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Malandra Downs consent monitoring 2019-2020

held by Malandra Downs Ltd List of tables Table 1 Summary of consents held by the company during the period under review 5 Table 2 Summary of performance for consent 7374-1.4 9 Table 3 Evaluation of previous environmental performance over time 10 page ii List of figures Figure 1 Regional map showing the location of the site 4 Figure 2 Aerial image of the Malandra Downs property disposal area 4 page 1 1 Introduction 1.1 …

TRC Interim Technical Memorandum Macroinvertebrates NOF Baseline State September 2023

FMU-based baseline states (expressed as percentages of stream lengths) for the macroinvertebrate numeric attribute states are shown in Table 6. Maps of stream widths under each NOF band for all three numeric attribute states are in Figure 9, Figure 10 and Figure 11. Table 6: FMU-based baseline states for the macroinvertebrate numeric attribute states (MCI, QMCI, ASPM) expressed as percentage waterway length in each FMU within each NOF attribute band. NOF Band No. sites MCI

Waitaha Catchment Annual Report 2020-2021

deployment period 66 Figure 19 Aerial view of Woodwards site and fire pit location 70 Figure 20 Aerial map showing site and sample locations in the Waitaha Catchment (TBS Coatings now SRG Global) 77 List of photos Photo 1 View of AICA (NZ) site 11 Photo 2 C & O Concrete site 19 Photo 3 Stockpiled material to be blasted on Energyworks site, March 2020 22 Photo 4 Intergroup Ltd oil treatment facility 30 Photo 5 Taranaki Sawmills site in the Waitaha Catchment 57

1aFurtherinformation

map identifying the location of stormwater channels including Stormwater flows from each pad, sediment traps, sediment ponds and flow paths. Refer to Appendix F - Stormwater channels 6. Use ground water data to provide an assessment of the impact on ground water as a result of irrigation to ground Refer to Appendix X - Ground water sampling of monitoring bores 7. Use soil sample data to provide an assessment of the impact on soil quality as a result of irrigation to

Appendix 1

page 73 6 Appendices 6.1 Appendix I: Taranaki erosion assessment sites G ibb(1978) (excel file: #640813) NZ Map Grid NZTM Northing Easting Northing Easting Years Rate 123 Patea 6158000 2637600 5596277 1727558 1872-1905 1.82 Patea 1905-1976 -0.85 124 Patea 6158000 2637300 5596277 1727258 1872-1905 -1 Patea 1905-1939 1.74 Patea 1939-1976 2.05 125 Power House Road 6162900 2631500 5601174 1721456 1901-1976 -0.05

Taranaki By Products Air and Water Monitoring Programme Annual Report 2020 2021

2001-2021 50 Figure 25 Long term NNN monitoring GND2226 2011-2021 51 Figure 26 Burial groundwater monitoring well locations 52 Figure 27 Taranaki By-Products biomonitoring site locations map 56 Figure 28 Location of biomonitoring sites in the Inaha Stream and an unnamed tributary of the Inaha Stream in relation to discharges from the Taranaki By-Products plant, with taxa number, MCI scores and SQMCI scores for each site. The orange line outlines the irrigation areas around the

Annual report 2016-2017

performance over time 22 List of figures Figure 1 Site location and regional inset 5 Figure 2 Site map and application areas Vanner Landfarm with BTW soil sample transects 11 Figure 3 Area F8 March 2015 North West projection 12 Figure 4 Area F8 November 2015 North West projection 13 Figure 5 Areas F9 and F10 November 2015 North West projection 13 Figure 6 Area F10 towards Area F9 May 2016 South East projection 14 Figure 7 Area F9 May 2016 South East projection 14

Pātea Beach greenwaste monitoring 2019-2020

Table 3 Evaluation of environmental performance over time 11 page ii List of figures Figure 1 Regional map showing the location of the Patea green waste site 4 Figure 2 Aerial view of the Patea Beach green waste disposal area 4 List of photos Photo 1 Southern edge of site 15 June 2020 7 Photo 2 Overall site photo 15 June 2020 7 page page 1 1 Introduction 1.1 Compliance monitoring programme reports and the Resource …

TRC Technical Memorandum Macroinvertebrates 20 June 2023

scale and can be interpreted as applying to a section of river segments in an FMU, rather than a specific monitoring site. FMU-based baseline states (expressed as percentages of stream lengths) for the macroinvertebrate numeric attribute states are shown in Table 6. Maps of stream widths under each NOF band for all three numeric attribute states are in Figure 9, Figure 10 and Figure 11. Table 6: FMU-based baseline states for the macroinvertebrate numeric attribute states (MCI,