This shapefile is the approximate location of mangroves within the boundary of Ten Thousand Islands NWR in 2014.

This shapefile is the approximate location of mangroves within the boundary of Ten Thousand Islands NWR in 2005.

This shapefile is the approximate location of mangroves within the boundary of Ten Thousand Islands NWR in 2005.

This shapefile compares the approximate location of mangroves within the boundary of Ten Thousand Islands NWR in 2005 to their location in 2014.

This shapefile compares the approximate location of mangroves within the boundary of Ten Thousand Islands NWR in 2005 to their location in 2014.

The mangroves of Torres Strait were mapped with classified Landsat TM satellite imagery. There was 15,663 ha of mangrove mapped on the islands and reefs of central Torres Strait. The largest area of mangrove, 4,744, 3,209, 1,484 and 1,142 ha were mapped on the islands of Boigi, Saibai, Moa and Turnagain Island respectively, which accounted for over two-thirds, 68%, of the mangroves of the central Torres Strait study area. Approximately one-third (49) of the 174 islands of central Torres Strait had mangroves. There was a significant correlation between the distribution of mangroves and the underlying geology; most of the mangroves in Torres Strait were located on coastal alluvium landform features. The mangrove basemaps have been entered into the Torres Strait Geographic Information System for future research, monitoring and conservation planning. Refer to the report: Long BG and McLeod I. (1997) Distribution of Mangroves in Torres Strait. CSIRO Marine Research. Cleveland, Australia. 17 pp.

In coastal wetlands, one of the most striking examples of climate change is the poleward range expansion of mangrove forests in response to warming winters. In North America, the Cedar Key region has often been considered the range limit for mangroves along the western coast of Florida (USA). However, within the past several decades, robust stands of Avicennia germinans and Rhizophora mangle have been observed in the Apalachicola Bay region, which is 200 km northwest of Cedar Key. This dataset characterizes the distribution and structure of the mangroves in the Apalachicola Bay area of Florida identified via extensive ground surveys and photointerpretation of aerial imagery from 2018 to 2019.

Mangrove inventory data from J.N. Ding Darling National Wildlife Refuge, Sanibel Island, Florida, USA collected in 2016 and 2017. Plot data includes X and Y downed dead wood count, mangrove species information and site descriptions. Tree data includes the three species found on the refuge: Avicennia germinans (Black mangroves), Laguncularia racemosa (White mangroves) and Rhizophora mangle (Red mangroves). They were inventoried for diameter at breast height (DBH), height, and dead status.

Mangrove inventory data from J.N. Ding Darling National Wildlife Refuge, Sanibel Island, Florida, USA collected in 2016 and 2017. Plot data includes X and Y downed dead wood count, mangrove species information and site descriptions. Tree data includes the three species found on the refuge: Avicennia germinans (Black mangroves), Laguncularia racemosa (White mangroves) and Rhizophora mangle (Red mangroves). They were inventoried for diameter at breast height (DBH), height, and dead status.