Search all sites near me now
Search your favourite swimming spots

Moutere Inlet

Moutere Inlet is a moderate-sized (764 ha), well-flushed, shallow, intertidally-dominated, estuary located near Motueka. The estuary consists of one main basin with a tidal opening at each end of Jacket Island, and several tidal embayments separated from the main estuary basin by roads/causeways. The estuary is shallow (mean depth ~2 m) and almost completely drains at low tide. Intertidal habitats are characterised by wide sandflats and mudflats - many perched high in the tidal range - and well flushed, steeply incised drainage channels, particularly near the entrances. These channels contain a variety of cobble, gravel, sand and biogenic (oyster, mussel, tubeworm) habitats, and support localised macroalgal growths. Although significantly reduced from their historical range, small patches of seagrass remain in the lower tidal reaches of the estuary, and salt marsh is present along the upper tidal margins.

Overall, despite extensive historical habitat modification, much reduced habitat diversity, and large areas of mud, the estuary retains significant ecological value, although it is currently expressing moderate symptoms of eutrophication and muddiness. Without reductions in current nutrient and sediment loads the estuary is likely to remain in a similar state to its present condition, and salt marsh losses are likely to increase in response to sea level rise.

 

The surrounding catchment is highly modified and dominated by pasture (53%), horticulture (15%), exotic forestry (12%) and built up areas (settlements) (2%), including the commercial port and marina located at Port Motueka. Native forest cover is low (2%).

The extent of mud-dominated substrates is the most significant current issue present in Moutere Inlet, in part as most of the sediment entering the estuary (96%) is predicted to be trapped and retained within it. Most mud is located in the central basin and to the southeast and, to a lesser degree, in the sheltered embayments on the western side of the estuary and north of Wharf Road – ideal settling areas for fine sediment. The spatial extent of mud is high in both a regional and national context although there appears to have been a recent reduction in mud extent (22 ha, 9% since 2013) and an obvious decrease in sediment volume in certain parts of the estuary, most particularly the central basin. Despite the high extent of mud-dominated substrates, analysis of sediment plate monitoring (collected by TDC) showed that net rates of measured sediment accumulation (average 0.2 mm/year over the past decade) were well below the 2 mm/year guideline value proposed for New Zealand estuaries, and comparable to the 0.9 mm/year calculated from NIWA’s national estuary sediment load estimator. However, in the central basin where deposition appears most pronounced, sediment cores analysed using forensic methods (lead and caesium radioisotopes) estimated mean sediment accrual is high at ~10 mm/year from 1988 to 2018.

In Moutere Inlet, the extent of High Enrichment Conditions (HEC) has expanded significantly over time, from an estimated ~1 ha (0.1% of estuary area) in 1947, to 37 ha (5%) in 2004 and to 60 ha (8%) in 2013, before decreasing to 31 ha (4.1%) in 2019. The large decrease in both macroalgal cover (48 ha) and HEC extent (29 ha) since 2013 is very positive, although the specific reasons for the changes are unclear.

Small seagrass (Zostera) beds were present (3.1 ha) primarily in the central basin near the Kina entrance, with an apparent increase of 1.1 ha since 2013 and 2.2 ha since the first reliable baseline in 2004.

Salt marsh vegetation is a prominent feature (83 ha, 10.8% of the estuary), with no appreciable change from 2004 or 2013. Salt marsh was dominated by rushland (55%) and herbfield (40%) and was most common within estuary embayments and on the northwest and southern tidal flats. Compared to historical extent, there has been an estimated reduction of ~45% since 1947, most losses due to reclamation and drainage.

The 200 m wide terrestrial margin bordering the estuary was also highly modified and dominated by residential/industrial development (21.7%), pasture (28.6%) and horticulture (19.5%). Only 16% was densely vegetated, half of which was exotic.

Estuary summary

What makes my estuary unique?

Explore the characteristics of this estuary

Overview

Estuary characteristics

  • Total area
    764 hectares

What's happening upstream?

See results from monitored river quality sites influencing this estuary

River quality

What's happening upstream?

The physical characteristics and health of estuaries are influenced by the rivers and streams flowing into them. For instance, when it rains the mud and contaminants generated on land can be washed into rivers and eventually flow into the estuary. The health of our rivers and streams can therefore be very important for Estuary Health, and understanding the upstream pressures can help with interpreting estuary monitoring data. Monitoring is undertaken for a range of river health indicators (e.g., water quality and ecology) in many catchments across the region. Where there are monitored river catchments that influence this estuary, these are shown below. You can click through to view monitoring results from these River Quality sites to see current state and how health has changed over time.

What surrounds my estuary?

See land cover information from monitored catchments that surround this estuary

Land cover

What surrounds my estuary?

The physical characteristics and health of estuaries are influenced by local geography and the way we use our land. This is because estuaries are the receiving environments for many of our land use activities. Land cover information can be used as an indicator of land use, therefore knowing the surrounding land cover can help us understand which pressures might be affecting Estuary Health. For example, the sandflats of estuaries surrounded by rural areas will typically contain contaminants related to rural activities (e.g., cadmium from crop fertilisers and copper from fungicides), whereas those surrounded by urban areas are more likely to contain contaminants associated with cities (e.g., zinc and lead from roads and building materials). Where there is land cover information available for nearby catchments, these are listed below. These figures show the types of vegetation and built or natural features that surround the estuary margins and the rivers that flow into this estuary. You can click through to the Land Cover topic to see these land cover classes broken down into further detail, and view changes over time.

Tasman Valley Stream
Moutere River

What do the Broad Land Cover Classes mean?

Land cover information on LAWA is grouped into land cover classes at two levels of detail – broad and medium. For this overview we are showing the six broad-level classes for the catchment.

  • Forest

    Inclusive of; indigenous and exotic forest.

  • Scrub / shrubland

    Inclusive of; indigenous and exotic scrub / shrubland.

  • Grassland / other herbaceous vegetation

    Inclusive of; tussock and exotic grassland and other herbaceous vegetation.

  • Cropland

    Inclusive of; cropping / horticulture.

  • Urban / bare / lightly-vegetated surfaces

    Inclusive of; natural bare/lightly-vegetated and artificial bare surfaces, and urban area

  • Water bodies
Monitored sites 2

Select a monitored site from the list below

...retrieving sites.

No sites found.