The area of the Hinchinbrook Channel estuary reporting zone can be defined by the pre-cleared extent of mangrove and saltmarsh remnant vegetation which is characterised by species that require periodic inundation of sea water.
This area includes the length of the channel (approximately 45 km) and extends due south along the coastline from the southern mouth of the channel for approximately 20 km, the area also extends west on the mainland for approximately 10 km and east on Hinchinbrook Island for approximately 6 km.
The area has numerous coastal tributaries that drain into the channel from the mainland and from Hinchinbrook Island. The assessment area of riparian extent extends upstream of the Herbert River further than the mangrove and salt marsh communities to the upper tidal limit and includes vegetation types that are more typical of freshwater environments.
On Hinchinbrook Island the estuary area is all within National Park. The estuary area on the mainland is predominantly conservation use (Girrigun National Park) whilst land uses in the area include forestry and pond aquaculture with some cropping and residential development in the southern reaches on the mainland around the Herbert River.
The towns of Cardwell, located at the north of the channel, and Ingham, located to the south of the channel are both on the mainland. The Hinchinbrook Channel is listed in the Directory of (Nationally) Important Wetlands.
The Hinchinbrook Channel grade has declined from ‘very good’ in 2016-17 to ‘ good’ and the score has decreased slightly from 81 in 2016-17 to 77 in 2017-18. The change was due to a lower water quality score.
The diagram below shows the detailed results for each indicator by year. Click on the timeslider to see data from previous years.
The Hinchinbrook Channel water quality remained ‘very good’ whilst the score decreased to 82 in 2017-18 from 90 in the previous year. Turbidity scored 61 and dissolved oxygen scored 73, and both were graded ‘good’. All other water quality indicators were graded ‘very good’ and scored 90. Unlike the other estuary zones, Hinchinbrook Channel has connectivity with coastal waters at either end of the channel and this feature may enhance water quality.
Water quality grades are based on aquatic ecosystem guidelines for protection of estuarine waters, and are not based on load reduction targets for the marine environment. The results are derived from three monitoring sites in the channel.
Habitat and hydrology
The habitat and hydrology index is comprised of three longer-term indicator categories that are updated every four years: mangrove and saltmarsh extent, riparian extent (both due for updates in 2018-19) and fish barriers (update due for 2019-20). The habitat and hydrology score has remained at 72 ‘good’.
The mangrove and saltmarsh extent scored 84 (‘very good’) with 4.1% loss from pre-clear to 2013. These results reflect a low level of development within the estuary area.
Riparian extent is assessed to the upper tidal limit of the river which extends upstream of the estuary area that is characterised by mangroves and saltmarsh. Riparian assessment therefore includes areas that have been cleared for agriculture and other developments. The riparian extent scored 51 (‘moderate’) with 21.9% loss from pre-clear to 2013.
Estuary fish barriers for the Hinchinbrook Channel are scored 80 (‘good’) and are graded 'very good’ for barrier density, ‘poor’ for percentage of stream length to the first barrier, and there is an absence of low passability barriers (graded ‘very good’)
The flow indicator could not be assessed for the Hinchinbrook Channel due to the lack of pre-development modelled flow and flow assessment sites, which are required for the analysis.
Although seagrass habitat occurs in Hinchinbrook Channel there is currently no seagrass monitoring in the estuary and a seagrass grade and score is not available.
The fish index is currently under development and will be available in future report cards.