LAWA River Health - National Picture 2023

 

Published: 24 October 2023*

LAWA presents river health information for more than 1,500 sites throughout New Zealand. Rivers and streams are monitored for a range of water quality (chemical-physical and bacterial) and ecological indicators by regional councils and unitary authorities, and the National Institute of Water and Atmospheric Research (NIWA).  State and trends for these indicators have been updated using data up to the end of June 2022.

This national picture summary focuses on the state of our rivers and streams. Here we report on six indicators:

A biological indicator of the health of wadeable rivers and streams:

• Macroinvertebrate Community Index (MCI)

Indicators of water quality contributing to river ecosystem health:

• Ammonia and nitrate toxicity - nutrients that can be toxic to in-stream life

• Dissolved reactive phosphorus (DRP) - a nutrient that can lead to problematic in-stream algal growth

• Clarity - a proxy for the impacts of suspended fine sediment that can affect river ecosystem health and the amenity value of waterways

An indicator of human health risk:

• Escherichia coli (E. coli) - a bacterium that can indicate faecal contamination and the presence of harmful pathogens which may cause illness to recreational water users

 

This summary provides information on the state of river health in New Zealand, how it varies by land cover, and how it has changed over time. As data are only available for sites where monitoring has been conducted, and monitoring sites are often located in areas at greater risk of degradation from human activities, this summary is not necessarily a balanced representation of all rivers and streams across the country.

LAWA evaluates conditions (state) at sites nationwide against attribute bands described in the National Policy for Freshwater Management 2020 (NPS-FM 2020), from A (good) to D or E (poor). The 'current state' for 2022 at each site is based on monthly data over the previous five hydrological years (from 1 July 2017 to 30 June 2022). This LAWA evaluation requires an almost complete five-year history of monthly measurements before a grade can be assigned, not all river sites that feature on the LAWA website meet this requirement to be assigned attribute bands.  See this factsheet for more information.

 

Current river health state

The current state of our rivers and streams varies by indicator (Figure 1).

Impaired ecological health is evident at almost two-thirds of monitored river sites, demonstrated by the proportion of MCI sites classified as attribute band C and D.

Dissolved reactive phosphorus (DRP) and water clarity (as a proxy for suspended fine sediment) are factors that contribute to river and stream ecosystem health. It is positive that 55% of the sites assessed for clarity are in the A band. However, around 35% of sites are in the C and D bands indicating that suspended fine sediment is impacting aquatic life at these sites. For DRP, which is a nutrient that may contribute to excessive in-stream plant and algae growth, just over half of sites monitored are in band C or D. It is worth noting that some sites have naturally high levels of DRP, in some cases due to phosphorus-rich volcanic soils.

The risk of toxic effects of nitrate and ammonia on sensitive aquatic species is an issue at only a small percentage of monitored sites. Therefore, it is not likely that such toxicity is driving the widespread ecological health impairments we’re seeing through the MCI results.

Nitrogen can also stimulate problematic plant and algae growth in rivers at lower concentrations than those causing direct toxic effects. When assessing the risk of nutrients driving problematic plant and algae growth, resource managers are required under the NPS-FM 2020 to look at the combined dissolved nitrogen forms (collectively called dissolved inorganic nitrogen – DIN). There are currently no attribute band definitions for DIN in the NPS-FM 2020, and therefore it is not included in this summary. The NPS-FM 2020 does require management of these nutrients to protect the ecological health of rivers and we intend to report further on this in the future as more data and reporting guidance become available.

For New Zealand's primary indicator of faecal bacterial contamination (E. coli), two-thirds of monitored sites are graded band D or worse, indicating these sites are considered unsuitable for swimming (i.e. the predicted average infection risk is greater than 3% on any given day) from a public health risk perspective.

 

LAWA National River Health Summary of State (2022)

Figure 1. Percentages of monitored sites by attribute bands for all six indicators discussed in this national picture summary. Bands were calculated over the five-year hydrological period (1 July 2017 – 30 June 2022). The number of sites with suitable data to determine an attribute band for each indicator is shown below each bar. 

 

Current river health state by land cover

Land use is a key driver of water quality and river ecosystem health. In the following analyses we show differences in indicator state for 2022, among four different land cover categories, as defined by the River Environment Classification (REC) system.

There is a general pattern (Figures 2–6) among land cover categories for the six indicators that we are focusing on in this national summary, with the highest proportion of better scoring streams in native vegetation, followed by exotic forest, and then pasture. Urban streams generally receive the worst scores.

Rivers and streams with catchment cover classified as being predominantly native vegetation make up 48% of Aotearoa New Zealand’s channel length, while pasture is also common making up 45%. Exotic forestry streams account for 5% of channel length and urban streams are less common at 1%. While urban streams only make up a small proportion of the country’s total river length, these waterways are important to our communities as almost 9 out of 10 New Zealanders live in urban areas, so many people’s local rivers and streams are currently in poor health.

The catchments in the native vegetation land cover class are least affected by human activities but are not necessarily 100% naturally vegetated. The land cover definition allows them to include some urban, pasture, and exotic forest in the catchment upstream, as long as they are still predominantly in native vegetation. Geological differences (different rock and soil types) among streams may also explain high concentrations for some indicators. For example, phosphorus concentrations tend to be naturally high in catchments draining volcanic soils. Similarly, dissolved reactive phosphorus and ammonia can be elevated in wetlands and in streams draining high organic-content soils (e.g. peat soils). The combination of these factors may explain why some “native vegetation” sites are not in the A band.

 

LAWA National River Health State (2022) by Land Cover Class

Macroinvertebrate Community Index (MCI)

Figure 2. Comparison of attribute bands for the Macroinvertebrate Community Index (MCI) across four land cover classes. Bands were calculated over the five-year hydrological period (1 July 2017 – 30 June 2022) at 1024 sites. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

LAWA National River Health State (2022) by Land Cover Class

Ammonia (toxicity)

 

Figure 3. Comparison of attribute bands for ammonia (toxicity) across four different land cover classes. Bands were calculated over the five-year hydrological period (1 July 2017 – 30 June 2022) at 861 sites. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

LAWA National River Health State (2022) by Land Cover Class

Nitrate (toxicity)

Figure 4. Comparison of attribute bands for nitrate (toxicity) across four different land cover classes. Bands were calculated over the five-year period (1 July 2017 – 30 June 2022) at 874 sites. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

LAWA National River Health State (2022) by Land Cover Class

Dissolved Reactive Phosphorus (DRP)

Figure 5. Comparison of attribute bands for dissolved reactive phosphorus (DRP) across four different land cover classes. Bands were calculated over the five-year period (1 July 2017 – 30 June 2022) at 872 sites. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

LAWA National River Health State (2022) by Land Cover Class

Clarity (Suspended Fine Sediment)

Figure 6. Comparison of attribute bands for clarity (as a proxy for suspended fine sediment) across four different land cover classes. Bands were calculated over the five-year hydrological period (1 July 2016 – 30 June 2021) at 550 sites and take into account the different suspended sediment classes defined in the NPS-FM 2020. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

LAWA National River Health State (2022) by Land Cover Class

E. coli 

Figure 7. Comparison of attribute bands for the faecal indicator bacteria E. coli across four different land cover classes. Bands were calculated over the five-year hydrological period (1 July 2017 – 30 June 2022) at 785 sites. The number of sites with suitable data to determine an attribute band for each land cover class is shown below each bar. The location and attribute band of these monitoring sites is shown on the map.

 

River health state over time

The above plots look at the current state, but how has state changed over time? To examine this, we identified sites that had an almost-complete sampling record over the last 15 years. This enabled us to calculate attribute bands for each five-year interval over the last decade. Each state band assessment is based on the previous five years of information, so the 2013 grades, for example, are based on a five-year hydrological dataset from 1 July 2008 – 30 June 2013. The following figures show results only for those sites that have this long and comprehensive sampling history.

At a national level, some indicators (e.g. clarity, dissolved reactive phosphorus, ammonia toxicity) show some signs of positive change over time with an increase in the proportion of sites in healthier attribute bands, while others (e.g. MCI) show some signs of worsening condition.

Macroinvertebrates are sampled to provide an indicator of the ecological health of wadeable streams and rivers.

Species that are sensitive to poor water quality are only found at healthy river sites whereas species that are tolerant of poor water quality tend to dominate the macroinvertebrate community at polluted sites. The MCI summarises the pollution tolerances of the species that make up the community at a river site and these species respond to multiple drivers (e.g. physical habitat change, oxygen, climate change etc).

MCI shows a reduction in the number of sites in A and B bands, and more sites in C and D bands over the last 10 years (Figure 8). Sites graded in the D band are typically in lowland areas draining heavily modified catchments, while sites in the A-band are typically draining higher elevation areas with more natural land cover. An improvement in the MCI requires ecosystem-level improvements across habitat, water quality, water quantity, and ecological processes before sensitive species can return to these environments. This will take time. MCI may show a delayed response to actions taken to improve waterway health in the catchment, relative to some of the other indicators.

 

LAWA National River Health State Change Over Time (2013 - 2022)

Macroinvertebrate Community Index (MCI)

Figure 8. Changes in attribute bands for the Macroinvertebrate Community Index (MCI) from 2013 - 2022 at the 537 sites where there were enough data to determine a result each year. The location of these monitoring sites and current state attribute band (2022) is shown on the map.

 

Ammonia is one of several forms of nitrogen that exist in aquatic environments. In addition to contributing to growth of in-stream plant and algae biomass, at high concentrations ammonia is toxic to aquatic fauna. Most monitoring sites had low levels of ammonia where toxicity is unlikely but may still be at levels that contribute to excessive growth of plants or algae. There has been an increase in the proportion of sites in the A and B bands, and a reduction in the C band over the last 10 years (Figure 9).

 

LAWA National River Health State Change Over Time (2013 - 2022)

Ammonia (toxicity)

Figure 9. Changes in attribute bands for ammonia (toxicity) from 2013 - 2022 at the 424 sites where there were enough data to determine a result each year. The location of these monitoring sites and current state attribute band (2022) is shown on the map.

 

Nitrate is another of several forms of nitrogen present in aquatic environments, and like ammonia, it can contribute to growth of in-stream plant and algae biomass, but at high concentrations is toxic to aquatic fauna. Sites assessed as being in the A or B bands for in-stream toxicity effects can still have nitrate levels that increase the risk of excessive algal growth, because this occurs at much lower concentrations than toxicity. Most monitoring sites had levels of nitrate nitrogen that were below levels where toxicity is likely. The sites with potentially toxic (C and D band) concentrations of nitrate are typically lowland spring-fed streams with flow dominated by inputs of high nitrate groundwater. There is limited evidence of improvement, with an increase in the proportion of sites in the A and B bands, and a reduction in the C band over the last 10 years (Figure 10).

 

LAWA National River Health State Change Over Time (2013 - 2022)

Nitrate (toxicity)

Figure 10. Changes in attribute bands for nitrate (toxicity) from 2013 - 2022 at the 463 sites where there were enough data to determine a result each year. The location of these monitoring sites and current state attribute band (2022) is shown on the map.

 

Phosphorus is an important nutrient contributing to the growth of algae and other aquatic plants in freshwater systems, but when phosphorus concentrations are high there is an increased risk of nuisance algal blooms occurring. We often focus on dissolved reactive phosphorus (DRP) because that is the form of phosphorus that is most available for uptake by aquatic plants. The number of sites in the A and B bands have increased with a corresponding decrease in the D band over time (Figure 11). Sites with elevated DRP are typically in lowland areas draining heavily modified land and/or areas with naturally phosphorus-rich volcanic soils (more common in the North Island).

 

LAWA National River Health State Change Over Time (2013 - 2022)

Dissolved Reactive Phosphorus (DRP)

Figure 11. Changes in attribute bands for dissolved reactive phosphorus from 2012 - 2021 at the 386 sites where there were enough data to determine a result each year. The location of these monitoring sites is shown on the map.

 

The amount of fine sediment suspended in the water is a key factor affecting water clarity. High concentrations of suspended sediment can also affect the feeding behaviour of some aquatic organisms (they can’t see their food), affect their ability to breathe (it clogs up their gills), and can reduce the amenity value (it can be less pleasant for people to swim in discoloured water). If sediment deposits on the stream bed it can influence habitat and food quantity/quality for aquatic life. Suspended fine sediment also often carries phosphorus with it.

Fine sediment can get into waterways through erosion and surface runoff from the land, erosion of stream banks, and from some discharges. Land use and management practices can have a big effect on erosion and run-off of fine sediment, but there are also natural differences in climate, geology, and slope which can influence sediment inputs to waterways. The NPS-FM 2020 recognises these natural differences by defining four different classes of stream based on their climate, geology and slope, which have different expectations in terms of water clarity state. Sediment run-off is a significant issue affecting New Zealand’s freshwater bodies, so it is promising to see some evidence of an increase in the proportion of A band sites and reduction in D band sites in the 175 sites that have a long monitoring record (Figure 12).

 

LAWA National River Health State Change Over Time (2013 - 2022)

Clarity (Suspended Fine Sediment)

Figure 12. Changes in attribute bands for clarity (suspended fine sediment) from 2013 - 2022 at the 175 sites where there were enough data to determine a result each year. The attribute bands take into account the differences in state expected for the four suspended sediment classes in the NPS-FM 2020. The location of these monitoring sites and current state attribute band (2022) is shown on the map.

 

E. coli is the main type of faecal indicator bacteria monitored in freshwater systems in New Zealand. High concentrations of E. coli indicate that there are significant sources of faecal matter upstream – such as stock inputs, runoff, birds, or untreated wastewater discharges. High levels of faecal indicator bacteria in river water are a concern as they suggest other harmful bacteria or pathogens may be in the water, which could make us sick.

E. coli monitoring is conducted at popular swimming sites during the summer as well as year-round regardless of the flow conditions at State of the Environment monitoring sites. The data presented here are from the State of the Environment sites only and show that around two-thirds of these sites are scoring poorly and are in the D and E bands. This has been a relatively consistent picture over the last 10 years with some indication of a reduction in the proportion of A band sites and an increase in the proportion of D band sites (Figure 13). Sites in the D band and E band are typically in lowland areas draining heavily modified catchments.

 

LAWA National River Health State Change Over Time (2013 - 2022)

E. coli

Figure 13. Changes in attribute bands for the faecal indicator bacteria E. coli from 2013 - 2022 at the 363 sites where there were enough data to determine a result each year. The location of these monitoring sites and current state attribute band (2022) is shown on the map.

 

River health monitoring and reporting

This National Picture provides an aggregated overview of the state of river and stream health across six indicators using data from regional councils, unitary authorities, and NIWA.

Understanding the changing health of our rivers and streams is reliant on high quality data from long-term monitoring programmes. State of the Environment river health monitoring data on LAWA is available from 2004 onwards, and there are over 1.8 million records for water quality and macroinvertebrate monitoring. These numbers represent the huge collective effort and investment by regional councils, unitary authorities, research agencies and others. In recent times, monitoring staff across the country have worked hard to get back to sampling as soon as possible through COVID-19 lockdowns and extreme weather events. In some cases, these challenges have created gaps in our long-term data which we openly acknowledge and do our best to minimise the impact of.

As a project, we are working to further align our reporting with the NPS-FM 2020 and include information on a wider variety of indicators as long-term monitoring data becomes increasingly available over time. There will be a broader range of indicators available to better understand the health of our rivers as councils introduce changes to their monitoring network to better respond to up-and-coming legislative requirements, such as being able to report on ecosystem health, human contact, mahinga kai, and threatened species. Once more indicators are available, we will be able to provide a more holistic ‘health check’, and integrate assessments of rivers, lakes, groundwater, and estuaries.

LAWA Project partners are working hard to improve the consistency of monitoring across  New Zealand through the development and use of National Environmental Monitoring Standards (NEMS). As these standards are implemented, we expect to see further improvements in the availability of high-quality data on our environment.

 

Monitoring to inform actions and track progress

There is a lot of work underway to restore the health of our waterways. However, there can be a long lag time between actions people undertake to help the environment, and the resulting environmental change that can be detected and reported on in our rivers and lakes. Keeping track of land management actions to improve our waterways provides a more immediate indicator of progress towards catchments that support freshwater health, but data has typically been unavailable or difficult to access at a national level. An Our Land and Water National Science Challenge project has developed a Healthy Waterways Register for landowners, community groups, and agencies to submit information on their actions to improve the environment. It is early days, but as of the beginning of September 2023, there have been around 18,970 actions entered in the database, and this number is increasing every day. The next topic to launch on the LAWA website, named Actions for Healthy Waterways, will report on the restorative or protective actions that people are making to improve waterway health in catchments. By gathering and reporting on this information we will be better able to link the actions that have been done on the land, to the water quality outcomes being sought, and better understand which actions work best to inform future efforts.

 

Figure 14.  An infographic showing a river journey towards restored ecosystem health. The river under pressure with poor ecosystem health (left panel), actions underway to improve river health (middle panel), and a future state moving towards a thriving river ecosystem (right panel).

 

Explore more on LAWA

Looking at individual site data alongside contextual information at a catchment and regional level is useful for mana whenua, community groups, landowners, and others interested in how local waterways are tracking. Information specific to monitored sites can be accessed either by clicking on a site dot on the map to the left of the LAWA main screen (desktop and tablet users), or by navigating menus to the region, then catchment, and then site of interest.  The organisation responsible for monitoring an individual site can provide further contextual information to the results shown.

 

 

*Updated from 24 September 2023: The method for calculating ammonia toxicity state attribute bands has been updated in line with the latest version of the NPS-FM 2020 (February 2023).  This revised calculation has resulted overall in a higher proportion of river sites in the A band, and reductions in the number of sites in the B, C and D bands.  For example, for the current state 78% (previously 59%) of sites are in the A band, and 20% (was 34%) are in the B band. The proportion of sites below the national bottom line remain low and have also reduced: C band now 2% (was 5%) and D band now <1% (was 1%).