ArticlePDF Available

Abstract and Figures

Commercial farming of wildlife, particularly in Southeast Asia, is currently the subject of much debate and to date, its conservation impact has been largely unexplored. This study used semi-structured interviews to build a detailed understanding of the dynamics of the commercial farming of Southeast Asian porcupine (Hystrix brachyura) in the northwest Vietnamese province of Son La. Although farm owners are obliged by law to propagate stock solely from farm-bred animals, 58% of farm owners admitted purchasing wild founder stock, with at least 19% continuing to buy wild individuals. Despite the number of farms, the primary demand on them is to supply other farms, and wild meat restaurants were still sourcing their meat from wild populations. Lower cost was a major factor driving the trade in wild animals, with wild adult porcupines being bought for half the price of farm-bred adults. With high demand from farms and restaurants, increased targeted hunting may be the cause of a dramatic decline in the wild population of porcupines across the region.
Content may be subject to copyright.
The conservation impact of commercial wildlife farming of porcupines in Vietnam
Emma G.E. Brooks
a,*
, Scott I. Roberton
b
, Diana J. Bell
a
a
Centre for Ecology, Evolution and Conservation, University of East Anglia, Norwich, NR4 7TJ, UK
b
Wildlife Conservation Society – Vietnam, PO BOX 179, Hanoi GPO, Viet Nam
article info
Article history:
Received 27 January 2010
Received in revised form 23 May 2010
Accepted 25 July 2010
Available online 19 August 2010
Keywords:
Porcupine
Wildlife trade
Commercial farming
Vietnam
abstract
Commercial farming of wildlife, particularly in Southeast Asia, is currently the subject of much debate
and to date, its conservation impact has been largely unexplored. This study used semi-structured inter-
views to build a detailed understanding of the dynamics of the commercial farming of Southeast Asian
porcupine (Hystrix brachyura) in the northwest Vietnamese province of Son La. Although farm owners
are obliged by law to propagate stock solely from farm-bred animals, 58% of farm owners admitted pur-
chasing wild founder stock, with at least 19% continuing to buy wild individuals. Despite the number of
farms, the primary demand on them is to supply other farms, and wild meat restaurants were still sourc-
ing their meat from wild populations. Lower cost was a major factor driving the trade in wild animals,
with wild adult porcupines being bought for half the price of farm-bred adults. With high demand from
farms and restaurants, increased targeted hunting may be the cause of a dramatic decline in the wild pop-
ulation of porcupines across the region.
Ó2010 Elsevier Ltd. All rights reserved.
1. Introduction
Throughout the world, wildlife products are an essential source
of food and income (Chardonnet et al., 2002). Whilst humans have
been hunting wildlife for more than 100,000 years, today many
species are threatened by the scale of hunting and the situation
has been exacerbated by the increase in human populations
(Bennett and Robinson, 2000; Milner-Gulland and Bennett, 2003).
Unsustainable wildlife trading is one of the most devastating
underlying causes of biodiversity loss (Bennett, 2002; Broad et
al., 2003) and the wild meat trade alone has now surpassed habitat
loss as the greatest threat to wildlife in the humid tropics (Milner-
Gulland and Bennett, 2003; Redmond et al., 2006). To date much of
the research has focused on Africa (Bell et al., 2004; Redmond et al.,
2006; Swift et al., 2007), but the rapid, recent acceleration of hunt-
ing most likely first occurred in Southeast Asia (Milner-Gulland
and Bennett, 2003), and has grown considerably in the last few
decades.
Hunting has expanded into a multi-million dollar commercial
trade where wildlife is exploited for consumption, alleged medici-
nal properties, ornaments, clothing, pets and zoo exhibits (Broad et
al., 2003; Bell et al., 2004). In most regions the levels of biodiversity
loss due to hunting are largely unexplored and can vary consider-
ably (Fa et al., 2002). The highest levels of wildlife hunting are for
meat. Whilst in Africa, meat from wild animals is an important
source of protein for many, across much of Southeast Asia it is con-
sumed as a speciality food (IUCN, 2001; Roberton, 2007), at a scale
that is having a devastating effect on wild populations (Whitfield,
2003).
Commercial wildlife farming has been advocated as a possible
solution to meeting a growing demand for wildlife products, par-
ticularly wild meat (Cooper, 1995). Although it has been proposed
as a means of providing food security since the 1950s, it is not in
widespread use across the tropics (Mockrin et al., 2005). However,
over the past decade, there has been a substantial increase in the
number of wildlife farms appearing across much of Southeast Asia,
including Vietnam (WCS, 2008). Wildlife farms are seen as a way of
providing food security to local communities, as well as a possible
means of poverty alleviation and economic development in rural
areas (Cicogna 1992; Hardouin 1995; Revol 1995). It also has been
suggested that they may promote biodiversity conservation by
reducing hunting pressure on wild populations (Jori et al., 1995;
Parry-Jones, 2001; Lapointe et al., 2007). It has been argued that
wildlife farms provide a cheaper, acceptable alternative to wild
animals (Bulte and Damania, 2005; Lapointe et al., 2007) and as
such, commercial wildlife farming is being actively encouraged
by governments across much of Southeast Asia (Parry-Jones,
2001; WCS and TRAFFIC, 2004).
Arguments against wildlife farming include concerns that in-
creased availability may increase consumer demand and pressure
on wild populations for founder stock, and that farms will be used
for laundering illegally-caught animals (Bulte and Damania, 2005;
WCS, 2008; Cooper, 1995; Mockrin et al., 2005). To date, farms have
been poorly monitored and their impacts are largely unknown.
0006-3207/$ - see front matter Ó2010 Elsevier Ltd. All rights reserved.
doi:10.1016/j.biocon.2010.07.030
*Corresponding author. Tel.: +44 (0) 7727 125063.
E-mail addresses: emma.brooks@iucn.org (E.G.E. Brooks), sroberton@wcs.org
(S.I. Roberton), d.bell@uea.ac.uk (D.J. Bell).
Biological Conservation 143 (2010) 2808–2814
Contents lists available at ScienceDirect
Biological Conservation
journal homepage: www.elsevier.com/locate/biocon
The Vietnamese wildlife trade, including farming, is mainly reg-
ulated by Decree 32/2006/ND-CP and Decree 159/2007/ND-CP. The
task of monitoring and enforcing these laws falls upon the govern-
ment’s Forest Protection Department (FPD). Legislation states that
all wildlife farms should be registered with the relevant provincial
FPD and farms maintain accurate stock records and proof of the le-
gal origin of their stock. Violation of these laws should result in
confiscation of the animals, a fine equivalent to the value of the
animals up to US$1850, and the possibility of having their farm
registration certificate revoked (Decree 159/2007/ND-CP). The
main taxa reported in these Vietnamese wildlife farms are croco-
dile (Crocodylus siamensis), python (Python molurus and Python
reticulates), cobra (Naja naja and Ophiophagus hannah), soft-shelled
turtle (Pelodiscus sinensis), bear (Ursus thibetanus and Ursus malay-
anus), macaque (Macaca fascicularus), deer (Cervus unicolor) and
porcupine (Hystrix brachyura)(WCS, 2008).
The Southeast Asian porcupine (H. brachyura) is one of the 11
species of Old World Porcupines (Family: Hystricidae). It is cur-
rently classified as Least Concern by the IUCN Red List (Lunde et
al., 2008), with overhunting cited as its greatest threat, and a re-
ported decline in total population size of at least 20% in the
1990s (Nowak, 1999). Farming of porcupines in Vietnam is becom-
ing progressively more popular, and there has been a notably rapid
increase in the number of porcupine farms in Son La province since
2000.
In the present study, we set out to conduct an evidence-based
case study quantifying the direct impact of commercial farming
on the local wild population using the Southeast Asian porcupine
as a model species. This was investigated by determining the scale
of porcupine farming in Son La province, the incentives for contin-
ued purchase of wild animals, and the effectiveness of the FPD in
enforcing the wildlife farming regulations. Commercial wildlife
farming can only be advocated if failings in the trade can be iden-
tified and dealt with, to minimise negative impacts on wild popu-
lations of species.
2. Methods
2.1. Study site
Son La province is located within the Hoang Lien Mountains, in
northwest Vietnam, on the Lao PDR border (Fig. 1). Although con-
siderable deforestation has occurred in recent decades to make
way for agriculture, 41% of the province remains forested (Anon,
2006). In 2007, the construction of a section of road linking south-
ern Son La to Lao PDR was completed.
2.2. Household interviews
Face-to-face interviews were conducted with 67 porcupine
farm owners in April and May 2008. In this context, anyone breed-
ing porcupines was considered to be a farm owner, and the terms
‘‘farm owner” and ‘‘farmer” are used interchangeably. Interviewees
were identified by snowball sampling, using recommendations
from respondents to establish contact with others (Bryman,
2004). Although this could provide a bias towards older and more
established farms, it would be impossible to select a random sam-
ple of farms in this instance, as despite current laws, not all farms
are registered.
Semi-structured interviews were carried out by a team of two
researchers, one British and one Vietnamese. Questions and re-
ported answers were translated into English by the Vietnamese
member of the team. Trading in wild animals is illegal, and so to
minimise response biases a role-play approach was used, positing
that data were being collected in order to assess porcupine farming
as a means of poverty alleviation for households in the central
highlands of Vietnam. Respondents were found to be very willing
to talk openly in detail about their farms, most probably aided by
the presence and interest of the foreign interviewer.
The interviews followed topics set out in an interview guide,
but remained flexible in nature to allow the respondents to discuss
issues at their own pace, and to allow the interviewer to follow up
on any key topics (Bryman, 2004). Data were collected on the size
and history of the farm, animal husbandry practises, prices of prod-
ucts and basic expenses, the origin and quality of founder stock
(male/female pairs), and perceived views on wild stock. All an-
swers (including uncertain responses) were recorded in a notebook
during the interview.
2.3. Data analysis
Response frequencies are presented as percentages. Due to the
open nature of interviews, the number of respondents varies be-
tween questions, and thus frequencies also are shown as fractions
of the total number of interviewees that were asked that question.
When considering questions that required a numerical response, if
interviewees gave a range, statistics were calculated from the mid-
point of the range.
A Pearson’s correlation was used to evaluate the price trend of
juvenile founder stock over time. Prices were converted to US Dol-
lars at the currency exchange rate for the relevant year (OANDA,
2008), and adjusted for inflation to the 2008 rate (BLS, 2008). Prof-
its and expenses of farming and trading were calculated using
mean values gathered from the interviews. The prices of wild meat
versus farmed meat equivalent were compared with a one-way
ANOVA, and a Tukey’s post hoc examination. The farmed meat
equivalent was calculated by dividing the mean price of farmed
breeding-age founder stock pairs by the mean reported maximum
weight of an adult porcupine, and then halved to account for only
one individual.
2.4. Forest Protection Department interview
A semi-structured face-to-face interview was conducted with
the Deputy Director of the Son La FPD. Topics covered included
Fig. 1. Districts of Son La Province, Vietnam. 1. Sop Cop, 2. Song Ma. 3. Mai Son, 4.
Thuan Chau, 5. Son La town, 6. Muong La and 7. Quynh Nhai. Districts in darker
shading (1–5) were sampled during study, due to their proximity to the Lao PDR
border.
E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814 2809
the laws and regulations governing porcupine farming in Son La,
monitoring effort, punishments and rate of prosecutions, and staff
numbers and training. Data were provided on the number and size
of registered porcupine farms in the province of Son La at a district
level, as well as the number of convictions for possession of porcu-
pines of unknown origin in 2007.
2.5. Restaurant interviews
A small survey was conducted with restaurant owners in the
greater Hanoi region. Of 35 suspected wild meat restaurants ap-
proached, only nine restaurant owners admitted selling porcupine
meat, and were willing to participate. Short semi-structured inter-
views were conducted, with data collected on aspects of the price,
trade and consumer preferences of porcupine meat in restaurants.
3. Results
3.1. Porcupine farming and husbandry practises
In total, 449 porcupine farms were registered with the FPD in
the province of Son La, although the FPD admits that this is an
underestimate of the true number. In mid-2008 Son La provincial
FPD reported a little over 8000 porcupines in successful breeding
programs in farms to National FPD. A total of 67 porcupine farm
owners were interviewed in five districts of Son La province. All
were current farm owners except for one, who had sold all of his
porcupines within the last year, but intended to start farming por-
cupines again as soon as possible.
3.2. Trade dynamics
Fifty-eight per cent (39/67) of farm owners reported that their
original founder stock of porcupines was of wild origin; of these,
31% (12/39) continued to buy porcupines of wild origin on some
scale. Sixty-seven per cent (18/27) claimed that wild porcupines
could no longer be found locally, with another 30% (8/27) saying
there were very few. Only one respondent (1/27) thought that wild
porcupines could still be readily found locally. Fifty-three per cent
(28/53) of respondents reported that wild-caught porcupines orig-
inated from Lao PDR. Although 36% (19/53) of farmers reported
wild-caught porcupines originated from Song Ma or Sop Cop dis-
tricts, nearest the Laotian border, 100% (11/11) of respondents in
these areas reported that there were no, or very few, wild porcu-
pines to be found in the area.
All farm owners reported that they sold porcupines to other
farms for founder stock (67/67). The sale destinations of the foun-
der stock included much of northern Vietnam, with sale to some
provinces further south coinciding with large urban centres. One
farm owner (1/67) also reported selling to China. Only two out of
67 farmers reported also selling porcupines to restaurants for
meat, though both said that this was only occasional, and as a re-
sult of accidental death, or if they had a surplus of old males. Six
farm owners volunteered the information that the supply of porcu-
pines from farms was not large enough to meet the demand for
meat, so porcupines of wild origin supplied restaurants.
3.3. Scale of porcupine trade
3.3.1. Growth of farming
The number of porcupine farms has increased significantly in
the last decade (Fig. 2), with 55% of respondents having established
their farms in the past 3 years. The number of founder stock pur-
chased to start the farm ranged from 2 to 39, with a mean ± SE of
8.77 ± 0.94 (n= 66). There was a slight trend for increased numbers
of founder stock to be purchased in the more recently established
farms (Fig. 3), however this was not found to be statistically signif-
icant (
s
= 0.15, n= 66, p= 0.06). Only 8% (5/61) of respondents had
no wish to expand their farm further.
There has been no significant decline in the proportion of farms
buying wild founder stock over time (r=0.1, n= 13, p> 0.05).
Whilst the majority of farmers who bought porcupines of wild ori-
gin claimed to buy them for founder stock for their own farm, there
was also evidence of farm owners trading in wild porcupines di-
rectly. Six per cent (4/67) of the farm owners were reported as,
or admitted to, trading wild animals directly, accounting for a total
of 910 wild porcupine individuals traded onto other farms from
those four farms alone. One respondent also worked in the border
army on the main road to Lao PDR and claimed that 20 pairs of
wild-caught porcupines were brought across the border every
night. Without verification, reliable conclusions cannot be drawn
here, but if this estimate is accurate it would amount to over
14,000 wild porcupines being brought from Lao PDR per annum,
and pose a serious threat to wild populations in Lao PDR that re-
quires immediate attention.
3.3.2. Economics of farming
The high level of income gained was the reason given for farm-
ing porcupines by 78% (46/59) of respondents, followed by 54%
(32/59) citing low maintenance requirements, and 44% (26/59) of
Fig. 2. Frequency of reported start-up dates of 67 porcupine farms in Son La
province, Vietnam (r= 0.72, n= 12, p< 0.004).
Fig. 3. Number of porcupine founder stock purchased against year of establishment
of 65 farms in Son La province, Vietnam.
2810 E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814
respondents stating that they farmed porcupines because unlike
some livestock, porcupines are disease-free. Four farm owners sta-
ted that porcupines brought the highest profit of any animal. There
has been a significant increase in the value of porcupines in the
past seven years (Fig. 4).
Twenty-five per cent (17/67) of farm owners were retired. Of
the remaining 75%, none reported profit from breeding porcupines
as their only source of income, though 73% (41/56) of respondents
reported porcupine farming as their main source of income. The
alternative sectors of employment of the farm owners are govern-
ment, retail and agricultural. Thirteen farmers (13/29) swapped
from farming another species to porcupine farming, with 46% (6/
13) of these citing the increase in profits as the reason for the swap,
23% (3/13) reporting the lack of diseases in porcupines as the rea-
son, 15% (2/13) commenting on the lower maintenance effort of
farming porcupines in relation to other species, and 8% (1/13)
reporting the smaller amount of land required as the reason for
the swap. Many farm owners favourably compared farming porcu-
pines with other species in terms of income and ease of work, with
six stating that porcupine farming brought in at least ten times the
income of pig farming.
Based on mean figures of the main expenses incurred by porcu-
pine farmers, an average profit of US$1000/breeding pair each year
can be made through the sale of juvenile captive-bred offspring.
Assuming a population of ten breeding pairs (the average per farm
found in this study), a farmer could expect to make a profit of
US$10,000 pa. Each of the three farm owners who admitted trading
wild individuals directly, made a profit of $61.19 (1 million VND)
per pair sold. Even excluding any food or maintenance costs that
may be incurred (dependent on how long they held the animals),
a farm owner would have to trade 164 pairs of wild porcupines
to make the same amount of profit as from ten pairs of farmed
stock. None of the four respondents who were trading wild porcu-
pines directly reported porcupines as their main source of income.
3.4. Threats to wild populations
3.4.1. Demand
Ninety-nine per cent (66/67) of farm owners believed that de-
mand for porcupines was increasing, and the remaining farm own-
er had no perception if demand was increasing or not. All (58/58)
of the respondents reported that demand was higher than supply,
with one respondent estimating that current supply was only 10%
of demand. All respondents (47/47) reported that there was no
competition between farmers, and porcupines were easy (5/19)
or very easy (14/19) to sell due to the high demand.
3.4.2. Price
Only 13% (8/63) of farm owners regularly sold their stock at
breeding-age, while 87% (55/63) sold founder stock pairs whilst
still juvenile, with the mean ± SE age of sale being
3.1 ± 0.19 months (n= 55). There was a significant difference be-
tween the price of captive-bred juvenile founder stock pairs, cap-
tive-bred adult founder stock pairs, and founder stock pairs of
wild origin (Fig. 5). A Tukey’s post hoc analysis showed that
farm-bred founder stock pairs sold at juvenile-age were signifi-
cantly cheaper than those sold as adults (p< 0.001). Founder stock
pairs of wild origin were significantly cheaper than farmed adults
(p< 0.001), but not than those sold whilst still juvenile (p= 0.16).
Ninety-three per cent (13/14) also reported that wild origin foun-
der stock was cheaper than farm-bred porcupines.
3.5. Enforcement
Son La FPD reported that regulations governing the monitoring
of porcupine farms in Son La started in 2004 in the districts of Sop
Cop and Song Ma, due to the availability of good quality wild foun-
der stock from Lao PDR. Since 2005, the same regulations have ap-
plied across the entire province. All farms should register with the
FPD, whereupon a certificate and notebook for monitoring the pop-
ulation will be issued. The FPD should be informed of the numbers
of births on the farm, which will be confirmed by a visit from an
FPD ranger. The FPD must also be informed if buying or selling of
stock occurs, when the population numbers will again be checked
and the legal origin of the animals verified. All FPD staff receive ba-
sic training, including identification of characteristics of wild
animals.
Only three respondents (3/67) admitted to not being registered
with the FPD, although it could only be confirmed with the FPD re-
cords that 43% (29/67) of those interviewed were legally regis-
tered. This number is likely to underestimate the number of farm
owners registered because of multiple ownership of properties,
and that a farmer may hold animals at two locations and only reg-
ister one of these. Although 100% of farmers, when asked, reported
that FPD ‘‘did a good job”, or monitored farms closely (29/29), the
FPD only made three convictions for unlawful possession of porcu-
pines in 2007. Whilst farm owners were consistently correct in
describing monitoring procedures of porcupine farms by the FPD,
Fig. 4. Price trend for commercial sales of founder stock pairs of juvenile
porcupines in Son La province, Vietnam (
s
= 0.62, n= 96, p< 0.001). Values adjusted
to 2008 prices to account for inflation rates.
Fig. 5. Mean (±SE) sale price of founder stock porcupine pair (US$) sold in Son La
province, Vietnam, as juveniles or breeding-age of farmed stock, or of wild origin
(F
2,79
= 136.05, p< 0.001).
E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814 2811
65% (11/17) failed to mention that a fine (as well as confiscation of
porcupines) was part of the punishment for unregistered porcu-
pines. Although registering porcupines with the FPD is free of
charge, 89% (8/9) of farm owners reported some sort of fee associ-
ated with registering or selling porcupines.
3.6. Further threats to wild populations
Six farm owners volunteered the information that porcupine
meat was supplied exclusively from the wild. Fourteen farm own-
ers declared that wild founder stock often carry injuries, from
which the porcupines often do not recover. Eleven also said that
as a result of the high mortality rate when capturing wild animals,
there is a constant supply of injured and/or deceased porcupines
for the meat market. When asked if there was a difference in the
quality of the meat, 37% (17/46) responded that wild meat was
preferable to farm-bred meat and only 2% (1/46) responded that
farmed meat was of higher quality. Fifty per cent (23/46) thought
that there was no difference between meats of different origins,
though many added that there was a perceived difference by
consumers.
In a sample of wild meat restaurants, all nine that admitted sell-
ing porcupine meat reported that the animals were sourced from
the wild, with 2/9 saying they had also tried selling farm-bred
meat. All (9/9) reported that there was a perceived difference be-
tween wild and farm-bred meat, and that customers preferred wild
meat. Fifty-seven per cent (4/7) added that despite this, they did
not believe that customers would be able to tell the difference be-
tween the two sources of meat.
The two most common reasons given for sourcing porcupine
meat from wild rather than farmed populations were availability
and price (both given by 50% (3/6) of restaurant owners). Thirty-
three per cent (2/6) sourced wild porcupine meat because of cus-
tomer preference, and 17% (1/6) because of the assumed higher
quality of wild meat. There was a significant difference between
the price of: (a) wild meat reported by the farm owners in Son
La province, (b) wild meat reported by the restaurant owners,
and (c) the price of farmed meat (Fig. 6). A Tukey’s post hoc anal-
ysis found no significant difference between the wild meat prices
reported by the farm owners and the restaurant owners
(p= 0.22), but farmed meat was significantly more expensive than
the wild meat prices reported by both farm owners (p< 0.001) and
restaurant owners (p< 0.001).
4. Discussion
This study provides valuable data to help understand the con-
servation impact of commercial farming. At least 58% of the 67
farms in this study had purchased wild founder stock, and at least
19% are continuing to buy wild animals. The scale of commercial
porcupine farming has increased dramatically in recent years
alongside an increase in selling price of porcupines from farms.
The results here highlight that under current management, com-
mercial farming could potentially cause local extirpations of even
relatively common and fast-breeding species like porcupines.
4.1. A large and rapidly growing industry
Whilst there are 449 porcupine farms registered with the FPD in
Son La province, the department admits that this is an underesti-
mation of the true number. Indeed, only half of those interviewed
were verified as registered farms. Accounts volunteered from inter-
viewed farm owners suggest there may be as many as 600 farms in
Son La and Song Ma towns alone, with many more unregistered
farms across the province where FPD reports there are none (e.g.
in the districts of Muong La and Quynh Nhai, shown in Fig. 1).
We recorded a rapid growth in porcupine farming in recent years,
with more than half of farm owners interviewed stating they
started in the last three years. The snowball sampling method used
to identify farms would be expected to result in a right-skewed
bias towards older and more established farms (i.e. better known
to people than newer ones) so it is unlikely that this increase is
due to sampling bias.
The vast majority of farms were household enterprises, and fre-
quently enclosures were simply adaptations of existing enclosures
for other domestic livestock (e.g. pigs). Resource constraints, or
lack of economic viability, are often cited as reasons that wildlife
farming is often unsuccessful (e.g. Mockrin et al., 2005) but the
minimal husbandry requirements and the reported ease with
which porcupines are bred indicate that these are not limiting fac-
tors for this species.
Large profits are available from the breeding of porcupines, with
the sale of just two pairs of porcupines far exceeding the GNI per
capita of Vietnam of US$890 (World Bank, 2008a), hence the
increasing interest in porcupine farming, and high demand for
founder stock. The accelerated growth in the number of farms
starting up each year is likely to continue, with the increased price
and demand encouraging a greater level of hunting of wild popula-
tions (Redmond et al., 2006).
The current porcupine trade dynamics are encouraging growth
of trading by recruiting more porcupine farmers, whilst not passing
on the porcupine product of meat to the consumers. This trade
structure is akin to a pyramid scheme, and is an unsustainable
model.
4.2. Direct threats to wild porcupine populations
This study found however that the greatest threat to the wild
populations is not from demand for founder stock, but from farms
laundering wild animals, and selling them across the country. Four
farms which were willing to talk openly, reported trading almost
1000 wild porcupines each year, predominantly to other farms as
founder stock. At least two further farms were suspected of laun-
dering animals, based on interview reports yet this could not be
verified. Due to the illegal nature of this activity, it is more likely
that farm owners would hide this information, so figures reported
Fig. 6. Mean (±SE) price (US$) of meat per kg (F
2,33
= 53.12, p< 0.001). Reported
wild meat prices were collected from farm owners in Son La province, and
restaurant owners in Hanoi. Equivalent farmed meat prices are from porcupine
farms in Son La.
2812 E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814
should be considered a conservative estimate of the true scale of
the illegal trade of porcupines through the farms.
Most farm owners are very aware their trade was resulting in
the decline of wild populations. However, they were either uncon-
cerned or ignorant of the implications of this. Several interviewees
reported that porcupines used to be found locally in Son La prov-
ince, but have been largely or entirely wiped out in the past
20 years through hunting. Without preventative measures, the
wild porcupine populations sourcing the farms in Son La could also
be facing extirpation.
4.3. Economics of porcupine trade
The viability of wildlife farming as an alternative to illegal hunt-
ing relies upon the farm producing a cheaper, acceptable product
to the consumer (Brown and Layton 2001; Bulte and Damania,
2005). This model does not apply in this study where we found
wild individuals to be sold for half the price of farmed individuals.
In addition, the simple economic models often used to justify wild-
life farming fail to incorporate the strategic responses of illegal
traders, who take advantage of weak management of wildlife farms
to make additional profit from illegal sales.
Although profit can be made from direct trading of wild ani-
mals, rather than breeding them, farm owners can receive a
greater income through closed-cycle breeding due to the higher
sale price of farm stock. Nonetheless, despite having facilities
and capital for breeding, a number of farm owners still chose
to trade wild porcupines. It appears that legalisation of the trade
and government support relaxes law enforcement efforts, provid-
ing opportunity for illegal traders to make additional profit from
wild porcupine sales. This is facilitated through continued
demand for wild porcupines from restaurant owners who favour
wild porcupines due to lower price and consumer preference for
wild over farm-raised.
The price of porcupines has increased sharply, with the cost of
juvenile founder stock doubling between 2005 and 2008, and this
was regularly cited as a limitation to more people starting farms.
Demand for porcupines as founder stock will likely decrease over
coming years as the market is saturated and prices will ultimately
fall. Whether farmed porcupines can substitute the demand for
wild porcupines from restaurants is likely to decide the fate of
the farms from that point onwards but results from this study indi-
cate that is unlikely. The trade may be continued through the ex-
port of porcupines to Chinese markets rather than for sale in
Vietnam. One farm owner has already exported at least once to
China and received 800,000 VND (US$49) per kg, far greater than
estimates for sale prices in Vietnam.
4.4. Porcupine farms are poorly managed and monitored
The monitoring and control of the wildlife trade in Vietnam
(including wildlife farms) is under-resourced, weak and ineffectual
(Vu, 1999; Nguyen, 2003; WCS and TRAFFIC, 2004; WCS, 2008).
Current management of the porcupine farms is inadequate to pre-
vent wild animals entering the trade. Many farms are established
with porcupines of wild origin and then being registered by the
FPD; whilst others bring in wild stock and register them as births.
In other Vietnamese provinces farm owners reported replacing
sick/injured animals or any lost with those from the wild, knowing
that the authorities cannot distinguish individuals. Eighty-nine per
cent of farmers reported paying FPD a fee for processing their farm
registration, which given the fact this is a free process, strongly
suggests corruption may play a large part in facilitating this illegal
trade.
4.5. Do the porcupine farms provide a substitute for illegally-sourced
wild porcupine meat?
Large amounts of porcupine meat are consumed in restaurants.
In a study in the central provinces of Vietnam, Roberton (2007)
found that porcupine was the second most frequently reported
wild meat to be sold in restaurants after wild pig, at an average
of 47.6 kg per week per restaurant.
This study found that due to the high price of farmed porcu-
pines, restaurants source almost all their porcupine meat from ille-
gal wild sources. Therefore, the farms are yet to address the
potential positive conservation impact they hold. However, since
there is a preference for wild meat, should prices of farmed animals
fall, restaurant owners may continue to source meat from the wild
to fulfil consumer demand, even if there is a locally-available, legal
and cheaper alternative (Roberton, 2007). In addition to this, the
high mortality rate of trapped animals provides a steady source
of meat to restaurants.
4.6. Are porcupine farms driving the decline of porcupines in Lao PDR?
Whilst there has been a suggested link between wildlife farms
and local extirpations of species populations, there have been no
direct studies of farms having a resultant impact on wild popula-
tions. WCS (2008) discusses a possible connection between porcu-
pine farms in the province of Son La, and the decline in wild
populations in Nam Et-Phou Louey National Protected Area (NEPL
NPA) directly across the border from Son La in Lao PDR. Prelimin-
ary analysis of camera-trap data collected in the NPA showed a sig-
nificant decline in the number of sites recording the presence of
Southeast Asian porcupines (H. brachyura) between 2003 and 2007.
Although overexploitation has caused the decline in a range of
taxa in NEPL NPA in neighbouring Lao PDR (Johnson et al., 2006),
the Southeast Asian porcupine has shown a greater rate of decline
compared to similar species also part of the wildlife trade, such as
muntjacs, Muntiacus sp (A. Johnson, unpublished data). As well as
reports by residents and officials in the local area of NEPL NPA that
live porcupines are hunted for sale to farms in Son La province (A.
Johnson, pers. comm.), the confiscation from offenders of male/fe-
male pairs of porcupines provides evidence that the species is
being targeted to meet the demand for founder stock. Fifty-three
per cent of Son La farm owners confirmed that wild porcupines
originated from populations in Lao PDR. A further 36% thought that
wild porcupines were captured in the districts of Song Ma or Sop
Cop, but since all respondents in these districts reported there
were no, or very few, wild porcupines to be found locally, it is likely
that these animals actually originated from Lao PDR, despite being
sold by hunters or traders in Song Ma and Sop Cop.
Illegal wildlife trade increases as access for hunters and traders
improves (Milner-Gulland and Bennett, 2003; Redmond et al.,
2006). The completion of the new road joining NEPL directly with
Son La will have facilitated the transfer of hunted animals.
Thousands of porcupines are being removed from the NPA to sup-
ply the demand from the farms in Son La alone, and there may be a
similar situation developing in the neighbouring province of Dien
Bien, also joined to NEPL by road. With the increase in demand
for founder stock, there is an expanding market for hunters to
profit from, and with such high prices, even at source level, the
incentives to continue the illegal trade are considerable. Hunters
trapping porcupines in NEPL NPA were selling these to traders at
US$250 per pair in 2007 (A. Johnson, pers. comm.). Whilst this is
lower than the mean sale price to Son La farmers of US$657, it is
still a significant source of income, and the sale of just two pairs
of porcupines by hunters would meet the equivalent of the GNI
per capita of Lao PDR of US$500 (World Bank, 2008b). Punishment
for hunters and illegally operating farm owners alike is confisca-
E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814 2813
tion of the animals and a fine equivalent to their retail value. For
large-scale offenders, this is an inadequate disincentive when pros-
ecution rates are so low, and the sale of just two more pairs of por-
cupines would cover their losses.
5. Conclusions
Advantages and disadvantages of wildlife farming cannot be ap-
plied universally. For instance, whereas in Africa wildlife farming is
argued to be an alternative to wild meat, providing food security
(see Mockrin et al. (2005)), this is not the case for species farmed
in Vietnam. Wild meat in Vietnam supplies a luxury, urban market
and as such commands a high value. It is likely that these species
will continue to be hunted from the wild as long as populations
do not diminish so much as to become unprofitable to the hunters
(Mockrin et al., 2005).
Currently, commercial porcupine farming is driving hunting
and is thought to be, at least in part, responsible for the decline
of wild porcupines in NEPL NPA in adjacent Lao PDR. However well
the farms are managed, as long as there is consumer demand for
porcupine products, without serious disincentives for the hunters,
hunting of the wild populations will continue. Contrary to the
claims of proponents of wildlife farmers, the porcupine farms in
Son La province are not providing a cheaper alternative, nor are
they providing an adequate substitute since meat is still sourced
from the wild. Monitoring and enforcement of these farms and
the restaurants is inadequate and needs to be addressed to ensure
the protection of wild porcupine populations.
Farming wildlife is a growing enterprise in Vietnam and across
much of Southeast Asia (WCS, 2008). Wildlife farms have been
linked to the decline and extirpation of once-common species such
as sika deer (Cervus nippon) and Siamese crocodile (Crocodylus sia-
menis) in Vietnam (Polet, 2004). Southeast Asian porcupines are a
relatively common species within their distribution range, yet this
study highlights that commercial farming could be responsible for
a rapid decline in Northern Vietnam. The gaps in current regula-
tions and management found here and in other studies indicate
the significant risks to populations of threatened species.
Acknowledgements
We would like to thank Nguyen Thi Oanh for her assistance in
conducting the interviews. Thanks to Dr. Arlyne Johnson for access
to her data and discussion on the status of porcupines in Lao PDR.
E. Brooks was supported by a NERC studentship.
References
Anon, 2006. Land Use by Province (As of 1 January 2006). General Statistics Office of
Vietnam. <http://www.gso.gov.vn> (accessed June 2008).
Bell, D., Roberton, S., Hunter, P.R., 2004. Animal origins of SARS coronavirus:
possible links with the international trade in small carnivores. Philosophical
Transactions of the Royal Society of London Series B – Biological Sciences. 359,
1107–1114.
Bennett, E.L., 2002. Is there a link between wild meat and food security?
Conservation Biology 16, 590–592.
Bennett, E.L., Robinson, J.G., 2000. Hunting of Wildlife in Tropical Forests:
Implications for Biodiversity and Forest Peoples. The World Bank,
Washington, DC.
BLS, 2008. US Bureau of Labor Statistics. CPI Inflation Calculator. <http://
data.bls.gov/cgi-bin/cpicalc.pl> (accessed June 2008).
Broad, S., Mulliken, T., Roe, D., 2003. The nature and extent of legal and illegal trade
in wildlife. In: Oldfield, S. (Ed.), The Trade in Wildlife: Regulation for
Conservation, 3–22. Earthscan Publications Ltd., UK.
Brown, G., Layton, D., 2001. A market solution for preserving biodiversity: the black
rhino. In: Shogren, J., Tschirhart, T. (Eds.), Protecting Endangered Species in the
United States: Biological Needs, Political Realities, Economic Choices.
Cambridge University Press, Cambridge, UK, pp. 32–50.
Bryman, A., 2004. Social Research Methods, second ed. Oxford University Press, New
York.
Bulte, E.H., Damania, R., 2005. An economic assessment of wildlife farming and
conservation. Conservation Biology 19, 1222–1233.
Chardonnet, P., des Clers, B., Fischer, J., Gerhold, R., Jori, F., Lamarque, F., 2002. The
value of wildlife. Revue Scientifique et Technique de l’Office International des
Epizooties 21, 15–51.
Cicogna, M., 1992. The first international seminar on farming of invertebrates and
other minilivestock. Tropicultura 10, 155–159.
Cooper, J.E., 1995. Wildlife species for sustainable food production. Biodiversity and
Conservation 4, 215–219.
Fa, J.E., Peres, C.A., Meeuwig, J., 2002. Bushmeat exploitation in tropical forests: an
intercontinental comparison. Conservation Biology 16, 232–237.
Hardouin, J., 1995. Minilivestock – from gathering to controlled production.
Biodiversity and Conservation 4, 220–232.
IUCN, 2001. Commercial Captive Propagation and Wild Species Conservation.
Workshop Report. IUCN/SSC Wildlife Trade Programme. Florida, USA.
Johnson, A., Vongkhamheng, C., Hedemark, M., Saithongdam, T., 2006. Effects of
human-carnivore conflict on tiger (Panthera tigris) and prey populations in Lao
PDR. Animal Conservation 9, 421–430.
Jori, F., Mensah, G.A., Adjanohoun, E., 1995. Grasscutter production – an example of
rational exploitation of wildlife. Biodiversity and Conservation 4, 257–265.
Lapointe, E., Conrad, K., Mitra, B., Jenkins, H., 2007. Tiger Conservation: It’s Time to
Think Outside the Box. IWMC World Conservation Trust. Lausanne, Switzerland.
Lunde, D., Aplin, K., Molur, S., 2008. Hystrix brachyura. In: IUCN 2009. IUCN Red List
of Threatened Species. Version 2009.1. <www.iucnredlist.org> (accessed
September 2009).
Milner-Gulland, E.J., Bennett, E.L., 2003. Wild meat: the bigger picture. Trends in
Ecology & Evolution 18, 351–357.
Mockrin, M. H., Bennett, E. L., LaBruna, D.T., 2005. Wildlife Farming: A Viable
Alternative to Hunting in Tropical Forests? WCS Working Paper No. 23, New
York.
Nguyen Van Song, 2003. Wildlife Trading in Vietnam: Why It Flourishes. Hanoi
Agricultural University # I, Vietnam. Hanoi.
Nowak, R.M., 1999. Walker’s Mammals of the World, sixth ed. The John Hopkins
University Press, Baltimore & London.
Parry-Jones, R., 2001. Captive Breeding and Traditional Medicine. In Commercial
Captive Propagation and Wild Species Conservation. IUCN/SSC Wildlife Trade
Programme. Florida, USA.
Polet, G., 2004. Re-establishment of Crocodylus siamenis in Cat Tien National Park,
Vietnam. IUCN Species Survival Commission, Australia, pp. 12–16.
Redmond, I., Aldred, T., Jedamzik, K., Westwood, M., 2006. Recipes for Survival:
Controlling the Bushmeat Trade. Report for WSPA, London.
Revol, B., 1995. Crocodile farming and conservation, the example of Zimbabwe.
Biodiversity and Conservation 4, 299–305.
Roberton, S., 2007. The Status and Conservation of Small Carnivores in Vietnam.
PhD Thesis, University of East Anglia.
OANDA. 2008. FXHistory
Ò
: Historical Currency Exchange Rates. <http://
www.oanda.com> (accessed June 2008).
Swift, L., Hunter, P.R., Lees, A.C., Bell, D.J., 2007. Wildlife trade and the emergence of
infectious diseases. Ecohealth 4, 25–30.
Vu Ngoc Thanh. 1999. Biodiversity Loss – Lessons Learned in Vietnam. Regional
Project: RAS/93/102 Subregional Biodiversity Conservation Component. UNDP
Vietnam.
Wildlife Conservation Society, 2008. Commercial Wildlife Farms in Vietnam: A
problem or Solution for Conservation? WCS, Hanoi, Vietnam.
WCS & TRAFFIC. 2004. Hunting and Wildlife Trade In Asia: Proceedings of a
Strategic Planning Meeting of the Wildlife Conservation Society (WCS) and
TRAFFIC, Bali, Indonesia, August 2004.
Whitfield, J., 2003. Bushmeat – the law of the jungle. Nature 421, 8–9.
World Bank, 2008a Vietnam Data & Statistics. <http://go.worldbank.org/
KPB5TK9CF0> (accessed March 2010).
World Bank. 2008b. Lao PDR Data & Statistics. <http://go.worldbank.org/
NNAO5U9G90> (accessed March 2010).
2814 E.G.E. Brooks et al. / Biological Conservation 143 (2010) 2808–2814
... The loss of animals from forest ecosystems and the resultant disruption of ecological and ultimately evolutionary processes, changes in species composition and probable reduction in biological diversity are collectively known as the empty forest syndrome (Wright, 2009). Brooks (2014) on the basis of reports from the hunting activities literature, it seems likely that a majority of tropical nature reserves may already be considered empty forests meaning that all bird and mammal species larger than approximately two kilograms barring a few gaming activities-tolerant species have either been extirpated or exist at densities well below natural levels of abundance. The disruption of ecological functions caused by the loss of symbionts further compromises the capacity of these reserves to conserve biodiversity over the long term. ...
... The literature reviewed (Brooks, 2014;Dau, Mai & Dawaki, 2015) revealed that the pattern of gaming activities explained why very little surviving wildlife are around areas of high human population. The uncontrolled or unregulated gaming activities have resulted in loss of biodiversity. ...
... The loss of animals from forest ecosystems and the resultant disruption of ecological and ultimately evolutionary processes, changes in species composition and probable reduction in biological diversity are collectively known as the "empty forest syndrome. The result is also in line with Brooks (2014) whose study revealed that a majority of tropical nature reserves may already be considered empty forests meaning that all bird and mammal species larger than approximately two kilograms barring a few gaming activities-tolerant species have either been extirpated or exist at densities well below natural levels of abundance. The disruption of ecological functions caused by the loss of symbionts further compromises the capacity of these reserves to conserve biodiversity over the long term. ...
Article
Full-text available
This study investigates the relationship between gaming activities and forest resources degradation in Obubra Local Government Area of Cross River State. To achieve the purpose of this study, two research questions and two null hypotheses were formulated. Correlational research design was adopted for the study. The area of the study was Obubra LGA, Cross River State. The target population was all household members who are farmers aged 18 to 35 years. Multistage sampling techniques were adopted in selecting four hundred and fifty (450) respondents used for the study. A ten item modified four point Likert scale questionnaire titled "Gaming activities and Forest Resources Degradation Questionnaire (GAFRCQ)" was the instruments used for collecting data for the study. To test the hypothesis formulated for the study, Pearson product moment correlation statistical tools was used as statistical tool for data analysis. The hypotheses formulated were tested at 0.05 level of significance. The statistical report of research question one established that there are several gaming activities taking place in the study area. The report in research question two established that forest resources degradation are available in the study Area. The results of the analysis revealed that there is a significant relationship between hunting for sport and forest resources degradation. There is a significant relationship between hunting for bush meat and forest Ilorin Journal of Education (IJE). Vol. 44 No.2. March 2024 333 resources degradation. Based on the findings it was recommended among others that the government and other environmental stakeholders should ensure that community dwellers participate on mobilization and awareness against unsustainable gaming activities.
... Porcupines (Order: Rodentia) fall into this category whereby they are hunted throughout their range but there are few studies on the impacts of trade on wild populations (Brooks et al. 2010, Heinrich et al. 2020, Gomez 2021, Hassan and Csanyi 2022. Porcupines play a vital ecological role, contributing to the health and balance of ecosystems through their foraging, disturbance, seed dispersal, nutrient cycling, and habitat provision behaviours (Roze 2012). ...
... There is a growing body of research highlighting the significant threat posed by uncontrolled poaching and trade in porcupines in many parts of Asia (Brooks et al., 2010, Chung et al., 2016, Salviana et al. 2017, McEvoy et al. 2019, Hassan and Csanyi, 2022. Porcupines are hunted for various purposes: their meat is valued as an alternate source of protein; they produce bezoars (i.e., a non-digestible food material that forms a stone like mass in their gut), which is valued as a potential traditional cure for a range of diseases including cancer, diabetes, dengue, typhoid, epilepsy, hepatitis, etc; and their quills, although valued in traditional medicine, are also primarily used as hairpins by pregnant women and as souvenirs or talismans against black magic (Brooks et al. 2010, Brown 2015, Lee et al. 2015, Yeung 2019, Hassan and Csanyi, 2022. ...
... There is a growing body of research highlighting the significant threat posed by uncontrolled poaching and trade in porcupines in many parts of Asia (Brooks et al., 2010, Chung et al., 2016, Salviana et al. 2017, McEvoy et al. 2019, Hassan and Csanyi, 2022. Porcupines are hunted for various purposes: their meat is valued as an alternate source of protein; they produce bezoars (i.e., a non-digestible food material that forms a stone like mass in their gut), which is valued as a potential traditional cure for a range of diseases including cancer, diabetes, dengue, typhoid, epilepsy, hepatitis, etc; and their quills, although valued in traditional medicine, are also primarily used as hairpins by pregnant women and as souvenirs or talismans against black magic (Brooks et al. 2010, Brown 2015, Lee et al. 2015, Yeung 2019, Hassan and Csanyi, 2022. They are also persecuted as agricultural pests in some places (Safeer et al. 2018, Mustikasari et al. 2019. ...
Article
Full-text available
Background and Research Aims Porcupines are frequently traded in Asia but evidence of this remains undocumented. This study was undertaken to address the dearth of information on porcupine trade dynamics using Malaysia as a case study. Methods To accomplish this, traditional Chinese medicine (TCM) outlets throughout the country were surveyed, the existence of porcupine farms were determined and porcupine seizures in Malaysia from 2011 – 2019 were analysed. Results The data revealed that porcupines are coveted predominantly for bezoars used in TCM and for breeding stock. Porcupine bezoars were found in 90% of TCM outlets surveyed though it is likely that the market consists of genuine and fake products. Porcupine farming appears to be gaining popularity and predominantly caters to a demand for breeding pairs. There were 47 seizures amounting to 110 porcupines of at least three species. Seizures included mostly live animals but also meat and quills. Conclusion The harvesting and consumption of porcupines is legally permitted in Malaysia. However, it is evident that illegal hunting of porcupines is also occurring. Captive breeding is unlikely to reduce poaching of porcupines considering the high value associated with wild-sourced bezoars. Local use is also driving international trade of bezoars particularly from Indonesia. Implications for Conservation Research on porcupine trade dynamics in Southeast Asia is limited. This is a conservation concern particularly as porcupines are valued as commercial commodities. As Asian porcupines face a multitude of synergistic threats ( i.e., habitat loss, human conflict and illegal hunting), understanding these cumulative impacts on wild populations is a conservation priority. More research on international trade dynamics is also warranted as it is currently occurring without any regulation or monitoring. Listing porcupines in the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) could potentially mitigate this.
... It has been believed that wildlife farming will help meet the increasing demands on wild products, reduce the consumption of wild-caught animals, and change the consumers' preference for wild-caught animals 50 . Wildlife farming helped to improve the accessibility to wild products and create substitutability 41,50,55,56 , and in Viet Nam, wildlife farming has provided economic benefits to local communities and households 14,16,38,[41][42][43]45,48,55,57 . ...
... Four studies have pointed out that wildlife farming has failed in fulfilling its role as a conservation tool, and instead, it contributed to the increased illegal poaching and exploitation 42,41,57,38,55 . The reason for this situation is that consumers still prefer wild-sourced animal products over captive ones. ...
... All levels of administration, from the national level In addition, the existing regulations are not either detailed or updated in terms of risk management of wildlife farming, or the management mechanism is not strong enough to adequately monitor the activities at farming facilities 15,39,40,43,48,58,60 . As a result, illegal activities at farms could be overlooked, such as mixing illegally sourced animals with registered animals for farming 16,40,48,55 , and slaughtering both registered animals and illegally poached animals 38,55,57 . The issues of wildlife farms holding captive animals from the wild, slaughtering, and selling illegal wild animals have been well documented in many reports 38,48,[55][56][57] . ...
Article
Full-text available
Wildlife farming is a long-standing practice in Viet Nam, dating back to the late 1800s, and it has experienced significant expansion alongside the country's economic development. In light of the growing concern about zoonotic disease spillover at this human-animal interface, particularly in the context of a suspected escalation of wildlife farming activities in Viet Nam to meet the demand in China following regulatory measures to reduce wildlife farming after COVID-19, this study endeavored to examine the management of zoonotic disease risks related to wildlife farming in Viet Nam. The work established a comprehensive understanding of the existing policy framework, shedding light on the key areas that may warrant improvement for risk management to systematically mitigate the risks of zoonotic disease emergence from wildlife farming practices in Viet Nam.
... In Bangladesh, Asiatic brush-tailed porcupines are listed as Data Deficient, whilst Malayan porcupines are unassessed, given their insufficient documentation (IUCN Bangladesh, 2015). In any case, these species are likely threatened by uncontrolled poaching and persecution, as documented in other areas of Asia (e.g., Brooks et al., 2010;Gomez, 2021;Gomez and Min Sheng, 2024;Heinrich et al., 2020;Loke et al., 2020;McEvoy et al., 2019). ...
... There are already indications that Malayan porcupines are extensively harvested for nutritional, medicinal, and decorative uses in several other Asian countries, where concern of uncontrolled poaching is growing (e.g., Brooks et al., 2010;Gomez, 2021;Gomez and Min Sheng, 2024;Heinrich et al., 2020;Loke et al., 2020;McEvoy et al., 2019). In this study, more than half of the incidents we logged from our literature and media searches referred to the rescue of Malayan porcupines from mob beating, or the confiscation of porcupines from bushmeat hunters. ...
Article
Many aspects of Hystricidae porcupine ecology in South Asia, including that of the Malayan porcupine (Hystrix brachyura), remain poorly studied. Part of this species’ global range falls within Bangladesh, where the presence and distribution of porcupines is generally unclear. In Bangladesh, 2–3 species are thought to occur: the Malayan porcupine, the Asiatic brush-tailed porcupine (Atherurus macrourus), and the Indian crested porcupine (Hystrix indica). However, the presence of the latter is disputed. In this study, we used camera trapping data from mixed evergreen forests in northeastern Bangladesh and country-wide occurrence records from a literature and media report to clarify current knowledge of porcupine distributions in the country. Our results expand the known distributions of Malayan and Asiatic brush-tailed porcupines in Bangladesh but provide no evidence of the Indian crested porcupine. Additionally, using the camera trapping data, we explore previously unreported aspects of the ecology and activity patterns of Malayan porcupines. We examined their temporal activity against that of Asiatic brush-tailed porcupines, carnivores and anthropogenic stressors, as well as investigated the effect of nighttime illumination on activity patterns. We found that Malayan porcupines are generally more active over winter. However, they consistently reduced their activity levels on brighter nights and avoided full-moon periods as a potential anti-predator mechanism. The species exhibited high temporal overlap with similarly nocturnal Asiatic brush-tailed porcupines and mesocarnivores, but little to no overlap with largely diurnal human activity, livestock or feral dog movements. Considering the limited data available on these porcupine species as well as the growing demand for bushmeat and medicinal products, concerns for porcupine populations in South and Southeast Asia are growing. Improved knowledge is crucial for conservation monitoring and management; therefore, further ecological and threat studies are needed to tackle this knowledge gap and inform conservation plans appropriately.
... In Bangladesh, Asiatic brush-tailed porcupines are listed as Data Deficient, whilst Malayan porcupines are unassessed, given their insufficient documentation (IUCN Bangladesh, 2015). In any case, these species are likely threatened by uncontrolled poaching and persecution, as documented in other areas of Asia (e.g., Brooks et al., 2010;Gomez, 2021;Gomez and Min Sheng, 2024;Heinrich et al., 2020;Loke et al., 2020;McEvoy et al., 2019). ...
... There are already indications that Malayan porcupines are extensively harvested for nutritional, medicinal, and decorative uses in several other Asian countries, where concern of uncontrolled poaching is growing (e.g., Brooks et al., 2010;Gomez, 2021;Gomez and Min Sheng, 2024;Heinrich et al., 2020;Loke et al., 2020;McEvoy et al., 2019). In this study, more than half of the incidents we logged from our literature and media searches referred to the rescue of Malayan porcupines from mob beating, or the confiscation of porcupines from bushmeat hunters. ...
... Efforts to govern facilities are undermined by insufficient governance structures, corruption, and limited prosecutorial force (Nijman et al., 2018). In Vietnam, 89% of porcupine farmers reported paying the government's Forest Protection Department a fee for farm registration, which is a free process, strongly indicating corruption whilst many farmers freely admit to having used wild specimens to replenish their breeding stock (Brooks et al., 2010). In Indonesia, 92% of python farmers admitted to circumventing laws and regulations by paying off officials (Lyons & Natusch, 2011). ...
... NGOs such as the Sepik Wetlands Management Initiative have provided critical funding to nascent captive-breeding programmes and further NGO involvement would support the delivery of sustainable, rural livelihoods (Daltry et al., 2016). Whilst subsidising sourcing of captive stock will increase legitimate participation and reward established wildlife farms, such payments may finance a growing re-sale market and reduce the volume of captive-bred products displacing wild-sourced commodities, diminishing the conservation value of wildlife farming (Brooks et al., 2010). ...
Article
Full-text available
Demand for wildlife and their products continues to grow, often despite increasingly militarised regulation and consumer awareness campaigns. We review the sustainability, legality and feasibility of wildlife farming of animals, as a potential conservation tool to ensure the development of an equitable and sustainable trade model. While there are some positive examples of well-managed wildlife farming in trade, we identify common themes of misuse including the intentional mislabelling of wild-caught specimens in global trade and the use of wild-caught individuals to supplement captive stocks. We also highlight the frequent failure to incorporate biological data into management strategies, resulting in the widespread use of species with potentially unfavourable life history traits, which constrain the economic and biological sustainability of wildlife farming programmes. We develop a structured decision framework to aid the examination of when wildlife farming may most benefit or hinder species conservation. Synthesis and applications. Key opportunities include developing species suitability assessments and removing barriers to legitimate participation with wildlife farming among poor, rural communities. In the absence of management strategies that address the issues of species suitability and accessibility, wildlife farming will continue to place significant strain on wild populations while failing to provide conservation value and sustainable economic returns.
... Animal welfare concerns, abuse, and overexploitation of wild populations have been identified in some Asian wildlife farming practices, where wild populations are often used as seed stock, exemplified with the dramatic decline of the porcupine (Hystrix brachyura) [102]. Contrastingly, such issues have not been identified in the Caribbean region. ...
Article
Full-text available
This opinion piece clarifies the impact of climate change on animal production in the Latin America and Caribbean (LAC) region and proposes a sustainable solution. Anthropogenic climate change has resulted in higher ambient temperatures, rainfall, humidity, storms and desertification. These events have direct and indirect effects on conventional animal performance and this piece will highlight the impact of increased temperatures on their welfare, health and production in the LAC. Alternative species such as neo-tropical wildlife animals have been proposed as climate resilient animals for use in the LAC, as they are well adapted to the climate and environment in the tropics. Some of these animals include capybara, lappe, agouti, caiman, cocrico and collared peccary. Neo-tropical animal production has the potential to produce nutritious meat, quality leather, reduce pollution and serve as a form of sustainable production. These animals can be inserted into a sustainable production system as their feed resources can be supplied through the use of local feedstuff, they also require less water and energy for maintenance, as they are well adapted to the high temperature and humidity in comparison to domesticated animals such as cattle, pigs and chickens. Finally, the key challenges including the legal use of the animals throughout the year, lack of technical experience and limited knowledge on the biology of these animals are discussed.
... A medida que ésta avanza hacia áreas anteriormente vírgenes, las operaciones de alimentos silvestres, que responden a una gran demanda por parte de granjas y restaurantes, deben adentrarse aún más para obtener sus productos. Por otro lado, el menor costo de los animales salvajes respecto de aquellos criados en granjas (hasta un 50% menos) es un factor importante que ha impulsado el comercio de especies salvajes en todo el sudeste asiático (Brooks, Roberton y Bell, 2010). ISSN 2683-8915 [en línea] https://posicion-inigeo.unlu.edu.ar/ ...
Article
Full-text available
Resumen. La pandemia de COVID-19 vigorizó los debates sobre el capitalismo monopolista financiero y su correlación con las crisis ecológica y epidemiológica. Las tradicionales explicaciones sobre la etiología de las enfermedades zoonóticas contemporáneas ofrecidas desde el marco individualista biomédico se vieron fuertemente confrontadas con los argumentos nutridos por la perspectiva ecológica que consideran el notorio aumento de las Enfermedades Infecciosas Emergentes desde la década de 1980 como una manifestación nefasta de problemáticas más amplias relacionadas con el modelo de acumulación extractivista y complejos circuitos de capital que imprimen cambios globales en el modo e intensidad del uso de la tierra, y crean interfaces peligrosas entre personas, ganado y reservorios de vida silvestre de enfermedades zoonóticas. Con base en esta hipótesis y valiéndonos de evidencias científicas, examinamos la incidencia que ha tenido en el contexto latinoamericano la aceleración del ritmo de reproducción del capital iniciado con el giro neoliberal, en los procesos de deterioro ambiental y ecosistémico, y en la concomitante disminución de las tasas de reproducción de la vida y la salud. Se abordan específicamente tres nudos problemáticos: los rasgos que caracterizaron la emergencia y manejo del COVID-19, el rol del extractivismo en la potenciación de riesgos biológicos catastróficos, y la relación entre enfermedades globales y Cambio Global. Abstract. The COVID-19 pandemic has invigorated debates on financial monopolistic capitalism and its correlation with ecological and epidemiological crises. Traditional explanations for the etiology of contemporary zoonotic diseases offered from the individualistic biomedical framework were strongly confronted with arguments nurtured by the ecological perspective, which consider the notable increase in Emerging Infectious Diseases since the 1980s as a dire manifestation of broader issues related to the extractivist accumulation model and complex capital circuits that imprint global changes in the mode and intensity of land use, creating dangerous interfaces between humans, livestock, and wildlife reservoirs of zoonotic diseases. Based on this hypothesis and relying on scientific evidence, we examine the impact that the acceleration of capital reproduction initiated by the neoliberal turn has had on environmental and ecosystem deterioration in the Latin American context, and the concomitant decrease in reproduction rates of life and health. Specifically, three problematic nodes are addressed: the characteristics that marked the emergence of COVID-19 and its management, the role of extractivism in enhancing catastrophic biological risks, and the relationship between global diseases and Global Change.
... 14,15 Porcupine meat is popular due to its high protein, low fat and low cholesterol, which has further resulted in a rapid increase in the number of porcupine farms. 16 Porcupine has not only edible value but also high medicinal value in traditional Chinese medicine, such as the porcupine stomach has the effect of clearing heat and dampness, porcupine spines have the effect of skin allergy treatment. 17 Especially, porcupine bezoars have been used in medicine for centuries. ...
Article
Full-text available
BACKGROUND Porcupine quills, a by‐product of porcupine pork, are rich in keratin, which is an excellent source of bioactive peptides. The objective of this study was to investigate the underlying mechanism of anti‐proliferation effect of porcupine quills keratin peptides (PQKPs) on MCF‐7 cells. RESULTS Results showed that PQKPs induced MCF‐7 cells apoptosis by significantly decreasing the secretion level of anti‐apoptosis protein Bcl‐2 and increasing the secretion levels of pro‐apoptosis proteins Bax, cytochrome c, caspase 9, caspase 3 and PARP. PQKPs also arrested the cell cycle at G0/G1 phase via remarkably reducing the protein levels of CDK4 and enhancing the protein levels of p53 and p21. High‐performance liquid chromatography–tandem mass spectrometry (HPLC–MS/MS) analysis identified nine peptides with molecular weights less than 1000 Da in PQKPs. Molecular docking results showed that TPGPPT and KGPAC identified from PQKPs could bind with p53 mutant and Bcl‐2 protein by conventional hydrogen bonds, carbon hydrogen bonds and van der Waals force. Furthermore, the anti‐proliferation impact of synthesized peptides (TPGPPT and KGPAC) was shown in MCF‐7 cells. CONCLUSION These findings indicated that PQKPs suppressed the proliferation of MCF‐7 breast cancer cells by triggering apoptosis and G0/G1 cell cycle arrest. Moreover, the outcome of this study will bring fresh insights into the production and application of animal byproducts. © 2023 Society of Chemical Industry.
Article
Full-text available
The commercial exploitation of wildlife affects many species, including porcupines that are traded for meat, as pets, and for medicinal purposes. Here we report on a novel trade in Sunda Porcupine Hystrix javanica skulls in Bali specifically for curios and as aquarium novelty objects. Since 2018, the species is protected within Indonesia and the sale of skulls is illegal. Between December 2022 and November 2023, we visited wildlife shops in seven towns, and conducted a survey of online sellers. We recorded 44 porcupine skulls in 11 shops and 10 skulls online. Skulls sold as curios were intricately carved and were priced at USD 61, whereas skulls sold as hiding caves for aquarium fish were not carved and priced at USD 22. Porcupine skulls were sourced from Bali and Java. Especially the carved skulls are marketed primarily for international tourists and may be inadvertently taken abroad. The novel trade in skulls adds to a multitude of threats faced by porcupines, and there is a need for improved regulations and enforcement against illegal trade. Appropriate mitigation measures need to be developed to protect porcupines from unsustainable and illegal exploitation and will require the full operation of the commercial sector, local and national governments, the tourism industry and the Indonesian public.
Article
Full-text available
Unique to South-east Asia, Lao People's Democratic Republic contains extensive habitat for tigers and their prey within a multiple-use protected area system covering 13% of the country. Although human population density is the lowest in the region, the impact of human occurrence in protected areas on tiger Panthera tigris and prey populations was unknown. We examined the effects of human– carnivore conflict on tiger and prey abundance and distribution in the Nam Et-Phou Louey National Protected Area on the Lao–Vietnam border. We conducted intensive camera-trap sampling of large carnivores and prey at varying levels of human population and monitored carnivore depredation of livestock across the protected area. The relative abundance of large ungulates was low throughout whereas that of small prey was significantly higher where human density was lower. The estimated tiger density for the sample area ranged from 0.2 to 0.7 per 100 km 2 . Tiger abundance was significantly lower where human population and disturbance were greater. Three factors, commercial poaching associated with livestock grazing followed by prey depletion and competition between large carnivores, are likely responsible for tiger abundance and distribu-tion. Maintaining tigers in the country's protected areas will be dependent on the spatial separation of large carnivores and humans by modifying livestock husban-dry practices and enforcing zoning.
Article
Full-text available
We calculated extraction and production rates of bushmeat species in two main tropical, moist-forest regions, the Amazon and Congo basins. Extraction was estimated from the average number of animals consumed per person per year from anthropological studies that reported animal kills brought into settlements in the regions. W e calculated extraction rates (kg/km(2)/year) for 57 and 31 mammalian taxa In the Congo and Amazon, respectively. We then examined the sustainability of these extraction rates by basin and by taxa, using extraction-to-production (E:P) mass-balance equations. Production (tonnes/year) was calculated as the product of r(max)(the intrinsic rate of natural increase), mammal biomass, and total area of forest in each region. Species exploitation rates at specific body masses were significantly greater in the Congo than in the Amazon. The E:P ratio for the Congo was 2.4, 30 times the Amazon's ratio of 0.081. Thus, Congo Basin mammals must annually produce approximately 93% of their body mass to balance current extraction rates, whereas Amazonian mammals must produce only 4% of their body mass. We calculated sustainability levels derived from Robinson and Redford's harvest model for each taxa. On a basin-wide level, 60% and none of the mammal taxa in the Congo and Amazon basins, respectively were exploited unsustainably. To evaluate the effect of error on the estimates of E:P, we conducted a sensitivity analysis, which suggests that the mass-balance was most sensitive to error in standing stock but that our results are robust. We estimated that over 5 million tons of wild mammal meat feed millions in Neotropical (0.15 million) and Afrotropical (4.9 million),forests annually. Our Congo basin estimates are four times bigger than those calculated for the region by other workers, and we conclude that the current situation of bushmeat extraction in African rainforests is More precarious than previously thought.
Article
Crocodile farming is an important and lucrative activity in Zimbabwe which provides meat for human consumption and skins for the luxury leather industry. Because it gives an economic value to this otherwise unfriendly animal, farming crocodiles has a positive side effect on the conservation of this species in the wild. This paper gives an overview of the crocodile industry in Zimbabwe.
Article
Uncertainty gives rise to two decision errors in implementing the U.S. Endangered Species Act: listing species that are not in danger of extinction and delisting species that are in danger of extinction. I evaluated four methods (minimum standard, precautionary principle, minimax regret criterion, adaptive management) for deciding whether to list or delist a species when there is uncertainty about how those decisions are likely to influence survival of the species. A safe minimum standard criterion preserves some minimum amount or safe standard (population) of a species unless maintaining that amount generates unacceptable social cost. The precautionary principle favors not delisting a species when there is insufficient evidence on the efficacy of state management plans for protecting them. A minimax regret criterion selects the delisting decision that minimizes the maximum loss likely to occur under alternative ecosystem states. When the cost of making a correct decision is less than the cost of making an incorrect decision, the minimax regret criteria indicates that delisting is the optimal decision. Active adaptive management employs statistically valid experiments to test hypotheses about the likely impacts of delisting decisions. Safe minimum standard and minimax regret criterion are not compatible with the U.S. Endangered Species Act. The precautionary principle comes closest to describing how federal agencies make delisting decisions. Active adaptive management is scientifically superior to the other methods but is costly and time consuming and may not be compatible with the U.S. National Environmental Policy Act.