International Journal of Marine Science, 2017, Vol.7, No.33, 316-343
320
Continued Table 2
Aggregations
Genetic diversities
h
±SD
π
±SD
N
RL90
0.605 ±0,111
0.0123 ±0.0070
21
DO90
1
0.669 ±0.034
0.0102 ±0.0057
90
BA90
1
0.740 ±0.024
0.0093 ±0.0053
78
USVI90
1
0.750 ±0.036
0.0108 ±0.0060
68
MI90
0.724 ±0.033
[0.833 ±0.081]
0.0596 ±0.0293
[0.0725 ±0.0382]
93
13
MIRes00
0.676 ±0.050
0.0521 ±0.0260
51
MI♂00
[0.677 ±0.060]
[0.0346 ±0.0175]
54
CI00
0.666 ±0.036
0.0559 ±0.0276
89
FKW00
0.584 ±0.052
0.0424 ±0.0213
47
FPB00
0.490 ±0.056
0.0268 ±0.0137
91
ToL00
0.7721 ±0.057
0.0620 ±0.0321
17
ToW00
0.6003 ±0.065
0.0479 ±0.0240
49
TnC00
0.733 ±0.033
0.0541 ±0.0272
36
Note: JR: Jardines del Rey, Cuba; DL: Doce Leguas, Cuba; IJ: Isla de la Juventud, Cuba; RL: Rio Lagartos, Yucatan, Mexico; DO:
south of Dominican Republic; BA: Bahamas; USVI: Buck Island, United States Virgin Islands; MI: Mona Island, Puerto Rico; CI:
Bloody Bay and west of Grand Cayman, Cayman Islands; FKW: Key West National Wildlife Refuge, Florida, USA; FPB: Palm
Beach County, Florida, USA; ToL: Tobago leeward; ToW: Tobago windward; TnC: Turks and Caicos; Ad: adult individuals, N:
number of individuals with haplotypes, NA: non-adult individuals, Res: platform resident juveniles from Velez-Zuazo et al. (2008),
SD: standard deviation. 00: decade of 2000, 04-06: total samples of the present study, 90: decade of 1990 from Díaz-Fernández
(1999);
1
values extracted from Bowen et al. (2007); ♂: males; ♀: females
1.2 Mixed stock analysis
1.2.1 Non-adult aggregations
Contributions to the non-adult fishing aggregation of JR were heterogeneous in each MSA conducted (Figure 1).
The Mexican (ME) and Tobago rookeries were the major contributors during the 1990s using the 384 bp length,
while in 2004 and 2005 the ME rookery was the main contributor. For the MSAgr, ME maintained contributory
supremacy followed by Mona Island (MI) and Barbados leeward coast (BaL). In 2004, using the 740 bp length,
the major contributor to JR was the Barbados windward coast, followed by the MI and ME rookeries. In 2005 the
ME rookery contributed highly to JR but in the MSAgr the MI rookery was the main contributor.
Many aggregations had contributions in the MSAoa congruent with those of the MSAgr. For Rio Lagartos the ME
source was the primary contributor, while for the Tobago windward aggregation the BaL rookery was the major
contributor with either 384 or 740 bp (Supplementary Material 1A). In Florida aggregations, the ME source was
the highest contributor for any sequence length (Supplementary Material 1B).
Other aggregations presented different results given the MSA approach or the sequence length. The Turks and
Caicos foraging aggregation had higher contributions from ME followed by the Tobago rookery in the MSAoa,
but the second contributor was the BaL rookery in the MSAgr (Supplementary Material 1C). In Cayman Islands
the Tobago rookery was the major contributor using the 384 bp length, while the BaL rookery was the major
contributor when using the 740 bp length (Supplementary Material 1C). The Bahamas aggregation received a
higher contribution from the ME rookery in the MSAoa but was a secondary contributor to the BaL rookery in the
MSAgr (Supplementary Material 1D). In the feeding aggregation of the Dominican Republic the Tobago rookery
presented the greatest contribution in the MSAoa but the BaL rookery was the major contributor in the MSAgr
(Supplementary Material 1D). Similarly, the Doce Leguas fishing aggregation had a majority contribution from
the homonymous rookery while for the MSAgr it was BaL (Supplementary Material 1E). In addition, the major
contributor to the Tobago leeward coast aggregation was the Nicaragua rookery in both sequence lengths of the
MSAoa, but in the MSAgr this rookery was substituted by the BaL rookery (Supplementary Material 1E). The
remaining non-adult aggregations of the WC had not primary contributors but even contributions among different
