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Ambergris Caye Belize Resort Development - Department of ...

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Most <strong>of</strong> the grasses and weeds, and vines, and herbaceous bracts and shrubs were confined to the<br />

Beach Berm [See PL 2.17], and the seaward 1/4 th <strong>of</strong> the Littoral Forest Seaward Consolidated<br />

Berm. The succeeding berms or ridges were heavily forested. Except for a small area at the midlatitude<br />

<strong>of</strong> the property immediately landward <strong>of</strong> the beach berm, as well as the survey trails [See<br />

PLs’ 2.18 and 2.27 respectively], there were no signs <strong>of</strong> previous land-clearing [Pers. comm.., G.<br />

Myvett]. The forest was surmised to be <strong>of</strong> primary growth form [See PL’s 2.19 & 2.20].<br />

The Mangrove Scrub component <strong>of</strong> the forest included two (2) components, viz: an area<br />

characterized by littoral forest species interspersed by mangroves species, and a zone dominated<br />

90-100% by mangroves. The mixed mangrove shrub component was located mainly in the area<br />

titled ‘Littoral Forest Lagunal Berm’. The mangrove species found in this area were the Black<br />

Mangrove (Avicennia germinans) and the White Mangrove (Laguncularia racemosa) [See Table<br />

2.2A]. The more frequently encountered species was the Black Mangrove (Avicennia<br />

germinans).<br />

The monospecific mangrove zone has been defined as the Laguna de Cantena Low-lands<br />

[LdCLL] in Table 2.2A. Although all three (3) species <strong>of</strong> mangroves present in <strong>Belize</strong> were<br />

found in the area, the most dominant species was the Red Mangrove (Rhizophora mangle) [See<br />

PL’s 2.7 & 2.8], followed by the Black Mangrove (Avicennia germinans).<br />

Apart from the land-based trees, shrubs and grasses, the site was also richly invested with subtidal<br />

or sea-based plant life. The dominant species was the Turtle Grass (Thalassia testudinium)<br />

which formed extensive meadows or ‘bed’ [See PL’s 2.2 & 2.3], which proceeded from the<br />

nearshore areas, to the medial shallows about 400-500 m from the shoreline [See D Fig. 2.1].<br />

Apart from the Turtle Grass (Thalassia testudinium) [See PL 2.12], the two (2) other seagrass<br />

species found in the area included the Manatee Grass (Syringodium filiforme) [See PL 2.13] and<br />

Halodule (Halodule beaudettel) [See Table 2.2A].<br />

The macro-algae figured prominently in regards to the sub-tidal species found in the area. The<br />

Shag Carpet Algae (Dasycladus vermicularis) was found in great pr<strong>of</strong>usion in the Laguna de<br />

Cantena. The Disc Tree Halimeda (Halimeda copiosa) [See PL 2.11] was found in the midreaches<br />

<strong>of</strong> the barrier lagoon in the seas <strong>of</strong>f the front or eastern side <strong>of</strong> the property. The floating<br />

seaweed or sargassum (Sargassum polycerathum) was also found <strong>of</strong>f the front <strong>of</strong> the property in<br />

the barrier lagoon, as well as on the beach [See PL’s 2.6, 2.17 & 2.22]. Other macro-algal<br />

species <strong>of</strong> note found in the area include: the Dichotomously Branched Algae (Dictyota spp.),<br />

Valonia (Valonia ventricosa), the Feather Algae (Caulerpa prolifera) and the Cactus Branchlets<br />

(Caulerpa cupressoides) [See Table 2.2B].<br />

Much <strong>of</strong> the macor-algae were found in the primary reef zone, including the pavement area and<br />

backreef zone [See F, Fig. 2.1].<br />

Grimshaw and Paz [2004] cited the existence <strong>of</strong> 37 species seagrasses and macro-algae in the<br />

greater Bacalar Chico National Park and Marine Reserve [BCNP/MR]. The Tunich Nah Survey<br />

Team documented 19 species, <strong>of</strong> which 3 were not previously cited by Grimsha and Paz [2004].<br />

2-11

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