marine outfall discharge on the local intertidal communities were not evident from the 2022
summer survey results. Two potential impact sites had greater species richness and diversity results than the
control site, Waihi Reef, while the other site (350 m NW of the outfall) had recently experienced a natural
rock fall event and was buried by large boulders and other debris. Seven years ago, the site 200 m SE of the
outfall was also buried during a rock fall event. Species richness and diversity
controls as to how it is to be managed.
Implementing much of the NPS-HPL will fall to territorial authorities through their
District Plans.
13. Set out below is a summary of the overall policy direction to be implemented by
Councils:
13.1. Restrict rezoning of highly productive land, but allowing tier 1 and 2 territorial
authorities to consider rezoning subject to requirements of the NPS-HPL.
13.2. Avoid rezoning of HPL for rural lifestyle and avoid subdivision generally of HPL,
is less than 1 % of the allocated take through resource
consents.
Rain water is also collected and stored for stock and domestic use.
There are 21 rural water supply schemes in the region that serve stock, domestic water
and in some cases industrial use and mean farmers do not have their own intake
systems. In this case the
take is concentrated at
one point rather than
being spread through a
catchment.
Figures 1 and 2 show
rural water supply
PM2.5 concentration 17
Figure 13 Comparison of the diurnal variation in PM2.5 concentration during different seasons 17
page
iii
Figure 14 Pearson’s correlation matrix of PM2.5 with different meteorological variables 18
Figure 15 Pollution rose for entire monitoring period 20
Figure 16 A comparison of wind roses for days falling into different PM2.5 air quality categories 20
Figure 17 Daily time series of PM2.5 for the monitoring period. 21
Figure 18 …
year-round monitoring and
compliance, even at times when it would
be foolhardy to swim because of weather
and/or dangerous currents and flows,
imposes significant costs but with little
purpose or community benefit.
� Proposed broad-brush national
requirements for excluding stock from
waterways fall short of what is actually
required to reduce faecal contamination,
and risk undermining successful and
proven local initiatives such as Taranaki’s
award-winning riparian
the later (eastern) portions.
The most significant structures/components within the Race and lake are summarised within
Table 2 and are discussed further as follows.
Table 2: Race and Lake Structures/Components
Component Race Chainage (m) Comment
Manganui River 0 Upstream end of race.
Intake Structure 90 Controls abstraction from the Manganui
River into race.
Tariki Weir 720 Weir assists race flow measurements.
Drop Structure 1270 Race invert level falls by
three leachate 23
Table 3 Results of analysis of under liner drainage 23
Table 4 Chemical analysis of the Manganaha Stream 24
Table 5 Chemical analysis of the Puremu Stream, sampled on 7 September 2011 25
Table 6 Chemical analysis of the Puremu Stream, sampled on 16 March 2012 26
Table 7 Results of rain event monitoring samples taken on 16 May 2012 28
Table 8 Results of rain event monitoring samples taken on 21 June 2012 29
Table 9 Chemical analysis of Colson Rd
14 of the Resource Management Act stipulates that no person may take, use,
dam or divert any water, unless the activity is expressly allowed for by a resource
consent or a rule in a regional plan, or it falls within some particular categories set
out in Section 14.
Approximate
site
boundary
Unnamed tributary
NNNN
page
7
As Taranaki Ventures Limited was unable to estimate the rate or volume of the take,
and as such, might exceed the limits of the
Policy and Planning Agenda October 2024
Revised Assessment of Environmental Effects (AEE) - June 2020