Ga. Kendrick et al., Landscape-scale changes in seagrass distribution over time: a case study from Success Bank, Western Australia, AQUATIC BOT, 65(1-4), 1999, pp. 293-309
Seagrasses in temperate Australia persist on sand habitats in shallow coast
al environments by recruitment from seedlings and lateral spread of rhizome
s from existing meadows. These colonizing processes, combined with seagrass
loss from physical disturbance, result in a mosaic of sand and seagrass ha
bitats. Here we describe these changing seagrass landscapes on Success Bank
, Western Australia over a 20-year period, using aerial photographs.
The 4 ha landscape units (LUs), selected from areas of current Posidonia co
riacea Cambridge and Kuo and Amphibolis griffithii (Black) Den Hartog meado
ws, were analyzed for seagrass cover from aerial photographs from 1972, 198
2 and 1993. Two LUs for each species;were chosen from three regions (west,
central and east) across Success Bank. Changes in landscape features of LUs
were then summarized into total area and length of edge to area ratios of
seagrass patches and meadows; Seagrass cover in LUs increased by 20,000 to
30,000 m(-2) between 1972 and 1993. Such a large increase in seagrasses has
not been documented elsewhere in Australia:for these seagrass genera. Seag
rass expansion was observed as an increase in the number and size of seagra
ss patches (<50 m(2)).
A simple model of seagrass colonization, based only on radial extension via
rhizome growth, was constructed to test whether such large increases in se
agrass cover could be accounted for solely by rhizome: elongation. The mode
l fitted observed increases in seagrass cover in some, but not all landscap
e units. The greatest divergence was in the western region where observed c
over was higher than modeled rates. in central and eastern regions the mode
led and observed increase in seagrass cover were similar.
From aerial photographs, seagrasses have been actively colonizing Success:
Bank over the last 20 years. These observed changes can be accounted for by
published rates of horizontal rhizome elongation for some, but not all, la
ndscape units, suggesting that rhizome elongation is only part of the activ
e seagrass colonization process observed on Success Bank. Future studies sh
ould target more accurate assessment of rhizome elongation rates, and colon
ization by seedlings of P. coriacea and A. griffithii, which were observed
in great numbers. Whether the observed increase in seagrass cover is a phen
omenon unique to Success Bank and to the seagrass species studied, or more
generally applicable to other locations and seagrasses, also requires furth
er study. (C) 1999 Elsevier Science B.V. All rights reserved.