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North Taranaki kaimoana survey 2000-2001

that the reefs had become more polluted (than by the river-borne wastes) since the marine outfall was installed (1978). Evidence was given of “sick mussels” on Orapa Reef, which were reported to be fragile and to crumble when walked on or even squeezed by hand. It was accepted by the Tribunal that a combination of coastal alignment and prevailing winds was responsible for driving Waitara sewage and wastes further east along the coast, even as far as Motunui.

Pole planting - maintenance

firm, not loose Blanking Not all of the poles planted will strike. 100% survival of a planting is rare; 90% after the first year is a good survival rate. Sometimes due to adverse conditions such as cattle damage, possum browse or summer drought, survival drops to 50% or less. Where mortality is heavy, it’s essential to blank (re- plant) next winter. If this isn’t done, tree spacing won’t be sufficiently dense for roots to anchor the soil, and Fig. 2 A pruned stand of poplars slips or

Investigation of air quality arising from flaring of fracturing fluids

has focused on the nature of potential effects arising from the use of hydraulic fracturing (HF) fluids within production enhancement activities, as these fluids include compounds additional to those used in drilling. These compounds will include biocides, gelling and gel-breaking agents, inert proppants such as sand or microscopic ceramic beads, and ‘slicking’ agents. Normal exploration practice is to separate the recovered fluids from the entrained hydrocarbon gas. However, under

Annual report 2014-2015

Kaponga, or Patea treatment systems on adjacent receiving waters were recorded in late summer-autumn under low flow conditions during the monitoring period (at which time the Waverley system had been desludged with bio-bugs, the Manaia system had been upgraded with the addition of two wetlands, the Kaponga pond subsurface discharge rate was very low and receiving water dilution very high) in early winter under higher flow conditions (when the Patea upgraded ponds system discharged continuously),

Annual report 2016-2017

presents recommendations to be implemented in the 2017-2018 monitoring year. A glossary of common abbreviations and scientific terms, and a bibliography, are presented at the end of the report. 1.1.3 The Resource Management Act 1991 and monitoring The RMA primarily addresses environmental ‘effects’ which are defined as positive or adverse, temporary or permanent, past, present or future, or cumulative. Effects may arise in relation to: a. the neighbourhood or the wider community around

Agenda

procedural or process changes. It represents the second phase of the Government’s resource management reform programme. Major changes to the RMA arising from enactment of the Resource Legislation Amendment Act concern national level policy making and direction, regional and district plan making and the resource consents process. Staff will be developing an implementation plan to give effect to the Resource Legislation Amendment Act 2017 over the coming months. Recommendations That the

Bus Transport in Taranaki

Competencies: • Relating to others • Thinking Essential Skills: • Communication • Information gathering • Work and study Values: • Equity • Community and participation • Respect Make a list of people you could invite to your class to talk to you. Your list could include: 1. Someone from your local bus depot or local bus driver. 2. Taranaki Regional Council Transport Services Manager. 3. New Plymouth District Council ‘Let’s Go’

SEM groundwater2017 web

sites. The main factor influencing E.coli concentrations measured across the network is well construction, and inadequate wellhead protection or isolation at some monitored locations. Drilled and screened wells installed specifically for monitoring purposes recorded significantly lower numbers of E.coli detections and MAV page exceedances in comparison to dug and/or unlined wells. These results are indicative of differing E.coli transport pathways by well

Groundwater quality report 2016-2017

sites. The main factor influencing E.coli concentrations measured across the network is well construction, and inadequate wellhead protection or isolation at some monitored locations. Drilled and screened wells installed specifically for monitoring purposes recorded significantly lower numbers of E.coli detections and MAV page exceedances in comparison to dug and/or unlined wells. These results are indicative of differing E.coli transport pathways by well

Agenda

http://www.mfe.govt.nz/fresh-water/national-policy-statement-freshwater-management/2017-changes annotation http://www.mfe.govt.nz/fresh-water/national-policy-statement-freshwater-management/2017-changes http://www.mfe.govt.nz/fresh-water/national-policy-statement-freshwater-management/2017-changes page Changes in the NPS-FM require regional councils to monitor ecosystem health, maintain or improve overall water quality, manage nitrogen and phosphorus, consider economic wellbeing in freshwater decision-making and plan (with local iwi) for Te Mana o te Wai. Where there