PPB Environmental Management Plan Supporting Document
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DUCK HUNTING in VICTORIA 2020 Background
DUCK HUNTING IN VICTORIA 2020 Background The Wildlife (Game) Regulations 2012 provide for an annual duck season running from 3rd Saturday in March until the 2nd Monday in June in each year (80 days in 2020) and a 10 bird bag limit. Section 86 of the Wildlife Act 1975 enables the responsible Ministers to vary these arrangements. The Game Management Authority (GMA) is an independent statutory authority responsible for the regulation of game hunting in Victoria. Part of their statutory function is to make recommendations to the relevant Ministers (Agriculture and Environment) in relation to open and closed seasons, bag limits and declaring public and private land open or closed for hunting. A number of factors are reviewed each year to ensure duck hunting remains sustainable, including current and predicted environmental conditions such as habitat extent and duck population distribution, abundance and breeding. This review however, overlooks several reports and assessments which are intended for use in managing game and hunting which would offer a more complete picture of habitat, population, abundance and breeding, we will attempt to summarise some of these in this submission, these include: • 2019-20 Annual Waterfowl Quota Report to the Game Licensing Unit, New South Wales Department of Primary Industries • Assessment of Waterfowl Abundance and Wetland Condition in South- Eastern Australia, South Australian Department for Environment and Water • Victorian Summer waterbird Count, 2019, Arthur Rylah Institute for Environmental Research As a key stakeholder representing 17,8011 members, Field & Game Australia Inc. (FGA) has been invited by GMA to participate in the Stakeholder Meeting and provide information to assist GMA brief the relevant Ministers, FGA thanks GMA for this opportunity. -
Expenditure Review - Melbourne Water 2021 Price Submission
Expenditure review - Melbourne Water 2021 Price Submission Expenditure review - Melbourne Water 2021 Price Submission FINAL REPORT for the Essential Services Commission - Public 23 February 2021 1 Expenditure review - Melbourne Water 2021 Price Submission Commercial-in-confidence Contents Glossary ii Executive summary iii About this report iii Operating expenditure iii Capital expenditure v 1 Introduction 1 1.1 Background 1 1.2 Scope of review 1 1.3 Approach to review 1 1.4 Structure of this report 2 2 Summary of forecast expenditure 3 2.1 Key expenditure drivers 3 2.2 Operating expenditure 9 2.3 Capital expenditure 12 3 Operating expenditure assessment 15 3.1 Overview of approach 15 3.2 Historical controllable expenditure (2019-20) 17 3.3 Baseline growth-efficiency improvement rate 23 3.4 Forecast variations to baseline expenditure 27 3.5 Individual controllable expenditure items 41 3.6 Recommendations 55 4 Capital expenditure assessment 56 4.1 Overview of approach 56 4.2 Historical capex 57 4.3 Overall assessment of capital planning and asset management 62 4.4 Overall assessment of capital delivery 62 4.5 Overview of major programs / allocations 63 4.6 Major water projects 66 4.7 Major sewerage projects and programs 77 4.8 Major waterways and drainage projects 90 4.9 Recommendations 102 Appendix A – Demand forecast review 106 Key findings of the demand review 106 Population forecast comparison 107 Waterways and drainage 120 Sewage demand 125 Water demand 136 Limitation of our work 143 General use restriction 143 i Expenditure review -
Experimental Support Towards a Metabolic Proxy in Fish Using Otolith Carbon Isotopes Jasmin C
© 2020. Published by The Company of Biologists Ltd | Journal of Experimental Biology (2020) 223, jeb217091. doi:10.1242/jeb.217091 RESEARCH ARTICLE Experimental support towards a metabolic proxy in fish using otolith carbon isotopes Jasmin C. Martino1,*,‡, ZoëA. Doubleday1,*, Ming-Tsung Chung2 and Bronwyn M. Gillanders1 ABSTRACT field metabolic rates can be difficult to measure in fish. The doubly Metabolic rate underpins our understanding of how species survive, labelled water method, which involves measuring the elimination of reproduce and interact with their environment, but can be difficult to an introduced oxygen isotope signature, is used for most air-breathing measure in wild fish. Stable carbon isotopes (δ13C) in ear stones animals but is unsuitable for fish (Nelson, 2016; Treberg et al., 2016). (otoliths) of fish may reflect lifetime metabolic signatures but Metabolic rates have therefore been measured using electromyogram experimental validation is required to advance our understanding of telemetry (Cooke et al., 2004; Quintella et al., 2009), heart rate the relationship. To this end, we reared juvenile Australasian snapper monitoring (Clark et al., 2005; Thorarensen et al., 1996) or (Chrysophrys auratus), an iconic fishery species, at different accelerometry (Metcalfe et al., 2016). However, these approaches ‘ ’ temperatures and used intermittent-flow respirometry to calculate only offer short-term snapshots of metabolic rates in live fish. standard metabolic rate (SMR), maximum metabolic rate (MMR) and Records conserved in hard-calcified structures offer a valuable absolute aerobic scope (AAS). Subsequently, we analysed δ13C and alternative to uncovering long-term and retrospective histories. oxygen isotopes (δ18O) in otoliths using isotope-ratio mass Furthermore, biogeochemical techniques can reconstruct histories spectrometry. -
Uva-DARE (Digital Academic Repository)
UvA-DARE (Digital Academic Repository) The adequacy of aging techniques in vertebrates for rapid estimation of population mortality rates from age distributions Zhao, M.; Klaassen, C.A.J.; Lisovski, S.; Klaassen, M. DOI 10.1002/ece3.4854 Publication date 2019 Document Version Other version Published in Ecology and Evolution License CC BY Link to publication Citation for published version (APA): Zhao, M., Klaassen, C. A. J., Lisovski, S., & Klaassen, M. (2019). The adequacy of aging techniques in vertebrates for rapid estimation of population mortality rates from age distributions. Ecology and Evolution, 9(3), 1394-1402. https://doi.org/10.1002/ece3.4854 General rights It is not permitted to download or to forward/distribute the text or part of it without the consent of the author(s) and/or copyright holder(s), other than for strictly personal, individual use, unless the work is under an open content license (like Creative Commons). Disclaimer/Complaints regulations If you believe that digital publication of certain material infringes any of your rights or (privacy) interests, please let the Library know, stating your reasons. In case of a legitimate complaint, the Library will make the material inaccessible and/or remove it from the website. Please Ask the Library: https://uba.uva.nl/en/contact, or a letter to: Library of the University of Amsterdam, Secretariat, Singel 425, 1012 WP Amsterdam, The Netherlands. You will be contacted as soon as possible. UvA-DARE is a service provided by the library of the University of Amsterdam (https://dare.uva.nl) Download date:01 Oct 2021 1 Appendix S4. -
Western Treatment Plant Bird Watching Access Map N
Map not to scale Western Treatment Plant Scale at A3 1:75,000 (approximately) Werribee, Victoria NEW FARM RD Gate open 6am to 9pm 0 1 2 3 7 days. N Werribee Western Treatment Plant Bird Watching Access Map Kilometres Operations & Maintenance and Discovery Centre. September 2010 Gate open 6am to 5:30pm Melbourne Monday to Friday. Permit Werribee inductions are held here. MALTBY BYPASS Road Closure GEELONG RD Access to bird watching areas is only via Point Wilson Road. RD ROWAN LANE You must lock all gates immediately after entry and exit. Restricted Bird Watching Permit does not permit any other Access FREEWAY OLD BOUNDARY RD Future Werribee River Regional activity or access to areas not managed by RD FARM Park. Pedestrian 40 SOUTH RD RD access only. Melbourne Water. RD 25 WEST RD RD Refer to permit conditions for more information. 80 SOUTH RD Little River Register your visit: 9235 2828 120 SOUTH Werribee South Emergency: 9742 9208 (or 000) LITTLE RIVER RD PRINCES RD Lara 160 SOUTH River More information: 131 722 or melbournewater.com.au 145 WEST RD METROPOLITAN 15 EAST 55 EAST 95 EAST River MURTCAIM RD RYANSRYANSRYANS RYANSRYANSRYANSRYANSRYANS SWAMSWAMSWAMPPP SWAMPSWAMPSWAMSWAMSWAMPPP Little Bird watching WALSH’S RD 55E LAGOON General access General access access via 115E LAGOON WALTER 25W LAGOON permit gate (1 to 7) permit route Pt Wilson Rd 95 E RD 65 W RD 15 EAST RD RD RD 8 145WA LAGOON PRINCES FREEWAYPARADISE 7 Special access Special access RD 6 WALSH LAGOON 145WB LAGOON permit gate (8) permit route 85WA LAGOON 85WB LAGOON JUBILEE -
International Symposium on Circle Hooks in Research, Management, and Conservation Abstracts*
BULLETIN OF MARINE SCIENCE. 88(3):791–815. 2012 http://dx.doi.org/10.5343/bms.2012.1031 INTERNATIONAL SYMPOSIUM ON CIRCLE HOOKS IN RESEARCH, MANAGEMENT, AND CONSERVATION ABSTRACTS* Challenges OF circle hook adoption in Indonesian live bait long- line Fisheries by Ahmad Hafizh Adyas and Imam Musthofa Zainudin.—Since 2005, WWF-Indonesia has facilitated efforts to reduce sea turtle bycatch on tuna longlines. The onboard observer data collected between 2006 and 2010 covering 49 vessels documented 359 sea turtles harvested. While fishermen did not think this bycatch was a major problem, con- sidering the large number of vessels in the fleet there is a large potential of cumulative im- pacts. Forty vessels from Benoa-Bali and Bitung North Sulawesi have been involved in circle hook trials and adoption between 2006 and 2010, covering 128 fishing trips, 3361 settings, and using >70,000 circle hooks. The results are promising—circle hooks reduced sea turtle bycatch by 78% while catching target fish as effectively as traditional J-hooks. However, the circle hooks (C16) could not be applied in live bait fisheries due to their large size; the 5 mm shank of the circle hook was inadequate to hold the bait (typically milkfish of 15–20 cm) and also the bait typically dies faster. Given that around 90% of Indonesia’s tuna longline fleet use live bait (with shallow sets), this is a considerable issue to resolve. Other obstacles for adop- tion stem from the use of monofilament line and the basket hauling technique, and the shape and weight of the circle hooks, all of which are perceived by fishermen as making their work more difficult (e.g., harder to haul and also causes a rumpling in the line). -
Inquiry Advisory Committee Scott S Chidgey Expert
Scott Chidgey: Response to Expert Witness Statements and IAC RFI CEE Pty Ltd Environmental scientists and engineers Gas Import Jetty and Pipeline Project Environment Effects Statement (The EES) Inquiry Advisory Committee Scott S Chidgey Expert Witness Response to Marine Biodiversity to Expert Witness Statement Submissions & IAC Request for Information Prepared for: Ashurst and Hall&Wilcox Lawyers September 2020 CEE Pty Ltd Unit 4 150 Chesterville Road Cheltenham VIC 3192 03 9553 4787 cee.com.au Scott Chidgey Response to Expert Witness Statements and IAC RFI Marine Biodiversity Impact Assessment CONTENTS Response to Expert Witness Statement 1. Prof Perran Cook 3 Response to Expert Witness Statement 2. Cardno Australia Pty Ltd 8 Response to Expert Witness Statement 3. Dr Matt Edmunds 14 Response to Expert Witness Statement 4. Mr Frank Hanson 19 Response to IAC Request for Further Information 21 Declaration 29 Appendix to Item 6 30 Gas Import Jetty and Pipeline Project Environmental Effects Statement Page 2 of 41 Scott Chidgey: Response to Expert Witness Statements and IAC RFI CEE Pty Ltd Environmental scientists and engineers Response to Expert Witness Statement 1. Prof Perran Cook Professor Cook is a Professor of Chemistry at Monash University and provides a balanced discussion of matters presented in EES Technical Appendix A and its Annexure A, related to chlorine toxicity and the formation of halogenated organic compounds. My responses to his discussion are listed with reference to the Item numbers used in Prof Cook’s Statement. 1. In Item2, 3 and 4, Prof Cook discusses the derivation and acceptability of the guideline value for chlorine established by CSIRO. -
Inactivation of Cryptosporidium Across the Wastewater Treatment Train: Recycled Water Fit for Purpose (Phase II)
Inactivation of Cryptosporidium across the wastewater treatment train: Recycled water fit for purpose (Phase II) Brendon King, Stella Fanok, Renae Phillips, Melody Lau, Ben van den Akker and Paul Monis Project 8OS – 8012 Final Report – March 2015 1 Table of Contents 1 INTRODUCTION ..................................................................................................................................................................... 19 1.1 OVERVIEW ............................................................................................................................................................................................... 19 1.2 CRYPTOSPORIDIUM AND CRYPTOSPORIDIOSIS .................................................................................................................................... 20 1.3 CRYPTOSPORIDIUM SPECIES PRESENT IN THE AUSTRALIAN COMMUNITY ..................................................................................... 21 1.4 CURRENT METHODS FOR ISOLATION AND DETECTION FOR CRYPTOSPORIDIUM .......................................................................... 22 1.5 ASSESSMENT OF CRYPTOSPORIDIUM INFECTIVITY ............................................................................................................................ 23 1.5.1 In vitro assays for assessing viability of Cryptosporidium ........................................................................................... 23 1.5.2 Human infectivity assays .......................................................................................................................................................... -
Melbourne Water Annual Report 2012–13 Contents
Enhancing Life and Liveability Melbourne Water Annual Report 2012–13 Contents Overview Page 1 Chairman’s Report Page 2 Managing Director’s Report Page 3 Service delivery Page 4 Water Page 6 Alternative water sources and integrated water cycle management Page 14 Sewerage Page 22 Waterways Page 28 Corporate Page 36 Environmental stewardship Page 38 Relationships Page 46 Financial sustainability Page 52 Organisational capability Page 62 Financial Report Page 68 Performance reporting Page 127 Statutory information Page 140 Overview About us Melbourne Water is owned by the Victorian Government. We manage water supply catchments, treat and supply drinking and recycled water, remove and treat most of Melbourne’s sewage, and manage waterways and major drainage systems in the Port Phillip and Westernport region. In all our business decisions we consider social, environmental and financial effects, and short-term and long-term implications. Our customers include metropolitan water retailers, other water authorities, land developers and businesses that divert river water, and the 1.8 million households that receive waterways and drainage services in the greater Melbourne region. We deliver our services in partnership with others including government agencies, local councils, catchment authorities, contractors and suppliers. About this report Accessibility Melbourne Water’s Annual Report An accessible text format of this report 2012–13 describes our annual progress is available on our website at towards achieving our vision of Enhancing melbournewater.com.au Life and Liveability in the greater Melbourne If you want to obtain a copy of this report, region, and how we met our regulatory or sections of it, in a different accessible obligations from 1 July 2012 to 30 June format, please contact Melbourne Water 2013. -
Environmental Improvement Plan for the Eastern and Western Treatment Plants November 2017
Environmental Improvement Plan for the Eastern and Western Treatment Plants November 2017 Contents 1. Purpose 2 2. Scope 2 3. General Description 2 4. Legislative Requirements and Guidelines 4 5. Environmental Policy and Strategy 4 6. Environmental Management System 5 7. Contingency Planning 5 8. Operational Arrangements to Achieve Objectives 5 9. Environmental Improvement Plan Action Summary 6 10. Priority Improvement Areas 9 10.1. Water Plan 3 Achievements 9 10.2. Treated Effluent Discharge 9 10.3. Odour Emissions 10 10.4. Recycled Water 12 10.5. Biosolids 13 10.6. Energy and Greenhouse Gas 14 10.7. Waste Management 15 10.8. Biodiversity Improvement 16 10.9. Improving Liveability 17 10.10. Groundwater and Land management 18 10.11. 2016 Price Submission Priorities 18 11. Stakeholder, Customer and Community Engagement 19 12. Performance Monitoring and Reporting 20 13. Plan Auditing and Review 20 14. Glossary of Terms 21 15. Endorsement by Management 22 16. Appendix A: Eastern Treatment Plant Site Maps 24 17. Appendix B: Western Treatment Plant Site Map 26 18. Appendix C: Legislative Requirements and Guidelines 27 Environmental Improvement Plan for the Eastern and Western Treatment Plants | 1 1. Purpose 3. General Description This Environmental Improvement Plan describes how The Eastern Treatment Plant (ETP) and the Western Melbourne Water uses various processes to provide Treatment Plant (WTP) are owned and operated by continuous improvement in environmental management Melbourne Water and are located in the suburbs of at the Eastern Treatment Plant (ETP) located in Bangholme Bangholme and Werribee. The ETP and WTP are the two and the Western Treatment Plant (WTP) located in Werribee. -
Proceedings of the Research Workshop on the Rapid Estimation of Fish Age Using Fourier Transform Near-Infrared Spectroscopy (FT-NIRS)
AFSC PROCESSED REPORT 2019-06 Alaska Fisheries Science Center Resource Ecology and Fisheries Management Division Age and Growth Program Proceedings of the Research Workshop on the Rapid Estimation of Fish Age Using Fourier Transform Near-Infrared Spectroscopy (FT-NIRS) SEPTEMBER 2019 This report does not constitute a publication and is for information only. All data herein are to be considered provisional. U.S. Department of Commerce | National Oceanic and Atmospheric Administration | National Marine Fisheries Service oope r This document should be cited as follows: Helser, T. E., I. M. Benson, and B. K. Barnett (editors). 2019. Proceedings of the research workshop on the rapid estimation of fish age using Fourier Transform Near Infrared Spectroscopy (FT-NIRS). AFSC Processed Rep. 2019-06, 195 p. Alaska Fish. Sci. Cent., NOAA, Natl. Mar. Fish. Serv., 7600 Sand Point Way NE, Seattle WA 98115. - - - This document is available online at: Document available: https://www.afsc.noaa.gov/Publications/ProcRpt/PR2019-06.pdf Reference in this document to trade names does not imply endorsement by the National Marine Fisheries Service, NOAA. Proceedings of the Research Workshop on the Rapid Estimation of Fish Age Using Fourier Transform Near-Infrared Spectroscopy (FT-NIRS) T. E. Helser1, I. M. Benson1, and B. K. Barnett2 (editors) ‘ 1 Nationallaska Fisheries Marine Fisheries Science Center Service ResourceA Ecology Fisheries Management Division 7600 Sand Point Way NE Seattle WA 98115 2National Marine Fisheries Service Southeast Fisheries Science Center Panama City Laboratory 3500 Delwood Beach Road Panama City, FL 32408 September 2019 PREFACE Knowing how long fish live and the number of different age groups in a fish population is essential information to sustainably manage our Nation’s valuable fisheries. -
Victorian Water Accounts 2016–2017 a Statement of Victorian Water Resources
Victorian Water Accounts 2016–2017 A statement of Victorian water resources Victorian Water Accounts 2016–17 1 Contents Foreword .................................................................................................................................. 3 Executive summary ................................................................................................................. 6 PART 1: OVERVIEW OF VICTORIAN WATER RESOURCES 2016–17 ............................. 9 1. Management of Victoria’s water resources ................................................................ 10 1.1 Types of water resources ...................................................................................................... 10 1.2 Water sector institutional arrangements ................................................................................ 13 1.3 Water entitlement and water resource planning frameworks ................................................. 16 1.4 Monitoring and reporting ........................................................................................................ 23 2. Water availability ........................................................................................................... 24 2.1 Rainfall................................................................................................................................... 24 2.2 Streamflow ............................................................................................................................. 27 2.3 Storages ...............................................................................................................................