‘hold’ button<br />
• stop/start button<br />
• battery life symbol<br />
24 25
Photoshop Technique:<br />
Image Analysis<br />
Our common idea of photography is that our images tell a story, capture<br />
moments and leave us with a lasting memory. From a scientific point of<br />
view however, images can be used for a lot more and techniques in image<br />
analysis to obtain data are becoming more and more common in research<br />
methods.<br />
Here we look at some simple image analysis techniques that can be<br />
carried out using Photoshop. To get started open your image in Photoshop<br />
and follow the steps below:<br />
Measurements<br />
Fig 39: A microscopic image<br />
of a Stensor sp. taken at x10<br />
magnification.<br />
Inset - Fig 40: graticule bar<br />
for reference measurements<br />
also at x10 magnification.<br />
Step 1: Ensure the measurement<br />
log window is visible by selecting<br />
‘Measurement Log’ from the ‘Window’<br />
menu.<br />
Step 2: Set a scale for your image by<br />
selecting ‘Analysis’ followed by ‘Set<br />
measurement scale’ from the ‘Image’ menu.<br />
Select custom to bring up the window<br />
below. The ruler tool is automatically<br />
activated. Drag it along your reference<br />
measurement to set pixel length.<br />
Step 3: Enter the logical<br />
length and logical units for<br />
your measurment. In the<br />
example shown, 431 pixels<br />
is equal to the logical length<br />
and units of 100µm.<br />
Step 4: Select the ruler tool and drag it along the length of the area you would like<br />
to measure. Press record measurements in the measurement log panel and repeat<br />
the process for different ares of your image if required.<br />
Hint: You can save your scale for future use by selecting ‘Save Preset’ and add a<br />
scale bar to your image by selecting ‘Place Scale Marker’ under ‘Analysis’.<br />
Recording Numbers<br />
Fig 41: A flock of American flamingos (Phoenicopterus<br />
ruber) that disappear amongst one another. The counting<br />
tool is an easy way to mark each one without losing count.<br />
Results<br />
This image of flamingos is quite crowded and at times<br />
it can be hard to differentiate one from another. The<br />
counting tool allows us to mark each one as it is<br />
counted and then record the results when finished. The<br />
number of flamingos in the image is 30 as recorded<br />
below. We can clear the counters on the image and<br />
repeat to be sure our results are accurate and correct.<br />
Step 1: Again, select ‘Measurement Log’ from the<br />
‘Window menu.<br />
Step 2: Select the ‘123 counting tool’ from the side<br />
bar. Hint: Its grouped<br />
together with the eye<br />
dropper tool and ruler<br />
tool.<br />
Step 3: Click on your<br />
image once for each<br />
item you would like to<br />
count. In the example image, I clicked once on each<br />
flamingo.<br />
Step 4: Click ‘Record Measurements’ in the<br />
‘Measurment Log’ dialog box. You will then see your<br />
data appear which you can export if you wish.<br />
Data is exported as a txt file, which you can then<br />
easily copy and paste into a spreadsheet for further<br />
analysis if necessary.<br />
By using our custom scale to measure the diameter of<br />
one of the food vacuoles of the Stensor sp. our image<br />
analysis results tell us that it is aproximmately 40µm in<br />
length. We could go on to measure more of the food<br />
vacuoles, comparing them to one another or analysing<br />
their length in relation to another part of the Stensor sp.<br />
Clicking here will record your<br />
measurments below.<br />
Above you can select, deselect,<br />
export and delete records.
Urban<br />
<strong>Wild</strong>life<br />
Fig 43: An urban rabbit<br />
(Lepus curpaeums) with<br />
a possible eye infection,<br />
University of Nottingham<br />
campus.<br />
Fig 42: Short tailed field vole (Microtus agrestis) amongst plants, Cambridge Botanical Gardens<br />
The rate at which areas are becoming urbanized is<br />
increasing all the time and, as a result urban ecosystems<br />
are extremely common. As of 2008, half the world’s<br />
population (approximately 3.3 billion at the time)<br />
were recorded as living in urban areas. This number<br />
is predicted to increase to 5 billion by the year 2030.<br />
Urban ecosystems bring with them pros and cons to<br />
both the people living there and the wildlife that inhabit<br />
the area. Advantages include increased awareness of<br />
conservation issues and the protection of different<br />
species, as people are able to connect more easily<br />
with local wildlife. Efforts to conserve natural wildlife<br />
habitats are shown to be in decline and so conservation<br />
in urban areas may take on greater importance in the<br />
future.<br />
The presence of wildlife in urban environments<br />
also results in ecological benefits such as pollination<br />
of flowers and the improvement of air quality. From<br />
an economical perspective, the value of property in<br />
these urban green locations may increase resulting in<br />
financial gain for a number of people.<br />
Disadvantages to wildlife include the isolation<br />
of natural populations, which limits dispersal and<br />
connectivity between individuals. This can result<br />
in a smaller gene pool and therefore lead to genetic<br />
problems in offspring. Animals in cities are also at risk<br />
of suffering injury or death as a result of collisions with<br />
vehicles. To the annoyance of humans, wildlife in urban<br />
areas can cause substantial damage to gardens and<br />
property and at times may attack domesticated pets.<br />
In terms of health, areas that are populated with high<br />
numbers of both people and wildlife run a greater risk<br />
of the spread of zoonotic pathogens, diseases that can be<br />
transferred from wildlife to humans.<br />
Animals living in urban habitats face challenges that<br />
members of the same species in rural environments<br />
do not have to contend with. As a result many urban<br />
populations have adapted their behaviour in order to<br />
better deal with and over come human-induced stress.<br />
Modifications to behaviour include diet, reproduction<br />
and timing of movement and activity. As humans are<br />
more active during the day, some species may adapt<br />
their behaviour so that they venture out less in daylight<br />
hours and more throughout the night. This can have<br />
an impact on food availability especially for predators<br />
attempting to locate prey.<br />
In terms of diet, animals living in urban environments<br />
have access to artificial food sources such as food<br />
provided by humans, discarded food from rubbish<br />
bins and road kill in the case of birds. Urban wildlife<br />
tend to feed on much higher concentrations of these<br />
food sources compared to if they were living in rural<br />
areas. Although not faced with problems related to food<br />
shortage, these animals may be more likely to suffer<br />
from disease. Density related issues could also arise<br />
whereby a higher number of individuals are competing<br />
for the same food sources in a much more confined<br />
area.<br />
These nutritional changes can also have an affect on<br />
reproduction. An increased volume of food can lead to greater<br />
reproductive success with increased litter sizes and offspring<br />
survival rates. In contrast however, common characteristics<br />
of urban environments such as noise, pollution and human<br />
disturbance can have an adverse effect on reproductive<br />
behaviour. Noise caused by heavy traffic may potentially limit<br />
the breeding success of species that depend on vocalisation to<br />
attract and find a mate. Abandonment rates may increase due<br />
to disturbances by humans, which will in turn have a knock<br />
on effect on the likelihood of offspring surviving.<br />
Survival and mortality rates are greatly influenced by an<br />
animal inhabiting an urban area compared to a rural one. As<br />
mentioned previously, the increased potential for collisions<br />
with vehicles puts urban wildlife at a greater risk of mortality.<br />
Just as urban wildlife may attack pets, domesticated animals<br />
are just as capable of attack, with small mammals such as<br />
mice, voles and and rabbits particularly at risk.<br />
Although much information may be known about the<br />
ecology and behaviour of a particular species in a rural<br />
environment, the above must be considered when plans<br />
are put in place to manage and control wildlife in urban<br />
environments. It is not enough to assume that members<br />
of a population in urban areas will behave as they would<br />
in a more natural rural environment. Careful research and<br />
continued monitoring is therefore required in order to reduce<br />
conflict and clashes between humans and wildlife, to assess<br />
if management of a particular species is required and to<br />
implement plans and strategies if necessary.<br />
Fig 44: Short tailed field vole (Microtus<br />
agrestis) feeding on flowers, Cambridge<br />
Botanical Gardens<br />
29
A Closer Look at<br />
Fig 45: Lantana camara displaying unpollinated<br />
yellow flowers and pollinated pink flowers.<br />
COLOUR<br />
Macro photography allows us to capture a subject and view<br />
it at a 1:1 ratio. Some lenses enable you to view a magnified<br />
image of up to five times the actual size and therefore allows<br />
us to notice details we wouldn’t be able to see with the<br />
naked eye. Macro photography not only creates potentially<br />
beautiful images but also plays an important role in science<br />
by allowing people to view small subjects such as insects in<br />
a way they haven’t before. This leads to new perspectives,<br />
sparks interest and curiosity, and facilitates learning.<br />
The use of digital cameras can also improve research<br />
methods in colour analysis of insects and plants.<br />
Traditionally a spectroadiometer would be used to analyse<br />
and record the wavelengths at which an object reflects light.<br />
This piece of equipment however is not only expensive<br />
but also takes an average of reflected light. This can lead to<br />
inaccuracies in recreating colour in way that humans and can<br />
comprehend.<br />
As well as the difficulties in recreating colour, descriptions<br />
of colour by researchers may also lead to inaccuracies.<br />
Colour description may vary between different cultures and<br />
languages. There is also the problem of colour blindness<br />
in some individuals and slight differences in the pigments<br />
absorbed by the cones present in our eyes, all of which make<br />
colour perception a subjective matter. By capturing images<br />
using digital SLR cameras, the pixels that make up an image<br />
can be analysed for their components of red, green and<br />
blue (RGB). By recording these components, colour can<br />
be recreated accurately and consistently for use in animal<br />
behaviour studies. Using macro lenses can further enhance<br />
this process as they allow colour differences to be detected in<br />
areas made up of just a few pixels.<br />
Lantana camara<br />
Lantana camara is a tropical plant originating in South America that is now widely distributed throughout the<br />
rest of the world. As a result of hybridisation it now exists in many different forms with variances in flower colour.<br />
Flowers are usually yellow when they first open and change to pink, white or red after pollination. This change in<br />
colour acts as a visual cue to butterflies and other insects, indicating that the flower has already been pollinated.<br />
Colour change in response to pollination is beneficial to both the plant and insect. It permits the plant a more<br />
impressive, attractive flower display whilst enabling insects to forage more efficiently by avoiding plants that have<br />
reduced nectar.
Butterfly Wing Patterns<br />
Couloration in Butterflies<br />
The patterns and colours on the wings of butterflies are<br />
interesting in the fact that they are individuated characters as<br />
opposed to random markings. These markings are the result of<br />
anatomical elements and each spot or stripe will therefore be<br />
in the exact same location on each member of a given species.<br />
The colours and patterns on a butterfly wings are therefore more<br />
similar to the bones of a vertebrate skeleton rather than unique<br />
characteristics such as human fingerprints and patterns on an<br />
animal’s fur.<br />
Butterfly wing colouration and patterns are formed as a result of<br />
a symmetry system, which is broken up by wing veins that act as<br />
boundaries. The symmetry system is usually made up of three<br />
different parts – the border, central and basal system. Pigment is<br />
distributed symmetrically so that the wings of a butterfly mirror<br />
one another. Between the three bands of symmetry, the pigment<br />
is usually darker accounting for the background colour of the<br />
wing. The emerging patterns within each of the three symmetry<br />
systems also vary between one another. A number of eyespots<br />
are commonly formed along the edge of the wing where the<br />
border symmetry system lies. Within the central symmetry<br />
system, there is usually one large mark that sometimes takes the<br />
shape of a single eyespot.<br />
Fig 49: Tailed jay butterfly<br />
(Graphium agamemnon)<br />
Fig 50: Glasswing butterfly<br />
(Greta oto)<br />
Fig 46 (top): Area of border<br />
symmetry system on the wing of<br />
a blue morpho (Morpho peleides)<br />
butterfly.<br />
Fig 47: (above): Eyspot on the<br />
blue morpho (Morpho peleides)<br />
butterfly.<br />
Fig 48 (right): The underside of a<br />
blue morpho (Morpho peleides)<br />
butterfly.<br />
Although the symmetry system is linear, it does not appear so<br />
due to the wing veins, which as mentioned previously, visibly<br />
cross over and break up each section. In doing so they cause<br />
the dislocation of each band of pigment, separating them into<br />
smaller individual sections.<br />
The colours that appear on butterfly wings are<br />
the result of light being absorbed by pigments at<br />
different wavelengths. Any light that is not absorbed<br />
is reflected and scattered, giving the resultant colour.<br />
In the tailed jay butterfly (Graphium agamemnon),<br />
the bile pigment sarpedoblin is produced through<br />
the conversion of two other pigments, pteroblin and<br />
phorcabilin using light. This pigment is responsible<br />
for blue/green colouration and combined with<br />
lutein, a carotenoid that absorbs blue, results in<br />
green coloured wing patches. This provides G.<br />
agamemnon the ability to blend in with the green<br />
colours of plant leaves.<br />
The glasswing butterfly (Greta oto) is unique as its<br />
wings have a natural transparency. Transparency<br />
is more commonly found in organisms living deep<br />
under water however some moths, butterflies<br />
and freshwater insect larvae display this trait.<br />
Transparency plays an important role in defense<br />
against predators. The glasswing butterfly’s<br />
wings contain submicroscopic protrusions on<br />
the surface that don’t absorb or reflect light at<br />
visible wavelengths. Light is therefore completely<br />
transmitted through the wing, creating a transparent<br />
effect. This serves as a good defence mechanism as<br />
birds that prey on butterflies are less able to spot G.<br />
Colouration in butterflies also plays a role in mating behaviour. The scales present on their wings reflect bright<br />
colours and in some species also cause polarization. This is useful in habitats of dense forest in order to detect<br />
potential mates.<br />
33
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Children: £5.25 (under 3’s free)<br />
Concession, group rates and<br />
season tickets available.<br />
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utterfly<br />
Farm<br />
www.butterflyfarm.co.uk<br />
Insects<br />
Birds<br />
and more....<br />
Meet our friendly<br />
caterpillars and learn<br />
about their life<br />
cycle!<br />
10% discount<br />
for online<br />
bookings<br />
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References<br />
Animals in Captivity: Can the Captive Save the <strong>Wild</strong>?<br />
Hayward, M. and Somers, M. (2009). Reintroduction of top-order predators. Chichester, UK: Wiley-Blackwell.<br />
Mason, G. (2010). Species differences in responses to captivity: stress, welfare and the comparative method. Trends<br />
in Ecology & Evolution, 25(12), pp.713-721.<br />
Morell, V. (2007). WILDLIFE BIOLOGY: Can the <strong>Wild</strong> Tiger Survive?. Science, 317(5843), pp.1312-1314.<br />
Ricklefs, R. and Cadena, C. (2007). Lifespan is unrelated to investment in reproduction in populations of mammals<br />
and birds in captivity. Ecol Letters, 10(10), pp.867-872.<br />
Williams, S. and Hoffman, E. (2009). Minimizing genetic adaptation in captive breeding programs: A review.<br />
Biological Conservation, 142(11), pp.2388-2400.<br />
Wwf.org.uk, (2015). <strong>Wild</strong>life. [online] Available at: http://www.wwf.org.uk/wildlife/ [Accessed 27 Apr. 2015].<br />
Birds: Vultures, an endangered species<br />
Balmford, A. (2013). Pollution, Politics, and Vultures. Science, 339(6120), pp.653-654.<br />
de Lucas, M., Ferrer, M., Bechard, M. and Muñoz, A. (2012). Griffon vulture mortality at wind farms in southern<br />
Spain: Distribution of fatalities and active mitigation measures. Biological Conservation, 147(1), pp.184-189.<br />
Martà nez-Abraà n, A., Tavecchia, G., Regan, H., Jiménez, J., Surroca, M. and Oro, D. (2011). Effects of<br />
wind farms and food scarcity on a large scavenging bird species following an epidemic of bovine spongiform<br />
encephalopathy. Journal of Applied Ecology, 49(1), pp.109-117.<br />
Ogada, D., Keesing, F. and Virani, M. (2011). Dropping dead: causes and consequences of vulture population<br />
declines worldwide. Annals of the New York Academy of Sciences, 1249(1), pp.57-71.<br />
Prakash, V., Bishwakarma, M., Chaudhary, A., Cuthbert, R., Dave, R., Kulkarni, M., Kumar, S., Paudel, K., Ranade,<br />
S., Shringarpure, R. and Green, R. (2012). The Population Decline of Gyps Vultures in India and Nepal Has Slowed<br />
since Veterinary Use of Diclofenac was Banned. PLoS ONE, 7(11), p.e49118.<br />
Landscapes: Analogue Photography Loch Lomond<br />
Lochlomond-trossachs.org, (2015). Key Facts - Loch Lomond and The Trossachs National Park. [online] Available<br />
at: http://www.lochlomond-trossachs.org/learning/key-facts/menu-id-109.html [Accessed 23 Apr. 2015].<br />
Nts.org.uk, (2015). Ben Lomond. [online] Available at: http://www.nts.org.uk/property/ben-lomond/ [Accessed 23<br />
Apr. 2015].<br />
van Dijck, J. (2008). Digital photography: communication, identity, memory. Visual Communication, 7(1), pp.57-76.<br />
Urban <strong>Wild</strong>life<br />
Ditchkoff, S., Saalfeld, S. and Gibson, C. (2006). Animal behavior in urban ecosystems: Modifications due to<br />
human-induced stress. Urban Ecosystems, 9(1), pp.5-12.<br />
Lowry, H., Lill, A. and Wong, B. (2012). Behavioural responses of wildlife to urban environments. Biol Rev, 88(3),<br />
pp.537-549.<br />
Magle, S., Hunt, V., Vernon, M. and Crooks, K. (2012). Urban wildlife research: Past, present, and future. Biological<br />
Conservation, 155, pp.23-32.<br />
Ramalho, C. and Hobbs, R. (2012). Time for a change: dynamic urban ecology. Trends in Ecology and Evolution,<br />
27(3), pp.179-188.<br />
35
Small Worlds: A Closer Look at Colour<br />
References<br />
Binetti, V., Schiffman, J., Leaffer, O., Spanier, J. and Schauer, C. (2009). The natural transparency and piezoelectric<br />
response of the Greta oto butterfly wing. Integrative Biology, 1(4), p.324.<br />
Byers, J. (2006). Analysis of Insect and Plant Colors in Digital Images Using Java Software on the Internet. an,<br />
99(5), pp.865-874.<br />
Miller, R., Owens, S. and Rørslett, B. (2011). Plants and colour: Flowers and pollination. Optics & Laser<br />
Technology, 43(2), pp.282-294.<br />
Nijhout, H. (2001). Elements of butterfly wing patterns. J. Exp. Zool., 291(3), pp.213-225.<br />
Pandey, H. and Chauhan, S. (2012). Lantana camera: a journey from eradication to adaptive management.<br />
Bioherald, 2(2), pp.99-109.<br />
Stavenga, D., Giraldo, M. and Leertouwer, H. (2010). Butterfly wing colors: glass scales of Graphium sarpedon<br />
cause polarized iridescence and enhance blue/green pigment coloration of the wing membrane. Journal of<br />
Experimental Biology, 213(10), pp.1731-1739.<br />
Sweeney, A., Jiggins, C. and Johnsen, S. (2003). Insect communication: Polarized light as a butterfly mating signal.<br />
Nature, 423(6935), pp.31-32.<br />
Tellerà a, M. (2003). Pollen harvest by solitary bees ( Ptilothrix relata , Hym. Apidae, Emphorini) in the Argentine<br />
pampas: preliminary results. Grana, 42(4), pp.244-248.<br />
Willmer, P., Stanley, D., Steijven, K., Matthews, I. and Nuttman, C. (2009). Bidirectional Flower Color and Shape<br />
Changes Allow a Second Opportunity for Pollination. Current Biology, 19(11), pp.919-923.<br />
Fig. 4: Egyptian vulture (Neophron<br />
percriopterus)<br />
1/320<br />
f5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 5: A captive Amur leopard<br />
(Panthera pardus orientalis)<br />
1/400<br />
f5.6<br />
ISO 250<br />
Fig 6: A captive Amur tiger<br />
(Panthera tigris altaica)<br />
1/60<br />
f5.6<br />
ISO 4000<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
55mm<br />
Flash: No<br />
Tripod: No<br />
Fig. 1: Amur tiger (Panthera tigris<br />
altaica)<br />
Fig 7: A captive Amur leopard<br />
(Panthera pardus orientalis)<br />
1/640<br />
f5.0<br />
ISO 250<br />
150mm<br />
Flash: No<br />
Tripod: No<br />
1/800<br />
f8.0<br />
ISO 250<br />
400mm<br />
Flash: No<br />
Tripod: No<br />
Fig. 2: Butterfly wing displaying<br />
large eyespot.<br />
1/250<br />
f5.6<br />
ISO 800<br />
55mm<br />
Flash: No<br />
Tripod: No<br />
Fig 8: Giraffes (Giraffa<br />
camelopardalis) in captivity have a<br />
shorter lifespan<br />
1/800<br />
f5.6<br />
ISO 250<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig. 3: Digital image showing view<br />
of Ben Lomond<br />
Fig 9: African Lion (Panthera Leo)<br />
in captivity *Unmarked<br />
1/250<br />
f16<br />
ISO 200<br />
48mm<br />
Flash: No<br />
Tripod: No<br />
1/640<br />
f5.6<br />
ISO 250<br />
400mm<br />
Flash: No<br />
Tripod: No<br />
37
Fig 10: Amur leopard (Panthera<br />
pardus orientalis) in captivity<br />
Fig. 16: Ashley Holmes.<br />
1/400<br />
f6.3<br />
ISO 250<br />
75mm<br />
Flash: No<br />
Tripod: No<br />
1/60<br />
f4.0<br />
ISO 800<br />
31mm<br />
Flash: No<br />
Tripod: No<br />
Fig 11: Amur tiger (Panthera tigris<br />
altaica) in captivity *Unmarked<br />
Fig. 17: Ashley in action.<br />
1/320<br />
f4.5<br />
ISO 250<br />
130mm<br />
Flash: No<br />
Tripod: No<br />
1/60<br />
f3.5<br />
ISO 4000<br />
21mm<br />
Flash: No<br />
Tripod: No<br />
Fig 12: A captive Amur tiger<br />
(Panthera tigris altaica) grooming<br />
Fig. 18: The lighting at a dance<br />
show can prove tricky at times.<br />
1/640<br />
f5.6<br />
ISO 250<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
1/60<br />
f5.6<br />
ISO 4000<br />
55mm<br />
Flash: No<br />
Tripod: No<br />
Fig 13: Captive animals like the Amur<br />
leopard (Panthera pardus orientalis)<br />
are provided with sufficient food<br />
1/1000<br />
f8.0<br />
ISO 250<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 19: The population of cinereous<br />
vultures (Aegypius monachus) came<br />
under threat in Asia.<br />
1/160<br />
f8.0<br />
ISO 200<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 14: A captive Amur leopard<br />
(Panthera pardus orientalis)<br />
leaping from a climbing structure<br />
1/640<br />
f5.6<br />
ISO 250<br />
135mm<br />
Flash: No<br />
Tripod: No<br />
Fig 20: Vultures cover vast areas<br />
and use their wings to glide.<br />
*Unmarked<br />
1/500<br />
f5.6<br />
ISO 800<br />
75mm<br />
Flash: No<br />
Tripod: No<br />
Fig 15: An image from Ashley’s<br />
banner.<br />
1/60<br />
f4.0<br />
ISO 800<br />
30mm<br />
Flash: No<br />
Tripod: No<br />
Fig 21 : The lappet faced vulture<br />
(Torgos tracheliotus) is extinct in<br />
parts of Africa.<br />
1/400<br />
f5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
39
Fig 22 :The Egyptian vulture<br />
(Neophron percriopterus) is now<br />
classed as endangered.<br />
Fig 28: Comparison of a view<br />
taken with a digital then medium<br />
format camera *unmarked<br />
1/320<br />
f5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
1/200<br />
f16<br />
ISO 400<br />
33mm<br />
Flash: No<br />
Tripod: No<br />
Fig 23 : Griffon vultures (Gyps<br />
fulvus) are vulnerable to collissions<br />
with wind turbines in Europe.<br />
Fig 29: Comparison of a view<br />
taken with a digital then medium<br />
format camera * unmarked<br />
1/320<br />
f5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
1/200<br />
f16<br />
ISO 400<br />
33mm<br />
Flash: No<br />
Tripod: No<br />
Fig 24 : The claws of a of cinereous<br />
vulture (Aegypius monachus).<br />
1/320<br />
f5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 30: A digitally coloured image<br />
of the view from Loch Lomond<br />
1/250<br />
f16<br />
ISO 200<br />
Based on digital SLR reading<br />
Fig 25: The view from Loch<br />
Lomond captured using a medium<br />
format camera<br />
Fig 31: Ky Lewis’ lumen prints<br />
entitled ‘Evanecent Growth’.<br />
1/500<br />
f16<br />
ISO 200<br />
Based on digital SLR reading<br />
1/160<br />
f5.6<br />
ISO 800<br />
22mm<br />
Flash: No<br />
Tripod: No<br />
Fig 26: A pier and hills in the<br />
distance at Loch Lomond<br />
*Unmarked<br />
1/250<br />
f16<br />
ISO 200<br />
Based on digital SLR reading<br />
Fig 27: The top of Ben Lomond on<br />
a misty day<br />
Fig 32: One of Anthony Carr’s heat<br />
sensitive pieces.<br />
1/125<br />
f5.6<br />
ISO 800<br />
Fig 33: Intervalometer<br />
52mm<br />
Flash: No<br />
Tripod: No<br />
1/500<br />
f16<br />
ISO 200<br />
Based on digital SLR reading<br />
1/160<br />
f16<br />
ISO 100<br />
18mm<br />
Flash: Yes<br />
Tripod: Yes<br />
41
Fig 34: Intervalometer<br />
1/160<br />
f16<br />
ISO 100<br />
18mm<br />
Flash: Yes<br />
Tripod: Yes<br />
Fig 40: graticule bar for reference<br />
measurements also at x10<br />
*Unmarked<br />
1/60<br />
x1o<br />
magnification<br />
ISO 640<br />
Flash: No<br />
Tripod: No<br />
Fig 35: Timelapse sequence<br />
of a daffodil bud opening<br />
photographed *unmarked<br />
1/25<br />
f2.8<br />
ISO 100<br />
100mm<br />
Flash: No<br />
Tripod: Yes<br />
Fig 41: A flock of American<br />
flamingos (Phoenicopterus ruber)<br />
*Unmarked<br />
1/1250<br />
f5.6<br />
ISO 200<br />
120mm<br />
Flash: No<br />
Tripod: No<br />
Fig 36: Timelapse sequence<br />
of a daffodil bud opening<br />
photographed *unmarked<br />
1/50<br />
f2.8<br />
ISO 100<br />
300mm<br />
Flash: No<br />
Tripod: Yes<br />
Fig 42: Short tailed field vole<br />
(Microtus agrestis) amongst plants.<br />
1/1600<br />
f10<br />
ISO 6400<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 37: Timelapse sequence<br />
of a daffodil bud opening<br />
photographed *unmarked<br />
1/8<br />
f2.8<br />
ISO 100<br />
100mm<br />
Flash: No<br />
Tripod: Yes<br />
Fig 43: An urban rabbit (Lepus<br />
curpaeums) with a possible eye<br />
infection.<br />
1/400<br />
f9.0<br />
ISO 400<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 38: Timelapse sequence<br />
of a daffodil bud opening<br />
photographed *unmarked<br />
1/4<br />
f2.8<br />
ISO 100<br />
100mm<br />
Flash: No<br />
Tripod: Yes<br />
Fig 44: Short tailed field vole<br />
(Microtus agrestis) feeding on<br />
flowers<br />
1/1000<br />
f10<br />
ISO 2500<br />
300 mm<br />
Flash: No<br />
Tripod: No<br />
Fig 39: A microscopic image<br />
of a Stensor sp. taken at x10<br />
magnification. *Unmarked<br />
1/500<br />
x1o<br />
magnification<br />
ISO 1250<br />
Flash: No<br />
Tripod: No<br />
Fig 45: Lantana camara displaying<br />
unpollinated yellow flowers and<br />
pollinated pink flowers.<br />
1/15<br />
f16<br />
ISO 500<br />
100mm<br />
Flash: No<br />
Tripod: Yes<br />
43
Fig 46: Area of border symmetry<br />
system on the wing of a blue<br />
morpho (Morpho peleides)<br />
Ad 2: International Birds of<br />
Prey Centre, Snowy Owl (Bubo<br />
scandiacus)<br />
1/160<br />
f16<br />
ISO 100<br />
65mm<br />
Flash: Yes<br />
Tripod: No<br />
Birds in<br />
Flight<br />
11:30am 2:00pm<br />
4:15pm<br />
Gloucester<br />
GL18 1JJ<br />
www.icbp.org<br />
1/1000<br />
x5.6<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
Fig 47: Eyspot on the blue morpho<br />
(Morpho peleides) butterfly.<br />
1/160<br />
f16<br />
ISO 100<br />
65mm<br />
Flash: Yes<br />
Tripod: No<br />
A day the<br />
whole family<br />
can enjoy!<br />
10% discount<br />
for online<br />
bookings<br />
www.wwt.org.uk<br />
Ad 3: Slimbridge (Phoenicopterus<br />
ruber).<br />
1/1250<br />
f5.6<br />
ISO 200<br />
297mm<br />
Flash: No<br />
Tripod: No<br />
Fig 48: The underside of a blue<br />
morpho (Morpho peleides)<br />
butterfly.<br />
1/100<br />
f9.0<br />
ISO 800<br />
48mm<br />
Flash: No<br />
Tripod: No<br />
Tropical<br />
B<br />
B<br />
Adults: £6.25<br />
Children: £5.25 (under 3’s free)<br />
Concession, group rates and<br />
season tickets available.<br />
utterfly<br />
STRATFORD-UPON-AVON<br />
Farm<br />
Insects<br />
Birds<br />
and more....<br />
Meet our friendly<br />
caterpillars and learn<br />
about their life cycle!<br />
Ad 4: Stratford Butterfly Farm<br />
Image 1: 1/500, f5.6, ISO 500,<br />
55mm (Idea leuconoe)<br />
Image 2: 2.0, f16, ISO 100, 100mm,<br />
tripod (Papilio demodocus)<br />
Fig 49: Tailed jay butterfly<br />
(Graphium agamemnon)<br />
1/25<br />
f10<br />
ISO 800<br />
100mm<br />
Flash: No<br />
Tripod: No<br />
Ad 5: Peak District<br />
Image 1: 1/80, f16, ISO 320, 40mm<br />
Image 2: 1/80, f5.6, ISO 100, 18mm<br />
Image 3: 1/13, f9, ISO 100, 55mm<br />
Fig 50: Glasswing butterfly (Greta<br />
oto)<br />
Ad 6: Yorskshire <strong>Wild</strong>life Park,<br />
wallaby (Macropus rufogriseus)<br />
1/4<br />
f16<br />
ISO 100<br />
100mm<br />
Flash: No<br />
Tripod: Yes<br />
YORKSHIRE<br />
<strong>Wild</strong>life Park<br />
1/800<br />
f10<br />
ISO 250<br />
300 mm<br />
Flash: No<br />
Tripod: No<br />
Relax and<br />
enjoy our<br />
beautiful<br />
surroundings<br />
Ad 1: Cambridge Botanical<br />
Gardens<br />
1/800<br />
f9.0<br />
ISO 800<br />
300mm<br />
Flash: No<br />
Tripod: No<br />
45
YORKSHIRE<br />
<strong>Wild</strong>life Park<br />
Debra McFarlane<br />
MSc Biological Photography & Imaging<br />
CD14204