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Annual report 2013-2014

variation): to divert water from the river into Lake Mangamahoe 66 Table 26 Summary of performance for consent 2054: to dam the Mangamahoe Stream for HEP generation purposes 67 Table 27 Summary of performance for consent 4886: to erect and maintain structures in, and dam, the Mangamahoe Stream for the formation of Lake Mangamahoe for HEP generation purposes 67 Table 28 Summary of performance for consent 4887: to erect and maintain structures associated with the diversion of Waiwhakaiho

Inventory of coastal areas of local or regional significance in the Taranaki region

136 62 Patea Beach and River Mouth 138 63 Waitore Swamp 140 64 Whenuakura Estuary 142 65 North and South Traps 144 66 Waipipi Dunelands 146 67 Waverley Beach 148 68 Waitotara Estuary and Dunes 150 69 Waiinu Beach and Reef 152 page 15 page 16 Mokau-Mohakatino (Epiha Reef) Number: 1 GPS: 2649936E 6274891N General description Epiha reef is a large intertidal reef system between Mokau and Mohakatino Rivers, just north of the Waihi Stream. It is the most extensive

iventory of coastal areas significance taranaki

136 62 Patea Beach and River Mouth 138 63 Waitore Swamp 140 64 Whenuakura Estuary 142 65 North and South Traps 144 66 Waipipi Dunelands 146 67 Waverley Beach 148 68 Waitotara Estuary and Dunes 150 69 Waiinu Beach and Reef 152 page 15 page 16 Mokau-Mohakatino (Epiha Reef) Number: 1 GPS: 2649936E 6274891N General description Epiha reef is a large intertidal reef system between Mokau and Mohakatino Rivers, just north of the Waihi Stream. It is the most extensive

Annual report 2014-2015

3.4 Recommendations from the 2013-2014 Annual Report 67 3.5 Alterations to monitoring programmes for 2015-2016 67 4. Recommendation 68 Glossary of common terms and abbreviations 69 Bibliography and references 71 Appendix I Resource consents held by NPDC for Colson Road landfill Appendix II Biomonitoring reports for Colson Road landfill Appendix III Groundwater Results page iii List of tables Table 1 Summary of the resource consents held by NPDC 6

Annual report 2012-2013

(Section 2.1), the Company also provided results of their own analysis of KW-2 injectate samples. The results of the analyses are presented below in Table 8. Table 8 Range of contaminants in KW-2 injectate samples (2012-2013) Parameter Unit Number of samples Maximum value Minimum value Mean value pH pH units 36 7.5 6.7 7.0 Salinity g/m3 36 25,800 9,100 19,806 Chloride ppm 36 11,125 5,652 9,711 Total suspended solids g/m3 36 67 24 43 Total dissolved solids g/m3 34 33,560

Mangati catchment consent monitoring 2018-2019

site inspections, 67 discharge samples, 13 receiving water samples, 16 macroinvertebrate samples, several point source/ambient air particulate surveys, discussions with site operators over site management, and odour surveys. Historically, chemical and biological monitoring results for the Mangati catchment have shown there to be a two-stage reduction in water quality, one below the main stormwater outlet from Tegel Foods poultry processing plant, the other below the industrial drain which