K Raine N W Walker C S Williamson Apologies Notification of Late Items Item Page Subject Item 1 4 Confirmation of Minutes Item 2 16 Consents and Regulatory Committee Minutes Item 3 22 Policy and Planning Committee Minutes Item 4 30 Executive, Audit and Risk Committee Minutes Item 5 35 Remuneration Authority Information Paper: Determining the Remuneration of Local Government Elected Members - Oversight of Issues; and Local Government Members (2018/19)(Local
Operations and Regulatory Agenda 30 April 2024
the treatment of gas at the McKee LPG Plant and the Mangahewa Extraction Train 2 (MET2). July 2009 June 2021 June 2039 1.3.1 Water abstraction permit Section 14 of the RMA 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. The Company holds water abstraction permit 1226-1 to take water from
prepared as a separate appendix. This report deals only with historic heritage located in or on the boundary of the Coastal Marine Area. The Coastal Marine Area is defined as the area seaward of Mean High Water Springs (MHWS) to the 12 nautical mile limit, and in river mouths as defined by the Taranaki Coastal Plan, Appendix 2: Coastal marine boundaries at river mouths. Identification and protection of archaeological sites located on the landward side of these boundaries falls within the
prepared as a separate appendix. This report deals only with historic heritage located in or on the boundary of the Coastal Marine Area. The Coastal Marine Area is defined as the area seaward of Mean High Water Springs (MHWS) to the 12 nautical mile limit, and in river mouths as defined by the Taranaki Coastal Plan, Appendix 2: Coastal marine boundaries at river mouths. Identification and protection of archaeological sites located on the landward side of these boundaries falls within the
environmental sensors $5,000 per year In stream temperature monitor $300.00 per year Portable (12v) groundwater pump $120.00 per day Suspended particulate sampler $30.00 per hour Vandorn sampler $50.00 per day Black disc $20.00 per deployment Bladder pump $110.00 per day Calibration test equipment $100.00 per hour Disposable bailer $20.00 per sample Peristaltic pump $60.00 per day Groundwater level logger $180.00 per year Rain gauge calibration $300.00 per deployment Automatic water quality
year In stream temperature monitor $300.00 per year Portable (12v) groundwater pump $120.00 per day Suspended particulate sampler $30.00 per hour Vandorn sampler $50.00 per day Black disc $20.00 per deployment Bladder pump $450.00 per day Calibration test equipment $100.00 per hour Disposable bailer $20.00 per sample Peristaltic pump $120.00 per day Groundwater level logger $180.00 per year Groundwater probe $100.00 per day Rain gauge calibration $300.00 per deployment Automatic water
managed, and the tip face appeared stable. No cracking or slumping was evident on either the fill area or the tip face. The pre-fill gully was well grassed with no sign of sediment runoff. The stormwater drains were grassed and contained minor amounts of stormwater following heavy rain the previous day. The stormwater ponds were moderately full, and the final pond was discharging at a trickle flow. There was no visible effect noticeable in the receiving waters downstream of the discharge. Silt
Settlement (13 December 2016) 11 January 2017 Conditions were fine with a moderate westerly wind. It had rained in the catchment in the two days preceding the inspection. The camp was reasonably quiet during the inspection, with seven camping parties present on site. There was no weed coverage on the western filter bed and low coverage on the eastern bed. There was a small amount of ponding on the western bed (<5% of the surface) and no ponding on the eastern bed. There was a noticeable
summary of historical bacteriological results from January 1993 to January 2013 is presented in Table 3. The results of the bacteriological monitoring undertaken during the 2013-2014 summer monitoring period are presented in Table 4. Although it was not raining on the morning of sample collection (9 January 2014) there had been heavy rainfall overnight which is reflected in the high faecal indictor bacteria counts obtained (Table 4). Table 3 Summary of previous bacteriological results