Key findings from HAPINZ 3.0

This section presents key findings about the health impacts of air pollution in New Zealand in 2016.  These results come from the HAPINZ 3.0 study, which was published in July 2022. 

Air pollution includes fine particulate matter (PM2.5) and nitrogen dioxide (NO2). Health impacts include premature deaths, hospitalisations, asthma, and restricted activity days, as well as the social costs from illness and deaths.  

Only impacts from human-made (anthropogenic) sources of air pollution are included here, as these are something we can potentially control and change.

More than 3,300 deaths from human-made air pollution in 2016

Air pollution does significant harm to many New Zealanders, including children.

In 2016, human-made (anthropogenic) air pollution in New Zealand resulted in an estimated:

  • 3,317 premature deaths (in people aged 30+ years)
  • 13,155 hospitalisations for cardiovascular and respiratory disease, including 845 hospitalisations for childhood asthma
  • 13,229 cases of childhood asthma
  • about 1.75 million restricted activity days (days on which people could not do the things they might otherwise have done if air pollution had not been present).

If there was no air pollution (ie PM2.5 or NO2 from human-made sources) in New Zealand, then about 3,300 deaths would have been avoided in 2016.  This represented about 11% of all deaths in New Zealand in 2016.

Air pollution harms were mainly caused by transport and domestic fires – with transport having a much larger impact than previously thought

Motor vehicles were the largest contributor to air pollution health impacts in New Zealand in 2016, with 2,247 deaths (Figure 1).  Most of the motor vehicle-related deaths were due to nitrogen dioxide (NO2) (2,025 deaths), with a smaller number due to PM2.5 (222 deaths). The significant impact due to motor vehicle-related NO2 was a new finding for New Zealand. 

After motor vehicles, domestic fires were the second largest contributor (962 deaths), followed by wind-blown dust (106 deaths) and industry (2 deaths).  These sources all contribute PM2.5 air pollution.

Figure 1: Number of premature deaths due to human-made air pollution (NO2 and PM2.5) in New Zealand in 2016, by air pollutant and source of air pollution (people aged 30+ years)

Social costs from human-made air pollution were $15.6 billion in 2016

In 2016, the social costs from human-made air pollution were $15.6 billion.  These social costs reflect the total cost of all air pollution impacts to New Zealand - not only in terms of direct costs incurred in the health system but also due to loss of life, lost quality of life and lost productivity.

The social costs were mainly from air pollution from motor vehicles ($10.5 billion) (Figure 2).  Air pollution from domestic fires resulted in social costs of about $4.6 billion in 2016.

Figure 2: Social costs from human-made air pollution (NO₂ and PM₂.₅) in New Zealand, by air pollutant and source of air pollution, 2016 ($millions)

The largest health impacts of air pollution were in Auckland and Christchurch

In 2016, the territorial authorities (TAs) with the highest number of premature deaths due to air pollution were Auckland City (939 deaths) and Christchurch City (462 deaths) (Figure 3).

Other TAs with high numbers of premature deaths from air pollution included Dunedin City (126 deaths), Tauranga City (107 deaths) and Hamilton City (100 deaths).

Figure 3: Number of premature deaths due to air pollution (PM2.5 and NO2) (among people aged 30+ years), by territorial authority (TA), 2016 

Note: To view the legend, click the arrows (››) in the map.

To explore more data at the territorial authority level, view the HAPINZ 3.0 dashboard

 

The lower South Island had higher rates of premature deaths from air pollution

Accounting for population size, territorial authorities in the lower South Island had higher rates of premature deaths from air pollution (Figure 4).

The highest rates of premature deaths from air pollution were in Invercargill City (219 per 100,000 people aged 30+ years), Christchurch City (206 per 100,000), Waitaki District (191 per 100,000) and Timaru District (186 per 100,000).

Figure 4: Premature deaths due to air pollution (PM2.5 and NO2), rate per 100,000 people aged 30+ years, by territorial authority (TA), 2016

Note: To view the legend, click the arrows (››) in the map.

To explore more data at the territorial authority level, view the HAPINZ 3.0 dashboard

 

Health impacts from air pollution have increased since 2006, driven by NO₂

From 2006 to 2016, there was an overall increase in deaths, hospitalisations and social costs from human-made air pollution in New Zealand (Table 1).  In particular, the number of deaths from human-made air pollution increased from 3,005 to 3,317. The increase in health impacts was driven by nitrogen dioxide (NO2).

Table 1: Changes in health impacts from human-made air pollution (NO2 and PM2.5) in New Zealand, 2006 to 2016 (numbers and rates)   

For more information, see Changes over time.

A large proportion of the population is exposed to poor-quality air, with persisting inequities for Pacific peoples

In 2016, 81.0% of the New Zealand population lived in areas with an annual average PM2.5 exceeding the World Health Organization (WHO) 2021 guideline level (of 5µg/m3) (Figure 5).  The proportion was slightly lower among Māori (77.6%) but much higher among Pacific peoples (94.4%), reflecting differences in where they live.

Figure 5: Percentage of population living in areas with PM2.5 higher than WHO 2021 guidelines (5µg/m3), total population and by ethnic group, 2006 and 2016

In 2016, 31.4% of New Zealanders lived in areas with annual average NO2 levels exceeding the WHO 2021 guideline level (of 10µg/m3) (Figure 6).  The proportion was lower among Māori (23.1%), but much higher among Pacific peoples (54.5%), again reflecting differences in where they live.

Figure 6: Percentage of population living in areas with NO₂ higher than WHO 2021 guideline (10µg/m3), total population and by ethnic group, 2006 and 2016

For more information on exposure, see Exposure to poor air quality.

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