Appendix 6: Agrichemicals training
page 173 Regional Air Quality Plan for Taranaki Appendix VI: Training requirements for qualifications to apply agrichemicals page 174 Regional Air Quality Plan for
page 173 Regional Air Quality Plan for Taranaki Appendix VI: Training requirements for qualifications to apply agrichemicals page 174 Regional Air Quality Plan for
Development Capacity (NPS-UDC) was gazetted on 3 November 2016 and came into force 28 days later (1 December 2016). It requires local authorities to monitor and plan for housing and business development capacity in urban environments, to maximise wellbeing now and in the future. Under the Resource Management Act 1991 (the RMA), regional policy statements and plans must give effect to any national policy statement. The NPS-UDC contains provisions for areas defined as medium and
Advisory note: Rules 52-57; 59; 61 & 64 of this Plan do not apply to existing structures on river and lake beds associated with plantation forestry activities regulated under the Resource Management (National Environmental Standards for Plantation Forestry) Regulations 2017 (NES-PF). The NES-PF regulations prevail over these rules in relation to plantation forestry.36 Activity Rule Standards/Terms/Conditions Classification Notification Control/Discretion Policy Reference Use of existing
resource users against regional plans and consents. Compliance monitoring, (covering both activity and impact) monitoring, also enables the Council to continuously assess its own performance in resource management as well as that of resource users particularly consent holders. It further enables the Council to continually re-evaluate its approach and that of consent holders to resource management, and, ultimately, through the refinement of methods, and considered responsible resource utilisation
Environmental performance is concerned with actual or likely effects on the receiving environment from the activities during the monitoring year. Administrative performance is concerned with the Trust’s approach to demonstrating consent compliance in site operations and management including the timely provision of information to Council (such as contingency plans and water take data) in accordance with consent conditions. Events that were beyond the control of the consent holder and unforeseeable
plans; and maintains an overview of performance of resource users against regional plans and consents. Compliance monitoring, including impact monitoring, also enables the Council to continuously assess its own performance in resource management as well as that of resource users particularly consent holders. It further enables the Council to continually re-evaluate its approach and that of consent holders to resource management, and, ultimately, through the refinement of methods, to move closer
inasmuch as is appropriate for each discharge source. Monitoring programmes are not only based on existing permit conditions, but also on the obligations of the Act to assess the effects of the exercise of consents. In accordance with section 35 of the Act, the Council undertakes compliance monitoring for consents and rules in regional plans; and maintains an overview of performance of resource users against regional plans and consents. Compliance monitoring, including impact monitoring, also
the monitoring year. Administrative performance is concerned with GPL’s approach to demonstrating consent compliance in site operations and management including the timely provision of information to Council (such as contingency plans and water take data) in accordance with consent conditions. Events that were beyond the control of the consent holder and unforeseeable (that is a defence under the provisions of the RMA can be established) may be excluded with regard to the performance
Nationally Significant, Regionally Significant or Locally Significant. Four surf breaks – Waiwhakaiho, Stent Road, Backdoor Stent and Farmhouse Stent – are protected through the national-level New Zealand Coastal Policy Statement. Any new activities or developments at these breaks or‘nationally significant’ within the will not be allowed to haveSignificant Surf Area any adverse effects. Surf breaks classed as in the‘regionally significant’ Proposed Coastal Plan will also be
adverse effects occurring as a result of the exercise of any of SDC’s landfill consents, the Stratford landfill was not being managed according to the site management plan resulting a number of noncompliant aspects. The contouring at the site and a poorly constructed drain that has been noted in the 2015-2017 years resulted in an increased amount of ponding during the year under review. There was also ponding due to an overflowing water trough, widespread minor stock damage and a small amount of