Abstract

Annual biomass and productivity of Thalassia testudinum were determined during a year at a seagrass bed located in the Parque Nacional Morrocoy, Venezuela. Leaf, rhizome and root biomass were determined monthly, together with short-shoot density, from February 1992 to January 1993, from nine replicated core samples. Productivity was measured using the methodology by Zieman (1974) with minor modifications, and leaf turnover rate was calculated. Leaf biomass values ranged between 101.73 dry g m(-2) in February and 178.11 dry g m(-2) in August. Productivity ranged from 1.69 dry g m(-2) d(-1) in April and October to 3.30 dry g m(-2) d(-1) in July, showing two annual peaks: one in July and one in March. The leaf turnover rate showed the highest value in June (2.41% d(-1)) and the lowest in May (1.23% d(-1)). Sampling time differences in leaf biomass, productivity and turnover rate were statistically significant. Short-shoot density values varied between 811.10 shoots m(-2) in April and 1226.08 shoots m(-2) in December, but the differences were not significant along the year. These results indicated seasonal trends for leaf biomass, productivity and turnover rate of T. testudinum in the Southern Caribbean (latitude 10 degrees N).

Highlights

  • Biomass and density in natural populations of seagrasses have been determined for temperate and sub-tropical areas: e.g. Thalassia testudinum (Zieman 1975); Zostera marina (Jacobs 1979, Aioi 1980); T. testudinum and Syringodium filiforme (Barber and Behrens 1985); Amphibolis antarctica and Posidonia australis (Walker and McComb 1988); Posidonia oceanica (Buia et al 1992) and Zostera noltii (Vermaat and Verhagen 1996)

  • The highest leaf productivity for T. testudinum at Las Luisas was found in July, when the salinity was 38.3

  • Salinity values found at Las Luisas in the high productivity months were greater than the ones reported by Zieman (1975) as being optimal for T. testudinum growth in subtropical areas

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Summary

Introduction

Biomass and density in natural populations of seagrasses have been determined for temperate and sub-tropical areas: e.g. Thalassia testudinum (Zieman 1975); Zostera marina (Jacobs 1979, Aioi 1980); T. testudinum and Syringodium filiforme (Barber and Behrens 1985); Amphibolis antarctica and Posidonia australis (Walker and McComb 1988); Posidonia oceanica (Buia et al 1992) and Zostera noltii (Vermaat and Verhagen 1996). Production and distribution have been determined for T. testudinum (Banks ex König), species that dominates the highly productive seagrass meadows of the Caribbean Sea

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