compliance monitoring. The inspection was undertaken with
sampling of surface waters and soil. At the time of inspection approximately 11 mm of rain had fallen at the
site overnight. This had resulted in the surface being damp and the Haehanga Stream and associated
unnamed tributaries being turbid and slightly elevated. Weather conditions were still, warm with total cloud
cover. Rain was falling intermittently throughout the sampling run. The inspection found that the paunch
pond had approximately
Taranaki Regional Council meeting agenda May 2020
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
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
Cheal Petroleum Limited Deep Well Injection Annual Report 2023-2024
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