(Chairman) M J Cloke M G Davey M P Joyce D L Lean (Deputy Chairman) C L Littlewood M J McDonald D H McIntyre B K Raine N W Walker C S Williamson Apologies Councillor D H McIntyre Notification of Late Items Item Page Subject Item 1 3 Hearing of Submissions on the Consultation Document for the 2018/2028 Long-Term Plan List of Submitters who wish to be heard Submissions received on the 2018/2028 Long-Term Plan Submissions 1-19 Submissions
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
The site is approximately 2.4ha in size and comprised of cutover semi-coastal Tawa, kohekohe, rewarewa, hinau, podocarp forest remnants on hill slopes, flat land and stream terraces. The remnants are of a native forest type that is classified as 'Chronically Threatened' in Taranaki and falls within 'Acutely Threatened' Land Environment (LENZ) F5.2b. Remnants such as this provide important habitat for common, rare and threatened species. Barrels Creek contributes good connectivity with other
year. The volume of waste to landfill peaked at 65,257 tonnes in 2013-2014 What we know and reduced significantly from 2015 when all three district councils aligned their recycling collection services and created a regional materials recovery facility in New Plymouth to process recyclables. In 2014, the waste to landfill in the region per person was 595kg falling to 311kg per person in 2020-2021. In Stratford and South Taranaki, there has been additional
contaminants. Only a pilot flare was operating. The API separator and all bunds and ring drains were clear. Everything was satisfactory. 1 November 2012 The site was inspected during fine weather with no significant rain having occurred for a week or more. The skimmer pits were clear and not discharging. The ring drains were free of contaminants and a frog was in residence at the top end of the drain. Some flaring was being undertaken, but this was very minor and no downwind effects were noted. The
monitoring bore GND2103 varied in response to abstraction from GND2010. When abstraction volumes increase over the summer months the groundwater levels fall in response and during the winter months, when abstraction decreases, the groundwater levels recover. In summary, groundwater level monitoring data gathered by the Council does not indicate any long-term reduction in shallow or deep groundwater levels as a result of the abstraction authorised by consent 7470- 1.2. As such, the potential for