Offset and Compensation Plan

Total Page:16

File Type:pdf, Size:1020Kb

Offset and Compensation Plan Matawii Water Storage Reservoir – Offset and Compensation Plan 24 July 2020 puhoistour.co.nz PUHOI STOUR LIMITED LYSAGHT BUILDING | 101 PAKENHAM STREET AUCKLAND 1010 Matawii Water Storage Reservoir – Offset and Compensation Plan Prepared by Puhoi Stour Ltd in association with Tonkin & Taylor Ltd. David Pickett, Justine Quinn, Josh Markham, Martin Neale. Document History PSL Report Number 2020/09 Version Date Reviewed by Draft for PSL review 23 July 2020 Martin Neale Final 24 July 2020 Martin Neale Table of Contents Table of Contents ........................................................................................................................................................................... 3 1. Introduction ............................................................................................................................................................................ 5 1.1 Plan purpose and scope ............................................................................................................................................... 5 1.2 Responsibilities and competencies ............................................................................................................................... 6 1.3 Plan structure ............................................................................................................................................................... 6 2. Ecological values and effects summary ................................................................................................................................ 7 2.1 Terrestrial and wetland biodiversity .............................................................................................................................. 7 2.1.1 Terrestrial ecological values ................................................................................................................................ 7 2.1.2 Summary of terrestrial ecological effects ............................................................................................................. 8 2.1.3 Measures to avoid, remedy or mitigate effects .................................................................................................... 9 2.2 Freshwater biodiversity ............................................................................................................................................... 10 2.2.1 Freshwater ecological values ............................................................................................................................. 10 2.2.2 Summary of freshwater ecological effects ......................................................................................................... 10 2.2.3 Measures to avoid, remedy or mitigate effects .................................................................................................. 11 2.3 Measures to address residual adverse ecological effects .......................................................................................... 11 2.3.1 Biodiversity offset accounting model (BOAM) .................................................................................................... 12 2.3.2 Stream ecological valuation and environmental compensation ratio (SEV and ECR) ....................................... 13 3. Ecological enhancement and restoration plan ..................................................................................................................... 16 3.1 Offsetting principles .................................................................................................................................................... 16 3.2 Restoration and enhancement principles.................................................................................................................... 17 3.2.1 Fragmentation .................................................................................................................................................... 17 3.2.2 Connectivity ....................................................................................................................................................... 17 3.2.3 Nursery species and succession........................................................................................................................ 17 3.2.4 Seed bank .......................................................................................................................................................... 17 3.2.5 Ecological buffer ................................................................................................................................................ 17 3.2.6 Whole ecosystem approach ............................................................................................................................... 17 3.3 Implementation of restoration activities ...................................................................................................................... 18 3.3.1 Site preparation .................................................................................................................................................. 18 3.3.2 Weed plant control ............................................................................................................................................. 18 3.3.3 Plant establishment pest animal control ............................................................................................................. 19 3.3.4 Stock-proof fencing ............................................................................................................................................ 19 3.3.5 Planting guidelines ............................................................................................................................................. 20 3.3.6 Plant species specifications ............................................................................................................................... 20 3.3.7 Post-planting maintenance ................................................................................................................................ 21 3.3.8 Programme ........................................................................................................................................................ 21 3.4 Biosecurity measures ................................................................................................................................................. 23 3.4.1 Myrtle rust .......................................................................................................................................................... 23 3.5 Monitoring and reporting requirements ....................................................................................................................... 23 3.5.1 Compliance confirmation report ......................................................................................................................... 23 3.5.2 Incident reporting ............................................................................................................................................... 23 3.5.3 Compliance monitoring reporting ....................................................................................................................... 23 4. Report applicability .............................................................................................................................................................. 25 5. Appendices .......................................................................................................................................................................... 26 Appendix A: Offset Plan ........................................................................................................................................................... 27 Appendix B: Indicative offset sites - photographs .................................................................................................................... 29 Appendix C: Proposed offset species lists ............................................................................................................................... 30 1. Introduction Te Tai Tokerau Water Trust Board have received provincial growth funding to provide improved water supply in Northland. Williamson Water and Land Advisory (WWLA) is leading the provision of a range of technical services to inform the project. Puhoi Stour Limited (PSL) and its subconsultant Tonkin & Taylor Limited (T+T) have collaborated to prepare this Offset and Compensation Plan to address the residual ecological effects associated with the proposed Matawii Water Supply Reservoir (the Project) at 5435 State Highway 12 Kaikohe, in the Far North (Figure 1). Te Tai Tokerau Water Trust Board proposes to construct a new water supply reservoir, by constructing a dam across the Kopenui Stream, and inundating a section of the Kopenui Stream, including parts of four headwater gullies, and surrounding land. The construction and ongoing operation of the water supply dam is anticipated to have effects on terrestrial, wetland and aquatic ecological values. The detail regarding these ecological values and effects is presented in the Matawii Water Storage Reservoir: Assessment of Ecological Effects report (AEcE, PSL Report Number 2020/02, dated 10 July 2020). Figure 1: Location of proposed reservoir at 5435 State Highway 12, Kaikohe. 1.1 Plan purpose and scope A suite of Fauna Management Plans will
Recommended publications
  • Samara Newsletter July & August 2020
    SamaraThe International Newsletter of the Millennium Seed Bank Partnership Special issue featuring projects and research from The Global Tree Seed Bank Programme, funded by the Garfield Weston Foundation August/September 2020 Issue 35 ISSN 1475-8245 Juglans pyriformis in the State of Veracruz Conserving and investigating native tree seeds to support community-based reforestation initiatives in Mexico Veracruz Pronatura Photo: Mexico is the fourth richest country in the world in terms of plant Millennium Seed Bank. Seed research has species diversity, after Brazil, China, and Colombia with a flora of been carried out on 314 species to study ca. 23,000 vascular plants. Around half of the plant species are their tolerance to desiccation for seed endemic and nearly 3,500 are trees. banking and to determine germination requirements to inform propagation activities. One of the key project species ELENA CASTILLO-LORENZO (Latin America Projects Coordinator, RBG Kew), MICHAEL WAY is Cedrela odorata (Spanish cedar), whose (Conservation Partnership Coordinator (Americas, RBG Kew) & TIZIANA ULIAN (Senior Research conservation status is vulnerable (IUCN Leader – Diversity and Livelihoods, RBG Kew) 2020) due to exploitation for its highly Trees and forests provide multiple goods Iztacala of the Universidad Autónoma valued wood. C. odorata is also used for and benefits for humans, such as high- de México (Fes-I UNAM). The aim medicinal purposes by local communities quality wood, fruit, honey, and other of this project was to conserve tree in Mexico, with the leaves being prepared ecosystem services, including clean water, species through a collaborative research in herbal tea to treat toothache, earache, prevention of soil erosion and mitigation of programme focusing on endemic, and intestinal infections.
    [Show full text]
  • Species-Specific Basic Stem-Wood Densities for Twelve Indigenous Forest and Shrubland Species of Known Age, New Zealand
    Marden et al. New Zealand Journal of Forestry Science (2021) 51:1 https://doi.org/10.33494/nzjfs512021x121x E-ISSN: 1179-5395 published on-line: 15/02/2021 Research Article Open Access New Zealand Journal of Forestry Science Species-specific basic stem-wood densities for twelve indigenous forest and shrubland species of known age, New Zealand Michael Marden1,*, Suzanne Lambie2 and Larry Burrows3 1 31 Haronga Road, Gisborne 4010, New Zealand 2 Manaaki Whenua – Landcare Research, Private Bag 3127, Hamilton 3240, New Zealand 3 Manaaki Whenua – Landcare Research, PO Box 69041, Lincoln 7640, New Zealand *Corresponding author: [email protected] (Received for publication 19 July 2019; accepted in revised form 26 January 2021) Abstract Background: Tree carbon estimates for New Zealand indigenous tree and shrub species are largely based on mean of sites throughout New Zealand. Yet stem-wood density values feed directly into New Zealand’s international and nationalbasic stem-wood greenhouse densities gas accounting. derived from We a limitedaugment number existing of publishedtrees, often basic of unspecified stem-wood age density and from data a limited with new number age- old, across 21 widely-distributed sites between latitudes 35° tospecific estimate values carbon for 12stocks. indigenous forest and shrubland species, including rarely obtained values for trees <6-years and 46° S, and explore relationships commonly used Methods: The volume of 478 whole stem-wood discs collected at breast height (BH) was determined by water displacement, oven dried, and weighed. Regression analyses were used to determine possible relationships between basic stem-wood density, and tree height, root collar diameter (RCD), and diameter at breast height (DBH).
    [Show full text]
  • Introduction Methods Results
    Papers and Proceedings Royal Society ofTasmania, Volume 1999 103 THE CHARACTERISTICS AND MANAGEMENT PROBLEMS OF THE VEGETATION AND FLORA OF THE HUNTINGFIELD AREA, SOUTHERN TASMANIA by J.B. Kirkpatrick (with two tables, four text-figures and one appendix) KIRKPATRICK, J.B., 1999 (31:x): The characteristics and management problems of the vegetation and flora of the Huntingfield area, southern Tasmania. Pap. Proc. R. Soc. Tasm. 133(1): 103-113. ISSN 0080-4703. School of Geography and Environmental Studies, University ofTasmania, GPO Box 252-78, Hobart, Tasmania, Australia 7001. The Huntingfield area has a varied vegetation, including substantial areas ofEucalyptus amygdalina heathy woodland, heath, buttongrass moorland and E. amygdalina shrubbyforest, with smaller areas ofwetland, grassland and E. ovata shrubbyforest. Six floristic communities are described for the area. Two hundred and one native vascular plant taxa, 26 moss species and ten liverworts are known from the area, which is particularly rich in orchids, two ofwhich are rare in Tasmania. Four other plant species are known to be rare and/or unreserved inTasmania. Sixty-four exotic plantspecies have been observed in the area, most ofwhich do not threaten the native biodiversity. However, a group offire-adapted shrubs are potentially serious invaders. Management problems in the area include the maintenance ofopen areas, weed invasion, pathogen invasion, introduced animals, fire, mechanised recreation, drainage from houses and roads, rubbish dumping and the gathering offirewood, sand and plants. Key Words: flora, forest, heath, Huntingfield, management, Tasmania, vegetation, wetland, woodland. INTRODUCTION species with the most cover in the shrub stratum (dominant species) was noted. If another species had more than half The Huntingfield Estate, approximately 400 ha of forest, the cover ofthe dominant one it was noted as a codominant.
    [Show full text]
  • Predation As a Primary Limiting Factor: a Comparison of the Effects of Three Predator Control Regimes on South Island Robins (Petroica Australis) in Dunedin, NZ
    Predation as a primary limiting factor: A comparison of the effects of three predator control regimes on South Island robins (Petroica australis) in Dunedin, NZ. A thesis submitted for the degree of Master of Science at the University of Otago, Dunedin, New Zealand Michael Alexander Terence Jones 10/02/2016 1 ACKNOWLEDGEMENTS I would like to thank Ian Jamieson for his tireless efforts as my supervisor, mentor and friend. He provided me with an opportunity to work in some of the most remarkable places in New Zealand with some of its most treasured species. He also enabled me to contribute to the field of zoology, one I have been passionate about since as early as I can remember. Without Ian’s support and guidance none of this could have been achieved. I would also like to thank Yolanda van Heezik and Phil Seddon for their willingness to take me and the robin project on after Ian’s passing. They have worked tirelessly to help me mould my thoughts and writing into a legible thesis and I will be forever grateful for their help. This research would not have been achievable without the dedication and hard work of all the field workers and volunteers over the years. I would like to thank Leon ‘Leroy Bernard’ Berard, Jamie Cooper, Fiona Gordon, Tracy Dearlove, Rebecca McMillan and Luke Easton for all the long hours they spent watching countless robins. A special thanks to Sam Ray for organising everything and making sure all the equipment was available and booked and putting up with Leon and myself over the long summer period.
    [Show full text]
  • Template Forest Management Plan in Accordance with Smartwood Outline
    China Forestry Group New Zealand Company Ltd Northern Region FSC Forest Management Plan For the period 2018 - 2023 Prepared by S E Moore PO Box 1127 ROTORUA Tel: 07 921 1010 Fax: 07 921 1020 [email protected] www.pfolsen.com FOREST MANAGEMENT PLAN FSCGS04 China Forestry Group New Zealand Company Limited Table of Contents 1. INTRODUCTION ...........................................................................................................................5 Foundation Principle ...................................................................................................................5 About this plan ............................................................................................................................5 The Landscape Context ............................................................................................................................6 2. The Forest Land ...........................................................................................................................6 Overview ......................................................................................................................................6 Legal ownership ...........................................................................................................................6 Forests & location ........................................................................................................................7 Topography ..................................................................................................................................7
    [Show full text]
  • NLM Leptospermum Lanigerum – Melaleuca Squarrosa Swamp Forest
    Vegetation Condition Benchmarks version 3 Non-Eucalypt Forest and Woodland NLM Leptospermum lanigerum – Melaleuca squarrosa swamp forest Community Description: Leptospermum lanigerum – Melaleuca squarrosa swamp forests dominated by Leptospermum lanigerum and/or Melaleuca squarrosa are common in the north-west and west and occur occasionally in the north-east and east where L. lanigerum usually predominates. There are also extensive tracts on alluvial flats of the major south-west rivers. The forests are dominated by various mixtures of L. lanigerum and M. squarrosa but with varying lesser amounts of various species of Acacia and rainforest species also present. Trees are usually > 8 m in height. Benchmarks: Length Component Cover % Height (m) DBH (cm) #/ha (m)/0.1 ha Canopy 70% - - - Large Trees - 10 25 800 Organic Litter 40% - Logs ≥ 10 - 20 Large Logs ≥ 12.5 Recruitment Episodic Understorey Life Forms LF code # Spp Cover % Tree or large shrub T 4 20 Medium shrub/small shrub S 3 15 Herbs and orchids H 5 5 Grass G 1 1 Large sedge/rush/sagg/lily LSR 1 1 Medium to small sedge/rush/sagg/lily MSR 2 1 Ground fern GF 2 5 Tree fern TF 1 5 Scrambler/Climber/Epiphytes SCE 2 5 Mosses and Lichens ML 1 20 Total 10 22 Last reviewed – 5 July 2016 Tasmanian Vegetation Monitoring and Mapping Program Department of Primary Industries, Parks, Water and Environment http://www.dpipwe.tas.gov.au/tasveg NLM Leptospermum lanigerum – Melaleuca squarrosa swamp forest Species lists: Canopy Tree Species Common Name Notes Leptospermum lanigerum woolly teatree Melaleuca
    [Show full text]
  • Patterns of Flammability Across the Vascular Plant Phylogeny, with Special Emphasis on the Genus Dracophyllum
    Lincoln University Digital Thesis Copyright Statement The digital copy of this thesis is protected by the Copyright Act 1994 (New Zealand). This thesis may be consulted by you, provided you comply with the provisions of the Act and the following conditions of use: you will use the copy only for the purposes of research or private study you will recognise the author's right to be identified as the author of the thesis and due acknowledgement will be made to the author where appropriate you will obtain the author's permission before publishing any material from the thesis. Patterns of flammability across the vascular plant phylogeny, with special emphasis on the genus Dracophyllum A thesis submitted in partial fulfilment of the requirements for the Degree of Doctor of philosophy at Lincoln University by Xinglei Cui Lincoln University 2020 Abstract of a thesis submitted in partial fulfilment of the requirements for the Degree of Doctor of philosophy. Abstract Patterns of flammability across the vascular plant phylogeny, with special emphasis on the genus Dracophyllum by Xinglei Cui Fire has been part of the environment for the entire history of terrestrial plants and is a common disturbance agent in many ecosystems across the world. Fire has a significant role in influencing the structure, pattern and function of many ecosystems. Plant flammability, which is the ability of a plant to burn and sustain a flame, is an important driver of fire in terrestrial ecosystems and thus has a fundamental role in ecosystem dynamics and species evolution. However, the factors that have influenced the evolution of flammability remain unclear.
    [Show full text]
  • Breeding Systems and Reproduction of Indigenous Shrubs in Fragmented
    Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Breeding systems and reproduction of indigenous shrubs in fragmented ecosystems A thesis submitted in partial fulfilment of the requirements for the degree of Doctor of Philosophy III Plant Ecology at Massey University by Merilyn F Merrett .. � ... : -- �. � Massey University Palrnerston North, New Zealand 2006 Abstract Sixteen native shrub species with various breeding systems and pollination syndromes were investigated in geographically separated populations to determine breeding systems, reproductive success, population structure, and habitat characteristics. Of the sixteen species, seven are hermaphroditic, seven dioecious, and two gynodioecious. Two of the dioecious species are cryptically dioecious, producing what appear to be perfect, hermaphroditic flowers,but that functionas either male or female. One of the study species, Raukauaanomalus, was thought to be dioecious, but proved to be hermaphroditic. Teucridium parvifolium, was thought to be hermaphroditic, but some populations are gynodioecious. There was variation in self-compatibility among the fo ur AIseuosmia species; two are self-compatible and two are self-incompatible. Self­ incompatibility was consistent amongst individuals only in A. quercifolia at both study sites, whereas individuals in A. macrophylia ranged from highly self-incompatible to self-compatible amongst fo ur study sites. The remainder of the hermaphroditic study species are self-compatible. Five of the species appear to have dual pollination syndromes, e.g., bird-moth, wind-insect, wind-animal. High levels of pollen limitation were identified in three species at fo ur of the 34 study sites.
    [Show full text]
  • Aquatic Ecology of the Montagu River Catchment
    Aquatic Ecology of the Montagu River Catchment A Report Forming Part of the Requirements for State of Rivers Reporting David Horner Water Assessment and Planning Branch Water Resources Division DPIWE. December, 2003 State of Rivers Aquatic Ecology of the Montagu Catchment Copyright Notice: Material contained in the report provided is subject to Australian copyright law. Other than in accordance with the Copyright Act 1968 of the Commonwealth Parliament, no part of this report may, in any form or by any means, be reproduced, transmitted or used. This report cannot be redistributed for any commercial purpose whatsoever, or distributed to a third party for such purpose, without prior written permission being sought from the Department of Primary Industries, Water and Environment, on behalf of the Crown in Right of the State of Tasmania. Disclaimer: Whilst DPIWE has made every attempt to ensure the accuracy and reliability of the information and data provided, it is the responsibility of the data user to make their own decisions about the accuracy, currency, reliability and correctness of information provided. The Department of Primary Industries, Water and Environment, its employees and agents, and the Crown in the Right of the State of Tasmania do not accept any liability for any damage caused by, or economic loss arising from, reliance on this information. Preferred Citation: DPIWE (2003). State of the River Report for the Montagu River Catchment. Water Assessment and Planning Branch, Department of Primary Industries, Water and Environment, Hobart. Technical Report No. WAP 03/09 ISSN: 1449-5996 The Department of Primary Industries, Water and Environment The Department of Primary Industries, Water and Environment provides leadership in the sustainable management and development of Tasmania’s resources.
    [Show full text]
  • MANA ISLAND, WELLINGTON, NEW ZEALAND Summary: Mana Island (217 Ha) Provides Opportunities for Conservation Despite Over 150 Years of Farming
    SUSAN M. TIMMINS1, IAN A.E. ATKINSON2 and COLIN C. OGLE1 57 1 Science and Research Directorate, Department of Conservation, P.O. Box 10-420, Wellington, New Zealand 2 Botany Division, DSIR, Private Bag, Lower Hutt, New Zealand CONSERVATION OPPORTUNITIES ON A HIGHLY MODIFIED ISLAND: MANA ISLAND, WELLINGTON, NEW ZEALAND Summary: Mana Island (217 ha) provides opportunities for conservation despite over 150 years of farming. It is free from all introduced mammals except mice. It supports native coastal communities representative of the region and already has nationally threatened plants and animals. To take best advantage of these opportunities, it is suggested that: the present native plants, animals and communities are protected; part of the island is revegetated; selected species of threatened native plants and animals are introduced; and the island and its natural and human history are used for education, interpretation and recreational enjoyment. Attention is drawn to some unanswered questions and potential conflicts associated with these management proposals. Keywords: Mana Island; revegetation; threatened species conservation; reserve management; mammal-free island. Introduction Mana, a 217 ha island near Wellington, has been farmed for over 150 years and, although highly modified, has no introduced mammals except mice (Mus musculus). Reflecting a groundswell of opinion that Mana has considerable biological value and untapped conservation potential, numerous land use studies have been conducted over the last 15 years (for example, Department of Lands and Survey, 1980, 1981). A radical change in the management regime began in 1986 after farming ceased and the current management plan was adopted (Department of Lands and Survey, 1986).
    [Show full text]
  • Is Kanuka and Manuka Establishment in Grassland Constrained by Mycorrhizal Abundance?
    172 AvailableNew on-lineZealand at: Journal http://www.newzealandecology.org/nzje/ of Ecology, Vol. 37, No. 2, 2013 Is kanuka and manuka establishment in grassland constrained by mycorrhizal abundance? Murray Davis1*, Ian A. Dickie2, Thomas Paul3 and Fiona Carswell2 1Scion, PO Box 29237, Christchurch 8540, New Zealand 2Landcare Research, PO Box 69040, Lincoln 7640, New Zealand 3Scion, Private Bag 3020, Rotorua 3046, New Zealand *Author for correspondence ([email protected]) Published online: 14 May 2013 Abstract: Two indigenous small tree and shrub species, kanuka (Kunzea ericoides) and manuka (Leptospermum scoparium), have potential as reforestation species in New Zealand as they are forest pioneer species that can invade grassland naturally from present seed sources. The aim of this study was to determine if establishment of kanuka and manuka from seed in grassland distant from stands of these species might be constrained by lack of appropriate mycorrhizal fungi. Both species were grown in an unsterilised grassland soil from a low- productivity montane site assumed to be devoid of appropriate mycorrhizal fungi and inoculated with sterilised or unsterilised O-horizon or mineral soil from beneath three kanuka and three manuka communities expected to contain such fungi. Inoculation with unsterilised O-horizon soil improved kanuka biomass by 36–92%, depending on the source of the inoculant. Inoculation did not improve manuka biomass. No ectomycorrhizal infection was observed on either kanuka or manuka in samples examined under binocular microscope. The biomass response by kanuka to inoculation may be due to introduction of more effective arbuscular mycorrhizal fungi from kanuka communities or possibly to the introduction of soil microorganisms.
    [Show full text]
  • Oceania Species ID Sheets
    Species Identification Sheets for Protected Wildlife in Trade - Oceania - 3 Mark O’Shea 1 Mike McCoy © Phil Bender 5 Tony Whitaker © 2 4 Tony Whitaker © 6 WILDLIFE ENFORCEMENT GROUP (AGRICULTURE & FORESTRY · CONSERVATION · N. Z. CUSTOMS SERVICE) Numbered images above Crown Copyright: Department of Conservation Te Papa Atawhai. Photographers:1) Dick Veitch 1981, 2) Rod Morris 1984, 3) Gareth Rapley 2009, 4) Andrew Townsend 2000, 5) Paul Schilov 2001, 6) Dick Veitch 1979 Introduction Purpose of this resource: - Additional species that should be included in this booklet Wildlife trafficking is a large-scale multi-billion dollar industry worldwide. The illegal trade of - Sources of information, such as identification guides or reports, related to these wildlife has reached such prominence that it has the potential to devastate source populations species of wildlife, impacting on the integrity and productivity of ecosystems in providing food and - Domestic legislation regarding the regulation of trade in wildlife - Sources of photographs for identification purposes resources to the local economy. In order to protect these resources, legislation has been put in place to control the trade of wildlife in almost every country worldwide. Those assigned with - Details of wildlife seizures, including the smuggling methods enforcing these laws have the monumental task of identifying the exact species that are being traded, either as whole living plants or animals, as parts that are dried, fried or preserved, or as Any feedback can be provided directly to the Wildlife Enforcement Group: derivatives contained within commercial products. Stuart Williamson Senior Investigator, Wildlife Enforcement Group This booklet “Species Identification Sheets for Protected Species in Trade – Oceania” has been Customhouse, Level 6, 50 Anzac Avenue, Auckland, New Zealand developed to address the lack of resources, identified by customs agencies within Oceania, for Ph: +64 9 3596676, Fax: +64 9 3772534 identification of wildlife species in trade.
    [Show full text]