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Submission to Australia's Faunal Extinction Crisis Inquiry
Supplementary to my submission of the 5th September 2018 I would appreciate it if the panel would take the following information into account most of the local information has been taken from the web site: Campbelltown Koala Research and Database.com. which is Report undertaken by Prof. Robert Close and his team over a 27 year period.. www.campbelltown research and database.com 13th August 2019 Submission to Australia’s Faunal Extinction Crisis Inquiry Patricia Durman 28th July 2019 Thank you for allowing us to submit a submission into the state of koalas in NSW, my knowledge is mainly restricted to the local koala population and I have aimed this submission to the protection of these animals, but regard all native animals including koalas as part of the ecosystem that is required to keep the planet healthy. It is unfortunate that unless the panel has the power to delay development until they have made their report and it has been accepted by the government the Campbelltown koala population will have been seriously endangered by subdivision and the installation of new roads. I have referred to the koala population as the Campbelltown population, but this, of course, refers to all koalas living in the South West region of Sydney including Sutherland. HISTORY Although there were a few extinctions of native flora and fauna once the Aboriginal people had landed in Australia 40,000 years ago, perhaps even longer in the Cape York region, it wasn’t until Europeans arrived and cleared vast areas of bushland that the extinction of native animals escalated and in only 200 years we have become the continent with the most amount of extinction in the world. -
Gosford City Centre Masterplan the Gosford Challenge Gosford City Centre Masterplan
City, Our destiny Gosford City Centre Masterplan The Gosford ChallenGe Gosford City Centre Masterplan r City, u O destiny a World Class reGional Waterfront City r City, iii u O destiny The Gosford ChallenGe Gosford City Centre Masterplan acknowledgments JOINT PROJeCt SPONSORS DESIGn TEAM Gosford City Council land and property Gosford Challenge team Clr Chris Holstein Management authority Colleen Worthy-Jennings Mayor Hon Tony Kelly MHR Stephen Fairnham Clr Craig Doyle Warwick Watkins Duncan Clarke Deputy Mayor Graham Harding Helen Polkinghorne Clr Chris Burke Brett Phillips John Tilston Clr Peter Freewater Stewart Veitch Barbara Cruise Clr Amy Houston Robert Eyre Clr Terri Latella Scott Burton Clr Jim Macfadyen Steve Green Clr Laurie Maher Sue Verhoek Clr Vicki Scott Kerr Partnering Clr Jeff Strickson Cox Architects and Planners Peter Wilson Patrick Condon Stephen Glen Rob Lane Gary Chestnut Aurecon Rod Williams Arup Nic Pasternatsky Oculus Terry Thirlwell teaming with ideas r City, u O destiny Contents 1 GROWING A REGIONAL CITY 2 4 MAKING IT HAPPEN 92 1.1 gosford as a regional city 3 4.1 implementation plan 93 1.2 greater metropolitan context 4 4.2 the beginning - two priority areas 96 1.3 regional context 5 APPENDICES 1.4 local context 6 appendix 1 sustainability 102 1.5 attributes of a regional city 8 appendix 2 regional benchmarks 110 1.6 purpose of a masterplan 10 appendix 3 retail and commercial market 114 1.7 the journey 12 appendix 4 participants 116 1.8 planning context 14 1.9 key strategic opportunities 15 2 SPATIAL FRAMEWORK 16 2.1 the city framework 16 2.2 the masterplan 18 2.3 five precincts of activity 20 3 MASTERPLAN ELEMENTS 48 3.1 connecting places 50 3.2 activate the city 56 3.3 responsive built form 60 3.4 generate jobs and new enterprises 64 3.5 living in the city 72 3.6 access and movement 76 3.7 sustaining the city (enhancing the natural environment) 86 note: diagrams of future development are concept only. -
Estuary Surveillance for QX Disease
Estuary surveillance Student task sheet for QX disease The following tables show data collected Estuary Surveillance 2002: during estuary surveillance from 2001– During the 2002 sampling period a total of 2004 for New South Wales and 5250 oysters were received and processed Queensland. N is the number of oysters from 18 NSW estuaries and three tested in a random sample of the oyster Queensland zones using tissue imprints. population. Dr Adlard used two methods of disease detection in surveillance — tissue imprint and PCR. Table 2A: Tissue imprints used to detect the QX disease parasite Estuary Surveillance 2001: 2002 Survey results Table 1: Tissue imprint results for 2001 N 2001 Survey Results Estuary N infected % N Northern Moreton Bay 250 0 0 Estuary N infected % Central Moreton Bay 250 0 0 Tweed River 316 0 0 Southern Moreton Bay 250 2 0.8 Brunswick River 320 0 0 Tweed River 250 0 0 Richmond River 248 0 0 Brunswick River 250 0 0 Clarence River 330 5 1.52 Richmond River 250 102 40.8 Wooli River 294 0 0 Clarence River 250 55 22 Kalang /Bellinger 295 0 0 Wooli River 250 0 0 Rivers Kalang /Bellingen Rivers 250 0 0 Macleay River 261 0 0 Macleay River 250 0 0 Hastings River 330 0 0 Hastings River 250 0 0 Manning River 286 0 0 Manning River 250 0 0 Wallis Lakes 271 0 0 Wallis Lakes 250 0 0 Port Stephens 263 0 0 Port Stephens 250 0 0 Hawkesbury River 323 0 0 Hawkesbury River 250 0 0 Georges River 260 123 47.31 Georges River 250 40 16 Shoalhaven/ 255 0 0 Crookhaven Shoalhaven/Crookhaven 250 0 0 Bateman's Bay 300 0 0 Bateman's Bay 250 0 0 Tuross Lake 304 0 0 Tuross Lake 250 0 0 Narooma 300 0 0 Narooma 250 0 0 Merimbula 250 0 0 Merimbula 250 0 0 © Queensland Museum 2006 Table 2B: PCR results from 2002 on Estuary Surveillance 2003: oysters which had tested negative to QX During 2003 a total of 4450 oysters were disease parasite using tissue imprints received and processed from 22 NSW estuaries and three Queensland zones. -
Appendix 3 – Maps Part 5
LEGEND LGAs Study area FAIRFIELD LGA ¹ 8.12a 8.12b 8.12c 8.12d BANKSTOWN LGA 8.12e 8.12f 8.12i ROCKDALE LGA HURSTVILLE LGA 8.12v 8.12g 8.12h 8.12j 8.12k LIVERPOOL LGA NORTH BOTANY BAY CITY OF KOGARAH 8.12n 8.12o 8.12l 8.12m 8.12r 8.12s 8.12p 8.12q SUTHERLAND SHIRE 8.12t 8.12u COORDINATE SCALE 0500 1,000 2,000 PAGE SIZE FIG NO. 8.12 FIGURE TITLE Overview of Site Specific Maps DATE 17/08/2010 SYSTEM 1:70,000 A3 © SMEC Australia Pty Ltd 2010. Meters MGA Z56 All Rights Reserved Data Source - Vegetation: The Native Vegetation of the Sydney Metropolitan Catchment LOCATION I:Projects\3001765 - Georges River Estuary Process Management Authority Area (Draft) (2009). NSW Department of Environment, Climate Change PROJECT NO. 3001765 PROJECT TITLE Georges River Estuary Process Study CREATED BY C. Thompson Study\009 DATA\GIS\ArcView Files\Working files and Water. Hurstville, NSW Australia. LEGEND Weed Hotspot Priority Areas Study Area LGAs Riparian Vegetation & EEC (Moderate Priority) Riparian Vegetation & EEC (High Priority) ¹ Seagrass (High Priority) Saltmarsh (High Priority) Estuarine Reedland (Moderate Priority) Mangrove (Moderate Priority) Swamp Oak (Moderate Priority) Mooring Areas River Area Reserves River Access Cherrybrook Park Area could be used for educational purposes due to high public usage of the wharf and boat launch facilities. Educate on responsible use of watercraft, value of estuarine and foreshore vegetation and causes and outcomes of foreshore FAIRFIELD LGA erosion. River Flat Eucalypt Forest Cabramatta Creek (Liverpool LGA) - WEED HOT SPOT Dominated by Balloon Vine (Cardiospermum grandiflorum) and River Flat Eucalypt Forest Wild Tobacco Bush (Solanum mauritianum). -
Output Chunks
MooneyMooney MooneyMooney CreekCreek TrackheadTrackhead toto SomersbySomersby This enjoyable walk starts from where the old Length: 16.1 km Pacific Hwy where you walk along dirt roads and trails for while alongside the wide Mooney Time: 6 hrs Mooney Creek, and under the huge F3 Mooney Climb: 680 m Mooney bridge. The wide track continues upstream, passing a few campsites before crossing Style: One way the wide creek at a pleasant large rock platform. Rating: Track: Hard Not too long after crossing the creek you will pass the lower Mooney Mooney Dam where the old Where: 9.1 km W of Gosford trail leads you uphill past another campsite, a Transport: car bus quarry to the Somersby Reservoir. The track then leads past some rural properties and across the Visit www.wildwalks.com for more info delightful Robinson Creek among the Gymea Lilies before finishing with a section of road walking to the Somersby Store. Brisbane Water National Park Side trips and Alternate routes mentioned in these notes are not included in the tracks overall rating, distance or time estimate. The notes only describe the side trips and Alternate routes in one direction. Allow extra time for resting and exploring areas of interest. Please ensure you and your group are well prepared and equipped for all possible hazards and delays. The authors, staff and owners of wildwalks take care in preparing these notes but will not accept responsibility for any inconvenience, loss or injury sustained by using these notes or maps. Please take care and share your experience through the website. -
Macrobrachium Intermedium in Southeastern Australia: Spatial Heterogeneity and the Effects of Species of Seagrass
MARINE ECOLOGY PROGRESS SERIES Vol. 75: 239-249, 1991 Published September 11 Mar. Ecol. Prog. Ser. Demographic patterns of the palaemonid prawn Macrobrachium intermedium in southeastern Australia: spatial heterogeneity and the effects of species of seagrass Charles A. Gray* School of Biological Sciences, University of Sydney, 2006, NSW. Australia ABSTRACT. The effects of species of seagrass (Zostera capricorni and Posidonia australis) on spatial and temporal heterogeneity in the demography of estuarine populations of the palaemonid prawn Macrobrachium intermedium across 65 km of the Sydney region, southeastern Australia, were examined. Three estuaries were sampled in 1983 and 1984 to assess the magnitude of intra- and inter- estuary variability in demographic characteristics among populations. Species of seagrass had no effect on the demographic patterns of populations: differences in the magnitude and directions of change in abundances, recruitment, reproductive characteristics, size structures and growth were as great among populations within each species of seagrass as those between the 2 seagrasses Abiotic factors, such as the location of a meadow in relation to depth of water and distance offshore, and the interactions of these factors with recruiting larvae are hypothesised to have greater influence than the species of seagrass in determining the distribution and abundance of these prawns. Spatial and temporal heterogeneity in demography was similar across all spatial scales sampled: among meadows (50 m to 3 km apart) in an estuary and among meadows in all 3 estuaries (10 to 65 km apart). Variability in demographic processes among populations in the Sydney region was most likely due to stochastic factors extrinsic to the seagrasses then~selves.I conclude that the demography of seagrass-dwelling estuarine populations of M. -
“Are New Developments Cleaning up the Cooks River Or Creating More Problems?”
Capacity Building and training needs analysis: Stage 1 Report “Are new developments cleaning up the Cooks River or creating more problems?” FINAL Brian Keogh 24 June, 2016 Report Basis This report partially fulfils two Cobalt59 requirements: It provides a baseline evaluation of the capacity of the Cooks River councils within a critical systems area (planning assessment in relation to water management). It provides a training assessment that will assist in developing this capacity. Page 1 of 46 Contents 1. Executive Summary ....................................................................................................... 3 State Environment Protection Policies (SEPP) .................................................................. 3 Local Environment Plans (LEP) ......................................................................................... 3 Development Control Plans (DCP) .................................................................................... 4 Training Recommendations ............................................................................................... 7 2. Capacity Assessment – Systems ................................................................................... 9 3. Background .................................................................................................................. 11 4. Planning Overview ....................................................................................................... 13 5. NSW State Environment Protection Policies (SEPPs) ................................................. -
The March 1978 Flood on the Hawkesbury and Nepean
... I'., The March, 1978 flood on the Hawkesbury and Nepean River between Penrith and Pitt Town S. J. Riley School of Earth Sciences, Macquarie University, - North Ryde. N. S.W. 2113 .. ,.. ... .. ... ..... .. - ~ . .. '~,i';~;: '~ It'i _:"to "\f',. .,.,. ~ '.! . I .... I ,', ; I I ' }, I , I , I The March, 1978 flood on the I Hawkesbury and Nepean River I .. between PenDth and Pitt Town I I I I S.J. Riley 1 f I :''',i I I School of Earth Sciences, I Macquarie University, ·1 North Ryde. N.S.W. 2113 I I',.. , ··1 " " ., ~: ". , r-~.I··_'~ __'_'. ~ . '.," '. '..a.w-.,'",' --~,~"; l .' . - l~' _I,:.{·_ .. -1- Introduction As a result of three days of heavy rainfall over the Hawkesbury c:ltchment in March, 1978 floods occurred on all the streams in the Hawkesbury system. These floods caused considerable property damage and resulted in morphological changes to the channels and floodplains 1 of, the Hawkesbury system. This paper describes the flodd in the Hawkesbury-Nepean system in the reach'extending from Penrith to Pitt Town •. Storm Pattern An intense low pressure cell developed over the Coral Sea on the 16th March, 1978. This low pressure system travelled southeast towards the Queensland coast and gained in intensity (Fig.l). On the 18th March it,appeared that the cell would move eastwards away from Australia. However, the system reversed its direction of travel and moved inland. Resultant wind systems brought warm moist air from ,the east onto the .. " coast of New South Wal,es. Consequently, heavy rainfall$ occurred from f I .. the 18th to 24th March over the whole of eastern New South Wales. -
Jellyfish Catostylus Mosaicus (Rhizostomeae) in New South Wales, Australia
- MARINE ECOLOGY PROGRESS SERIES Vol. 196: 143-155,2000 Published April 18 Mar Ecol Prog Ser l Geographic separation of stocks of the edible jellyfish Catostylus mosaicus (Rhizostomeae) in New South Wales, Australia K. A. Pitt*, M. J. Kingsford School of Biological Sciences, Zoology Building, A08 University of Sydney, New South Wales 2006, Australia ABSTRACT: The population structure of the commercially harvested jellyfish Catostylus mosaicus (Scyphozoa, Rhizostomeae) was investigated in estuaries and bays in New South Wales, Australia. Variations in abundance and recruitment were studied in 6 estuaries separated by distances ranglng from 75 to 800 km. Patterns of abundance differed greatly among estuaries and the rank abundance among estuaries changed on 5 out of the 6 times sampling occurred. Great variation in the timing of recruitment was also observed among estuaries. Variations in abundance and recruitment were as extreme among nearby estuaries as distant ones. Broad scale sampling and detailed time series of abundance over a period of 2.7 yr at 2 locations showed no consistent seasonal trend in abundance at 1 location, but there was some indication of seasonality at the second location. At Botany Bay, the abun- dance of medusae increased with distance into the estuary and on 19 out of the 30 times sampling occurred medusae were found at sites adjacent to where rivers enter the bay. Medusae were found to be strong swimmers and this may aid medusae in maintaining themselves in the upper-reaches of estu- aries, where advection from an estuary is least likely. Variability in patterns of abundance and recruit- ment suggested regulation by processes occurring at the scale of individual estuaries and, combined with their relatively strong swimming ability, supported a model of population retention within estuar- ies. -
Brisbane Water Oyster Farmers Environmental
BRISBANE WATER OYSTER FARMERS ENVIRONMENTAL MANAGEMENT SYSTEM OLUNTARY NDUSTRY RIVEN NVIRONMENTAL NITIATIVE A V , I -D E I 0 | P a g e BRISBANE WATERS OYSTER FARMERS COMMITMENT It is the policy of the Brisbane Water Oyster Farmers to conduct all aquaculture activities in an environmentally responsible manner, appropriate to the nature and scale of operations. The Brisbane Water Oyster Farmers recognise that they have a responsibility to cultivate oysters on behalf of the community as sustainably as current technology and techniques allow, and to continually improve as new methods develop. Oyster farmers have a vested interest in maintaining and improving the local environment, with their livelihoods dependant on the health and productivity of the estuary. The oyster growers are demonstrating their commitment by voluntarily participating in this industry -driven Environmental Management System. To achieve this Brisbane Water Oyster Farmers will: Comply with relevant laws and regulations and implement industry best practice (e.g. Oyster Industry Sustainable Aquaculture Strategy) Plan for environmental hazards and work towards mitigating their potential impacts and respond to emergency situations working with the appropriate authorities Recognise and protect the cultural and aesthetic values of Brisbane Waters and its catchment Cultivate oysters in a manner that minimises: resource consumption; waste production; pollution Communicate openly with relevant stakeholders on environmental matters Contribute to scientific research and innovation relevant to oyster cultivation and estuarine environments Strive for continual improvement 1 | P a g e Brisbane Water Oyster Farmers provide healthy sustainable local seafood to the community Oysters have been consumed by Aboriginal Australians for thousands of years with shell middens dating back as far as 6,000 B.C. -
Towra Point Nature Reserve Ramsar Site: Ecological Character Description in Good Faith, Exercising All Due Care and Attention
Towra Point Nature Reserve Ramsar site Ecological character description Disclaimer The Department of Environment, Climate Change and Water NSW (DECCW) has compiled the Towra Point Nature Reserve Ramsar site: Ecological character description in good faith, exercising all due care and attention. DECCW does not accept responsibility for any inaccurate or incomplete information supplied by third parties. No representation is made about the accuracy, completeness or suitability of the information in this publication for any particular purpose. Readers should seek appropriate advice about the suitability of the information to their needs. The views and opinions expressed in this publication are those of the authors and do not necessarily reflect those of the Australian Government or of the Minister for Environment Protection, Heritage and the Arts. Acknowledgements Phil Straw, Australasian Wader Studies Group; Bob Creese, Bruce Pease, Trudy Walford and Rob Williams, Department of Primary Industries (NSW); Simon Annabel and Rob Lea, NSW Maritime; Geoff Doret, Ian Drinnan and Brendan Graham, Sutherland Shire Council; John Dahlenburg, Sydney Metropolitan Catchment Management Authority. Symbols for conceptual diagrams are courtesy of the Integration and Application Network (ian.umces.edu/symbols), University of Maryland Center for Environmental Science. This publication has been prepared with funding provided by the Australian Government to the Sydney Metropolitan Catchment Management Authority through the Coastal Catchments Initiative Program. © State of NSW, Department of Environment, Climate Change and Water NSW, and Sydney Metropolitan Catchment Management Authority DECCW and SMCMA are pleased to allow the reproduction of material from this publication on the condition that the source, publisher and authorship are appropriately acknowledged. -
Coastal Storms in Nsw and Their Effect on the Coast
I I. COASTAL STORMS IN N.s.w. .: AUGUST & NOVEMBER 1986 .1 and Their Effect on the Coast I 'I I 1'1 ! I I I I I I I I I I , . < May 198,8 , 'I " I I : COASTAL STORMS· IN N.s.w. I AUGUST & NOVEMBER 1986 I and Their Effect on the Coast I I I I I 1: 1 I I I I I M.N. CLARKE M.G. GEARY I Chief Engineer Principal Engineer I Prepared by : University of N.S.W. Water Research Laboratory I bID IPTIID311IIcr: ~Th'¥@~ , I May 1988 ------..! Coaat a Rivera Branch I I I I CONTENTS LIST OF FIGURES ( ii ) I LIST OF TABLES (iv) 1. INTRODUCTION I 2. SUMMARY 2 3. ENVIRONMENTAL CONDITIONS 5 I 3.1 METEOROLOGICAL DATA 5 3.2 TIDE LEVELS 7 3.3 WAVE HEIGHTS AND PERIODS 10 I 3.4 STORM mSTORY - AUGUST 1985 TO AUGUST 1986 13 4. WAVE RUN-UP 15 I 4.1 MANLY WARRINGAH BEACHES 15 4.2 BATEMANS BAY BEACHES 15 I 4.3 THEORETICAL ASSESSMENT 16 4.4 COMPARISON OF MEASURED AND THEORETICAL RUN-UP LEVELS 23 5. BEACH SURVEYS 25 ·1 5.1 GOSFORD BEACHES 25 5.2 MANLY W ARRINGAH BEACHES 28 I 5.3 BATEMANS BAY BEACHES 29 6. OFFSHORE SURVEYS . 30 6.1 SURVEY METHODS 30 I 6.2 GOSFORD BEACHES 30 6.3 WARRINGAH BEACHES 31 I 6.4 ASSESSMENT OF ACCURACY OF OFFSHORE SURVEYS 32 7. OFFSHORE SEDIMENT SAMPLES - GOSFORD BEACHES 34 7.1 SAMPLE COLLECTION 34 I 7.2 SAMPLE CLASSIFICATION 34 , 7.3 SAMPLE DESCRIPTIONS 34 I 7.4 COMPARISON OF 1983/84 AND POST STORM OFFSHORE DATA 36 8.