REGIONAL XPLORER
STDC, SDC and TRC collaborate to
provide regional geographic
information system (GIS) services
to the community via Taranaki
Regional Xplorer.
Regional Xplorer is a free web-
based mapping and local authority
information service. Users have
page
18
access to property information, infrastructure services, environmental services, planning
information and aerial photgraphy.
Benefits
Cost-savings from creating and maintaining a single system.
Figure 4 Location of sampling sites in relation to the Eltham
wastewater treatment system 20
page
iv
Figure 5 Aerial location map 21
Figure 6 Trend in MCI at the Mangawhero Stream site downstream
of the outfall (MWH000490) 28
Figure 7 Trend in MCI at the Mangawhero Stream site upstream of
the outfall (MWH000380) 28
List of photos
Photo 1 Overflow retention pond, 21 July 2011 8
Photo 2 Replacement aerator, June 2013 14
page
1
consent 43
4. Recommendations 44
Glossary of common terms and abbreviations 45
Bibliography and references 47
Appendix I Resource consents held by Trustpower Ltd in relation to the Patea HEPS 1
Appendix II Lake Rotorangi Hazard Maps 1
page
ii
List of tables
Table 1 Summary of breaches of flow rise and recession rates in the 2011-2014
period 17
Table 2 Summary of lake levels in relation to consent conditions 20
Table 3 Reports submitted to
TRC Guidelines for the Control of Drilling Wastes 50
Appendix IV Schrider Landfarm Results 545
Appendix V Maps of Landfarmed Sites 58
Appendix VI Spence Road Landfarm results 60
Appendix VII Agknowledge landfarm review report 63
page
iii
List of tables
Table 1 Summary of landfarming consents covered by this report 5
Table 2 Soil samples taken on 12 June 2013 at Geary Landfarm 12
Table 3 Origin supplied soil results from the Geary
adequately capture the “true” variability of water
quality state. Secondly, lack of spatial representation arises from the limited spatial coverage of the existing
monitoring network. Each type of uncertainty is identified and assessed in the following sections.
Maps of the site-specific baseline attribute states for ammonia, nitrate, and DRP concentrations at each
state of environment monitoring site are presented in Figure 1, Figure 2 and Figure 3, respectively.
page
interventions summary table 16
Table 4 Individual performance for all irrigation consent holders 18
List of figures
Figure 1 Percentage of water irrigation allocation per activity in the Taranaki region 3
Figure 2 Source of water for irrigation in Taranaki during the 2021-2022 period 3
Figure 3 Total consented water abstractions – distributed by activity 2021-2022 3
Figure 4 Pasture irrigation zones and locations of consented irrigation in Taranaki 4
Figure 5 Distribution map
3953-3 43
Table 16 Chemical analysis of samples taken in the vicinity of the Patea closed
landfill site 48
Table 17 Summary of performance for Patea closed landfill stormwater and
leachate consent 0427-3 49
Table 18 Summary of performance for Patea closed landfill air discharge
consent 4636-2 50
Table 19 Summary of performance for Patea closed landfill stormwater and
sediment consent 7268-1 51
List of figures
Figure 1 Regional map of STDC landfills 5
Figure 2 Eltham
site activity .................................................................................................................... 7
3.1 Site map .................................................................................................................................................... 7
3.2 Description of the site activity ................................................................................................................ 8
3.3 Composting operation
located around the edge of Beatrix Bay. Backbones (surface structures) on
the 37 marine farms span approximately 8.5 km (33%) of total shoreline
length at sea level (but more under water). Approximately 85% of the surface
area (2,000 ha) of Beatrix Bay is not occupied by mussel farms.
[10] At the hearing, a map was produced showing Beatrix Bay and
the King Shag foraging in detail. It illustrates the necklace arrangement of
the granted marine farms, together with the dates of the grant of those
usefulness for monitoring purposes is studied as at
the moment they are uncapped and opened to the surface. It is possible that the water
samples from the wells encountered may be representative of different water-yielding
zones within the same aquifer; however, the data that could be obtained from them could
be used as up-gradient baseline conditions.
Unfortunately there is not enough topographical information available to determine
groundwater flow-lines and potentiometric groundwater maps