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Approved Document OPW24-0047 Noosa Springs Golf & Spa Resort Turf & Vegetation Management Plan 2024-25.pdf
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APPROVED DOCUMENT
OPW24/0047
NOOSA COUNCIL
18 FEBRUARY 2025
NOOSA SPRINGS GOLF
AND SPA RESORT TURF
AND VEGETATION
MANAGEMENT PLAN
Peter Woods: Golf Course Superintendent
NOOSA SPRINGS Links Drive, Noosa Heads, QLD 4567
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Section 2
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Contents 1. Introduction………………………………………………………………………………………………….3 2. Nutrition……………………………………………………………………………………………………… 5 3. Irrigation Suitability testing……………………………………………………………………………..10 4. Irrigation CirrusPRO……………………………………………………………………………………….11 5. POGO PRO Moisture Meter……………………………………………………………………………..13 6. Herbicides……………………………………………………………………………………………………16 7. Fungicides……………………………………………………………………………………………………19 8. Insecticides………………………………………………………………………………………………….20 9. TurfKeeper……………………………………………………………………………………………………23
Section 3
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
1.Introduction
1. Site Analysis and Assessment:
• Conduct a thorough assessment of the golf course site, considering factors such
as soil type, drainage patterns, microclimates, and prevailing weather conditions
in Noosa.
• Identify areas prone to erosion, compaction, and turf diseases.
• Assess the existing turf species and their adaptability to local climatic
conditions.
2. Goal Setting:
• Define the primary goals of turf management, such as improving playability,
enhancing aesthetics, conserving water, reducing chemical inputs, and
promoting environmental sustainability.
3. Turfgrass Selection:
• Select turfgrass species and cultivars suitable for SEQ QLD's climate, soil
conditions, and maintenance requirements. Greens – Tifdwarf, Tees, fairways,
surrounds and Roughs – Wintergreen and Greenlees Park.
• Consider factors such as shade tolerance, wear resistance, drought tolerance,
and disease resistance when choosing turfgrass varieties.
4. Soil Management:
• Implement soil testing to assess nutrient levels, pH, and organic matter content.
• Based on soil test results, develop a fertiliser program tailored to the specific
nutrient needs of the turfgrass species.
• Incorporate practices such as aeration, topdressing, and soil amendments to
improve soil structure, water infiltration, and root development.
5. Water Management:
• Implement efficient irrigation practices to minimize water usage while
maintaining turf quality.
• Use moisture sensors and weather-based irrigation controllers to optimize
irrigation scheduling based on real-time environmental conditions.
• Promote water conservation through proper irrigation system maintenance, leak
detection, and the use of drought-tolerant turfgrass species.
6. Pest and Disease Management:
• Monitor turfgrass regularly for signs of pests, weeds, and diseases.
• Implement integrated pest management (IPM) strategies, including cultural
practices, biological controls, and targeted pesticide applications, to minimize
pest damage while reducing chemical inputs.
Section 4
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
• Encourage natural predators of turf pests and promote biodiversity to enhance
ecosystem resilience.
7. Cultural Practices:
• Schedule mowing operations based on turfgrass growth rates, ensuring optimal
cutting heights and frequency to promote healthy turf and consistent playing
conditions.
• Implement proper grooming practices, such as Verti cutting and dethatching, to
reduce thatch buildup and improve turfgrass strength, water penetration and
firmness.
• Coordinate cultural practices with environmental factors such as temperature,
rainfall, and humidity to minimize stress on the turfgrass.
8. Environmental Stewardship:
• Develop and implement an environmental management plan to protect sensitive
habitats, conserve water resources, and minimize chemical runoff into adjacent
water bodies.
• Incorporate native vegetation and wildlife habitats into course design to
enhance biodiversity and ecosystem services.
• Educate staff, members, players and residents about the importance of
environmental stewardship and sustainable turf management practices.
9. Monitoring and Evaluation:
• Establish performance metrics and benchmarks to evaluate the effectiveness of
turf management practices.
• Regularly monitor turfgrass health, soil conditions, water usage, pest
populations, and other key indicators to identify trends and areas for
improvement.
• Use monitoring data to refine management strategies and adapt to changing
environmental conditions over time.
10. Continual Improvement:
• Foster a culture of continual improvement and innovation within the turf
management team.
• Stay informed about advances in turfgrass science, technology, and best
management practices through professional development opportunities,
industry conferences, and peer networking.
• Solicit feedback from golfers, course staff, and other stakeholders to identify
areas for enhancement and prioritize investments in course maintenance and
infrastructure.
Section 5
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN By following this turf management plan, Noosa Springs Golf Resort can maintain high-quality playing surfaces, protect the environment, and enhance the overall experience for golfers while ensuring long-term sustainability and resilience in the face of environmental challenges. 2. Nutrition Greens Nutrition program 1.2Ha total greens space of Tifdwarf couch 2 to 2.5kg actual Nitrogen (Ha) per year (this will depend on growth rate/season) Potassium actuals will be determined from soil tests. Total of 4 x granular applications per year, - February Greens Renovations, May application (Leading into winter) September (Winter repair) and November Greens renovations. Nitrogen, soluble / liquid applications (Fortnightly Boom spray applications) 12 x per year with the aim of light consistent growth patterns. Minimise growth/thatch build up. Nitrogen sources – Organic or has a large percentage of UMAXX / UFLEXX stabilised nitrogen technology, this provides protection against all three forms of nitrogen loss – Leaching, denitrification and volatilization. For example, (MP SPRING START16 - 1 - 10 + 2Ca + 1Mg + 0.5Mn 65% of nitrogen as UMAXX and 25% as IBDU for ultimate turf response for spring regeneration) or liquid, (MP BRILLIANCE 20 - 0 - 0 + 6Fe + 1Mg, High analysis stabilised liquid nitrogen fertiliser for long lasting feeding of turf. 6% iron for deeper green colour and greater turf vitality. 1% magnesium for enhanced chlorophyll production) (Or similar product). Other products used, MP Promote, MP Reinforce and Vitalise (Bio stimulants) Specially formulated liquid organic complex to stimulate and support turf during stressful growth periods. It contains a high concentration of plant derived amino acids in combination with beneficial microbes, humic and fulvic acid, kelp and carbohydrates to boost soil biology, increase soil carbon, stimulate plant growth and break down organic matter. • Inoculates treated plants with beneficial VAM fungi (40,000 propagules per 10 L) • Greater uptake of soil applied fertiliser - P, K, Fe, Zn • Improved drought tolerance and water use efficiency • Contains plant and root stimulants and trace minerals
Section 6
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
Green Nutrition program - Guide
100 Growth Potential
90
80
70
60
50
Warm
40 GP
30
20
10
0
1 2 3 4 5 6 7 8 9 10 11 12
Section 7
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Plant growth regulator may be added to control growth patterns in the months of December, January and February. Growing Degree Days (GDD) calculator/ method is used on our greens with PGR applications. See below example,
Section 8
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Six Monthly Soil tests to determine nutrient deficiencies with Potassium, Phosphorus, Calcium and traces - applied as required/recommended for optimum turf health and performance. Monitor soil pH and Sodium levels – Apply amendments, Lime, gypsum or dolomite as per recommendation/results Tees Nutrition Program 1.5Ha Winter Green/Greenlees Park Couch (Includes driving range Tee) Maximum of 2.5Kg Actual Nitrogen (Ha) per year (this will depend on growth rate/season) Maximum of 4 x granular applications per year, - February Tees Renovations, May application (Leading into winter) September (Winter repair) and November Tees renovations. 2 x Applications of MP COUCHMASTER 23 - 1 - 10 + 1.5Fe + 1.5Mg + 0.25Mn With 70% of nitrogen supplied as UMAXX, ultimate formula for feeding cool season and warm season grasses. Added micronutrients ensure fast green up and improved plant uptake. 2 x Applications of Poultry Fines at Renovations along with Gypsum/Lime or Dolomite (Depending on soil test results, pH/ Calcium levels)
Section 9
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN 6 x Foliar fertiliser applications with MP BRILLIANCE 20 - 0 - 0 + 6Fe + 1Mg, High analysis stabilised liquid nitrogen fertiliser for long lasting feeding of turf. 6% iron for deeper green colour and greater turf vitality. 1% magnesium for enhanced chlorophyll production. (Or similar product) Plant growth regulator may be added to control growth patterns in the months of December, January and February Fairways Nutrition Program 14Ha Winter Green/Greenlees Park Couch (Includes driving range fairway) Maximum of 2Kg Actual Nitrogen (Ha) per year (this will depend on growth rate/season) 1 x yearly Granular Application in September/October Renovations of MP COUCHMASTER 23 - 1 - 10 + 1.5Fe + 1.5Mg + 0.25Mn With 70% of nitrogen supplied as UMAXX, ultimate formula for feeding cool season and warm season grasses. Added micronutrients ensure fast green up and improved plant uptake. (Or similar product) 1 x yearly application of either Gypsum/Lime or Dolomite (Depending on soil test results, pH/ Calcium levels) in September/October Renovations. 8 x Foliar fertiliser applications with MP BRILLIANCE 20 - 0 - 0 + 6Fe + 1Mg, High analysis stabilised liquid nitrogen fertiliser for long lasting feeding of turf. 6% iron for deeper green colour and greater turf vitality. 1% magnesium for enhanced chlorophyll production. (Or similar product) PGR – Plant growth regulator may be added to control growth patterns in the months of December, January and February. Roughs Nutrition Program 15 Ha Winter Green/Greenlees Park Couch. Only spot fertilise, drive on, drive off areas in spring with Poultry Fines. Bunkers 71 bunkers in total, includes the practice bunker Total sqm = 7067 Rake and broom faces twice a week Whipper Snip, edge and pull couch runners monthly Apply ‘PGR’ Plant growth regulator, monthly on edges to slow down growth
Section 10
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Irrigation suitability Testing Six monthly irrigation suitability tests in both the freshwater lake and effluent lake.
Section 11
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
Noosa Springs installed a new irrigation system which was completed in October 2023. Brand
new communications, 900 x new irrigation 752 series rotors and IC central control system
(Rainbird Cirrus Pro)
Rain Bird 752 Series
Full Circle & Part Circle Golf Rotors
Rain Bird 752 Series Rotors offer unmatched flexibility, industry-leading uniformity, and a
consistent rotation speed. Full/part-circle 752 Series make it easier to maintain flawless turf.
Turn-of-a-screw adjustments and top serviceability saves you time, water, electricity and
labour.
The CirrusPRO™ IC: Integrated Control irrigation system by Rain Bird offers several features
that make it stand out:
1. Central Control: CirrusPRO allows you to adjust settings from any smart device,
providing real-time updates right from the system’s map1.
2. Hybrid Control: It lets you manage multiple types of field control (IC Systems, Satellite
Systems, Decoder Systems) for total control1.
3. Efficient Watering: CirrusPRO eliminates manual runtime calculations based on
precipitation rate, enabling precise irrigation by measurements2.
4. Customizable Interface: You can access all system features and course data from
anywhere, customize the interface, and choose from 10 languages1.
5. Real-Time Monitoring: Get up-to-the-minute information on station irrigation history,
remaining time, and active adjustments1.
6. Complete Course View: Easily manage multiple stations, perform audits, and conserve
water with crucial data at your fingertips1.
In summary, CirrusPRO combines smart features, ease of use, and efficient water management
for golf courses3.
Section 12
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN CIRRUSPRO™ — COURSE ACTIVITY PROGRAMS REPORTS — SYSTEMSETTINGS force) O) » a is Ce Cet Sore feed HB © WweaTHer oe BOON CUCL) rarer Ee IC) , ; vol se ecm al Oe ee eee Poa) Peete
Section 13
Section 14
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN 10:13 = 4) | 40275L FLOGRAPH - : — cS eee a en avo Cioite)|aelereyein Theoretical 5) Flow Rate (Li
Section 15
Section 16
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN POGO Pro moisture meter was purchased in 2022, where Moisture, EC and temperature are recorded along with the precise GPS location with every sample taken with the POGO. By viewing todays and past Visual Insight reports, along with automatically generated distribution uniformity analysis, you can see how moisture changes day to day or is impacted by routine operational procedures, and therefore know how your irrigation methods should be adjusted.
Section 17
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
rs 8th
NOOSA SPRINGS GOLF RESORT
Name
8th e
Status { e
Zone Type
Green v
Grass Type
Tifdwarf Bermudagrass v
Root Zone Type
USGA Specification v
Zone Boundary a
Number of points
45
Approach Marker
Set
Area
640.53 m?
Perimeter Length
99.9 meters
&
Section 18
Section 19
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN € 8th Warnings NOOSA SPRINGS GOLF RESORT Moisture (%) Critical Low Low Optimal High Critical High 16 22 22 28 28 34 EC (dS/m) o Critical Low Low Optimal High Critical High 0.15 0.2 0.2 0.28 0.28 0.33 § Temperature (°C) oa Critical Low Low Optimal High Critical High 12.8 18.3 18.3 25.6 25.6 31.1 jE Soil Temperature (°C) o Critical Low Low Optimal High Critical High 12.8 18.3 18.3 25.6 25.6 311, Salinity Index o Critical Low Low Optimal High Critical High 0.78 0.89 0.89 Ld Led. 1.3
Section 20
Section 21
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Herbicides / Greens No Boom spraying of herbicides on any green surfaces. Hand weed Spot dab weeds with the Yates Weeding Brushes. Only Turf Registered Herbicides used, HALOSULFURON-METHYL – Selective control of Sedges DSMA – Selective control of Paspalum, Summer Grass, Crab Grass Herbicides/Tees No Boom spraying of herbicides on any Tee surfaces. Only spot spray weeds (Knapsack, 100L Silvan Spot spray Tank or C Dax 400L spot sprayer) Only Turf Registered Herbicides ARE used, Chemical Groups to be swapped to avoid resistant issues. Where possible, the lowest chemical schedule herbicide is to be used. Below is an example of what is typically used, HALOSULFURON-METHYL – Selective control of Sedges DSMA/MSMA – Selective control of Paspalum, Summer Grass, Crab Grass BROMOXYNIL + MCPA – Selective Control of Broadleaf weeds QUINCLORAC - Selective control of Summer Grass, Kikuyu and Clover MONUMENT LIQUID - Selective control of Sedges, Broadleaf, Kikuyu and Bahia Grasses Herbicides/Fairways Pre-emergent Herbicides – Spectacle / Barricade – Pre -emergent control on Weeds – Boom spray. This minimises the post herbicide usage over a 6–12-month period. Post Herbicide usage below, Only spot spray weeds (Knapsack, 100L Silvan Spot spray Tank or C Dax 400L spot sprayer) Only Turf Registered Herbicides are used, Chemical Groups to be swapped to avoid resistant issues. Where possible, the lowest chemical schedule herbicide is to be used. Below is an example of what is typically used, HALOSULFURON-METHYL – Selective control of Sedges DSMA/MSMA – Selective control of Paspalum, Summer Grass, Crab Grass BROMOXYNIL + MCPA – Selective Control of Broadleaf weeds QUINCLORAC - Selective control of Summer Grass, Kikuyu and Clover MONUMENT LIQUID - Selective control of Sedges, Broadleaf, Kikuyu and Bahia Grasses
Section 22
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Herbicides/Roughs NO BOOM SPRAY BUFFER ZONES adjacent to wetlands and sensitive areas in the Roughs. Only spot spray weeds (Knapsack, 100L Silvan Spot spray Tank or C Dax 400L spot sprayer) Only Turf Registered Herbicides are used, Chemical Groups to be swapped to avoid resistant issues. Where possible, the lowest chemical schedule herbicide is to be used. Below is an example of what is typically used, HALOSULFURON-METHYL – Selective control of Sedges DSMA/MSMA – Selective control of Paspalum, Summer Grass, Crab Grass BROMOXYNIL + MCPA – Selective Control of Broadleaf weeds QUINCLORAC - Selective control of Summer Grass, Kikuyu and Clover MONUMENT LIQUID - Selective control of Sedges, Broadleaf, Kikuyu and Bahia Grass
Section 23
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN Landscape/Garden areas Spot spray weeds (Knapsack, 100L Silvan Spot spray Tank) Use of Aquatic/Registered Glyphosate only Mulch and Native grasses in designated areas to reduce use of Herbicides Fungicide Program – Greens surfaces 1. Disease Identification and Monitoring - Regular Scouting: Inspect greens frequently for early signs of disease. This includes checking for discoloration, patchiness, or unusual growth patterns. - Record Keeping: Maintain detailed records of disease occurrences, weather conditions, and treatment efficacy to help predict future outbreaks. 2. Cultural Practices - Mowing Practices: Adjust mowing heights to reduce stress on the turf. Avoid mowing when the grass is wet to prevent disease spread. - Aeration and Thatch Management: Regular aeration helps improve soil drainage and reduces thatch, which can harbor pathogens. - Irrigation Management: Water deeply but infrequently to promote deep root growth. Avoid watering in the late afternoon or evening to minimize leaf wetness periods that favour fungal growth. - Nutrient Management: Follow soil test recommendations for fertilization. Avoid excessive nitrogen, which can promote succulent growth susceptible to diseases. 3. Fungicide Selection - Broad-Spectrum and Targeted Fungicides: Use a mix of broad-spectrum fungicides and those targeted at specific pathogens identified on the greens. - Rotational Programs: Rotate fungicides with different modes of action to prevent resistance development. Follow the Fungicide Resistance Action Committee (FRAC) guidelines for rotating products. - Systemic and Contact Fungicides: Incorporate both systemic fungicides, which move within the plant, and contact fungicides, which remain on the surface, for comprehensive protection. 4. Application Timing - Preventive Applications: Apply fungicides preventively, especially during periods of known disease pressure based on historical data and current weather forecasts.
Section 24
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN - Curative Applications: Use curative treatments at the first sign of disease, ensuring the fungicide used is effective against the identified pathogen. 5. Common Diseases and Treatment Schedules - Dollar Spot (Sclerotinia homoeocarpa) Common during warm, humid conditions. Preventive treatments every 14-21 days during peak periods using fungicides such as iprodione, propiconazole, or thiophanate-methyl. - Pythium Blight (Pythium spp.) Thrives in hot, humid conditions, especially in poorly drained areas. Preventive applications with mefenoxam or fosetyl-Al before forecasted periods of high humidity. - Brown Patch (Rhizoctonia solani) Typically occurs in warm, wet conditions. Preventive applications of azoxystrobin, chlorothalonil, or flutolanil during humid weather. - Anthracnose (Colletotrichum cereale) Common during stress periods (high temperatures, drought). Use preventive treatments with fungicides such as azoxystrobin or thiophanate- methyl, especially when turf is under stress. - ERI (ectotrophic root-infecting) fungi are a factor in causing patchiness and poor root health in couch grass. ERI fungi grow over the root surface before they penetrate the inside of the root. ERI disease can cause thinning out of the surface and straw-coloured patches that range in size from 30 cm to 1 metre in diameter. ERI fungi are a complex of soil-borne pathogens that cause turfgrass patch diseases such as summer patch, take-all patch, and spring dead spot. 6. Environmental Considerations - Regulatory Compliance: Ensure all fungicides used are registered and approved by the Australian Pesticides and Veterinary Medicines Authority (APVMA). - Environmental Safety: Minimize drift and runoff by following best practices for application. Use buffer zones around water bodies and sensitive areas. 7. Review and Adaptation - Annual Review: At the end of each season, review the program’s effectiveness, disease occurrences, and product performance. - Adjustments: Make necessary adjustments based on new research, product availability, and changes in disease patterns.
Section 25
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
Fungicide Program – Used as a guide
Season WINTER SPRING SUMMER AUTUMN Winter
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 5 1 2 3 4 1 2 3 4 5
Peak Period of Damage
Pythium Program
Season WINTER SPRING SUMMER AUTUMN Winter
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 5 1 2 3 4 1 2 3 4 5
[email protected]/ha (wash-in) 1 1
Segway @ 1L/ha 1
Signature Extra @ 11 kg/ha 1 1 1
General Disease Program
Season WINTER SPRING SUMMER AUTUMN WINTER
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5
Peak Period of Damage
General Disease Program
Season WINTER SPRING SUMMER AUTUMN WINTER
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5
Interface [email protected] L/ha 1 1
Dedicate @ 3 L/ha 1 1 1
Reserve StressGard @ 20L/ha 1
Exteris Stressgard @ 10 L/ha 1
Heritage MAXX @ 6 L/ha 1
Bayfidan @ 6 L/ha 1
Headway MAXX @ 9 L/ha 1
[email protected]/ha (Fairy Ring) 1 1 1
StressGard Cover
Season WINTER SPRING SUMMER AUTUMN WINTER
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5
Interface
Reserve
Exteris
Signature
Pythium Cover
Season WINTER SPRING SUMMER AUTUMN WINTER
Month Aug Sep Oct Nov Dec Jan Feb Mar Apr May June July
Week 1 2 3 4 5 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5 1 2 3 4 1 2 3 4 1 2 3 4 5
Signature - Primary
Subdue MAXX - Primary
Banol - Primary
Headway MAXX - Secondary
Heritage MAXX - Secondary
Conclusion
Implementing a fungicide program for the golf course greens at Noosa Springs requires a
balanced approach that integrates regular monitoring, cultural practices, and strategic
fungicide applications. Tailoring the program to the specific conditions of the golf course and
being proactive in disease management will help maintain healthy and high-quality greens.
Insecticide program – Greens surfaces
Greens are treated on a preventative program with Acelepryn insecticide.
ACELEPRYN is an anthranilic diamide insecticide in the form of a suspension concentrate.
ACELEPRYN Turf Insecticide provides unmatched, season long grub and caterpillar control with
a single application. The benefits are protection for your turf against key insect pests as well as
peace of mind that you are looking after yourself, your staff and people enjoying the greenspace.
Features
Up to 6 months protection at the higher application rate
Exempt from poison scheduling
High turf safety
Section 26
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN
Benefits
Season-long grub and insect control
Ease of use with no re-entry periods and no PPE requirements
Low environmental impact - low toxicity to most non-target animals, including birds, fish
and bees
Venom Professional – (Bifenthrin) only used as curative knockdown if required.
Monarch (Fipronil) only used as curative knockdown if required, for Mole cricket and ants.
Tees-Fairways and Roughs
Are only to be treated on a curative program, and if/when turf surfaces are being visibly
damaged to an extent that impacts playability.
Lawn Armyworm and African Black beetle larvae/adults are our main pests in these playing
surfaces.
Venom Professional – (Bifenthrin) only used as curative knockdown if required and spot
treatment depending on insect pressure.
TurfKeeper
TurfKeeper has been designed by turf professionals who collectively have over 50 years’
experience in the turf industry. Conceived as a single, personalised and fully inclusive platform to
assist turf professionals deliver their daily responsibilities and driven by a desired for better
information and subsequent knowledge to inform future decision making.
In a web-based environment, TurfKeeper contains modules that deal with all the key areas of turf
management.
• Staff management - Important staff details, qualifications and training, bespoke access
levels, time sheet reports, plan, assign and track holidays, absence recording and
tracking, wage costs, working hours, overtime & time in lieu
• Task planning - schedule your day-to-day plans using our dynamic and effective planning
tool. Organise & plan daily tasks across an unlimited number of customisable areas,
reload regular daily routines, set maintenance schedules and future agronomic programs
• Machinery management - Links to spare part inventory, track fuel usage & cost,
equipment depreciation rates, downtime & repair costs, future maintenance planning and
alerts, full on-line maintenance records
• Inventory management - Categorise stock, manage machine spares, set minimum stock
levels, stock alerts
Section 27
NOOSA SPRINGS GOLF AND SPA RESORT TURF AND VEGETATION MANAGEMENT PLAN ena Oo Day Week Month Friday 21st June 2024 Search Tasks 24th June [# 25th June 26th June 27th June min 12.3°C max20.0°C min 13.9°C max 21.5°C min 13.9°C max 22.2°C min 16,8°C max20,0°C $20 Koh 0.0mm rainfall SE 12.Kph 028mm rant SE 10 Koh 0.80mm rainfall $19 Kph 31.54 rina & Routines | Savenew Routine plete alt Tasks ae Per Dad a ¥ Collapse Chart 00:00 01:00 02:00 03:00 04:00 12:00 13:00 14:00 18:00 16:00 Peter Woods (EET Damian Spats Darren Nopper Cr Lasse Abi Winston Quennet tan Tose Peter Bone ey dustin Cattanach @ Peter wooas Anthony Brown i Bai cog 6 Day Week Month Friday 21st June 2024 Search Tasks — +} Today's Direction of Cut Area: Applications Cut Type: a bo Direction: Notes: Crean Roll Green Reurey Cees ,
Section 28
Section 29
Managing wetlands/Lakes in Noosa Springs involves several critical tasks to ensure the health and sustainability of these ecosystems. Here’s an overview of the key aspects of wetland/Lakes management at Noosa Springs: 1. Weeding Weeding is crucial for maintaining the balance of native plant species. It involves: • Manual Removal: Hand-pulling invasive species to prevent them from outcompeting native plants. • Mechanical Methods: Using tools or machinery to remove larger infestations. • Chemical Control: Applying herbicides selectively to target invasive species without harming native plants. 2. Native Plants Introducing and maintaining native plant species helps preserve the ecological balance. Key activities include: • Planting Native Species: Lepironia articulata, Isolepis nodosa, Carex appressa • Rehabilitation Projects: Restoring disturbed areas with native vegetation. • Monitoring: Regularly checking the health and spread of native plants. 3. Maintenance Methods Maintaining wetlands involves: • Regular Monitoring: Keeping track of water quality, plant health, and wildlife. Quarterly Nutrient water testing is carried out through ALS (Australian Laboratory Services) Strategic placement of Aerators (Currently 3 have been added in 2024). Use of Probiotics - BioStim (Biology) • Hydrological Management: Ensuring proper water levels and flow to support wetland functions. (As per weir on the 5th hole) • Erosion Control: Implementing measures to prevent soil erosion and sedimentation. Continued planting along the water edges with native wetland plants (To create habitat, food and help with erosion issues) and use of rocks through fast flow areas and on corners/bends where we have erosion evident. Targeted areas to plant out (Water edge) in 2024, 25, 26 and 27 financial years in red on map below.
Section 30
Section 31
4. Chemicals Used Chemicals, particularly herbicides, are used sparingly and with care. Used herbicides include: • Aquatic registered Glyphosate: For general nonselective weed control. • Aquatic-safe Herbicides: Specifically formulated for use on/near water bodies, Aquatic registered Glyphosate and Diquat for Salvinia, Hyacinth, Water primrose and Amazon Frogbit (Frogbit found in Noosa Springs in March 2024) to minimize environmental impact. (Registered -APVMA approved Chemicals) All sprayer operators/contractors are Licenced 5. Habitat Creation and Protection Creating and protecting habitats involves: • Building / Planting Structures: Installing features like bird nesting boxes, fish shelters, and amphibian habitats. • Buffer Zones: Establishing buffer zones around wetlands to protect them from runoff and pollution.
Section 32
BUFFER ZONES • Conservation Plans: Developing and implementing plans to safeguard critical habitats and biodiversity. 6. Floating Plant Management Managing floating plants is essential to prevent them from covering water surfaces completely, which can harm aquatic life. Strategies include: • Physical Removal: Manually or mechanically removing floating plants. • Biological Control: Introducing natural predators or competitors to control the growth of floating plants. • Chemical Treatment: Using herbicides selectively to manage excessive growth. (As above Registered -APVMA approved Chemicals) All sprayer operators/contractors are Licenced Effective wetland management in Noosa Springs requires a holistic approach that integrates these various strategies to maintain the ecological health and biodiversity of these important ecosystems.
Section 33
1. Pest Identification and Monitoring:
• Identify common pests, including insects, weeds, and diseases, that affect
turfgrass on golf courses in SE QLD.
• Implement regular monitoring programs to assess pest populations and identify
pest hotspots.
• Use scouting techniques, such as visual inspections, trapping, and sampling, to
monitor pest activity and population dynamics.
2. Cultural Practices:
• Implement cultural practices that promote healthy turfgrass and minimize pest
pressure, such as proper mowing, irrigation, and fertilization.
• Adjust cultural practices based on pest monitoring data and environmental
conditions to prevent pest outbreaks.
3. Biological Control:
• Introduce natural enemies of turf pests, such as predatory insects, parasitoids,
and microbial pathogens, to control pest populations.
• Enhance habitat diversity and biological control by maintaining naturalized
areas, planting insectary plants, and conserving beneficial insect populations.
4. Mechanical and Physical Control:
• Use mechanical methods, such as hand-pulling weeds and mechanical removal
of thatch, to manage pests without the use of chemicals.
• Implement physical barriers, such as mulches or covers, to exclude pests from
sensitive areas or prevent weed germination.
5. Chemical Control:
• Use pesticides judiciously and as a last resort, following the principles of IPM.
• Select pesticides with low toxicity to non-target organisms and minimal
environmental impact.
• Rotate chemical classes to prevent the development of pesticide resistance in
pest populations.
• Apply pesticides according to label instructions, considering factors such as
application timing, dosage, and environmental conditions.
6. Cultural and Biological Control of Weeds:
• Implement cultural practices that promote dense, healthy turfgrass stands,
which can outcompete weeds for resources.
• Use biological control agents, such as herbivorous insects or pathogens specific
to target weed species, to suppress weed populations.
Section 34
• Employ mechanical methods, such as hand-weeding or mowing at appropriate
heights, to manage weeds without reliance on herbicides.
7. Disease Management:
• Implement cultural practices that promote turfgrass health and reduce disease
susceptibility, such as proper irrigation, drainage, and aeration.
• Use disease-resistant turfgrass varieties whenever possible to minimize the
need for fungicide applications.
• Apply fungicides preventatively based on disease forecasting models or when
early symptoms of disease are observed.
8. Record Keeping and Evaluation:
• Maintain detailed records of pest monitoring data, control actions taken, and
their outcomes.
• Regularly evaluate the effectiveness of IPM strategies in managing pest
populations and reducing reliance on chemical controls.
• Use monitoring and evaluation data to refine IPM programs and adapt
management strategies over time.
By implementing these IPM strategies, golf courses in Noosa Springs Golf Course can effectively
manage pest populations while minimizing environmental impacts and promoting long-term
sustainability of turfgrass ecosystems. Regular monitoring, careful pest identification, and a
holistic approach to pest management are key components of a successful IPM program.
Section 35
Vegetation Management Plan
Noosa Springs Golf Course
Site Address: Noosa Springs Golf & Spa
Links Drive, Noosa Heads,
Queensland 4567
Responsible Noosa Council
Council:
Date: Friday, 30 August 2024
V1
Prepared by:
Matthew Duncan
Director / Principal Arborist
e: [email protected]
m: 0450 355 770
ABN: 68 153 548 531
Q U AL I FI C AT IO N S
Matthew holds an AQF Level 5 Diploma of Arboriculture
(AHC50510), an International Society of Arboriculture’s Tree
Risk Assessment Qualification, valid from 2015 to 2030, and
has worked in the arboricultural industry since 1994. Since its
establishment in 2011, Consult Arborist has been engaged to
provide arboricultural advice and guidance on private, civil,
and capital works projects from cross-sector clients
throughout Queensland where he is a Queensland
Arboricultural Association (QAA) Qualified Member and
Approved Consultant.
Section 36
I NTRODUCTION T REE P LANTING G UIDELINES P LAN T
• Pre-soak the root ball in the pot to ensure hydration of compost while you
Noosa Spring Golf Course is a members-only golf course located on the Steps to get it Right • Create the hole and de-compact the surrounding ground as required.
southern side of the Noosa Council suburb of Noosa Heads adjacent to • Drain the pot/plant in the hole while you
1. Identify suitable Planting Locations
Lake Weyba. The fairways are divided by densely treed corridors which • Prepare your stakes and ties
2. Choose the right tree for the right place
are a mix of remnant, natives, and augmented by planted landscape • Remove the pot/bag and tease out the root ball
3. Prepare the planting location
feature trees. • Prune the girdling/woody roots with sharp secateurs
4. Plant
5. Nourish & Maintain • Insert the stakes in the correct position
This Tree Management Plan is designed to guide the active management
• Position the tree at the correct depth in the hole – a stake can be used to
of the treescape at the golf course to ensure that they continue to enhance
the aesthetics, amenity, and strategic sporting prowess the trees provide L O C AT IO N , L O C AT IO N , L O C AT IO N help with levelling
Not every empty space is suitable for planting. It is important to consider • Backfill the hole, gently compressing the soil
for patrons.
the hydrology of the area, the use (occupancy) of the area, and the ultimate • Create the watering dish at the surface
size of the tree, all of which can determine the amount of maintenance • Mulch area the tree
T REESCAPE required for the future. When you find your location, you can decide on the • Water/feed – approximately 5-10 litres per tree depending on the
style best suited for purpose. hydration of soil.
The treescape at the Noosa Springs Golf Course is a combination of
mature and emerging natives and landscape feature trees. Each age class R IG H T T R EE , R IGH T P L AC E
of tree has different requirements for care and management. The style of planting is dependant on the outcome that is required;
individual trees planted alone for specimen or memorial value; linear
G ENERAL P RUNING T ECHNIQUES groups for shade; groups of threes or fives for interest; and mass planting
to create a boundary, privacy, cluster or forest effect.
D E A DW O O D & D ET AI L
The removal of dead wood (>40mm in diameter and/or 1m in length), Within public spaces, trees provide shade, amenity and a sense of
dysfunctional, diseased, weakly attached, and low-vigor branches from the wellbeing that endorses a sense of community. In public areas trees
tree’s canopy. planted in garden beds in groups of three or five contribute a greater impact
than single planting and are more practical and generally establish better.
L I FT P R UN E Where single trees are required, an increased mulched area will improve
Remove the lower branches from a tree to provide clearance. establishment. The initial plant size can be smaller and so more cost-
effective, maintenance and watering are more efficient. The planting bed
R E DU C T IO N
covers a larger area increasing the quantity and benefits of the mulch
Canopy reduction aims to reduce the overall size of a tree by reducing a
application. The shape and size of the beds can be tailored to suit the
tree’s height or spread. This is accomplished by pruning back the leaders
available space aiding maintenance as mowing around a larger mulch bed
and branch terminals to suitable secondary branches large enough to
is easier than individual trees which can in the end just hamper the
assume the terminal roles (at least one-third the diameter of the cut stem),
mowing.
while maintaining the tree’s form and structural integrity. Figure 1: NUFA-tree planting guide-HR – Arboriculture Australia
When the style of planting is known, and the location has been chosen,
End-weight reduction is achieved by trimming off the concentration of N O UR ISH & M AIN T A IN
species selection becomes easier. Always think of the fully-grown tree.
excessive wood and foliage weight towards the extremity of the branch to While the tree is establishing additional maintenance will be required
lessen the overall load and branch failure potential. P R EP AR AT IO N
• Moisture level monitoring – and watering if required
As a guide, an area measuring 2m x 6m can accommodate three trees at
Reduce and Retain is usually instructed for important habitat trees when • Regular applications of a plant food /soil conditioner as per manufacturer's
2m spacings with a 1m on either end. At this spacing, the trees have 12m2
the trees I no longer viable thereby reducing the tree to a safe height and instructions
of improved ground in which to establish. The tree sizes can range from
size to limit hazards while retaining the remainder, including many hollows, • Formative pruning
300mm pots up to 100L stock, within a few years the trees usually grow to
for habitat. • Stake and tie adjustments as required
the same size and often the smaller planted trees are in better health with
• Re-mulching
R ET R EN C H M EN T P R UN E fewer establishment requirements.
• Hand weeding to avoid use of herbicides
Retrenchment pruning reduces the larger dominant leaders to allow the
tree to develop a new inner crown below the current one, resulting in a
When selecting a planting site, it is recommended the condition of the • Extend the mulch bed as the tree grows
shorter but still living tree. Larger, heavier branches should be prioritized
soil/ground is examined and if poor soil is found improvements made. De- • Underplant with grown covers for increased aesthetics where appropriate
compaction by gentle cultivation to a depth of 300-500mm is a quick way
working from the top down. Lower dead branches can be retained if safe
to resolve this, and introducing compost and sandy loam is recommended.
to do so. Retrenchment pruning helps reduce the wind load and stress
The site can then be mulched and where and when possible, left for a few
placed on a tree helping to prevent storm damage and extend the life of
months to allow for the soil life to establish and the mulch to begin to
the tree.
compost down. It is possible for trees to be planted immediately but they
will require additional after planting care. Watering with a weak dilution of
a seaweed-based plant food/soil conditioner will help to reduce the stress
placed on the new trees and improve the soil for long-term growth.
Trees are to be selected for good root development and form. Refer to AS
2303:2015 Tree stock for landscape use for tree stock quality standards.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 2 of 17
Section 37
P LANT Z ONE E NRICHMENT R EVEGETATION
Several steps can be taken while planting new plants or enhancing existing R EV EG G O AL S
ones to improve their establishment rate and boost their vigour. This not Revegetation and restoration efforts should aim to buffer and connect
only benefits the plant's overall health but also enhances the aesthetics it existing native vegetation patches, particularly those under protection, or
offers: with high ecological value. Research on wild birds and other wildlife
suggests that native revegetation is most effective when:
S O I L IM PR O V E M EN T S
De-compaction, if necessary, by gentle cultivation to a depth of 300- • Planted in block shapes rather than narrow strips
500mm. Spread a layer of sandy loam topsoil 50-100mm in depth spread
to increase the tree’s rooting area and raise the ground level around • Located in gullies or flat areas
surface roots and generally level the site where required. This additional
• Placed adjacent or among existing vegetated areas
soil provides fresh nutrients and encourages the development of smaller
non-woody feeder roots. The application of a seaweed-based soil • Established around large, mature trees
conditioner/plant food will support soil life colonisation and augment the
nutrients available for the plants and trees. Ideally, the revegetation will reconnect existing patches and create
"steppingstones" or "corridor" plantings through the golf course. Enhancing
M U L C H IN G
Spread decaying forest mulch over as large an area as possible around landscape connectivity in this manner may facilitate wildlife movement and
augment the user experience.
the tree to a depth of 100mm, avoiding the base of the trees itself. There
are numerous benefits mulching provides to the soil beneath and the tree When planning revegetation, it is important to select species that are
roots growing within it including moisture retention, an increase in locally adapted, to observe what thrives in the area. Adequate soil moisture
beneficial fungal growth as the mulch slowly decays and forms a layer of before planting and management of competition from weeds and browsing
compost providing an ideal environment for soil life and positive growing animals is a key preparation activity before any planting occurs.
conditions.
This scheme combines functionality with aesthetics, creating a lush and
As the works at the course are undertaken, the mulch can be directly inviting environment that enhances the golfing experience while
deposited and spread beneath the retained trees. respecting the local ecosystem.
Please note that mulch from weed trees in seed is to be removed from site The focus of the planting will be to embellish the existing treescape and
to avoid spread. replace vegetation where weeds have been removed of additional
opportunities are available.
A D D IT IO N A L P L AN T H EA L T H C AR E
In addition to a consistent watering schedule, especially during the initial Local native plant species to the area will we used, and this will be guided
phase of growth, to aid root establishment, regular applications of a by the local mapped RE.
seaweed-based soil conditioner/plant food will feed the soil life. Promoting
healthy growth for stronger safer trees that add amenity value to the local The Planting Catalogue offers a palate of planting that is suitable for the
area and the associated benefits that come with having a healthy Golf Course but is not exhaustive and can be embellished as required.
plantscape. ‘Approx. size at maturation’ reflects the maximum expected sizes that
www.nutri-tech.com.au could be reached on maturity of the trees.
In really poor soils – NTS Black Gold and NTS Liquid Humus M A PP E D R E GIO N AL E C O S YST EM S AT N O O SA S PR IN G S G O L F
C O UR SE IN C L U DE :
On new plantings – NTS Root and Shoot 12.2.5 & 12.2.7 - Open forest to low closed forest. These are Vegetation
Regular applications of Black-Gold on established garden beds/trees will Management Act class of least concern but can provide opportunities for
produce positive effects in a short space of time. native planting that can provide threatened species habitat.
12.2.12 & 12.2.15 - Closed heath on seasonally waterlogged sand plains.
These are Vegetation Management Act class of least concern and offers
opportunities for native planting that can provide threatened species
habitat.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 3 of 17
Section 38
P LANTING C ATALOGUE
Low Storey – Proposed groundcover
Canopy – Proposed Koala Trees Approx. size at
Planting size – Tube stock / 140s
Planting size - 300mm – 45l maturation
Botanical Name Common Name
Botanical Name Common Name Height Width
Austromyrtus dulcis Midyim
Corymbia intermedia Pink Bloodwood 30m 20m
Cyperus polystachyos Bunchy Sedge
Eucalyptus tereticornis Forest Red Gum 30m 20m
Daviesia umbellulate Bitterpea
Eucalyptus tessellaris Moreton Bay Ash 25m 15m
Dianella species Flax Lily
Melaleuca quinquenervia Broad-leafed Paperbark 15m 8m
Gahnia clarkei Tall Saw-Sedge
Hibbertia species Guinea Flower
Hovea acutifolia Purple pea
Leptospermum species Tea tree
Canopy – Proposed Trees Approx. size at Lomandra species Mat Rush
Planting size - 300mm – 45l maturation Opkismenus aemulus Creeping Shade Grass
Botanical Name Common Name Height Width Viola species Native violet
Callitris columellaris Bribie Island Pine 6-9m 3-5m
Elaeocarpus obovatus Hard Quandong 45m
Euroschinus falcatus Ribbonwood 30m -
Lophostemon suaveolens Swamp Brushbox 30m 8m
Mid Storey – Proposed Trees Approx. size at Low Storey Planting
Planting size - Large tube stock (140s) or 300mm maturation
Botanical Name Common Name Height Width
Acmena smithii Narrow-leaved Lillypilly 20m 10m
Acronychia imperforata Fraser Island Apple 8m 4m
Allocasuarina littoralis Black She-oak 10m
Babingtonia bidwillii Baeckea 3m
Backhousia citriodora Lemon-scented Myrtle 15m
Banksia integrifolia Coastal Banksia 10m m
Banksia robur Broad-leafed/Swamp 5m
Banksia
Casuarina glauca Swamp She-oak 10m
Cupaniopsis Tuckeroo 15 10
anacardioides
Elaeocarpus reticulatus Blue Berry Ash 10m Picture 2: Midyim, Austromyrtus dulcis Picture 3: Native Blue Tongue - Melastoma
Picture 1: Flax lily – Dianella species malabathricum subsp. malabathricum
Glochidion sumatranum Umbrella Cheese Tree 10m 8-10m
Leptospermum petersonii Lemon-scented Tea tree 5m 4m
Macaranga tanarius Parasol Leaf Tree 10m 5-7m
Melaleuca thymifolia Thyme-leafed honey 3m
myrtle
Melastoma Blue Tongue 3m 2m
malabathricum
Melicope elleryana Pink Euodia 10m 5m
Syzygium luehmannii Small-leaved Lilly Pilly 15-25m
Syzygium oleosum Blue Lilly pilly 14m 3m
Livistona australis Cabbage Palms 25m 4-6m
Picture 4: Bitter pea – Daviesia umbellulate Picture 5: Native hibiscus – Hibiscus species Picture 6: Hovea acutifolia
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 4 of 17
Section 39
W ORKS S CHEDULE - P LATE 1
Plate Vegetation GC Area Comments Recommended Actions Timing
Residential community boundary management:
Native vegetation Side branches encroaching towards residential
Hole 1 / Prune to reduce the encroachment of side lateral branches adjacent to the resident
1 predominantly Eucalypt properties. 24-36 months
Private boundary community 'The Fairways'.
species. Dysfunctional understory pioneer species.
Remove dysfunctional understory.
Course / Fairway encroachment management:
All-terrain EWP and/or climbing arborist to undertake selective pruning along the
edge of the fairway as marked.
Native vegetation Fairway encroachment from mid and upper canopy
Encroachment pruning to include the management of longer laterals to suitable
1 predominantly Eucalypt Fairway 1 Eucalypt species creates shade issues for the turf and 12-24 months
growth points where available.
species sight-line obstruction.
Pruning to include the creation of habitat if possible.
Management of lower-order understory trees with the removal of small malformed
and/or dysfunctional trees, e.g. Wattles, Soapy Ash.
Visual Tree Assessment based on health and safety with hazard mitigation works
recommended and undertaken as required.
Native Gaps in the existing native vegetation between the
Native vegetation Mulch from non-weed arisings to be spread throughout the area.
Vegetation & course holes, predominantly due to natural tree failure
1 predominantly Eucalypt Larger logs/timber to be suitably placed for ground habitat. Ongoing
Riparian Buffer and death.
species Weed removal of emerging woody weeds - with arising removed from the site if in
Areas Sporadic weed emergence.
seed.
Native infill planting - see planting schedule.
The area is to be managed to promote safe and effective golf play:
Remove lower-order vegetation.
1 HLA High Land Areas - focused ball drop locations. Ongoing
Lift prune for pedestrian access.
Ground to be cleared of larger debris.
Tee landscape maintenance:
Historical mixed exotic landscape planting with a mix of
Maintained native Replacement of exotic landscape plants with natives.
1 Tee 1 & 2 retained emerging native pioneer species in undesirable 12-24 months
landscaping Remove undesirable, weed, and naturally occurring pioneer species.
locations.
Side branch encroachment pruning to reduce shade throw.
Incrementally increase the mulch garden beds around the existing trees with the
Tee 3 & Parkland style remnant aged trees with gaps and clear
1 Native vegetation introduction of general native vegetation planting with the aim of creating a closed Ongoing
Driving Range ground.
canopy Native Vegetation Area over time.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 5 of 17
Section 40
P LATE 1 - H OLE 1, H OLE 2, D RIVING R ANGE (DR), T EE 3 24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 6 of 17
Section 41
W ORKS S CHEDULE – P LATE 2
Plate Vegetation GC Area Comments Recommended Actions Timing
Course / Fairway encroachment management:
All-terrain EWP and/or climbing arborist to undertake selective pruning along the
edge of the fairway as marked.
Native vegetation Fairway encroachment from mid and upper canopy
Encroachment pruning to include the management of longer laterals to suitable
2 predominantly Eucalypt Hole 3, 10, & 18 Eucalypt species creates shade issues for the turf and
growth points where available.
species sight-line obstruction.
Pruning to include the creation of habitat if possible.
Management of lower-order understory trees with the removal of small malformed
and/or dysfunctional trees, e.g. Wattles, Soapy Ash.
The area is to be managed to promote safe and effective golf play:
Remove lower-order vegetation.
2 HLA High Land Areas - focused ball drop locations. Ongoing
Lift prune for pedestrian access.
Ground to be cleared of larger debris.
Amenity landscaping at the toilet facilities. Amenity landscape maintenance:
Historical mixed exotic landscape planting with a mix of Shrub and understory pruning.
2 Landscape planting Amenity block
mature and emerging native pioneer species in Replacement of exotic landscape plants with natives.
undesirable locations. Remove undesirable, weed, and naturally occurring pioneer species.
Visual Tree Assessment based on health and safety with hazard mitigation works
Native vegetation Gaps in the existing native vegetation between the recommended and undertaken as required.Mulch from non-weed arisings to be
Native
2 predominantly Eucalypt course holes, predominantly due to natural tree failure spread throughout the area.Larger logs/timber to be suitably placed for ground Ongoing
Vegetation Areas
species and death.Sporadic weed emergence. habitat.Weed removal of emerging woody weeds - with arising removed from the
site if in seed.Native infill planting - see planting schedule.
Concentration of weed trees - Broad-leafed Pepper
2 Tee 4 Focused weed removal and native replanting.
trees, Schinus terebinthifolia.
Tee landscape maintenance:
Replacement of exotic landscape plants with natives.
2 Tee 1 & 4 Tee maintenance.
Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Driving Range
2 Palm planting Gaps in the existing palm planting. Infill palm planting opportunities.
Cart Park
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 7 of 17
Section 42
P LATE 2 - H OLE 3, H OLE 4, H OLE 8, H OLE 9, H OLE 18, & C LUB H OUSE 24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 8 of 17
Section 43
W ORK S CHEDULE – P LATE 3 & 4
Plate Vegetation GC Area Comments Recommended Actions Timing
Tee landscape maintenance:
Tee 5 & 7 Replacement of exotic landscape plants with natives.
3 Tee maintenance.
Hole 7 Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Concentration of weed trees - Broad-leafed Pepper
3 Fairway 5 Focused weed removal and native replanting.
trees, Schinus terebinthifolia.
Course / Fairway encroachment management:
All-terrain EWP and/or climbing arborist to undertake selective pruning along the
edge of the fairway as marked.
Native vegetation Fairway encroachment from mid and upper canopy
Encroachment pruning to include the management of longer laterals to suitable
3 predominantly Eucalypt & Fairway 6 Riparian Buffer Area species creates shade issues for
growth points where available.
Paperbark species the turf and sight-line obstruction.
Pruning to include the creation of habitat if possible.
Management of lower-order understory trees with the removal of small malformed
and/or dysfunctional trees, e.g. Wattles, Soapy Ash.
Tee landscape maintenance:
Replacement of exotic landscape plants with natives.
4 Landscape vegetation Tee 11, 13, & 18 Tee maintenance.
Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Course / Fairway encroachment management:
All-terrain EWP and/or climbing arborist to undertake selective pruning along the
edge of the fairway as marked.
Native vegetation Fairway encroachment from mid and upper canopy
Encroachment pruning to include the management of longer laterals to suitable
4 predominantly Eucalypt Hole 10 & 17 Native Vegetation Area species creates shade issues for
growth points where available.
species the turf and sight-line obstruction.
Pruning to include the creation of habitat if possible.
Management of lower-order understory trees with the removal of small malformed
and/or dysfunctional trees, e.g. Wattles, Soapy Ash.
Ground rehabilitation - mulch and soil replenishment.
4 Native grasses and sedges Tee 18 Areas of bare ground between grass plantings.
Planting with native grasses and ground cover plants.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 9 of 17
Section 44
PLATE 3 - HOLE 5, HOLE 6, & HOLE 7 evious Next es Department of Resources); © Commonwealth of Australie (Geoscience Australia); © 21AT, © Eerth-i, all rights reserved, 2024. | © State of Queensland (Department of Resources) 2023 | © Stete of Queensisnd (Deparment of Resources) 2024 | This 24 _08_30_VMP_NoosaSpringsGolfCourse_V1 ( onsult \rborist Course / Fairway encroachment management. Residential community encroachment management. Driveway / fence line vegetation management. Native vegetation - predominantly Eucalypt species. Riparian Buffer Area - predominantly Eucalypt and Paperbark. Amenity landscape maintenance (course amenities). Tee landscape maintenance. Infill native planting, Focused weed removal and native replanting, Ground rehabilitation. Native grass / ground planting. Replacement palm planting High Land Area Tee and direction of play. eh. date were creet... Page 10 of 17
Section 45
Section 46
P LATE 4 - H OLE 10, H OLE 17, H OLE 18, T EE 13 & T EE 11 24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 11 of 17
Section 47
W ORK S CHEDULE - P LATE 5
Plate Vegetation GC Area Comments Recommended Actions Timing
Native vegetation
Bare earth along vegetation at Hole 14 and between 12
5 predominantly Eucalypt Hole 12, & 14 Ground rehabilitation - mulch and soil replenishment.
& 14.
species
Visual Tree Assessment based on health and safety with hazard mitigation works
Gaps in the existing native vegetation on either side of recommended and undertaken as required.Mulch from non-weed arisings to be
Native vegetation
the hole 11 & 14 and between 12 & 14, predominantly spread throughout the area.Larger logs/timber to be suitably placed for ground
5 predominantly Eucalypt Hole 11, 12, & 14 Ongoing
due to natural tree failure and death.Sporadic weed habitat.Weed removal of emerging woody weeds - with arising removed from the
species
emergence. site if in seed.Native infill planting - see planting schedule.Ground rehabilitation -
mulch and soil replenishment.
Tee landscape maintenance:
Replacement of exotic landscape plants with natives.
5 Landscape planting Tee 11, 12, & 13 Tee maintenance.
Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Driveway / Fence line vegetation management:
Removal of all emerging species under 100mm stem diameter within 1m of the
fence line.
Mix of original planted Encroachment of trees.
Woody weed removal.
5 landscaping trees and Boundary fence Tree failure onto fence causing damage.
Remove dysfuncational and hazardous trees targeting the fence line.
emerging species. Emerging weeds and pioneer species.
Management of existing mature landscape trees to include the lift pruning of lower
branches, root pruning (Fig species), and reduction of longer laterals for
encroachment pruning.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 12 of 17
Section 48
P LATE 5 - H OLE 11, H OLE 12, H OLE 13, & H OLE 14 24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 13 of 17
Section 49
W ORKS S CHEDULE – P LATE 6 & 7
Plate Vegetation GC Area Comments Recommended Actions Timing
Native vegetation
6 Hole 14 & 15 Eroded ground conditions between Hole 14 & 15. Ground rehabilitation - mulch and soil replenishment.
predominantly Eucalypts
Visual Tree Assessment based on health and safety with hazard mitigation works
recommended and undertaken as required.
Native vegetation Gaps in the existing native vegetation between 14 & 15, Mulch from non-weed arisings to be spread throughout the area.
6 predominantly Eucalypt Hole 14 & 15 predominantly due to natural tree failure and death. Larger logs/timber to be suitably placed for ground habitat. Ongoing
species Sporadic weed emergence. Weed removal of emerging woody weeds - with arising removed from the site if in
seed.
Native infill planting - see planting schedule.
Tee landscape maintenance:
Replacement of exotic landscape plants with natives.
6 Landscape planting Tee 15 Tee maintenance.
Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Visual Tree Assessment based on health and safety with hazard mitigation works
recommended and undertaken as required.
Native vegetation Gaps in the existing native vegetation at Hole 15, Mulch from non-weed arisings to be spread throughout the area.
6 predominantly Eucalypt Hole 15 predominantly due to natural tree failure and death. Larger logs/timber to be suitably placed for ground habitat. Ongoing
species Sporadic weed emergence. Weed removal of emerging woody weeds - with arising removed from the site if in
seed.
Native infill planting - see planting schedule.
Driveway / Fence line vegetation management:
Removal of all emerging species under 100mm stem diameter within 1m of the
fence line.
Mix of original planted Encroachment of trees.
Woody weed removal.
6 landscaping trees and Boundary fence Tree failure onto fence causing damage.
Remove dysfuncational and hazardous trees targeting the fence line.
emerging species. Emerging weeds and pioneer species.
Management of existing mature landscape trees to include the lift pruning of lower
branches, root pruning (Fig species), and reduction of longer laterals for
encroachment pruning.
Course / Fairway encroachment management:All-terrain EWP and/or climbing
arborist to undertake selective pruning along the edge of the fairway as
Native vegetation Fairway encroachment from mid and upper canopy
marked.Encroachment pruning to include the management of longer laterals to
7 predominantly Eucalypt Hole 16 Eucalypt species creates shade issues for the turf and
suitable growth points where available.Pruning to include the creation of habitat if
species sight-line obstruction.
possible.Management of lower-order understory trees with the removal of small
malformed and/or dysfunctional trees, e.g. Wattles, Soapy Ash.
Tee landscape maintenance:
Replacement of exotic landscape plants with natives.
7 Landscape planting Tee 13, 16, & 17 Tee maintenance.
Remove undesirable, weed, and naturally occurring pioneer species.
Side branch encroachment pruning to reduce shade throw.
Ground rehabilitation - mulch and soil replenishment.
7 Bare ground Hole 17 Area with ground erosion occurring.
Planting with native grasses and ground cover plants.
24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 14 of 17
Section 50
( onsult \rborist PLATE 6- HOLE 14 & HOLE 15 vals o a MUU an rte ht Y. Sti Course / Fairway encroachment management. Residential community encroachment management. Driveway / fence line vegetation management. Native vegetation - predominantly Eucalypt species. Riparian Buffer Area - predominantly Eucalypt and Paperbark. ‘Amenity landscape maintenance (course amenities). Tee landscape maintenance. Infill native planting, Focused weed removal and native replanting. Ground rehabilitation. VV Native grass / ground planting. Replacement palm planting HLA High Land Area 1 > Tee and direction of play 24 _08_30_VMP_NoosaSpringsGolfCourse_V1 Page 15 of 17
Section 51
Section 52
PLATE 7 - HOLE 13, HOLE 16, TEE 17 2. _ Sa > sa #¥. ts reserved, 2024. | © State of Queensiand (Department of Resources) 2023 | © Stete of Queensland (Depsriment of Resources) 2024 | This cate were creat... 24 _08_30_VMP_NoosaSpringsGolfCourse_V1 83d VV HLA 1 > Tee and direction of play ( onsult \rborist Course / Fairway encroachment management. Residential community encroachment management. Driveway / fence line vegetation management. Native vegetation - predominantly Eucalypt species. Riparian Buffer Area - predominantly Eucalypt and Paperbark. ‘Amenity landscape maintenance (course amenities). Tee landscape maintenance. Infil native planting, Focused weed removal and native replanting. Ground rehabilitation. Native grass / ground planting. Replacement palm planting High Land Area Page 16 of 17
Section 53
Section 54
N OOSA P LAN 2020 O VERLAY M APS Figure 2: Noosa Plan Biodiversity overlay Figure 3: Noosa Plan Riparian Buffer overlay Figure 4: Noosa Plan Bushfire Hazard overlay Figure 5: SARA Overlay – Koala Habitat 24_08_30_VMP_NoosaSpringsGolfCourse_V1 Page 17 of 17
Section 55
ARBORICULTURAL REPORT
Visual Tree Assessment
Site Address: Noosa Springs Golf & Spa
Links Drive,
Noosa Heads, Queensland 4567
Responsible Council: Noosa Council
Date: Monday, 10 June 2024
Prepared by:
Matthew Duncan
Director / Principal Arborist
e: [email protected]
m: 0450 355 770
ABN: 68 153 548 531
Section 56
This document was prepared for the sole use of Noosa Springs Golf Course and any regulatory agencies involved in this project. No other party should rely on this information without the prior written consent of Consult Arborist. The findings laid out in this report are valid for 12 months from the date of the assessment. If the advice and recommendations made in this report are not strictly adhered to, no responsibility will be taken for the continuing health and condition of retained trees. Trees are dynamic living organisms that respond to changes in their environs; repeat assessments are key to maintaining tree vitality, and structural integrity and reducing any potential risk they may pose. C OPYRIGHT This report/document is subject to copyright laws and remains the property of Consult Arborist Pty Ltd. Penalties @280c per word per incident of unauthorised usage. No part of this report may be reproduced or used without the written permission of Consult Arborist Pty Ltd. No responsibility will be accepted by Consult Arborist Pty Ltd for unauthorised or partial use of this report. General Permission of use as subject to Consult Arborist Pty Ltd copyrights: • Hard copy permission: Entire copies may be printed by the Client for internal or Project liaison use. • Electronic permissions: Must be original PDF format for filing and/or limited to the agreed parties with a direct and vested interest in the case. D OCUMENT C ONTROL The latest approved version of this 24_06_10_VTA_Noosa Springs Golf Course_1 should be available to all personnel involved in the Project in consultation with Consult Arborist Pty Ltd. Each new revision should be distributed to all key personnel for review and endorsement. Version Date Written Reviewed Approved One (1) 10/06/2024 MJD SCD MJD 24_06_10_VTA_Noosa Springs Golf Course_1 Page 2 of 35
Section 57
C ONTENTS
Copyright .............................................................................................................................. 2
Document Control ................................................................................................................. 2
1 Brief ............................................................................................................................... 4
2 Site Inspection ............................................................................................................... 4
3 Scope and Limitations .................................................................................................... 5
3.1 Wildlife Considerations .......................................................................................... 6
3.2 Protected Trees ..................................................................................................... 6
3.3 Contractors Notes.................................................................................................. 6
3.4 Habitat Trees ......................................................................................................... 6
4 Site Location and Details ............................................................................................... 7
5 Findings April 2024 ........................................................................................................ 8
6 Plotted Site Map........................................................................................................... 13
7 Site Photographs ......................................................................................................... 14
8 Overlay Mapping .......................................................................................................... 21
9 Tree Planting Guidelines .............................................................................................. 23
9.1 Location, Location, Location ................................................................................ 23
9.2 Right Tree, Right Place........................................................................................ 23
9.3 Preparation .......................................................................................................... 23
9.4 Plant .................................................................................................................... 25
9.5 Establishment Care ............................................................................................. 25
10 Plant Zone Enrichment ............................................................................................ 26
10.1 Soil improvements ............................................................................................... 26
10.2 Mulching .............................................................................................................. 26
10.3 Additional Plant Health Care ................................................................................ 26
11 References: ............................................................................................................. 27
12 Assumptions and Disclaimers.................................................................................. 27
Appendix 1: Definition of Terms .......................................................................................... 28
Appendix 2: Tree Risk Assessment Methodology ............................................................... 29
Appendix 3: Definition of ISA Terms.................................................................................... 29
Appendix 4: Plot Maps ........................................................................................................ 30
24_06_10_VTA_Noosa Springs Golf Course_1 Page 3 of 35
Section 58
1 B RIEF
This assessment was commissioned by Peter Woods, Golf Course Superintendent of Noosa
Springs Golf Course. Consult Arborist Pty Ltd has been requested to carry out an independent
Visual Tree Assessment of trees in accessible amenity areas throughout the Golf Course
grounds.
The focus of the assessment is primarily on trees that may pose a health and safety concern
and trees which directly or indirectly pose a threat to players, staff, and guests or may
negatively impact buildings and infrastructure.
For each tree reported Consult Arborist will provide details on the following:
• Identification, attributes, health, and structural condition.
• Specifics will be noted, and a risk rating provided/priority of works.
• Recommendations for the management of the tree.
Findings are to be used to prioritise and carry out proactive tree maintenance works on the
grounds of health and safety, good arboricultural practice and to reduce infrastructure
damage.
2 S ITE I NSPECTION
Matthew Duncan, the Director and Principal Arborist of Consult Arborist undertook the Visual
Tree Assessment on the site from a ground level on Tuesday, 28 May 2024. Matthew holds
an AQF Level 5 Diploma of Arboriculture (AHC50510), an International Society of
Arboriculture’s Tree Risk Assessment Qualification, valid from 2015 to 2025, and has worked
in the arboricultural industry since 1994. Since its establishment in 2011, Consult Arborist has
been engaged to provide arboricultural advice and guidance on private, civil, and capital works
projects from cross-sector clients throughout Queensland where he is a Queensland
Arboricultural Association (QAA) Qualified Member and Approved Consultant.
It is recommended that a re-inspection of significant trees, where recorded, is carried out in
12 months or after a major weather event.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 4 of 35
Section 59
3 S COPE AND L IMITATIONS
This Arboricultural appraisal is based on the International Society of Arboriculture’s Risk
Assessment Methodology for trees. The level of assessment undertaken for this Arboricultural
Appraisal was a basic Level 1 visual assessment of the surrounding area and the subject
tree’s structure and health, from the ground on one side and a Level 2 assessment on all sides
of the tree was completed to assess further any visual defects noted.
It is a risk assessment that includes the use of basic tools and techniques, i.e. cavity probing,
minor root collar excavation, measuring tapes and devices and photography to gather
information and not a full assessment of any trees’ structural safety. No trunk decay detection
equipment or ground radar was used as part of this Arboricultural Appraisal, no conclusive
comments on what may have been or may be happening within the internal structure of the
tree or the tree’s roots will be made. No tissue or soil samples have been collected or
submitted for testing. All data is based on visual inspection based on known industry
methodology of visual tree assessment VTA, of the tree/s and its/their location, species,
health, and condition at the time of inspection unless otherwise stated.
The timeframe for this report is the inspection period; re-inspection should occur 1 year from
this inspection.
The focus of this assessment was on trees within and around the main site and access areas.
The trees captured within this report have been tagged with individual ID tags to aid with
identification.
The information contained in this report is based on a visual inspection of each recorded tree
and its location, species, health, and condition at the time of inspection unless otherwise
stated. It is the author's opinion and is a 'snapshot in time' of the specific tree's health and
condition at the time of the inspection and no guarantee can be given that faults or issues may
not arise in the future.
The relevant tree information has been recorded to be used as a functional proactive tool to
determine a safe management strategy for the tree, taking into account past works, age and
location. Trees that require proactive health and safety works within 6 months, or have been
identified for re-inspection, have been recorded.
See the attached Site Photographs and Site Map for identification purposes.
https://www.easymapmaker.com/map/24_05_NoosaSprings_GolfCourse
Note:
• The Plotted Site Map is for reference only and is not to scale, the locations for the tree
plots are a representation of the tree’s location with an iPad plotting function and are
mapped using www.easymapmaker.com. The site plan is to be used in conjunction
with the information within the VTA results.
• Photographs were taken with the iPad when required and the light/exposure has been
adapted to improve the clarity of the picture quality.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 5 of 35
Section 60
3.1 WILDLIFE CONSIDERATIONS The DESI (Department of Environment, Science, and Innovation) should be consulted regarding regulations concerning tree removal. The Nature Conservation Act 1992 provides statutory protection for most species of native animals and any tree work which affects them may constitute an offence. In addition, the Nature Conservation and Other Legislation (Koala Protection) Amendment Regulation amended the Environmental Offsets Regulation 2014, Planning Regulation 2017, Nature Conservation (Koala) Conservation Plan 2017 and Vegetation Management Regulation 2023 to provide increased protection to koala habitat areas in South East Queensland. A qualified Fauna Spotter-Catcher should be consulted prior to tree works being carried out where wildlife may be active. 3.2 PROTECTED TREES Prior to carrying out any tree work, it is recommended to check with the local authority to ensure there is no protection order placed on the trees. Should any tree be deemed to be legally protected, it will be necessary to consult the local Council before removal can be carried out. 3.3 CONTRACTORS NOTES Recommended arboricultural works are to be carried out by an arborist holding a minimum of a Level 3 AQF qualification in Arboriculture with good working experience. It is expected that the Arborist may encounter anomalies within the tree as they climb/work and as such may use their discretion to remove any further branches or limbs which they may deem could pose an immediate risk. Additional removals outside the recommendations or defects noted whilst in the tree are to be recorded and reported to the author and/or discussed with a Level 5 Arborist on site prior to undertaking the appropriate action. All pruning is to be in accordance with, or guided by AS 4373 – “Pruning of Amenity Trees” 3.4 HABITAT TREES When undertaking remedial tree works on habitat trees, please be aware of the fauna and their habitat. The creation of future habitats whilst undertaking remedial works is to be considered. When mitigating hazardous deadwood, hollow sections and large branches, minimal pruning or reduction of weight is required rather than total removal. Hollow sections take many years to be created and are a highly valuable habitat. Coronet cuts should be facilitated where appropriate to mimic natural branch failure on suitable trees in a natural setting. 24_06_10_VTA_Noosa Springs Golf Course_1 Page 6 of 35
Section 61
4 S ITE L OCATION AND D ETAILS
Noosa Spring Golf Course is a members-only golf course located on the southern side of the
Noosa Council suburb of Noosa Heads adjacent to Lake Weyba. The fairways are divided by
densely treed corridors which are a mix of remnant, natives, and augmented by planted
landscape feature trees.
This is the first formal tree assessment to be carried out at the golf course and as such it
focused on risk mitigation. The past regime of maintenance for trees appears to have been
sporadic, with a focus on high-use areas, this was evidenced by the number of dead and
defective trees recorded in this assessment throughout the course areas.
Information regarding woody weed removal, planting, and care of established trees to better
their health is offered and can be used to proactively manage the course trees between
assessments. In areas where it is suitable, the mulch from the works undertaken can be
spread beneath the retained trees throughout the course.
Generally, without the presence of a major defect, the ISA risk matrix records a 'Low risk' score
rating. Any tree that receives a 'Moderate' risk score requires mitigation and preventative
measures are recommended to manage the risk to reduce the score to an acceptable ‘Low
risk’ score. There is also a large difference between the definition of ‘Minor’ and ‘Significant’
in the Consequences of Failure. Consideration must be made as to whether any moderate
property damage or minor personal injury can be tolerated.
Due to the site being golf course grounds, the occupancy has been assessed for most trees
as being “Frequent.”
The weather at the time of the assessment was clear with a light breeze. The site conditions
were dry underfoot after recent heavy seasonal rains, good access was available to the areas
of the site that were assessed.
Figure 1: Google Maps overview of the area.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 7 of 35
Section 62
5 F INDINGS A PRIL 2024
The following is a table listing trees that have been recommended for work at this time. For
more information and definitions see the appendices.
Attributes Size (m) Priority
ID Location Species Comments Recommendations
AC H St Hg CS DBH /Risk
0.2- Dead tree with a
1 1 Dead M D P 8-10 2-4 Moderate Remove.
0.3 small Strangler Fig.
0.3- Dead trunk with the
2 1 Dead M D P 8-10 4-6 Moderate Remove.
0.4 vine attached.
0.2- Snapped tree hung
3 1 Brushbox EM P P 8-10 2-4 Moderate Remove.
0.3 up.
Remove vine from
the canopy.
Weeping 0.3- Monkey Rope Vine
4 1 M F F 8-10 4-6 Moderate Prune the tree as
Paperbark 0.4 engulfed canopy.
required following
the removal of the
vine.
10- 0.3- Tree at advanced
5 1 Wattle M P P 6-8 Moderate Remove.
12 0.4 lean.
Advanced lean
10- 0.3- with decay bracket
6 1 Wattle M F P 6-8 Moderate Remove.
12 0.4 fungi on the main
trunk.
Dead trunk
Brushbox 10- 0.3-
7 1 M D P 4-6 High growing towards Remove.
& Wattle 12 0.4
the hole.
Deadwood and
detail.
Twin stem.
14 - 12- 0.7-
8 1 Brushbox M P F Moderate Recently deceased
16 14 0.8 Canopy reduction to
top.
balance the retained
branches.
Upper management
Advanced decay at
to reduce the height
the base where the
of the tree by one-
Swamp 12- 0.7- secondary leader
9 1 AA F P 6-8 High third.
Mahogany 14 0.8 failed years ago.
Works aim to retain
Reinspect in 12
the tree.
months.
Dead tree in a
Swamp 10- 0.6-
10 1 AA D P 6-8 High frequently used Remove.
Mahogany 12 0.7
area.
Swamp 0.3- Major die back and Retrenchment
11 1 M P P 6-8 4-6 Moderate
Mahogany 0.4 deadwood. pruning.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 8 of 35
Section 63
Attributes Size (m) Priority
ID Location Species Comments Recommendations
AC H St Hg CS DBH /Risk
Selective pruning to
Forest Red 14 - reduce the trunk to
12 1 M D F 6-8 Moderate Dead trunk.
Gum 16 5m and retain as
habitat.
Swamp 12- 0.3- Advanced dead
13 1 M D F 4-6 Moderate Remove.
Mahogany 14 0.4 tree.
Three dead small
0.1-
14 1 Dead EM D P 6-8 2-4 High trees on the edge Remove.
0.2
of the path.
Swamp 12- 0.3- Structurally
15 1 M P P 4-6 High Remove.
Mahogany 14 0.4 compromised.
0.2- Advanced dead
16 1 Paperbark M D P 8-10 <2 Moderate Remove.
0.3 tree.
Clumps of dead
0.2-
17 1 Paperbark M D P 4-6 2-4 Moderate trees on the edge Remove.
0.3
of the green.
0.2- Increasing decay
18 2 Palm M P P 6-8 2-4 Moderate Remove.
0.3 at the base.
Two dead
0.3- Paperbarks.
19 2 Paperbark M P P 8-10 4-6 Moderate Remove.
0.4 Dead top on the
Swamp Mahogany.
10- 0.3- Dead tree on the
20 2 Eucalyptus M D P 2-4 High Remove.
12 0.4 edge of the green.
Dead tree clump
0.1-
21 2 Paperbark M D P 6-8 2-4 High on the edge of the Remove.
0.2
fairway.
Advanced dead
0.4-
22 2 Swamp M D P 8-10 6-8 Moderate tree next to the Remove.
0.5
path.
0.1- Advanced dead
23 2 Paperbark EM D P 6-8 <2 High Remove.
0.2 tree.
Advanced dead
Forest Red 14 - 0.5- tree with a large
24 2 M D P 4-6 High Remove.
Gum 16 0.6 canker on the main
trunk.
Retrenchment
pruning.
Reduce the centre
Forest Red 14 - 0.5- stem to 200mm
25 2 M P P 8-10 High Dead centre stem.
Gum 16 0.6 diameter, retain the
stub, and reshape
the remaining
canopy.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 9 of 35
Section 64
Attributes Size (m) Priority
ID Location Species Comments Recommendations
AC H St Hg CS DBH /Risk
Declining canopy
with epicormic
growth on the main Retrenchment
trunk. pruning.
Forest Red 10- 0.6- Long-term canopy
26 3 AA F F 25+ Moderate
Gum 12 0.7 and tree Create a large mulch
management area beneath the
strategy required. tree.
High value habitat
area.
Forest Red 10- 0.2- Dead tree in a
27 3 M D P 4-6 Moderate Remove.
Gum 12 0.3 group.
Rehabilitation:
Area to be Remove weeds and
rehabilitated with unwanted trees and
the works vine.
0.1-
28 Back of 4 Mixed M F F 4-6 2-4 Moderate undertaken in two
0.2
stages 1 to 2 years Mulch the area and
apart to retain replant with a mix of
screening. ground cover, shrubs
and small trees.
Planted tree in a
Weeping 0.2- Remove.
29 5 EM P P 6-8 4-6 Low group. Declining
Lilly Pilly 0.3 Stump grind.
health.
Weed species
Pepper growing along the
30 Left of 5 M G G <4 4-6 <100 Low Remove.
tree edge of the fairway
in multiple clumps.
Between 0.1- Recently deceased Remove.
31 Lilly pilly EM D P 4-6 2-4 Moderate
6&7 0.2 tree. Stump grind.
Dead tree in the
Forest Red 10- 0.3-
32 Start of 9 M D P 4-6 Moderate middle of the Remove.
Gum 12 0.4
group.
Cocus 0.3-
33 9 M G G 6-8 2-4 Low Weed species. Remove.
palm 0.4
Pepper Weed species -
34 10 M G G <4 4-6 < 100 Low Remove.
tree large clump.
Cocus 0.4-
35 10 M G G 6-8 2-4 Low Weed species. Remove.
palm 0.5
0.1- Advanced dead
36 10 Dead M D F 6-8 2-4 High Remove.
0.2 tree.
0.2- Advanced dead
37 11 Dead M D P 8-10 2-4 High Remove.
0.3 tree hung up.
Cocus 0.3-
38 11 EM G G 6-8 2-4 Low Weed species. Remove.
palm 0.4
24_06_10_VTA_Noosa Springs Golf Course_1 Page 10 of 35
Section 65
Attributes Size (m) Priority
ID Location Species Comments Recommendations
AC H St Hg CS DBH /Risk
Recently deceased
39 11 She oak EM D F 4-6 2-4 < 100 Moderate Remove.
tree.
0.3- Dead tree in a
40 11 Brushbox M D P 8-10 4-6 High Remove.
0.4 group.
Top of the tree is
10- 0.3- recently deceased.
41 12 Brushbox M P P 6-8 Moderate Remove.
12 0.4 Unsuitable location
for retention.
42 Blank Record
Retrenchment
pruning.
10- 0.3- Dead top, with
43 12 Brushbox M P P 4-6 Moderate
12 0.4 lower side growth.
Reinspect in 12
months.
Swamp 0.1- Dead tree next to
44 12 M D P 6-8 4-6 High Remove.
Brushbox 0.2 the path.
Group of dead
0.2-
45 14 Palms M D P 4-6 <2 Moderate stems next to the Remove.
0.3
lake.
Cocus 0.2-
46 14 EM G G 4-6 <2 Low Weed species. Remove.
palm 0.3
Cocus 0.3-
47 14 M G G 6-8 <2 Low Weed species. Remove.
palm 0.4
Cocus 0.3-
48 14 Toilet EM G P <4 2-4 Low Weed species. Remove.
palm 0.4
Swamp 0.3- Dieback in the Deadwood and
49 16 M D P 8-10 4-6 Moderate
Brushbox 0.4 canopy. detail.
Remove the old
dead Fig that was
growing in the tree.
High-value habitat
Selective pruning to
Forest Red 14 - 12- tree.
50 16 AA F F 0.8-1 High longer lateral
Gum 16 14 Old dead Fig in the
branches.
tree.
Reinspect in 12
months.
0.2- Three dead trees
51 16 Eucalyptus EM D P 8-10 2-4 Moderate Remove.
0.3 in a group.
Sizeable
Swamp 12- 0.4- Deadwood and
52 17 M F F 6-8 High deadwood over the
Mahogany 14 0.5 detail.
path.
Forest Red 20- 10- 0.6- Large dead Deadwood and
53 17 M F F High
Gum 25 12 0.7 section. detail.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 11 of 35
Section 66
Attributes Size (m) Priority
ID Location Species Comments Recommendations
AC H St Hg CS DBH /Risk
0.1- Recently deceased Remove.
54 18 Dead EM D F 4-6 2-4 Moderate
0.2 tree. Stump grind.
0.1- Recently deceased
55 18 She oak M D P 8-10 2-4 Moderate Remove.
0.2 tree in a group.
Driving Swamp 16- 0.6- Hanger over the Deadwood and
56 M F F 8-10 High
range Mahogany 20 0.7 path. detail.
Dead stem resting
Driving 10- 0.2-
57 Dead EM D P <2 High on the fence next Proactive removal
range 12 0.3
to the path.
Driving Swamp 10- 0.2- Dead tree next to
58 EM D P 2-4 Moderate Remove.
range Mahogany 12 0.3 the path.
Dead tree growing
Driving Swamp 12- 0.4- through the
59 M D P 8-10 High Remove.
range Mahogany 14 0.5 overhead mesh
next to the path.
Advanced dead
Driving Swamp 12- 0.4-
60 M D P 6-8 High tree next to the Remove.
range Mahogany 14 0.5
path.
Sizeable dead
Driving Swamp 14 - 10- 0.6- Deadwood and
61 M G F Moderate branches over the
range Mahogany 16 12 0.7 detail.
path.
Driving Swamp 0.1-
62 EM D P 8-10 2-4 Moderate Dead tree. Remove.
range Mahogany 0.2
Dead tree next to
Driving Swamp 10- 0.2-
63 EM D P 2-4 Moderate the path and Remove.
range Mahogany 12 0.3
shelter.
24_06_10_VTA_Noosa Springs Golf Course_1 Page 12 of 35
Section 67
( onsult \rborist PLOTTED SITE Map i = fa me a ee etna es ect ret Ge < NS Ae ra anil uence lat LB) ty Risk / priority: 9 GHigh F wow © Moderate 24_06_10_VTA_Noosa Springs Golf Course_1 Page 13 of 35
Section 68
Section 69
7 S ITE P HOTOGRAPHS
Picture 1: Tree 01 Picture 2: Tree 02 Picture 3: Tree 03
Picture 4: Tree 04 Picture 5: Tree 05 Picture 6: Tree 06
Picture 7: Tree 07 Picture 8: Tree 08 Picture 9: Tree 09
24_06_10_VTA_Noosa Springs Golf Course_1 Page 14 of 35
Section 70
Picture 10: Tree 10 Picture 11: Tree 11 Picture 12: Tree 12
Picture 13: Tree 13 Picture 14: Tree 14 Picture 15: Tree 15
Picture 16: Tree 16 Picture 17: Tree 17 Picture 18: Tree 18
24_06_10_VTA_Noosa Springs Golf Course_1 Page 15 of 35
Section 71
Picture 19: Tree 19 Picture 20: Tree 20 Picture 21: Tree 21
Picture 22: Tree 22 Picture 23: Tree 23 Picture 24: Tree 24
Picture 25: Tree 25 Picture 26: Tree 26 Picture 27: Tree 27
24_06_10_VTA_Noosa Springs Golf Course_1 Page 16 of 35
Section 72
Picture 28: Tree 28 Picture 29: Tree 29 Picture 30: Tree 30
Picture 31: Tree 31 Picture 32: Tree 32 Picture 33: Tree 33
Picture 34: Tree 34 Picture 35: Tree 35 Picture 36: Tree 36
24_06_10_VTA_Noosa Springs Golf Course_1 Page 17 of 35
Section 73
Picture 37: Tree 37 Picture 38: Tree 38 Picture 39: Tree 39
Picture 40: Tree 40 Picture 41: Tree 41 Picture 42: Tree 43
Picture 43: Tree 44 Picture 44: Tree 45 Picture 45: Tree 46
24_06_10_VTA_Noosa Springs Golf Course_1 Page 18 of 35
Section 74
Picture 46: Tree 47 Picture 47: Tree 48 Picture 48: Tree 49
Picture 49: Tree 50 Picture 50: Tree 51 Picture 51: Tree 52
Picture 52: Tree 53 Picture 53: Tree 54 Picture 54: Tree 55
24_06_10_VTA_Noosa Springs Golf Course_1 Page 19 of 35
Section 75
Picture 55: Tree 56 Picture 56: Tree 57 Picture 57: Tree 58
Picture 58: Tree 59 Picture 59: Tree 60 Picture 60: Tree 61
Picture 61: Tree 62 Picture 62: Tree 63
24_06_10_VTA_Noosa Springs Golf Course_1 Page 20 of 35
Section 76
8 O VERLAY M APPING
Noosa Springs Golf Course is listed under several planning maps including the following,
permission may be required from the council prior to undertaking any works that are not high
risk.
Figure 2: NC Overlay Mapping – MSES & Biodiversity Significance
Figure 3: NC Overlay Mapping - Koala Habitat Area
24_06_10_VTA_Noosa Springs Golf Course_1 Page 21 of 35
Section 77
Figure 4: NC Overlay Mapping – Riparian Buffer Area
Figure 5: NC Overlay Mapping – Bushfire Hazard
24_06_10_VTA_Noosa Springs Golf Course_1 Page 22 of 35
Section 78
9 T REE P LANTING G UIDELINES
Steps to get it Right
1. Identify suitable Planting Locations
2. Choose the right tree for the right place
3. Prepare the planting location
4. Plant
5. Establishment care
6. Maintenance
9.1 LOCATION, LOCATION, LOCATION
Not every empty space is suitable for planting. It is important to consider the hydrology of the
area, the use (occupancy) of the area, and the ultimate size of the tree, all of which can
determine the amount of maintenance required for the future. When you find your location,
you can decide on the style best suited for purpose.
9.2 RIGHT TREE, RIGHT PLACE
The style of planting is dependant on the outcome that is required; individual trees planted
alone for specimen or memorial value; linear groups for shade; groups of threes or fives for
interest; and mass planting to create a boundary, privacy, cluster or forest effect.
Within public spaces, trees provide shade, amenity and a sense of wellbeing that endorses a
sense of community. In public areas trees planted in garden beds in groups of three or five
contribute a greater impact than single planting and are more practical and generally establish
better. Where single trees are required an increased mulched area will improve establishment.
The initial plant size can be smaller and so more cost-effective, maintenance and watering are
more efficient. The planting bed covers a larger area increasing the quantity and benefits of
the mulch application. The shape and size of the beds can be tailored to suit the available
space aiding maintenance as mowing around a larger mulch bed is easier than individual trees
which can in the end just hamper the mowing.
When the style of planting is known, and the location has been chosen, species selection
becomes easier. Always think of the fully-grown tree.
9.3 PREPARATION
As a guide, an area measuring 2m x 6m can accommodate three trees at 2m spacings with a
1m on either end. At this spacing, the trees have 12m2 of improved ground in which to
establish. The tree sizes can range from 300mm pots up to 100L stock, within a few years the
trees usually grow to the same size and often the smaller planted trees are in better health
with fewer establishment requirements.
When selecting a planting site, it is recommended the condition of the soil/ground is examined
and if poor soil is found improvements made. De-compaction by gentle cultivation to a depth
of 300-500mm is a quick way to resolve this, and at this time the introduction of compost and
sandy loam is recommended. The site can then be mulched and where and when possible left
for a few months to allow for the soil life to establish and the mulch to begin to compost down.
Trees can be planted immediately but they will require additional after planting care. Watering
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with a weak dilution of a seaweed-based plant food/soil conditioner will help to reduce the
stress placed on the new trees and improve the soil for long-term growth.
Trees are to be selected for good root development and form. Refer to AS 2303:2015 Tree
stock for landscape use for tree stock quality standards.
Figure 6: Example of single tree planting with Figure 7: Example of a planting method to
a mulched area,1m x 1m minimum. encourage deep rooting.
Source: Brisbane City Council
Figure 8: Example of group planting of three fig trees in a continuous mulch bed.
Easy to mow around and improved growing conditions allowing the trees to thrive.
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9.4 PLANT
• Pre-soak rootball in the pot to ensure hydration of compost while you
• Create the hole and de-compact the surrounding ground as required.
• Drain the pot/plant in the hole while you
• Prepare your stakes and ties
• Remove the pot/bag and tease out the root ball
• Prune the girdling/woody roots with sharp secateurs
• Insert the stakes in the correct position
• Position the tree at the correct depth in the hole – a stake can be used to help with
levelling
• Backfill the hole, gently compressing the soil
• Create the watering dish at the surface
• Mulch area the tree
• Water/feed – approximately 5-10 litres per tree depending on the hydration of soil.
Figure 9: NUFA-tree planting guide-HR – Arboriculture Australia
9.5 ESTABLISHMENT CARE
While the tree is establishing additional maintenance will be required
• Moisture level monitoring – and watering if required
• Regular applications of a plant food /soil conditioner as per manufacturer's instructions
• Formative pruning
• Stake and tie adjustments as required
• Re-mulching
• Hand weeding to avoid use of herbicides
• Extend the mulch bed as the tree grows
• Underplant with grown covers for increased aesthetics where appropriate
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10 P LANT Z ONE E NRICHMENT Several steps can be taken while planting new plants or enhancing existing ones to improve their establishment rate and boost their vigour. This not only benefits the plant's overall health but also enhances the aesthetics it offers: 10.1 SOIL IMPROVEMENTS De-compaction, if necessary, by gentle cultivation to a depth of 300-500mm. Spread a layer of sandy loam topsoil 50-100mm in depth spread to increase the tree’s rooting area and raise the ground level around surface roots and generally level the site where required. This additional soil provides fresh nutrients and encourages the development of smaller non-woody feeder roots. The application of a seaweed-based soil conditioner/plant food will support soil life colonisation and augment the nutrients available for the plants and trees. 10.2 MULCHING Spread decaying forest mulch over as large an area as possible around the tree to a depth of 100mm, avoiding the base of the tree itself. There are numerous benefits mulch provides to the soil beneath and the tree roots growing within it including moisture retention, an increase in beneficial fungal growth as the mulch slowly decays and forms a layer of compost providing an ideal environment for soil life and positive growing conditions. As the works at the course are undertaken, the mulch can be directly deposited and spread beneath the retained trees. Please note that mulch from weed trees in seed is to be removed from site to avoid spread. 10.3 ADDITIONAL PLANT HEALTH CARE In addition to a consistent watering schedule, especially during the initial phase of growth, to aid root establishment, regular applications of a seaweed-based soil conditioner/plant food will feed the soil life. Promoting healthy growth for stronger safer trees that add amenity value to the local area and the associated benefits that come with having a healthy plantscape. www.nutri-tech.com.au In really poor soils – NTS Black Gold and NTS Liquid Humus On new plantings – NTS Root and Shoot To benefit Turf – NTS Turf-Tech Triple Ten Regular applications of Black-Gold on established garden beds/trees will produce positive effects in a short space of time. 24_06_10_VTA_Noosa Springs Golf Course_1 Page 26 of 35
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11 R EFERENCES :
• Australian Standards AS4970-2009 Protection of trees on development sites (2009).
• Australian Standards AS 4373 – 2007 Pruning of amenity trees. (2007).
• Barton, A. (2003). Wild plants of greater Brisbane. South Brisbane, Qld, Australia: Published by the Queensland Museum,
in partnership with the Environment and Parks Branch of the Brisbane City Council.
• Dunster, J., Smiley, E., Matheny, N. and Lilly, S. (n.d.). Tree risk assessment manual.
• Haslam, S. and Hauser, J. (2011). Noosa's native plants. Tewantin (Qld.): Noosa Integrated Catchment Assoc. Inc.
• Hayes, E. (2001). Evaluating tree defects. [S.l.]: Safetrees.
• Lonsdale, D. (1999). Principles of tree hazard assessment and management. London: Forestry Commission.
• Mattheck, C., Breloer, H., Lonsdale, D. and Strouts, R. (2003). The body language of trees. London: The Stationery Office.
• Strouts, R. and Winter, T. (1998). Diagnosis of ill-health in trees. Colegate, Norwich: Crown.
• IACA, 2010, IACA Significance of a Tree, Assessment Rating System (STARS), Institute of Australian Consulting
Arboriculturists, Australia, www.iaca.org.au
12 A SSUMPTIONS AND D ISCLAIMERS
This information contained in this report has been prepared on an independent basis, free of any bias and represents the honest
opinion of the consulting arborist.
All data is based on visual inspection of the tree/s and its/their location at the time of writing, unless otherwise stated, and contains
opinions, advice and recommendations based on information and data gathered from site inspections carried out by the author
and information supplied by the Client (Noosa Springs Golf Course).
All information received from the Client shall be deemed to be true, accurate and up to date.
To the extent permitted by law, you agree Consult Arborist Pty Ltd is not liable to you or any person or entity for any loss of or
damage caused or alleged to have been caused (including loss or damage resulting from negligence) either directly or indirectly,
by your use of the information made available in this report. In no event will the author be liable to you for any lost revenue or
profits, or for special, indirect, consequential, or incidental damage (however caused and regardless of the theory of liability)
arising out of or related to your use of that information, even if the author has been advised of the possibility of such a loss or
damage.
Consult Arborist cannot be held responsible for the effects of non-conformance works performed, by unsuitably qualified staff or
without the supervision of Consult Arborist.
Unless otherwise stated this report cannot be used within a court of law or any legal situation without the prior consent of Consult
Arborist Pty Ltd. The author shall not be required to give testimony or to attend court by reason of this report unless subsequent
contractual arrangements have been made.
The information contained in this report refers only to the tree/s that were inspected on 28/05/2024 and reflects the condition of
the tree/s at the time of the inspection.
There is no warranty or guarantee, expressed or implied, that the problems or deficiencies of the plants or property in question
may not arise in the future. Likewise, remedial treatments cannot be guaranteed.
Arboriculturalists cannot detect every condition that could possibly lead to the structural failure of a tree. Trees are living
organisms that fail in ways we do not fully understand. Conditions are often hidden within trees and below ground. Consult
Arborist Pty Ltd and the author cannot guarantee that a tree will be healthy or safe under all circumstances, or for a specified
period.
This report does not take into consideration the possibility of extreme weather or other events over which Consult Arborist Pty
Ltd has no control.
Treatment, pruning and removal of trees may involve considerations beyond the scope of the Arboriculturalists services, such as
property boundaries and ownership, disputes between neighbours, sightlines, landlord-tenant matters and related. Consult
Arborist Pty Ltd cannot take such issues into account unless the complete and accurate information is given to them. Likewise,
Consult Arborist Pty Ltd cannot accept any responsibility for the authorization or non-authorization of any recommended treatment
or remedial measure.
Arboriculturalists are tree specialists who use their education, knowledge, training and experience to examine trees, recommend
measures to enhance the beauty and health of trees and attempt to reduce the risk of living near trees. Trees can be managed,
but they cannot be controlled. To live or work near a tree involves some degree of risk. The only way to eliminate all risks
associated with a tree is to eliminate the tree.
Clients may choose to accept or disregard the recommendations of Consult Arborist Pty Ltd or to seek additional advice.
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A PPENDIX 1: D EFINITION OF T ERMS
Age Class (AC):
Y Young: Early stage of growth, immature size
EM Early Mature: Fast-growing well-established tree which has not yet reached mature size
M Mature: The tree reached its mature size, and exhibits slowing growth rates with early stages of naturally forming
dead or dysfunctional wood.
AA Advanced-Age: The tree has reached mature size and is unlike to increase significantly in height or mass.
Retrenchment of the upper crown with increased vegetative vitality in the lower crown, increased fungal activity
and wood decay, and increased colonisation by flora and fauna.
V: Veteran: Tree with advanced retrenchment, reduced crown size and annual increment growth, extensive hollowing,
crown collapse, low vigour, advanced heartwood decay, advanced colonisation by fauna and flora.
S: Senescence: the natural aging of plant tissues and organs, leading to irreversible decline in physiological functions.
Health (H):
GH Good: Tree with no defects or disorders which are notable. Full canopy with good colour foliage. Minimal pathogen
damage.
FH Fair: Tree with minor defects or disorders which are notable. Some dead wood within what can be an unbalanced
canopy, foliage generally with good colour although some discolouration may be present typical of species in
location. Minor pathogen damage.
PH Poor: Tree with major defects or disorders which are notable. The tree has considerable deadwood present and
discoloured or distorted leaves indicating a further decline of the tree. Detrimental pathogen damage.
D Dead or dysfunctional moribund tree.
Structure (St):
GS Good: Tree with good unions and no branch defects. Sound trunk with no / minor defects. Good buttress and root
structure.
FS Fair: Tree with minor defects or disorders which are notable. Small areas of bark missing. Small cavities or minor
unfavourable branch unions may be present. Minor damage to roots.
PS Poor: Tree with major defects, large hollows, weak unions and/or problematic damaged roots.
HS Hazardous: This implies a tree with a major defect that may fail at any time
Abbreviations:
Ht Height
CS Crown Spread
DBH Diameter at Breast Height - The approximate diameter of the trunk measured visually in millimetres or meters at a
height of 1.4m.
TPZ The Tree Protection Zone, as per AS 4970-2009 Protection of trees on development sites, is the principal means
of protecting trees on a development site. The TPZ is a combination of the root and crown area requiring protection
to be isolated from construction disturbance so that the tree can remain in a viable condition. The TPZ incorporates
the Structural Root Zone (SRZ).
The radius of the TPZ = DBH x 12
A TPZ should not be less than 2m or greater than 15m (unless crown protection is required).
SRZ The Structural Root Zone, as per AS 4970-2009 Protection of trees on development sites, is a mathematical
calculation of the surface area of protection required to maintain a tree’s stability – a larger area is required to
maintain a tree in viable health. It is only necessary to calculate the SRZ when a major encroachment into a TPZ
is proposed.
Recommended Works:
Aerial Inspection: Assessment is to be carried out either by Consult Arborist or a Qualified Arborist contractor to assess
defects within the canopy and report findings.
Canopy A combination of removing dead wood and selective pruning to benefit the tree’s future health and
management: canopy structure. The end-weight reduction of longer lateral branches, with the creation of future
growth points to sustain canopy growth and assist with natural canopy retrenchment.
Deadwood and detail Remove deadwood (>40mm in diameter and/or 1m in length), and dysfunctional, damaged, and weak
branches from the tree’s canopy.
End-weight Trimming of the concentration of excessive wood and foliage weight towards the extremity of the
reduction: branch to lessen the overall load and branch failure potential.
Mulch: The application of a layer of woodchip/forest mulch approximately 50-75 mm thick to the canopy drip
line where possible, leaving a small well around the base of the tree trunk.
Proactive removal To prevent future anticipated issues, remove the tree and replant with a more suitable species for the
location.
Prune away from Prune branches to reduce the encroachment and weight of the branches growing towards the adjacent
adjacent dwelling dwelling/building.
Reduce and retain Reduce the tree to a safe height and size to limit hazards while retaining the remainder for habitat.
Reinspect A repeat assessment is recommended to be carried out 12 months from the date of this assessment
or after any major weather event.
Selective pruning Prune selective / identified branches to reduce end weight/length
Soil/Plant Care Apply organic compost around the base of each tree 20-30mm thick, leaving a small well around the
base of the tree trunk. Additional seaweed-based plant food/soil conditioners applied as per the
manufacturers’ guidelines and will help to improve soil biology and maintain the tree’s health.
Stump grind Remove the stump by grinding to approximately 100mm below the surrounding ground level when
located within mown grass or damaging infrastructure.
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A PPENDIX 2: T REE R ISK A SSESSMENT M ETHODOLOGY
The methodology of rating risk used in this report is based on the following International Society of Arboriculture’s Tree Risk
Assessment and is calculated using qualitative risk matrix tables.
Initially, the Likelihood Matrix is used to estimate how likely a failure will be to impact a target. This is calculated by categorising
how likely failure is to occur and combining that with how likely that failure is to impact a target, as per Table 1.
Matrix 1 – Likelihood Matrix (M1)
Likelihood of Impacting Target
Likelihood of Failure
Very low Low Medium High
Imminent Unlikely Somewhat Likely Likely Very likely
Probable Unlikely Unlikely Somewhat Likely Likely
Possible Unlikely Unlikely Unlikely Somewhat Likely
Improbable Unlikely Unlikely Unlikely Unlikely
Table 1: Matrix 1 – Level likelihood of impact to a target.
Once the Likelihood of Failure & Impact level is determined a final level of Risk Rating can be calculated by combining the
Likelihood with the Consequences of Failure for each identified risk. This ascertains an overall Risk Rating for the tree, determined
in Table 2.
Matrix 2 – Risk Rating Matrix (M2)
Likelihood of Failure Consequences of Failure (CoF)
& Impact Negligible Minor Significant Severe
Very Likely Low Moderate High Extreme
Likely Low Moderate High High
Somewhat Likely Low Low Moderate Moderate
Unlikely Low Low Low Low
Table 2: Matrix 2 – Level of Risk
Where multiple risks are noted, these tables will be used for each risk and the highest level will be taken as the overall risk rating
for the tree. In this scenario, multiple mitigation options may be offered to the tree manager to return the risk to an acceptable
level within a reasonable timeframe as guided in Appendix 1.
A PPENDIX 3: D EFINITION OF ISA T ERMS
Likelihood of Failure
Improbable: The tree or branch is not likely to fail during normal weather conditions and may not fail in many severe weather
conditions within the specified time frame.
Possible: Failure could occur, but it is unlikely during normal weather conditions within the specified time frame.
Probable: Failure may be expected under normal weather conditions within the specified time frame.
Imminent: Failure has started or is most likely to occur in the near future, even if there is no significant wind or increased load.
This is an infrequent occurrence for a risk assessor to encounter and may require immediate action to protect people
from harm.
Likelihood of impacting a target
Very low: The likelihood of the failed tree or part impacting the specified target is remote. Occupancy rates are rare with no
protection or occasional with moderate protection.
Low: It is not likely that the failure will impact the target. The occupancy rates are frequent with partial protection or constant
with significant protection.
Medium: The failure is as likely as not to impact the target. The occupancy rates are frequent with single-side exposure or
constant with partial protection.
High: The failure is most likely to impact the target. Occupation is constant with no protection.
Occupancy rates (OR)
Constant: 24 hours a day, 7 days a week.
Frequent: A large portion of the day/week.
Occasional: The zone is occupied by people or targets infrequently or irregularly.
Rare: Not commonly used.
Consequences of Failure
Negligible: Low-value property damage or disruption that can be replaced or repaired, no personal injury.
Minor: Low to moderate property damage, small disruptions to traffic or infrastructure, or very minor injury to persons.
Significant: Property damage of moderate to high value, considerable disruption, or personal injury.
Severe: Serious personal injury or death, damage to high-value property or disruption of important activities.
Levels of risk
Extreme: Failure is imminent with a high likelihood of impacting the target, and the consequences are severe.
High: Failure is very likely or likely with significant consequences, or failure is likely with severe consequences.
Moderate: Failure is very likely or likely with minor consequences, or failure is somewhat likely with significant or severe
consequences.
Low: Failure is unlikely with negligible consequences or failure is somewhat likely with minor consequences.
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Tree Work - Maintenance Log Book Date of Works Location Description of Work Staff Member/s Attached Photos Additional notes