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Coastal monitoring

Results are available to the public live on our website. What we find is that water quality of the region’s bathing beaches is generally high, with around 95% of samples meeting New Zealand health guidelines for recreational use. Occasionally water quality can be affected. This is particularly evident after heavy rain when a large volume of river water is discharged to the sea, carrying contaminants such as bird faeces, sediment, urban stormwater, agricultural run-off and so on. In some circumstances

Pātea Beach greenwaste monitoring 2020-2021

stabilisation will be done using green waste disposed of at the Patea transfer station. Patea Beach is an elevated site which for most of the time is dry. Rain that does fall on the site drains away at a very rapid rate. The site does not suffer from flooding from rain or tidal action, due to its elevation. page 4 Figure 1 Regional map showing the location of the Patea green waste site Figure 2 Aerial view of the Patea Beach green waste disposal area Patea River

Annual report 2013-2014

monitoring inspection and to take water samples. The weather was fine with 13 mm rain falling over previous 72 hours and the stream system was in low flow. A truck was discharging drilling muds and a digger was operating blending in sawdust at time of inspection. A discussion was held with the digger driver and site manager on the drainage issues at the top of the lower irrigation area and the installation of novaflo in a few swampy areas on the main irrigation flats. Discussion included the

TRC Bulletin - 25 July 2017

freshwater and coastal swimming spots last summer found higher-than-usual levels of bacteria, reflecting the season’s higher rainfall, the Policy and Planning Committee was told. More rain meant dairy effluent ponds discharged for longer and more frequently than usual, and clouds prevented the sun from breaking down bacteria. Even so, waterfowl continued to be the main culprits at the worst freshwater sites, the Waiwhakaiho River near Lake Rotomanu and the mouths of Te Henui Stream and Waimoku Stream.

RKM Piggery Annual Report 2022-2023

Again odour was very minimal. No visual environmental impacts downstream of the discharge point to the Tawhiti Stream observed at any time during the financial year. Effluent collection points within piggery viewed during all inspections. Found to be in good condition, with no signs of spills or overflows even after heavy prolonged rain periods. Bunding functioning well. During the 8th May inspection a burst underground effluent pipe between the southern sheds was brought to the attention

Operations and Regulatory Committee Agenda November 2022

Rules 35 and 36 of the RFWP do not include any matters of control that expressly allow for the consideration of matters such as those expressed in the NPS-FM objective. Given that the Council can only consider policies that relate to the matters over which the Council has reserved control through the plan itself, the Council is unable to take into account matters that fall outside this scope. In terms of the notification assessment and when deciding whether a person is an affected person, the

Pātea Beach greenwaste monitoring 2019-2020

long and 25 m wide, and is shown in Figure 2. In the 2016-2017 monitoring period, issues were found with unacceptable wastes being exposed by coastal erosion. This resulted in the site being closed to the public in 2017. Any further dune stabilisation will be done using green waste disposed of at the Patea transfer station. Patea Beach is an elevated site which for most of the time is dry. Rain that does fall on the site drains away at a very rapid rate. The site does not suffer from …

Colson Road Landfill Monitoring Programme Annual Report 2020 2021

Bibliography and references 103 Appendix I Resource consents held by NPDC List of tables Table 1 Consents held by NPDC that relate to the Colson Road landfill 13 Table 2 Summary of monitoring activity for 2020-2021 14 Table 3 Chemical analysis of Colson Road landfill leachate 40 Table 4 Results of analysis of under liner drainage for the year under review. 42 Table 5 Results of rain event monitoring – discharge and Puremu Stream samples, 19 August 2020 47 Table 6 Results

Colson Road Landfill Monitoring Programme Annual Report 2020 2021 2990010

Bibliography and references 103 Appendix I Resource consents held by NPDC List of tables Table 1 Consents held by NPDC that relate to the Colson Road landfill 13 Table 2 Summary of monitoring activity for 2020-2021 14 Table 3 Chemical analysis of Colson Road landfill leachate 40 Table 4 Results of analysis of under liner drainage for the year under review. 42 Table 5 Results of rain event monitoring – discharge and Puremu Stream samples, 19 August 2020 47 Table 6 Results