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Concrete Batching Plants Annual Report 2022-2023

Fletcher Concrete (For a copy of the signed resource consent please contact the TRC Consents department) page Water abstraction permits 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. Permits authorising the abstraction of water are issued by the Council under

Schedules of charges 2019/2020

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

Schedules of charges

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

Annual Report 2016-2017

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

Annual report 2016-2017

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

Annual report 2013-2014

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

Irrigation consent monitoring 2018-2019

Waitotara. The remainder or irrigators are generally located inland, between Inglewood and Eltham. 1.1.7 Irrigation systems In general there are two types of irrigation methods; surface and pressurised. The majority of irrigation systems currently in operation in the province fall in to the pressurised category. Pressurised systems can be further differentiated based on the method of operation and equipment used. A summary of the systems encountered in the region is given below. K-line and

Irrigation consent monitoring 2017-2018

irrigation methods; surface and pressurised. The majority of irrigation systems currently in operation in the province fall in to the pressurised category. Pressurised systems can be further differentiated based on the method of operation and equipment used. A summary of the systems encountered in the region is given below. K-line and long-lateral types – Impact sprinklers mounted on moveable laterals (Photo 1) These are the most common systems found in the region, as they are a low cost

Appendix Y - assessment of odour effect

2.4 Irrigation to Land of Leachate Situated north of the compost and vermiculture operations is a series of leachate ponds that collects run-off from these activities. In addition to the collection of leachate and stormwater that falls in the composting area, wash down water from the truck wash is also collected in this pond; which further dilutes the compost leachate. Figure 2 highlights the area in purple, where water from these ponds are irrigated to land. Typically irrigation