zoos : the saviour of endangered species, or forced imprisonment for profit?
TRANSCRIPT
Zoos : The Saviour of Endangered Species, or Forced Imprisonment for Profit?
Hope Turner - 74530
26/01/2011
Word Count: 3035
ContentsAbstract.........................................................................................................................3
Introduction...................................................................................................................3
A History of Zoos.........................................................................................................4
Initial Zoo Animal Sourcing........................................................................................6
Current Zoo Animal Sourcing....................................................................................8
Physical and Mental Health of Zoo Animals and other costs...............................9
Contributions to Conservation.................................................................................11
A Frozen Future.........................................................................................................15
Conclusion..................................................................................................................16
Appendix 1..................................................................................................................18
References.................................................................................................................20
Abstract
Research into zoo claims regarding their role in conservation, and their actual
contributions to the preservation of endangered species. Zoos historically
have in fact been major contributors to the extinction process, which in turn
has raised the profiles of their exclusive exhibits and thus accrued greater
profits. Of over 10,000 zoos worldwide, only 1,000 are involved in ex-situ
breeding programs (Laidlaw, 2001), and of those the numbers of captive bred
animals released into the wild, which thrive there, are negligible; concluding
that whilst a small number of zoos are striving forward, the vast majority of
zoos are not breeding self-sustaining populations of endangered species and
have no valid claims on conservation status.
Introduction
Volunteering at Twycross Zoo gave a new insight into what goes on behind
the scenes. Twycross began as Molly Badhams’ personal collection of exotic
pets, escalating to zoo status through demands of the public and the
necessity to subsidise costs rather than through any motivation for
conservation, as the animals in the collection appeared abundant in the wild
at the time, due to the numbers of animals available on the market (Badham
et al. 2000).
In 2002 an amendment was made to the Zoo Licensing Act 1981 (Crown,
2002) and also under the EC Zoos Directive 2002 (EC Directive 1999/22/EC),
implemented a legal undertaking for all British zoos to demonstrate active
involvement in conservation (Hosey et al. 2009) however this “does not
specifically require zoos to participate in the captive breeding and
reintroduction of endangered species” (Rees, 2005).
This is an investigation into zoos as a whole, and their contribution or lack
thereof towards conservation.
A History of Zoos
Before zoos the rich and powerful had menageries (Croke, 1997), personal
collections of exotic pets, much in the same way as Molly Badham did
(Badham et al. 2000); the first recorded animal collecting expedition dates
back to 1490 B.C. in ancient Egypt (Croke, 1997).
In 1826 Sir. Stamford Raffles founded the Zoological Society of London (ZSL)
see Image 1 (Croke, 1997: Zoological Society of London, N.D.), and the
concept of zoos was born. London Zoos’ success, strengthened by a visit
from Queen Victoria in 1842 and its’ opening to the public in 1847 sparked a
“zoo boom”, and other European cities swiftly followed suit. The craze of
exhibiting creatures that were out of the ordinary even ran to humans, when in
1906 New York Zoological Society exhibited a 23 year old African Pygmy
named Ota Benga see Image 2, who later committed suicide (Croke, 1997).
Image 1 (Unknown, 1842)
Image 2(Unknown, 1906)
However, exhibit housing was bleak and cramped, mainly concrete floors and
bars see Image 3. Until 1902 no lion, tiger, parrot or monkey at London zoo
had fresh air, and the fact that “more animals died at most zoos than were
born there” was usually blamed on a “fatal draft”. In 1900, the famous exotic
animal collector, Carl Hagenbeck opened the first “zoo without bars”, including
naturalistic enclosures, igniting other zoos to alter their layouts, both for
aesthetic and animal welfare reasons (Croke, 1997).
Image 3 (Unknown, 1902)
Initial Zoo Animal Sourcing
Carl Hagenbeck was known to have said, when referring to elephants, that
“young specimens cannot as a rule be secured without first killing the old
ones” and in relation to other animals that “a large number of captives die
soon after they have been made prisoners, and scarcely half of them arrive
safely in Europe” (Croke, 1997).
Following the success of zoos, traveling zoos and circuses became popular,
and the demand for exotic animals for both exhibition and as pets
skyrocketed. However, without sufficient knowledge of how to take care of
them, this not only lead to the deaths of these creatures, but thousands of
their relatives in order to obtain them. Another famous animal supplier, Frank
Buck brought back 10,000 mammals and 100,000 birds to America, if that was
the half that survived transportation the numbers killed in the wild is
incalculable. A dealer named Lecomte lead an expedition in 1868, initiating
his journey home with 84 animals, but docking in London with only 8. Many
wild caught exhibits died within days of arrival at a zoo, so much so that when
a gorilla arrived on site all people interested were advised to see it
immediately, as by 1911 the only gorilla to reach America alive died within 5
days of arrival. It must be noted that these deaths were due to the complete
lack of knowledge of how to care for the animals, in addition to completely
unsuitable enclosures (Croke, 1997), as a gorillas’ diet, was:
Breakfast - 2 sausages and a pint of beer
Lunch - Cheese sandwiches
Dinner - Boiled potatoes, mutton and more beer (Blunt, 1835)
as compared to a modern day gorilla diet of mainly fruit and vegetables
(Appendix 1), of course back then medicine was in early stages and therefore
it is unlikely that the collectors would have known of the risk of human
diseases to great apes either.
Animal finding expeditions were leaving a path of destruction through
previously untouched Asian forests, South American jungles and African
savannahs (Croke, 1997).
Current Zoo Animal Sourcing
Importation of zoo animals falls under a number of different Acts, the
Endangered Species (Import & Export) Act 1981, the Wild Animals
(Restriction on Importation, etc.) Act 1990 and the Destructive Imported
Animals Act 1963, licenses for which can be obtained via the Department of
Environment Food and Agriculture (Crown, 2011).
79% of all UK public aquaria animals and over 70% of EU zoo elephants are
wild caught (Captive Animals’ Protection Society, N.D.). Approximately
35,000,000 “fish and other aquatic creatures” enter the UK via Heathrow each
year (City of London, N.D.).
Wild Dolphins are herded into a cove in Taiji, Japan, the ‘perfect specimens’
are sold to aquariums & zoos for $100,000, whilst the rest of the pod are
slaughtered for meat see Image 3. On 15th February 2011 161 dolphins were
taken from the cove into captivity, 755 were killed (Katsinis, 2011), current
dolphin slaughter numbers in Japan are estimated at 23,000 per year. Dolphin
herding at Taiji runs almost daily from September to March (Psihoyos, 2009),
if the figures from 15th February are average, that means an estimate 5867
dolphins are taken into captivity from the cove each year; showing very clearly
that dolphins do not survive in captivity and are not being bred for
conservation.
Image 3 (Psihoyos, 2009)
Whilst the majority of zoo animals are now captive bred, a Zoo Collection Plan
in order to maintain genetic diversity, must include “fresh blood”, bearing in
mind a general lack in reproduction in many captive animals, which demands
further capture of wild species. Much of the capture procedure of these
creatures is humanely done with tranquilizer darts, however even in these
scenarios, as opposed to those shown in Image 3, wild born animals are still
ripped from their natural habitats and family.
Physical and Mental Health of Zoo Animals and other costs
Willie B was a wild born gorilla, but spent 27 years in a concrete box with
metal bars on display in Atlanta, and was described by Terry Maple, the zoo
director, as the “loneliest gorilla in the world” (Croke, 1997); since then
perceptions have changed and “cages are now seen by visitors as
unacceptable” (Ironmonger, 1992).
Ric O’Barry explains that “captive dolphins get ulcers” due to stress, dolphins
are very sensitive to noise and can get so stressed by even the noise pollution
from filters in their tank, that they will consciously commit suicide by refusing
to take another breath (Psihoyos, 2009). A credit to the UK’s view of animal
welfare, is the fact that due to an amendment to the Zoo Licensing Act (1981)
in 1990, enforcing strict standards with regard to pool size, feeding, water
quality and handling, all pre-existing dolphinaria were closed, and there are
currently no captive dolphins in the UK.
In a Bristol University report only 20% of UK elephants had a normal gait, 75%
were overweight, and 54% showed stereotypical behaviour, concluding there
was a welfare concern for every UK housed elephant (Harris et al. 2008). The
median longevity of African Elephants in zoos is 16.9 years, and in the wild is
56 years (Clubb et al. 2008). Elephant fecundity is low with captive elephant
numbers declining at a rate of 10% per year (Clubb et al. 2009).
It costs one hundred times more to maintain a group of elephants in captivity
than to protect enough space for a similar group and their entire ecosystem in
the wild (Born Free Foundation/WSPA, 1994) and if their reproductive
capacity in captivity is negligible then their captivity in zoos cannot be
considered as a contribution to their conservation, in fact “zoos are not able to
maintain their elephant populations without importing new, wild-caught
animals" (Morell, 2008).
There are increased health risks from not being on completely natural diets
(Clauss et al. 2008: Schwarm et al. 2006: Crossley & del Mar Miguelez,
2001), including reduced oocyte production (Parthasarathy & Palli, 2011); or
in natural settings (Videan et al. 2007: Rees, 2004), as well as increased
mental health issues raised by having any natural behaviours allowed by their
captivity, disturbed by visitors (Birke, 2002).
Due to space restrictions and fight risk, most animals are un-able to be kept in
natural sized groups, this reduces sperm production in primates (Moller, 1988)
and often produces “a complete cessation of reproduction” (Dehnhard, 2011).
Obviously this combination of reduced oocyte & sperm production, as well as
the general lack of reproduction in captive animals as a whole, is completely
counterproductive to the ex-situ breeding of sustainable populations, although
conservation is generally a zoos justification for holding wild animals captive
(Lindburg, 2000).
According to Tom Regan, when taking into account the rights of the individual
animal, zoos are not morally defensible (Norton et al. 1995), nor does it seem
that they are all quite what they claim with regards to species survival.
Contributions to Conservation
The British and Irish Association of Zoos and Aquariums (BIAZA) collates the
breeding programs of its’ members in association with the European
Association of Zoos and Aquaria (EAZA), their main aim is to promote
improvement of welfare and ex-situ conservation, their website states their
role includes “to re-introduce and support to wild populations (if applicable..”
(BIAZA, 2005).
In 2005 only 17.1% of animals in BIAZA zoos were in recognised conservation
breeding programmes (BIAZA, 2006). An investigation by the Born Free
Foundation revealed that 91.1% of threatened mammals and 95% of
threatened birds species are not represented in the Consortium of Charitable
Zoos (CCZ) “the most progressive zoos in the country” (Born Free
Foundation, 2007). Another report found that “95% or more of the worldwide
zoo industry does not participate in, or make any effort to participate in,
recognized captive propagation and reintroduction initiatives” (Laidlaw, 2001).
These statistics are born out of the fact that zoos source animals that will
attract the most visitors (Moss & Esson, 2010), however, whilst this increases
revenue for the zoo, it does not necessarily contribute to conservational
breeding e.g. Philadelphia Zoos’ White Lion exhibit, brings in over $1 million a
year, but their breeding pair are brother and sister, whose father is also their
grand & great grand-father (Croke, 1997), this inbreeding for profit also seen
in white tigers, sold to entertainment acts by other zoos has no role in
conservation.
The effects of human choice of selectively breeding cannot be
underestimated, as whilst it may be based on pedigrees and phenotypes of
the potential mates it is not based, as it would be in the wild, due to natural
selection, on the genotypes (Mays & Hill, 2004).
The release of ex-situ captive bred felids, has not as yet been successful, only
50% of released animals were capable of hunting in order to support
themselves, and all were killed or died. “On average only one in three captive-
born carnivores survives in the wild” (Jule et al. 2008). In comparison in-situ
breed, rescue and release programs have increasing success rates (Hunter &
Rabinowitz, 2009: Coonan et al. 2010).
The release of 14 captive bred Golden Lion Tamarins in 1984 resulted in the
removal or death of 11 (79%) of the animals (Stolinski et al. 1997), leading to
an improved training program and a more successful reintroduction in 1995
(Hosey et al. 2009).
The oft-quoted reintroduction of the Arabian Oryx, failed when poaching
resulted in the necessity to re-capture those left in order to continue to
perpetuate the species; and the capture of all Californian Condors on the
brink of extinction in 1986 has fared little better due to the mortality rates of
released birds (Hosey et al. 2009). If the animals survive re-introduction, after
careful planning and much training, there is still a major risk of inbreeding,
(Jameson, 2011) potentially leading to lack of fertility and further loss of
genetic diversity due to the loss of the lines re-introduced.
Of the 194 members of the IUCN/SSC Re-introduction Specialist Group
(RSG), a group set up to advise on and promote “reintroduction of viable
populations of animals” only 17 work in zoos (IUCN, 2007).
The number of zoos involved with the conservation breeding program and the
space they have available for young counteracts their intensions as without
re-introducing these animals to the wild, they cannot hope to perpetuate these
species (Hosey et al. 2009) and often have to cull the very young they aim to
breed (Moore, 2007) due to a surplus. Zoo surplus figures for America have
been estimated at 80,000 animals per year (Croke, 1997). There are also
significant concerns about the potential of these captive bred groups due to
their lack of genetic diversity (Laike, 1999).
Very few zoos re-introduce, but these include The Aspinall Foundation
(Aspinall Foundation, 2010) and the Durrell Wildlife Conservation Trust
(Durrell Wildlife Conservation Trust, 2011) who have reserves for the animals
they release.
This being the case, zoos that don’t re-introduce, assist in reintroduction or
own reserves cannot truly be considered to be perpetuating a species other
than for exhibition purposes.
As far as financial contribution to in-situ conservation goes, “the CCZ appears
to spend an estimated 4-6.7% of gross income” (Born Free Foundation,
2007), however much all may not be as it seems, for example whilst Twycross
Zoo declared donations of £72,028 as amounting to around 12% of profit in
2008, this figure was after the transfer of over £3.5 million into a contingency
fund, making the zoos donations closer to 1.7% of profit. Twycross Zoo’s
running costs for 2008 were over £6.6 million, however the charity has no in-
situ reservations, nor does it release animals into the wild (Twycross Zoo,
2009), whereas by comparison the Born Free Foundations expenditure for
2008 was £2.3 million, (Born Free Foundation, 2008) protecting “ lions,
elephants, gorillas, chimpanzees, tigers, polar bears, wolves, dolphins, turtles,
sharks and lots more” in wildlife reserves across the globe (Born Free
Foundation, 2011).
The Zoological Society of London is extremely active in data collation, plan
creation and implementation of in-situ conservation programs around the
world, working with many other organisations through its sub-divisions like its’
Edge of Existence programme and 21st Century Tiger etc. (ZSL, 2010); and as
its existence launched zoos worldwide, it appears to continue to strive to be
first.
A Frozen Future
The Frozen Ark Project is the 21st centuries technological answer to the
increase in current extinction rates (Clarke, 2009), and the lack of successful
ex-situ captive breeding by zoos of self-sustaining populations of endangered
species. However, whilst eminently qualified scientists spend millions in the
collection ova, sperm and embryos from dying species, to store in liquid
nitrogen “just in case” questions remain:-
How can they be bred in the future without the correct wombs, and therefore
nutrients ,to carry them?
Where on Earth will they be released to, bearing in mind the current path of
total destruction of the last vestiges of our wild planet, through population
increase and global warming?
As John Seidensticker if the National Zoo in Washington D.C. says “it is not
enough to produced genetically diverse babies; we must also produce and
maintain behaviourally competent animals who can thrive in the wild” (Croke,
1997). Which begs the further question, how are they expected to survive in
the wild with no others of their species to teach them the ropes?
Conclusion
Of the millions of animals in thousands of Zoos across the globe, only a
handful have ever been re-introduced to the wild, and the majority of those
died within a very short space of time due to lack of knowledge or ability to
provide for themselves.
The results of much research into zoos has led to the realisation that the
captivity of carnivores “should be either fundamentally improved or phased
out” (Clubb & Mason, 2003), concepts of zoo animal welfare and its use in
justifying zoos are insufficient (Wickins-Drazilova, 2006), behavioural
husbandry often un-heard of (Melfi & Hosey, 2011), and the current breeding
program for conservation of species by zoos needs to be radically altered
(Leus, Traylor-Holzer, & Lacy, 2011).
“Captive breeding should be viewed as a last resort in species recovery”
(Snyder et al. 1996) therefore perhaps the way forward is being shown by
zoos like the Aspinall Foundation, the Durrell Wildlife Conservation Trust, and
the Zoological Society of London, as well as by other groups such as the Cat
Survival Trust (Cat Survival Trust, 2002), breeding in the UK and releasing
into protected reserves, as well as owning and protecting reserves elsewhere,
and ALERT (African Lion & Environmental Research Trust, 2011), breeding at
in-situ locations and rescuing orphaned animals, with long term goals of
providing life skills to enable self-sustenance, with staggered soft-releases
into the wild.
Therefore it can be said that a small number of zoos are a mechanism for
obtaining the means to preserve limited numbers of endangered species, but
the vast majority run for profit, who whilst portraying themselves as
conservation driven are in fact contributing to the “extinction effect” in their
constant need to replace exhibits, enforcing limited longevity and redundant
productivity, when not culling due to space issues, which in turn raises their
visitor numbers due to the exclusivity of their stock.
Appendix 1
Diet Sheet
Species: WESTERN LOWLAND GORILLA Gorilla gorilla gorilla
Number: Two adults (Gorilla Group)
BREAKFAST
Bongo:1 orange, 1 apple,1 banana, 2 oz carrots
Biddy: ½ apple
4 pints tea each, 2 dsps Vionate every 1st day
Above given in Bed Area. Bongo given slice bread once in Trap Area.
Scattered in day area:
6 oz carrots 4 oz cabbage 2 oz Chinese leaf
2 oz cauliflower 2 oz swede 2 oz parsnip
10:30 approx Midmorning routine - each:
portion yogurt, few nuts / raisins 1 item fruit
1 litre squash forage scattered in day are (sunflower seeds, corn)
11:45 – 12:45
leaves, 1 – 2 branches (approx. March to November)
EVENING Each individual comes into separate Bed Area for their teas.
Summer
17:30 – 18:00 All given 4 pints tea (or occasionally, Complan or squash)
Winter
16:40 – 17:00 2 items, eg. kiwi, cereal bar, ⅛ pineapple, slice bread
TEA
BONGO BIDDY
lettuce 1 1
cucumber ½ ½
tomato 4 4
celery ½ bunch ½ bunch
apple 1 ½
orange 1 ½
banana 1 1 small
pear ¼ ¼
grapes sm bunch sm bunch
lemon or grapefruit ¼ or ⅛ ¼ or ⅛
carrots 10 oz 4 oz
cauliflower 2 oz(+1 oz leaves)
1 oz
cabbage 4 oz (outer leaves)
2½ oz
Spring cabbage 4 oz 2½ oz
Red cabbage 1 oz 1 oz
Chinese leaf 1 ½ oz 1 oz
Chicory ⅛ ⅛
Brocolli 1 oz 1 oz
Pepper ¼ ¼
Swede 1 ½ oz 1 oz
Parsnip 1 ½ oz 1 oz
Pellets or nuts every 1st day
small handful
small handful
boiled egg every 2nd day
2 2
Potatoes (occasional)
1 oz 1 oz
Fennel / Aubergine / Courgette
small bit each
small bit each
In season use up to:
any type bean 3 oz 2 oz
peas 3 oz 2 oz
rhubarb 1 oz 1 oz
sprouts 1 - 2 oz 1 – 2 oz
(Twycross Zoo, 2008)
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