Soil

Soils are a fundamental part of all land-based ecosystems. They buffer and purify water, regulate optimum growing temperatures for diverse plant species, cycle nutrients, filter contaminants, provide habitat for billions of organisms and perform many ecosystem services critical for terrestrial life.

Soils are also vital to primary production and contribute to the economic wellbeing of Canterbury/Waitaha and New Zealand/Aotearoa. Much of the agricultural and forestry production in the region is exported and this generates significant regional and national economic benefits.

Soils generate so slowly that they can be regarded as a non-renewable resource. Once degraded, they are prone to irreversible loss through erosion.

Sustaining the health and productive capacity of the region’s soils is vital and its good management is of regional and national significance. 

Here are the current challenges and issues in relation to soil loss and health in Waitaha.

Erosion Raikaia Gorge Canterbury New Zealand

Issue: Loss of soil through erosion

Soil erosion can result in the loss of rich topsoil and a subsequent decrease in soil productivity, or a degradation of the soil.

Shallow landslides, which are one of the most widespread types of erosion in New Zealand/Aotearoa, remove soil nutrients and reduce its depth and water holding capacity. Eroded soils often have limited biodiversity.

Erosion is a widespread natural process in New Zealand/Aotearoa mainly due to weak and highly erodible rocks and high rainfall events.

Human actions that modify soil or vegetation can increase the rate of erosion more than natural rates. This is known as induced soil erosion. Common causes of induced erosion are vegetation removal, over-grazing by animals, excessive burning or cultivation and earthworks. The harvesting of plantation forests can also lead to soils becoming vulnerable to erosion, particularly on erodible steep land.

Natural causes of high rates of erosion include extreme weather events and natural hazards (earthquakes and storms).

Local impacts of soil erosion

There is a knowledge gap across New Zealand/Aotearoa on monitoring erosion and we have limited understanding of where, how, and to what extent it is happening. Environment Aotearoa 2022 reported that the regions with the highest levels of sediment movement into waterways were (in decreasing order) the West Coast/Tai Poutini, Gisborne/ Tairāwhiti, Otago/Ōtākou, Waitaha, Northland/Te Tai Tokerau and Manawatu/Whanganui.

Erosion and its effects in hill country areas – such as lost soil, nutrients and production, damage to trees, houses, infrastructure, and waterways – is estimated to cost the New Zealand/Aotearoa economy $100 to $150 million a year.

Climate change projections

Climate change is projected to alter weather patterns in Waitaha including more extreme weather events such as storms, high winds and droughts.

Changes such as these could exacerbate natural soil erosion processes in many parts of the region as well as increase the risk of human-induced soil erosion.

The forestry sector is particularly affected by extreme weather events and can worsen the effects of extreme weather events on soil. In recent years, heavy rain inland of Tolaga Bay to the north of Gisborne/Tai Rāwhiti mobilised a large volume of sediment and wood debris. The damage caused significant deposition of sediment and wood debris over farmland as well as damage to property and infrastructure. Events of this scale have not occurred in the Waitaha region, although smaller scale events such as at Gebbies Pass, Banks Peninsula/Horomaka have occurred.

Preventing soil loss

Soil loss can be prevented through a range of actions such as planting or retaining vegetation on sloping land, preventing livestock access to riverbanks, and adopting improved cultivation and livestock grazing strategies. Permanent forestry can also protect against erosion, once it is established, and can stabilise erosion prone land.

The Soil Conservation and Revegetation Programme (SCAR) is an initiative that aims to reduce erosion and sediment loss, and stabilise damaged hill country land in North Canterbury/Waitaha.


Temuka, Canterbury, New Zealand

Issue: Soil quality is degrading in parts of Waitaha

Healthy soil is teeming with life. Soils are home to over 25 percent of the world’s total biodiversity, and provide habitat for insects, worms, fungi, and micro-organisms. Microfauna has a critically important role in making nutrients available for plants to grow and protecting them from disease.

Soils are diverse in composition and distribution, and there is not one type of soil that is specifically valuable for all uses. Soils that are highly productive for arable crops may differ significantly from those that are highly valued for viticulture. Soils are dynamic and respond to the way we manage them. This can lead to improvement or degradation.

Soil versatility is an expression used to describe the ability of the soil to support a wide variety of agricultural uses without the need for many inputs such as fertiliser and water. Less versatile soil will need more active management to achieve similar production or may simply be unsuitable for growing crops or raising stock.

Waitaha has a range of soil types, including those classed as being high quality or highly productive. Find out more about the loss of highly productive land through urban expansion on our urban form page.

Impacts on soil quality in Waitaha

Cadmium concentrations in soil

Cadmium concentrations in Waitaha soils vary across the regionCadmium is a soft heavy metal that is toxic at certain concentrations and can contaminate food and fodder crops when these are grown in soils with elevated cadmium levels.

This can negatively impact human and livestock health as well as international trade if food safety standards are exceeded.

Increasing concentrations of cadmium in soil are cumulative and persist for the foreseeable future which can limit the versatility of soils for different land uses. It is uncertain whether the methods available to address this are feasible.

Sources of cadmium in soil

Cadmium is a natural impurity in phosphate rock used to produce phosphate fertiliser and its concentration varies geographically. Phosphate fertilisers are the primary source of cadmium in soils, but it can be added through other sources such as compost, irrigation water, dairy farm effluent, or be present due to natural processes.

Between 2001 and 2005, approximately 30 tonnes of cadmium per annum were added to agricultural soils in New Zealand/Aotearoa through phosphate fertiliser use.

Land use is a key driver of cadmium concentrations in soils. Soils subject to intensive agriculture that require high phosphate inputs, such as dairy farming, tend to have higher cadmium concentrations compared to other land uses. Other land uses with higher than the national average are the production of kiwifruit and berries, orchards, market gardens, beef farms, and drystock pasture.

Cadmium concentrations in Waitaha

Cadmium concentrations in Waitaha soils vary across the region. From 2000 to 2020, 40 percent of monitored arable and pastoral sites showed increases in soil cadmium, while 11 percent decreased and 49 percent showed no change. As of 2020, all monitored arable and pastoral sites had soil cadmium concentrations within acceptable levels.

Research trials from 2015 to 2017 found some potatoes grown throughout the region exceeded food safety standards for cadmium despite being grown in soils that did not have unacceptably high cadmium concentrations. The current recommended management strategy for potato growers in Waitaha is to grow varieties which take up low levels of cadmium. The reasons for these exceedances are not clear and more information is needed to understand the causes and extent of these elevated cadmium concentrations in some food crops.

Soil compaction in pastoral soils

Extracting a soil core to monitor wind erosion

Extracting a soil core

Soil compaction refers to the compression of open pore spaces in soils through which gases, water and dissolved nutrients move. Slower infiltration and movement of water in compacted soils has the potential to lead to faster overland flow runoff.

Soil compaction also increases resistance to plant root growth, and this can impact on productivity and increase susceptibility to soil erosion.

Emissions of nitrous oxide, a greenhouse gas, are known to increase from compacted topsoil.

Heavy machinery trafficking and livestock treading can cause soil compaction, and the use of irrigation can lower the resistance of soils to it. Topsoil compaction is particularly evident under irrigated dairy pastures.

Monitoring soil compaction

We monitor for the symptoms of soil compaction by looking at soil properties such as bulk density, macro-porosity, and penetration resistance. Our arable and pastoral soil quality monitoring programme tells us that soil structure changes are an issue for our lowland soils in arable and pastoral use. A high proportion of our lowland monitoring sites indicate increased vulnerability to becoming less permeable, water erosion, and contaminant run-off.

Our arable and pastoral soil quality monitoring programme also tells us that nearly half of our continuous cropping monitoring sites and a quarter of our mixed arable monitoring sites show degraded levels of soil organic matter. Soil organic matter is vital for many soil functions including soil structure and the capacity of soils to hold onto nutrients and water, retaining them until they are needed by plants and organisms. Low levels of soil organic matter in arable land translate to soils being more vulnerable to structural degradation, a reduced ability to effectively cycle and store nutrients and increased reliance on inorganic fertiliser inputs to reach target yields.

The most recent trend analysis of monitoring data suggests that topsoil structure has been declining in arable and pastoral lowland soils. Researchers have picked up on the widespread compaction of pastoral soils in New Zealand/Aotearoa, and are seeking to better understand its effects, review potential mitigation practices, and identify knowledge gaps.

Climate change projections

It is challenging to predict the likely impacts of climate change on the soil and vegetation of the region, as it is quite probable some parts of the region will get drier and others wetter.  Climate change has the potential to increase both droughts and storm events in the region and both have the potential to affect soil health.


Current actions or approach

The control of the use of land for the purpose of soil conservation is a regional council responsibility under the Resource Management Act 1991. The Canterbury Regional Policy Statement outlines the issues for soils in Waitaha and requires the maintenance of soil quality in the region. It requires newly induced soil erosion to be avoided, and existing erosion to be addressed, with a particular focus on maintaining vegetative cover on non-arable land.

The Canterbury Land and Water Regional Plan manages the impacts of activities in areas prone to soil erosion by identifying high soil erosion risk areas in the region and controls vegetation clearance and earthworks in these areas.

The National Environmental Standards for Plantation Forestry (NES-PF) includes requirements to prepare a harvest plan and a forestry earthworks management plan for the management of environmental risks and earthworks for various forestry activities such as harvesting and earthworks that involve more than 500m2 of soil disturbance.

There are no national regulations specifically targeted towards the maintenance of soil quality. The National Environmental Standard for Freshwater (NES-F) includes controls on intensive winter grazing farming activities including pugging (when wet soil is churned up and pushed down by livestock), sediment loss to waterways and the use of synthetic nitrogen fertiliser. These controls are focused more on freshwater quality rather than soil quality. 

The Canterbury Land and Water Regional Plan manages some activities which cause pugging from livestock or vegetation clearance of the land beside waterways, although this is more to address erosion and sedimentation effects on waterways rather than soil quality issues. The LWRP does not specifically address soil acidification or cadmium contamination of soil, although fertiliser use is managed through farm environment plans.

District Plans manage land use and include provisions to ensure erosion and sedimentation effects are addressed by these activities.

Our soil monitoring programmes

We use several monitoring programmes to analyse the quality of the region’s soils.

  • The ‘500 Soils’ monitoring programme covers a wide range of landforms and land uses in our region and generates state of the environment monitoring data for national reporting.
  • The Arable & Pastoral Soil Quality Monitoring programme focuses on soil quality issues specific to the intensively farmed lowland soils. This programme does not provide an assessment of soil quality on the hill or high country which will have a different risk profile.

Monitoring soil for cadmium

Soil cadmium is monitored as part of the regional monitoring programme. There are a range of actions being undertaken at a national level to minimise cadmium concentrations in soil including:

  • national voluntary limits on cadmium concentrations in fertilisers
  • food safety standards for cadmium in our food and animal food products (FSANZ, 2015)
  • managing the disposal of offal to minimise cadmium ingestion by humans
  • national soil guidelines
  • soil testing.

Comparison of soil monitoring in Waitaha between 2013 to 2021 against soil quality target ranges

This soil quality information for Waitaha between 2013 to 2021 shows the range of indicators we use to monitor the quality of lowland soils in our region.

It also shows whether the indicators are within a target range over a number of farming practices.

The monitoring information shows, through indicators of soil physical state like macro-porosity (the proportion of large pores in the soil that provide the air supply to roots) and penetration resistance , that soil compaction is an issue for lowland pastoral soils, particularly under dairying.

Low organic matter content is of concern for arable soils in Waitaha, with nearly half of our continuous cropping sites holding low levels of total organic carbon. Only 55 percent of long-term arable soils monitored between 2013 and 2021 met the target for soil carbon in the topsoil, and this proportion was 10 percent lower than for the preceding monitoring period (2004-2012).