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The Cairns region is on the wet tropical coast of northeastern Queensland. It includes several major catchments and river systems. Agricultural (e.g. grazing, forestry and cropping) and urban developments are the primary land uses in coastal catchments and contribute high loads of nutrients and sediments to nearshore coastal waters.

Thirteen seagrass species have been recognised for this region. The most extensive areas of seagrass occur around Low Isles, Green Island and Cairns Harbour. Intertidal seagrass meadows in the region are situated along nearshore sand and mud banks and mostly consist of Halodule uninervis and Halophila dominated meadows. In Cairns Harbour however, meadows are dominated by Zostera capricorni. Shallow subtidal coastal meadows consist of Halodule uninervis and Halophila communities mostly found along the sheltered coasts and harbours. Cymodocea spp., Thalassia hemprichii, Syringodium isoetifolium and a suite of Halophila species dominate intertidal reef platform habitats of this region. Yule Point Ellie Point Green Island

Seagrass meadows throughout the region are characterised by low nutrient concentrations and are primarily nitrogen limited. Nitrogen inputs to marine waters can therefore directly promote seagrass growth. The indirect consequences of high sediment and nutrient runoff can on the other hand detrimentally influence seagrass distribution and seasonality in the region. From December to March (wet season) low seagrass abundance often coincides with high rainfall and high loads of sediments and nutrients to nearshore marine waters. Sediments and nutrients decrease light availability for seagrass by reducing light penetration in the water column and promoting the growth of algae that can shade seagrass blades. Warm water temperatures during summer also promote growth of algae and can lower productivity of seagrass meadows. Coupled with physical disturbance from storm activity seagrass growth and abundance may therefore be severely depleted over the wet season. Seagrass meadows are generally most abundant in October-November following the dry season that has more favorable light and temperature conditions.

Monitoring of intertidal seagrass meadows occurs in three seagrass habitat types in the region: coastal, reef and estuarine.

Below is a conceptual diagram of coastal seagrass habitat in the Cairns region – major controls are pulsed terrigenous runoff from seasonal rains, salinity and temperature extremes, and sediment disturbance.

Below is a conceptual diagram of reef seagrass habitat in the Cairns region. Shallow unstable sediment, fluctuating temperature, and variable salinity in intertidal regions characterize these habitats. Physical disturbance from waves and swell and associated sediment movement primarily control seagrass growing in these habitats. Reef seagrass habitats in the region are often adjacent to areas of high tourism use and boating activity with propeller and anchor scarring impacts. Globally, nutrient concentrations are generally low in reef habitats due to the coarse nature of the sediments coral sand. In these types of carbonate sediments the primary limiting nutrient for seagrass growth is generally phosphate. This is due to the sequestering of phosphate by calcium carbonate sediments. In this region seagrass meadows inhabiting the near shore inner reefs and fringing reefs of coastal islands inhabit a mixture of terrigenous and carbonate sediments, such as Green Island. Seagrasses at this location have been shown to be nitrogen limited (Udy et al. 1999).

Below is a conceptual diagram of estuarine seagrass habitat in the Cairns region.  These habitats are also closely associated with mangrove forests, characterised by fine sediments and prone to high sedimentation and anoxic conditions. The physical and biological connectivity between these habitats is of high importance to support the detrital food chains and the productive faunal communities. The dominant influence of estuary habitats is terrigenous runoff from seasonal rains. Increased river/creek flow results in higher sediment loads which combine with reduced light to create potential light limitation for seagrass (McKenzie 1994). Estuary habitats also have higher loadings of micro and macro-algal epiphytes than those in other seagrass habitats. Salinity fluctuations and scouring make estuary and inlet habitats a seasonally extreme environment for seagrass growth. Estuary habitats also include the ports and shipping activities (including dredging).

 

Within seagrass canopy water temperatures

Mean within seagrass canopy water temperatures were generally within the 22 – 31°C range, with highest mean temperatures in the late Dry and Monsoon seasons. Extreme within seagrass canopy water temperature (41.5°C) was recorded at YP1 on the 5th February 2008. Over the last 12 months maximum mean temperatures were recorded in February (30.2°C at Yule Point) and October 2007 during the low spring tides. Temperatures at the coastal and reef-platform locations generally follow a similar pattern.

 

 

Reef Rescue Marine Monitoring Program (2007-2008)

Monitoring occurs at both coastal and reef seagrass habitats. Yule Point and Green Island meadows appear to have changed relatively little since monitoring began in 2000, however 2008 abundances were some of the highest recorded. Seagrass cover is seasonal with higher abundances in the early months of the year. Overall distribution is stable at Green Island, but appears to be increasing at Yule Point. Seed reserves and reproductive effort were considerably higher at Yule Point compared to other locations. Epiphyte cover appears to be increasing, however macro-algal cover has remained low.


Within this region there is a distinction in nutrient state between low light, nutrient rich (coastal habitats, Yule Point) and moderate light, nutrient poor (reef habitats, Green Island) in relation to plant tissue C:N and C:P ratios. Within habitats, a decline across years in C:N and C:P ratios coupled with an increase in plant tissue N:P was noted. This is suggestive of a moderate decline in water quality, despite declines recorded in levels of adsorbed sediment nutrients for this region. The tissue nutrient content of seagrass plants was indicative of being replete (satiated or full).


No herbicides were detectable in the sediments at these locations in early 2008, although diuron was detected at Green Island in 2006. Within canopy temperatures over the 2007/2008 sampling period were similar to the long term average. Extreme temperatures (>40°C) were recorded at Yule Point in February 2008.

Download Understanding diagrams and Icons pdf (870 kb)


 

Ellie Point

Monitoring: Suspended

Principal watchers: Tom Collis & Far North TAFE
Occasional and past watchers: Seagrass-Watch HQ
Location: On the north of Cairns Harbour, adjacent to the mouth of the Barron River
Site code: EP

EP1 position: S16.87617 E145.77796
Best tides: <0.8m Cairns (Port 59060)

Issues: Land runoff & boat traffic
Comments: Popular recreational fishing area and turtle feeding grounds

Status (Feb05):

  • Site appears to be showing a fairly typical seasonal pattern of seagrass abundance (higher in late spring-summer than winter).
  • Site is dominated by Zostera capricorni with Halodule uninervis and Halophila ovalis;
  • Site appears to be recovering in distribution and cover since the substantial loss of seagrass area and abundance reported in December 2001 (Campbell et al 2002).
  • Results of monitoring indicate that seagrasses at Ellie Point appear relatively healthy and that there had been an overall increase from values recorded in February 2002.

 

 

 

Green Island

Monitoring: Ongoing

Principal watchers: Seagrass-Watch HQ
Location: Reef-platform on Great Barrier Reef mid shelf reef approximately 27 km north east of Cairns
Site code: GI1, GI2

GI1 position: S16.76163 E145.97290 (heading: 180 degrees)

GI2 position: S16.76140 E145.97614 (heading: 180 degrees)
Best tides: <0.8m Green Island (Port 59070)

Issues: Elevated nutrients and land runoff
Comments: Green Island is a vegetated sand cay approximately 12 ha in area with a maximum elevation of 4.5m. There are extensive seagrass meadows in the waters surrounding Green Island with at least 9 species (Halodule, Cymodocea, Halophila, Thalassia, Syringodium) identified. Abundance of seagrasses highest in the sub-tidal area in the north western lagoon. Monitoring of reef habitats occurs at Green Island, on the large intertidal reef-platform south west of the cay. The meadow is dominated by Cymodocea rotundata and Thalassia hemprichii with some Halodule uninervis and Halophila ovalis.

The distribution of seagrass around Green Island has changed substantially in the last 50 years, possibly from poor water quality, a consequence of increases in tourist visitation and increased nutrients emanating from the adjacent sewage outfall. The most dramatic change however, has been the seagrass species composition, with the species Syringodium isoetifolium now dominating most of the lagoon meadows. How these changes in the seagrass composition and abundance on Green Island will effect the sea turtle, dugong and fisheries is unknown. Further reading -Udy et al (1999). The location is a Green (no fishing) zone of GBRMP, and a dugong and turtle feeding ground.

Status (Dec08):

  • Seagrass abundance appears to follow typical season pattern (higher in late spring-summer than winter).
  • Macroalgae generally increases in spring/early summer, although these are within levels of natural change.

  • Sites are dominated by Cymodocea rotundata, Thalassia hemprichii, Halodule uninervis and Halophila ovalis.
  • Seagrass species composition appears to fluctuate throughout the year, however no long-term trend is apparent.

Seagrass-Watch monitoring on Green Island is proudly supported by Great Adventures Cruises and Green Island Resort.

 

 

Yule Point

Monitoring: Ongoing

Principal watchers: Seagrass-Watch HQ, Tom Collis & Far North TAFE
Location: Coastal intertidal sand banks, protected by an extensive fringing reef
Site codes: YP1 YP2

YP1 position: S16.56932 E145.51240 (heading: 50 degrees)
YP2 position: S16.56387 E145.50925 (heading: 50 degrees)
Best tides: <0.8m Port Douglas (Port 59040)
Issues: Storm water & land runoff
Comments: The seagrass meadows at Yule Point are located on naturally dynamic intertidal sand banks. These meadows are dominated by Halodule uninervis with some Halophila ovalis. A small patch of Zostera capricorni has appeared closer inshore in recent years, however it is outside the monitoring sites. The meadows at Yule Point are often exposed to regular periods of disturbance from wave action and consequent sediment movement. The sediments are relatively unstable restricting seagrass growth and distribution. The meadows are also popular dugong feeding grounds, and grazing trails are abundant.

 

Status (Dec08):

  • Seagrass abundance appears to follow typical season pattern (higher in late spring-summer than winter). Sites are dominated by Halodule uninervis and Halophila ovalis.
  • Seagrass meadows at Yule Point are in a good condition, and results of monitoring indicate that seagrasses appear relatively healthy
  • Seagrass canopy height also showing clear season pattern - correlated with abundance.
  • Macroalgae generally increase in spring/early summer, but not of concern.
  • Epiphyte cover has recorded peaks in abundance at times, which may correlate with nutrient inputs from land runoff (ie. high epiphytes after heavy rains). Further research required.
  • Increase in finer sediments (e.g., fine sand) over last 6-9 months, but no obvious changes in seagrass species composition over monitoring period ·
  • Sites appears to have changed relatively little since 1967, when den Hartog (1970) photographed the area and described the species present and sediment condition.

  • Sites are dominated by Halodule uninervis and Halophila ovalis.
  • Seagrass species composition appears to fluctuate throughout the year, however no long-term trend is apparent.

  • A persistent and abundant seed bank was present at Yule Point. Seed abundance is significantly higher at YP1.
  • The proportion of germinated seeds was also high at this location, with significantly higher abundance at YP1. This may be a consequence of the high level of sediment movement and disturbance to the sites.

 

 
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Correct citation: McKenzie, LJ., Yoshida, RL., Mellors, JE & Coles, RG. (2006 - 2010). Seagrass-Watch. www.seagrasswatch.org. 228pp. Disclaimer: The views expressed on this site are those of the authors and not necessarily those of the Queensland Government. Website designed by McKenzie, LJ., Yoshida, RL.
 
Seagrass-Watch HQ
Address: Northern Fisheries Centre
PO Box 5396
Cairns Qld 4870
Australia
Phone: [+61][07] 40 350 100
Email: hq@seagrasswatch.org