guidelines prepared by the Ministry for the Environment (MfE) and the Ministry of Health (MfE, 2003).
Thirteen samples were collected at every monitored beach under dry weather conditions for State of the
Environment Monitoring (SEM) purposes, except when it was unsafe to do so. At eight of the ten coastal
sites monitored every year, an extra eight samples were collected to satisfy MfE requirements for the
number of seasonal samples to be used for grading purposes and to provide more
the
Council’s contingency plan and identifies:
Production facilities characteristics;
Spill potential and risks;
Sources and causes of spills;
page
Page 2 of 172 Taranaki Regional Council Marine Oil Spill Contingency Plan
Annex 4 Issue 3 October 2020 – Doc# 1099113
Spill prevention measures;
Potential hydrocarbon spills;
Spill consequences and priorities;
Modelling of off-shore oil spills;
Weathering of oil on shorelines; and
Potential
Zinc and copper monitoring data for dry weather Mangati
Stream water 160
Table 67 Numbers of taxa and MCI values recorded in previous
surveys in the Mangati Stream, together with results of the
December 2014 and February 2015 surveys 161
List of figures
Figure 1 Mangati catchment 3
Figure 2 Stormwater drainage systems in the industrial area of
Mangati catchment 10
Figure 3 Location of consent holders and surface water monitoring
sites 11
Figure 4 Location of
Garden. At
this time of the year, in late February, it
is this garden that shines at Pukeiti. The
summer perennials are still lingering, and
the autumn flowering ones are coming
into bloom. The Trust put a considerable
sum of money towards the establishment
of this garden, named for Robert Keiller,
an ex-Board member and a generous
donor to the Trust of both money and
expertise. It’s nice to see it looking so
good and the weather was lovely for our
stroll. Back at The Lodge we sat down
inspection and 27 mm of rainfall had been recorded over the previous week at the
Brooklands Zoo weather station. Pond SV8000 contained 900 m3 of stormwater, while SV9000 was full at
275 m3 and had overtopped into SV9100. The ponds had a clear appearance with some wind-blown pollen
with no sheen or odours noted. The incinerator was still offline, but was expected to be recommissioned in
October. Site housekeeping was excellent. All roadways and stormwater catchments were clean.
5 November 2020 …
suitable to meet its purpose"; and
(e) the production of the SC 18 report should not be at TRC's discretion, and
that SC 18(a) is useful for clarity and completeness.
3.6 The TRC officers agree with:
(a) SC 19 providing for total suspended particles (TSP) monitoring;
(b) not using 1-hour averages for SC 21(vii)(a)(i); and
(c) including a consent condition requiring a weather station, with minimum
parameters.
3.7 A marked up version of the
associated with the FECB plume from West
Bore 22
Figure 9 Total nitrogen concentration in groundwater associated with the FECB plume from East Bore 23
Figure 10 Total nitrogen concentration in groundwater associated with the granulator plume from Bore
25 24
Figure 11 Location of deposition gauge sites 26
Figure 12 Wind-rose for Hawera weather station during deployment of deposition gauges, 28 February
to 19 May 2022 26
Figure 13 Sampling site for ambient gas monitoring at ammonia
from the east side of the site) 6
Photo 4 Central Landfill, 3 July 2018 – northern side of southern gully 8
Photo 5 Central Landfill, 3 July 2018 – southern side of southern gully 8
Photo 6 Central Landfill, 12 June 2019 – southern side of southern gully after stabilisation 9
Photo 7 Central Landfill, 12 June 2019 – eastern side 9
Photo 8 Central Landfill, 12 June 2019 – along northern side of northern gully 10
Photo 9 Central landfill weather station, September 2017 41
Remediation New Zealand Ltd Uruti Composting Facility Monitoring Programme Annual Report 2020 2021
conditions and often where
saltwater penetration occurred.
Additional sampling (in accordance with the MfE, 2003 guidelines) at two principal usage
sites (Lake Rotomanu and Waiwhakaiho River) coincided on few occasions with wet
weather conditions and resulted in slight increases in the median bacteriological number at
one site and no change at the other. Few additional exceedances of limits occurred at the
river site and more at the lake site where poorer bacteriological quality followed wet