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Annual report 2016-2017

and K. M. Wards, trading under the name Waikaikai Farms Ltd. The predominant land use was previously dairy farming. The site location is detailed in Figure 1. The predominant soil type has been identified as black loamy sand and vegetation growth consists mostly of pasture. Test pitting and the logging of boreholes on site indicated a relatively shallow water table. Test bores were augured to 10 m both around the waste holding pit area and to the south-western site boundary, revealing

24Furtherinformation AppendixT

L TO Page 23 Document no: RU-P-650-01 OO-A Revision No V1.13 Date: 7-9-2018 Controller Colin Kay page Integrated Management System Manual Appendix B Uruti Site Reporting Templates e Document No. Document/Form Name RU-F-640-051 Legal Compliance Obligation (Monthly) T-620-001 Standard Operational Report (Monthly) RU-F-680 Uruti Irrigation Log RU-F-681 Uruti Weekly Bore & Stream Sampling Log RU-F-682 Uruti Inward Goods Log RU-F-682 Uruti Weekly Dairy

marfellplanjuly09

towards the end of the landfill’s life. Some information exists with respect to the amount of soil cover over the waste. Soil borings carried out by NPDC over the upper two levels in April 1995, possibly associated with planning the 1995 playing field upgrade, show cover depths of between about 600 mm and 1 m. Waste is located perhaps as little as 200 or 300 mm below the lowest parts of the BMX track, but is otherwise a metre or more down, while photographs of the excavation for the

Fact sheet 4: Checklist

timber from old sheep dip sites in domestic gardens. Avoid harvesting fruit, mushrooms and vegetables from the vicinity of a sheep dip site. Avoid harvesting ‘wildfoods’ such as watercress, tuna (eel), trout, waterfowl etc below any dip discharge outfall where it enters a wetland, swamp or drain. Be aware that discharges from sheep dips in coastal areas can cause residues in shellfish. Water supplies Do not install a bore or well in an area where there may be contaminated

Form 260: Land Use Consent

(including rivers, lakes, ponds and streams) o Any wetlands o Any subsurface drainage o Any bores or soakholes (these areas maybe within or outside the boundary of the farm)   Nature of the terrain surrounding the feedlots, including slope (flat, rolling, steep) and direction of slope  A north symbol (oriented to the top of the page if possible) and scale bar page 06/22 - # 2714652 Page 8 of 14 5.2. In addition to the map or aerial image you

OMV NZ Pohokura Production Station Annual Report 2022-2023

maintain a culvert in an unnamed tributary of the Waipapa Stream for State Highway 3 road widening purposes December 2003 2033 6577-1 To install, construct and maintain a water bore for horizontal directional drilling purposes April 2005 2023 page 6 Consent number Purpose Granted Expiry 10598-1 To discharge emissions to air from flaring of hydrocarbons and miscellaneous emissions on Pohokura Platform B September 2018 2033 10683-1 To discharge

Report 2013-2015

the well, while post-fracturing reports confirm details of what actually occurred. The specific range of information required in each report is stipulated in the conditions of the resource consents. 1.4.4 Chemical sampling The primary component of the monitoring programme implemented by the Council was the collection and analysis of samples from an existing groundwater well and a specifically installed groundwater monitoring bore in the vicinity of the Cheal-C wellsite. In

Service stations

containment device should be installed where practical. Underground fuel storage All underground tanks used for the storage of hydrocarbon products or wastes must be regularly monitored for signs of material escape. Regular bore monitoring for free phase hydrocarbon should be carried out. There is less need to monitor double skinned tanks. Remember: • Even small quantities of seemingly harmless materials can damage the environment • It is illegal to cause stormwater pollution •

TRC Technical Memorandum Water Quantity September 2023

and streams are generally accessible when water supply is needed. Where available, surface water supplies are typically preferred to groundwater sources, given they can be obtained at a much lower capital cost. The low yields from Taranaki aquifers often mean that multiple bores are required to supply high demand uses, making the use of groundwater uneconomic. Surface water systems are generally able to sustain the majority of current water demand in Taranaki. Notwithstanding