This page relates to the 2018-21 National Land Transport Programme.
This section provides guidance for assessing road improvement activities with an implementation cost over $1 million per activity. These activities target a specific increase in levels of service as part of a roading network.
Guidance for the assessment of low cost, low risk improvement activities costing less than $1.0 million to implement is provided separately.
For general information about developing an assessment profile including relevant reference frameworks, see Developing an assessment profile.
Before an investment proposal is assessed against the Investment Assessment Framework (IAF), a business case must be developed, which Waka Kotahi NZ Transport Agency assesses to ensure it:
The activity must be included in a regional land transport plan (RLTP).
For further information about prior requirements, see Developing an assessment profile.
The road improvements activity classes include local road improvements, state highway improvements and regional improvements, under the following work categories:
For road improvement activities, the results alignment can be low, medium, high or very high (see below).
For further information on results alignment assessment see Developing an assessment profile which includes definitions of terms used. Definitions of high and medium crash risk are provided below.
A road improvement activity may be given a low results alignment rating if the activity addresses one or more of the following criteria:
Strategic priority | Criteria for a low rating |
Safety |
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Access – thriving regions, liveable cities |
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A road improvement activity may be given a medium results alignment rating if the activity addresses one or more of the following criteria:
Strategic priority | Criteria for a medium rating |
Safety |
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Access – thriving regions |
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Access – liveable cities |
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Environment |
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A road improvement activity may be given a high results alignment rating if the activity addresses one or more of the following criteria:
Strategic priority | Criteria for a high rating |
Safety |
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Access – thriving regions |
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Access – liveable cities |
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Environment |
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A road improvement activity will only be given a very high results alignment rating if the activity addresses one or more of the following criteria:
Strategic priority | Criteria for a very high rating |
Safety |
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Waka Kotahi requires approved arganisations and Waka Kotahi (state highways) to use the Waka Kotahi Monetised benefits and costs manual (from August 2020) or Economic evaluation manual (superseded August 2020) procedures and templates to determine the benefit–cost ratio (BCR) for road improvement activities.
Non-monetised benefits and additional benefits should also be considered where appropriate.
For further information on cost–benefit appraisal including calculating the BCR and resulting rating see Developing an assessment profile.
Risks change over time, and up-to-date trends should be monitored to ensure safety programmes are addressing the biggest risks.
See Safety risk definitions for results alignment for details.
Waka Kotahi has set threshold levels for investment activities to address resilience. These take into account the expected duration and frequency of the road closure, the road's classification and any alternative routes. These thresholds can be used to determine when it is appropriate to propose investment activities to overcome resilience problems.
Results alignment is based on the number of route closures.
The table of acceptable closures provides the annual rate [note 1 below] for each road class when there is a viable alternative route. If there is no viable alternative route [note 2 below] the acceptable number of closures in the table is decreased by a factor of 2.5 (ie for a regional or arterial road the number of acceptable closures becomes 4 instead of 10 closures per year for the two to four hour closure period).
The resilience gap for results alignment is:
o low if all values of the number of road closures are lower than the values shown in the table (adjusted for whether a viable alternative route exists)
o medium if one or two values are greater than or equal to the values shown in the table (adjusted for whether a viable alternative route exists)
o high if three or more values are greater than or equal to the values shown in the table (adjusted for whether a viable alternative route exists).
Notes:
The table below shows the acceptable number of road closures per year for ONRC road classes when there is an alternative route.
Closure period |
ONRC classification |
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National high volume |
National |
Regional/ arterial |
Primary/secondary collector |
Access/access low volume |
|
2–4 hrs |
1 |
4 |
10 |
19 |
30 |
5–12 hrs |
0.5 |
2 |
5 |
9.5 |
14.8 |
13 hrs–2 days |
0.2 |
1 |
2 |
3.8 |
5.9 |
3–5 days |
0.1 |
0.2 |
0.5 |
0.9 |
1.5 |
6–14 days |
0.04 |
0.08 |
0.2 |
0.4 |
0.6 |
15–49 days |
0.02 |
0.04 |
0.10 |
0.19 |
0.30 |
50–120 days |
0.01 |
0.01 |
0.025 |
0.047 |
0.074 |
More than 120 days |
0.004 |
0.004 |
0.010 |
0.019 |
0.030
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Structural mitigation can be considered when road-traffic noise levels, as predicted by strategic mapping undertaken in accordance with the Guide to state highway noise mapping [PDF, 615 KB] (Draft) November 2013, exceed 65dB LAeq(24hr) at protected premises and facilities (PPF).
The criteria for road-traffic noise mitigation are:
Definition of PPF
PPF is defined in NZS6806:2010(external link). PPFs in urban areas should be located at a distance of less than 100m from the edge of the road seal. PPFs in rural areas should be located at a distance of less than 200m from the edge of the road seal.
The assessment methodology for road particulates provides a risk rating of low, medium or high.
To determine the risk rating, use the following tables:
Risk factor/score |
0 |
1 |
2 |
3 |
4 |
5 |
Traffic |
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5-day annual average daily traffic (AADT) of HCVs* |
0 |
1–5 |
6–10 |
11–25 |
26–50 |
More than 50 |
Speed limit of HCVs* (km/h) |
No HCVs |
20km/h |
50km/h or greater |
|
|
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5-day AADT of LCVs** |
Less than 100 |
101–300 |
More than 300 |
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|
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Speed of LCVs** (km/h) |
Less than 50 |
50–70 |
Greater than 70 |
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|
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Receptors (within 80m of roadway) |
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Number of dwellings (houses/km) |
0 |
1 |
2–4 |
5–7 |
8–10 |
More than 10 |
Other locations where people are likely to be exposed (eg schools, marae, or hospitals) (sensitive locations/km) |
None |
1–2 |
3 or more |
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|
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Ecologically sensitive areas such as rare species habitats or wetlands (sensitive locations/km) |
None |
1–2 |
3 or more |
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|
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Horticultural sensitive areas such as fruit orchards (sensitive locations/km) |
None |
1–2 |
3 or more |
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|
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Site characteristics |
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Location of roadway |
Open plains or costal area |
Some land features likely to slow winds |
Inland enclosed valley |
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|
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Frequency of rain days (> 5mm) |
More than 2 events per week |
0–1 event per week |
Less than one event every 2 weeks |
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|
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Longevity of logging route use |
Not a logging route |
1–2 years |
Longer than 3 years |
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|
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Notes:
*HCV = heavy commercial vehicle (vehicle with gross vehicle mass greater than 3,500kg). Research report 590 uses HDV which has been amended to HCV to reflect sector terminology.
**LCV = light commercial vehicle (vehicle with a gross vehicle mass of less than 3,500kg). Research report 590 uses LDV which has been amended to LCV to reflect sector terminology.
Calculations use a five-day average of the AADT from Monday to Friday
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Total dust risk score |
Dust risk category |
Potential benefit from dust mitigation |
Action to be taken |
0–9 |
Low risk |
Little or no benefit from mitigation |
End of decision-making process |
10–19 |
Medium risk |
There may some benefit from mitigation |
Return to and repeat the ‘Site dust risk factors and scores’ with refined site-specific information |
20–38 |
High risk |
There is likely to be a benefit from mitigation |
Complete assessment of suitable mitigation options |
Waka Kotahi research report 590, Impacts of exposure to dust from unsealed roads, provides a methodology to assess the level of health risk associated with individual unsealed roads. Undertaking an assessment using this methodology produces a numerical output which can then be used to determine the relative level of risk of harm to human health from unsealed roads. Approved organisations can also reference the National Environmental Standards (NES) for particulates which cover road dust, vehicle emission particulates, tyre dust, etc.
Research report 590 uses HDV and LDV which have been amended to HCV and LCV to reflect sector terminology.
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