Biology Reference
In-Depth Information
Table 1.3. Major traders of M. fascicularis with total number of
individuals and declared sources (2004-2008).
Source
Exporter
C
W
F
I
U
R
China
11,585.1
x
1,236
662
20
x
Indonesia
4,350
2,080
10,100
350
x
250
Mauritius
696
10,485.1
58,178.5
386
x
x
Philippines
107,398.1
1,760
x
153
x
x
Vietnam
33,744
32,774
1,670
x
x
x
C-captive bred, W-wild caught, F-f1 or subsequent generations, I-confiscated/seized,
U-unknown, R-ranched.
Table 1.4. Numbers of M. fascicularis
imported into the US from 2004-2008.
Year
Individuals
2004
16,844
2005
24,629
2006
25,878
2007
24,112
2008
26,509
comprising more than 45 percent of the total international trade between
2004 and 2008) ( Table 1.4 ) . In addition the US imported large quantities
of derivatives, bones and specimens of long-tailed macaques ( Table 1.5 ).
In a report by Fooden ( 2006 ) it is suggested that there were approximately
three million long-tailed macaques in Southeast Asia. If these population
estimates are remotely accurate, the trade levels seen from 2004-2008 are
extremely unsustainable.
Long-tailed macaques are considered common in Southeast Asia, but
local declines have recently been reported by conservation organizations
and macaque hunters alike. For example, in the Cambodian province
Ratanakiri farmers reported that no macaques were harvested due to drastic
population declines (Eudey, 2008 ). Levels of capture and export are consid-
ered to be unsustainable and acquisition is often carried out in violation of
national laws and CITES. As such, investigation and population censusing
is urgently needed to determine the actual numbers of macaques being har-
vested from the wild and the quantity being laundered into the international
 
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