Current Freshwater State
Water quality
Current SOE monitoring – NPS-FM attribute measures
The MDC surface water quality monitoring network was updated in 2020 to better align with the requirements of the NPSFM. Where possible, this included having one river water quality site per FMU for efficiency and clarity purposes. For the Marlborough Sounds Complex FMU, this site is “Ngakuta Bay Stream at Queen Charlotte Drive” which is one of two new monitoring sites developed in 2022 as part of the monitoring programme extension. The other new site is at Oyster Bay in Port Underwood, on the eastern periphery of the FMU. Both of these sites have only one year of monitoring and therefore not enough data for trend analysis.
Currently, there are five other monitoring sites in the network: Cullen Creek, Linkwater Stream, Waitohi River, Graham River, and Kenepuru Stream.
The below table details the most recent results from the 2020 and 2023 State of the Environment Reports for seven surface water attributes currently monitored and their results in terms of NPSFM classification. This classification is in ‘bands’ from A-E, which the A-band representing healthy ecosystems, while attribute states in the D and E bands are considered ‘below the national bottom line’. Unless caused by natural sources, attributes below the national bottom line are considered unacceptable.
Marlborough Sounds NPSFM monitoring results, State of the Environment Report 2020 | ||||||||
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Monitoring site | Periphyton | Ammonia | Nitrate | E-Coli | MCI1 | APSM2 | DRP3 | Clarity |
Cullen Creek | N/A | A | A | D | C | B | C | N/A |
Linkwater Stream | N/A | A | A | D | B | B | C | N/A |
Waitohi River | C | A | A | D | B | B | B | N/A |
Graham River | B | A | A | D | C | B | B | N/A |
Kenepuru Stream | N/A | A | A | D | C | B | B | N/A |
Marlborough Sounds NPSFM monitoring results, State of the Environment Report 2023 | ||||||||
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Monitoring site | Periphyton | Ammonia | Nitrate | E-Coli | MCI* | APSM** | DRP*** | Clarity |
Cullen Creek | N/A | A | A | D | C | B | C | A |
Linkwater Stream | N/A | A | A | E | B | B | C | D |
Waitohi River | C | A | A | C | C | C | B | A |
Graham River | B | A | A | D | C | B | C | A |
Kenepuru Stream | N/A | A | A | D | B | B | B | A |
* Macroinvertebrate Community Index – NPSFM State 1
** Macroinvertebrate Average Score Per Metric – NPSFM State 2
*** Dissolved Reactive Phosphorus
The above table is summarised into the below charts, firstly by all the attributes collated together and then by individual attributes. Please note that each chart includes attribute data for all monitoring sites. The band results are summarised by year. The inner circles are the 2020 SOE report results and the outer circles are the 2023 SOE report results. The two circles can be compared to see how attribute bands may have changed over the years of the two reports.
The highest scoring attributes in this FMU are Ammonia and Nitrate, which are in the A bands for all sites and both years. The main changes in attribute bands are the E. Coli 2023 results with both improvement and decline, as well as one individual decline each from B to C band for APSM and DRP attributes. The poorest scoring attribute state in this FMU is E. Coli, particularly as the Linkwater Stream declined to an E band at the 2023 report.
E. coli concentrations in natural conditions are typically low, with occasional spikes observed during rainfall runoff events. Streams in high rainfall areas in the north of the region experience more surface runoff events, resulting in higher E. coli concentrations and consequently lower NPS-FM states. This effect is particularly noticeable for some of the Marlborough Sounds Streams, such as the Graham, which has an NPS-FM state in the D-band despite a large area of native vegetation in the catchment. Linkwater Stream is one of two streams regionally exhibiting the highest E. coli concentrations, leading to its placement in the NPS-FM state within the E-band.
Generally, there is also an increase in E. coli concentrations with higher pasture cover. However, the patterns become more evident when waterways in high-rainfall areas are separated from those in areas with comparatively little rainfall. Regionally, four of the monitored streams show significantly higher E. coli concentrations than can be attributed solely to pasture cover. One of these is the Waitohi River, where urban sources from the Picton township are the primary reason for this discrepancy. In the case of the other three, particularly Linkwater Stream, potential causes include poor pastoral management practices or malfunctioning private sewage treatment systems.
Waterways with increasing DRP concentrations include the Kenepuru River. Although Dissolved Reactive Phosphorus (DRP) concentrations tend to be elevated in catchments with a substantial proportion of pastoral land cover, Linkwater Stream and Cullen Creek exhibit somewhat higher concentrations. A contributing factor to this is the naturally higher background levels of DRP. Catchment studies conducted in the Waitohi River and Linkwater area have revealed some of the highest DRP concentrations originating from native bush catchments within the region. This finding points to phosphorus-rich geological features in these parts of the Marlborough Sounds, which also explain the comparatively elevated DRP levels in the Graham River. Comparing DRP concentrations with those for the rest of New Zealand highlights that concentrations observed within Marlborough's waterways generally fall within the lower end of the spectrum.
Current SOE monitoring – Water Quality Index
The council’s freshwater monitoring network measures nine State of the Environment surface water quality parameters to form the Water Quality Index for each site. The WQI simplifies comparisons of water quality across various waterways and serves as a valuable tool for identifying degraded waterways and prioritising improvement actions.
In contrast to the single parameter scores used for the NPS-FM attributes, this index offers a comprehensive overview of the overall water quality at monitoring sites and enables the ranking of waterways. The WQI played a pivotal role in identifying waterways that are degraded or at risk of degradation. Since the WQI guidelines are based on NPS-FM limits wherever possible, the WQI is closely linked to the NPS-FM attribute states. The most recent data is shown below:
Marlborough Sounds Complex SOE monitoring sites – current WQI measures | |||
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Monitoring site | WQI 2018-2021 | WQI 2019-2021 | WQI 2020-2022 |
Cullen Creek | Fair | Fair | Fair |
Linkwater Stream | Marginal | Marginal | Marginal |
Waitohi River | Marginal | Marginal | Marginal |
Graham River | Fair | Fair | Fair |
Kenepuru Stream | Fair | Fair | Marginal |
Overall, all recent WQI measures are either Fair or Marginal in this FMU. General influencing factors include climate, vegetation cover, and the land uses in a catchment area.
One of the most significant factors influencing water quality is the alteration of natural land cover. Prior to human settlement, New Zealand was predominantly cloaked in forests. Since human arrival, extensive deforestation has occurred, transforming most of our waterways from pristine to altered states. Almost 30% of the region has been converted into pasture, primarily for sheep and beef farming, although dairy farming has also gained a foothold, including in the Linkwater areas. Production forests, mainly consisting of Pinus radiata, dominate lower hill regions of Wairau River tributaries, the Rai/Te Hoiere area, and parts of the Marlborough Sounds.
Dissolved Inorganic Nitrogen (DIN) constitutes the soluble nitrogen content within the water column, readily available for uptake by algae thriving on the river and stream beds. Elevated DIN concentrations can trigger excessive algae growth, posing detrimental impacts on both aquatic ecosystems and the visual appeal of water bodies. Naturally, DIN concentrations are very low. This can be seen for rivers with a high percentage of native vegetation cover within their catchment such as the Goulter River, Branch River and Black Birch Stream. Waterways with elevated DIN concentrations are found in catchments with significant areas of pasture and higher rainfall, such as the Rai, Ronga and Kaituna River as well as Cullen Creek and Linkwater Stream.
Catchments dominated by native vegetation and groundwater-fed streams tend to have the clearest water. Turbidity serves as a surrogate measure for the amount of sediment suspended within the water column. Sediment can have detrimental effects on sensitive downstream environments, such as estuaries, leading to the smothering of benthic habitats. Significant reductions in turbidity are evident in several waterways regionally, including the Linkwater Stream. Most of these sites also exhibit significant decreasing trends in Total Phosphorus concentrations, highlighting the close relationship between phosphorus and sediment.
On smaller streams, the presence of shading riparian vegetation can significantly affect water temperature. An example is Cullen Creek and neighbouring Linkwater Stream. Cullen Creek benefits from a comparatively intact riparian buffer composed of mature trees and shrubs along most of its length, while the lower reaches of Linkwater Stream lack adequate shading. Consequently, Cullen Creek consistently maintains lower and less variable water temperatures.
Municipal and domestic supply
Groundwater is known to exist in the Picton/Waitohi area but it has never been found in sufficient quantities to warrant a commercial supply. The Picton municipal water supply well-field at Speeds Road - which is located in the Wairau FMU - is the largest user of Tuamarina River Valley groundwater. The municipal supply was established in the early 1970s by the Picton Borough Council. This supply is supported by open catchment dams at Essons Valley. Isolated communities continue to use minor tributaries for domestic supplies throughout the outer sounds and use private wells. Seven of these schemes supply greater than 25 households, including schemes based in Ōkiwi Bay, Anakiwa, Ngakuta Bay and Belview Bay.
2019 report – Water Quality in the Linkwater Area
State of the Environment monitoring results pre 2019 showed that water quality was either degraded or at risk from degradation in the Linkwater catchment. Requirements in the Proposed Marlborough Environment Plan meant that Catchment Enhancement Plans needed to be developed for these streams. To support the future improvement efforts, the causes of water quality degradation needed to be known.
Existing SOE monitoring identified a number of parameters that were exceeding guideline levels at the time. These were:
- Elevated dissolved nutrient concentrations (both nitrogen and phosphorus),
- High E. coli concentrations (mainly during higher flows),
- Low pH levels (mainly in Linkwater Stream)
- Low Dissolved Oxygen levels
Of the three catchments monitored, Ada Creek generally had the best water quality. The main reasons were good riparian management for most of the stream length and less intensive irrigation of dairy pasture. Linkwater Stream had the poorest water quality. Livestock access to waterways, surface run-off and erosion were the main causes of degraded water quality. Nitrogen in upwelling groundwater in the lower reaches of Linkwater Stream was the source of the highest Dissolve Inorganic Nitrogen concentrations monitored during the study. During rainfall, run-off from cattle races that run adjacent to streams is causing contamination with sediment, nutrients and faecal material in Ada, Cullen and White Pine Creek.
A number of recommendations were concluded from the report for improving water quality in the area. It is important to note that although only the three largest streams were monitored, the findings of this study also applied to other, smaller streams in the Linkwater area. The recommendations were:
- Identify critical source areas on individual farms and reduce their impact on water quality
- Fence off livestock from waterways
- Establish tall riparian vegetation to stabilise stream banks and reduce algae growth; particularly along Linkwater stream
- Prevent surface run off from cattle races entering streams
- Minimise erosion from plantation forests
Water quantity and use
There has been no river flow monitoring site in this FMU due to the low number of surface takes.
There are no irrigation schemes in this FMU. Overall, irrigation water use is minor in scale. In the whole proposed FMU area there are 56 take consents, many of which are discrete in nature and unrelated to irrigation. Of the 56 total, 9 water take consents are located in the Havelock and Linkwater areas. The numbers are correct as at October 2023.