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FMD-ENV-STA-004 Design Standard Landscaping_Oct2012.doc Page 1 of 43 University of Wollongong Landscaping Design Standards October 2012 Version 4

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Page 1: Uow009695 Landscaping Design Standards

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University of Wollongong

Landscaping Design Standards October 2012 Version 4

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VERSION CONTROL SYSTEM Section Modified Description of Modification Version Organisation Representative Date Throughout UOW Logo added to headers V1 Asset Technologies Pacific Tom Poyner 28/11/06

11.2 Add risk assessment activity to conceptual design process.

V1 Asset Technologies Pacific Tom Poyner 1/12/06

11.4 Insert OH&S reference link V1 Asset Technologies Pacific Tom Poyner 1/12/06 11 & 11.3.8.1 Added preference for Australian native species. V1 Asset Technologies Pacific Tom Poyner 1/12/06 11. Added "maintain existing themes and ambience" V1 Asset Technologies Pacific Tom Poyner 1/12/06

11.1 Added "ensure at least 3 metres allowed between trees and buildings"

V1 Asset Technologies Pacific Tom Poyner 1/12/06

11.1 Added "ensure service easements remain free of trees and large shrubs"

V1 Asset Technologies Pacific Tom Poyner 1/12/06

11.3.3.5 Updated to note that trees are not desirable in areas of high pedestrian or vehicular traffic.

V1 Asset Technologies Pacific Tom Poyner 1/12/06

11.3.7.4 Changed to preference for curved edging V1 Asset Technologies Pacific Tom Poyner 1/12/06 11.6 Inserted design standard drawings V1.01 Asset Technologies Pacific Michael Lee 8/06/07 Throughout Reviewed V2 University of Wollongong Martin Bramston 14/10/09

Throughout Document updated to reflect name change from Buildings & Grounds (B&G) to Facilities Management Division (FMD) and rebranding logo

V3 University of Wollongong Yvonne Butcher 8/3/2012

Throughout Review to reflect changeover from Maintenance to Environmental Services V4 UOW David Low 16/10/12

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Contents 1. LANDSCAPING ..................................................................................................................... 41.1 OVERVIEW ........................................................................................................................ 41.2 DESIGN PROCESS ............................................................................................................ 51.3 DESIGN GUIDELINES ..................................................................................................... 6

1.3.1 General ............................................................................................................................ 61.3.2 Safety ............................................................................................................................... 61.3.3 Existing Environment ...................................................................................................... 61.3.4 Existing Services ............................................................................................................. 91.3.5 Excavations & Level Build-up ........................................................................................ 91.3.6 Soils ............................................................................................................................... 111.3.7 Grass .............................................................................................................................. 121.3.8 Plants ............................................................................................................................. 131.3.9 Shrub Beds .................................................................................................................... 151.3.10 Paving ........................................................................................................................ 151.3.11 Mulching ................................................................................................................... 161.3.12 Special Areas ............................................................................................................. 17

1.4 STANDARDS ................................................................................................................... 181.5 LIFE CYCLE COSTING .................................................................................................. 181.6 LANDSCAPE ELEMENTS ............................................................................................. 19

1.6.1 Drawings ....................................................................................................................... 19Appendix A ................................................................................................................................... 20

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1. LANDSCAPING Well designed landscaping can create an interesting and dynamic environment. It is important that the design produces both a functional and aesthetic environment that can be efficiently maintained. The design and construction should be carefully considered to ensure that it serves UOW's intended purposes including: Solar screening; Amenity and distinct landscape character for recreational areas; Direct the flow of pedestrian and vehicular traffic along paths and roadways; Safe and accessible areas; Habitat for wildlife; Noise reduction and privacy; Visual stimulation and creating interest; Define boundaries between two or more facilities; Screen undesirable objects from view; Maintain predominant plantings of Australian Native species; Maintain existing themes and ambience of the Wollongong Campus.

1.1 OVERVIEW

This design standard outlines the design requirements for landscaping at UOW. The landscape designer shall use these standards as a basis for the design. However, it is incumbent upon the landscape designer to ensure that the design is suitable for the purpose of the area, is cost efficient and complies with all relevant building codes, regulations and standards. As landscape environments need ongoing maintenance the following requirements aim to minimise this task. Ensure that grassed areas are large enough to manoeuvre ride-on mowing equipment; Ensure that shrub beds and grassed areas have adequate surface drainage; Plan the placement of trees in lawn areas to ensure efficient mowing; Ensure that a mowing edge is constructed against walls and planting beds and finish

edges flush with adjacent grass areas to avoid hand clipping; Plant trees and shrubs in beds with a minimum 75–100 mm depth of mulch; Plant trees and shrubs in large groups; Ensure that at least adequate distance is allowed between trees and buildings so that

they do not impact on each other eg. restrict root growth, block gutters with leaves; Ensure that service easements remain free of trees and large shrubs; Provide more plants than required at maturity so weed growth is restricted during

initial growth. As plants mature they will be thinned out; Choose plants that are locally endemic, long lived, hardy and require minimal

maintenance. Design paths and paving to accommodate the desired lines of access and egress; Ensure preparation of soil for planting and grassing. Where the landscape designer considers that an alternate design philosophy is more appropriate than that specified in the design standard, the landscape designer shall advise

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the principal of the functional, aesthetic or cost benefit that will be achieved through the implementation of the alternate design philosophy.

1.2 DESIGN PROCESS

This section provides an overview of the design process. The process shall be followed to achieve UOW's desired outcomes.

Figure 1.1 - Process Flow

Design & Development Planning

Establish budget Identify functional areas Perform feasibility study

Plant Selection

Identify appropriate plant types Assess maintenance implications

Conceptual Design

Identify design objectives Define functional areas Define area boundaries Identify appropriate materials Determine environmental impact Prepare life cycle costs

Detailed Design

Specify materials Specify equipment Specify plant types Specify mulching requirements Specify construction

requirements

Design Review

Verify design objectives Review budget against cost plan Review design against brief

Design Changes

Revised design specifications Revised design drawings

Design Validation

Verify objectives will be satisfied

Design Acceptance

Obtain unit manager/landscape supervisor sign-off

Obtain project manager sign-off

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1.3 DESIGN GUIDELINES

1.3.1 General

The landscape designer shall adopt a holistic approach to designing new landscaped areas. This will ensure consistent aesthetics and quality throughout the UOW campus. The landscape design shall be in accordance with all relevant building codes, regulations and standards.

1.3.2 Safety The designer shall consider the safety aspects when preforming all landscape designs. The designer shall implement the following guidelines: Position trees to ensure minimum clearance requirements for services and

sight lines are maintained; Position trees to ensure they do not conflict with existing or proposed

buildings; Choose appropriate plants with consideration given to the purpose of the

area (e.g. do not place shrubs with sharp or spiky foliage in areas such as pathways and playgrounds where they may cause injuries);

Ensure that the design does not restrict or interfere with access and egress; Ensure that the design considers disabled access requirements; Ensure that the design does not form a complete screen or enclosure where

pedestrians may feel vulnerable; Position trees and plants to ensure that they do not conflict with existing or

proposed security measures.

1.3.3 Existing Environment It is important that the designer considers the impact on the existing environment of the new landscape work. The designer shall ensure that provisions are allowed for to protect against the following: 1.3.3.1 Damage

Damage may occur to vegetation during the landscaping works. Damage generally occurs through physical disturbance of the area, incorrect chemical applications or through changes to existing drainage systems. The damage may involve: Severed roots caused by excavation and trenching for

underground services, kerbs and gutters and footings; Suffocated feeder roots caused by filling; Drought or water logging of the root zone caused by changes in

the drainage system;

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Physical damage to roots, suffocation and drought of the root zone caused by compaction;

Chemical damage caused by engine oil leaks, hydraulic fluid and other chemicals that are taken up by roots;

Physical damage to trunks and branches can facilitate the entry of disease and decay.

1.3.3.2 Tree Retention

During the design process, the designer shall assess and record information for all existing plants showing: species type, size (height, canopy spread and trunk circumference) and location. When established plants are designated for retention in development areas the canopy, trunk and roots shall be protected from damage. A decision to retain, prune or remove plants shall be made in the initial design stage with full recognition of their value, potential costs, advantages and disadvantages, and alternative design strategies available to retain the plants. If damage to the roots is likely to eventually kill a plant then removing the plant before work starts will avoid the difficulty and expense of later removal. The designer shall carefully consider retention of large trees in confined areas such as courtyards in view of safety and maintenance implications. In planning new landscaped areas, the appeal and value of the area can be greatly enhanced by retaining existing vegetation (both mature and semi-mature specimens). Techniques for achieving this include: Road Alignment – where good stands of trees occur, vary the

alignment of roads and services to avoid the trees;

Traffic Islands – dense stands of medium sized trees may be retained in adequately sized islands between carriageways or on roundabouts;

Laneways – design laneways wide enough to accommodate services, existing vegetation, paths and overland stormwater requirements;

Landmarks – design landscape layouts to use landmark trees for orientation and aesthetic effect, for example at the top of a hill or in a roundabout.

Retained vegetation often requires remedial action for drainage, aeration and irrigation. It is preferable to retain trees in a group in a large island than a single tree in a small island.

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1.3.3.3 Soil Compaction The simplest and most effective protection for trees during landscaping works is fencing out construction activity. The fences shall be maintained for the duration of the project and shall only be removed when essential activity such as final landscape shaping is being undertaken. Maintenance access to each tree shall be considered at the design stage. As a general rule, feeder roots grow in the top 150–300 mm of the soil. This feeder zone can extend two to seven times the diameter of the canopy drip line (the drip zone). Site sheds, building materials or vehicles shall not be placed within the drip zone of existing trees. The drip zone shall be fenced off, and all trees must be protected from compaction within the feeder zone. Heavy machinery shall not be allowed in this area.

1.3.3.4 Tree Staking Juvenile trees require support to protect them from wind, vermin and vandalism. Staking shall be provided to protect juvenile trees with the support they need to develop into mature trees.

1.3.3.5 Tree Guards and Grates

Metal tree guards offer protection to trees and add a decorative element. When installing metal tree guards the designer shall ensure that it allows for the tree to grow without damage to branches or the trunk. Tree grates protect the root system of the tree and add a decorative element. When selecting a tree grate ensure that the grate can be adjusted to accommodate the growth of the trunk. Tree guards and grates shall be installed for existing trees in areas of high pedestrian or vehicular traffic. New trees should not be planted in areas of high pedestrian or vehicular traffic. Newly planted trees in open space areas shall be protected with plastic tree guards. These guards protect the trees from vermin, make the small trees visible and create a microclimate with the guard. The guards are generally placed around the tree with three supporting stakes and the area around the tree is mulched. Plastic tree guards, which also provide water holding capacity and slow water release facility, shall be used where appropriate. These guards shall be used to provide a recently planted tree with a slow release of water, which reduces the need for additional hand watering and lessens the stress on the tree.

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1.3.4 Existing Services

Conflict between plants and existing UOW infrastructure such as powerlines, water pipes, street lights, paving, kerbs and signs shall be avoided. In developing a landscape design, an awareness of the location of existing services is essential. Conflicts may result in: Increased maintenance costs; Reduced longevity of the trees and loss of aesthetic value; Reduced public safety. Beneath power lines, plant only trees that will not encroach upon the acceptable safe distance from the power lines when mature. A corridor of 10 metres either side of the power lines should be maintained. A clear line of sight shall be provided to signs, lights and driveways. Low branching or weeping species shall not be selected for use near these items. Where possible, trees shall be planted the maximum distance available away from kerbs, driveways and footpaths to reduce root interference. A one metre minimum clearance (for desirable deep or fine rooted smaller trees), and a root barrier shall be installed to reduce the impact of a tree’s vigorous root system. When planting trees near buildings, species selection is important. The designer shall consider the mature size of the tree and its root system. Where possible, planting trees close to buildings shall be avoided. Trees with vigorous root systems are able to penetrate and interfere with underground services such as stormwater and sewer mains, and underground cabling such as telephone and electricity lines. Damage to these services can sometimes be reduced by the installation of root barriers. Root barriers may not be effective where water leaks out of pipes. Careful species selection is therefore essential. The designer shall select trees that do not have vigorous root systems within service easements.

1.3.5 Excavations & Level Build-up

Excavations and level build-up around trees shall be minimised. Level changes within the feeder zone of a tree will affect tree health. Some species are better able to recover from level changes than others. Root systems can be given some advance preparation to reduce the impact of a project involving a major change in ground level. A lead-time of at least one (1) year is necessary to make this effective. Up to 50% (depending on species and age of tree) of the roots that will be affected by the project shall be severed and new root growth encouraged within the area that will not be disturbed.

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1.3.5.1 Level Build-up

Where level build-up is necessary, the fill soil should be the same (or a coarser) texture as the original surface soil to ensure that downward capillary water flow is not affected. If the ground is heavily compacted, soil aeration should be performed before the fill soil is added. Where the change in level is no greater than 100 mm and is restricted to one side of the tree, no specific action is required. Drainage and aeration shall be provided when either of the following situations occurs: Fill depth is greater than 150 mm on one side of the tree and

within the drip zone; Fill depth is greater than 100 mm within the feeder zone on all

sides of the tree. 1.3.5.2 Excavation

The following factors should be considered before performing excavation that may interfere with the root system of a tree: Species and age of the tree; Size and stability of the tree; Depth and location of the excavation; Percentage of roots being severed.

Excavation occurring on one side of the tree, halfway from the drip line to the trunk will eliminate about 30% of the feeder roots. Healthy trees should be able to recover from such a loss if proper care is taken to nurture the tree after the works have been completed. When a project requires excavation around a tree, the designer shall implement the following guidelines: Make the design documentation adaptable and take into account

root locations identified during construction; Do not excavate within the feeder zone of mature Eucalyptus

species except where work is on one side of the tree only and outside the drip zone;

Do not excavate within 1 metre of the tree trunk. If the entire area around the tree is lowered more than 150 mm the tree may not survive unless soil is returned within an appropriate distance of the trunk (This distance will depend on the species, rooting pattern, and soil and moisture conditions at the site);

Where possible, the original level shall be maintained. Terracing can be implemented to accomplish this;

All work within the drip zone shall be performed by hand;

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Do not sever large roots (>30 mm diameter) closer than halfway from the drip line to the trunk;

Cut all roots cleanly with equipment that is specifically designed to cut roots;

Protect roots that are exposed during excavation from desiccation;

Do not use heavy machinery within the feeder zone. 1.3.5.3 Trenching To Install Services

Service trenches shall be placed as far from existing and proposed trees as possible. If services must be placed inside the drip line of a tree then tunnelling beneath the tree is preferable as it is less disturbing to the root system than tunnelling to the side. Trenching inside the drip line will seriously injure and possibly kill the tree.

1.3.6 Soils 1.3.6.1 Soil Drainage

The designer shall minimise disturbance to soil moisture levels. A change in moisture levels may cause a decline in vegetation health due to an increased susceptibility to pests and diseases. This will often lead to plant death. Changing the ground level commonly disturbs surface drainage. This may divert water away from root systems or increase runoff and lead to water logging or collar rot. Sub-soil drainage is affected when substantial areas of hard paving or buildings are placed near vegetation, where areas surrounding vegetation are heavily compacted, or where major changes to ground level occurs. Sub-soil drains shall be used where excess water is likely to be a problem.

1.3.6.2 Soil Selection Soil selection for plants is an important factor when designing landscaped areas. The selection of soil can mean the difference between a poorly performing landscape and a thriving landscape. Where the existing soil cannot provide plants with sufficient nutrients and water penetration for their survival, the soil shall be improved or soil imported to supplement the existing soil. Where importing soil is not an option, soil tests may indicate the most effective way to improve the soil.

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1.3.6.3 Structural Soils

The designer shall implement the use of structural soils to replace existing soil in areas where soil structure and composition is of poor quality for plant growth and where existing trees have struggled and performed poorly. Structural soil material is typically a gap-graded crushed rock combined with a clay loam soil and a stabiliser. The blended material creates a ratio of soil to rock that can be compacted in accordance with standard specifications for sub-base materials and still provide soil-filled voids between the stones where roots can penetrate freely. The soil component allows for adequate nutrient, water holding capacity and air movement. The material will not provide aeration or drainage unless particle size distributions are carefully specified and graded. Adequate drainage shall be installed with structural soils. The ratio of soil to stone materials is critical and is determined by local climatic conditions, landscape treatment i.e. pathways or carparks, and plant selection.

1.3.7 Grass

The designer shall consider the following when designing grassed landscape areas. 1.3.7.1 Irrigated Grass

Irrigated grass areas have high maintenance costs and shall be limited to areas subject to high usage or to areas with specific visual and design significance. Requirements for irrigated grass: Topsoil shall be of an appropriate quality; Areas shall have grades of no less than 1:70 and be able to drain

without ponding; Areas shall be easy to mow with appropriate equipment and

machinery; Irrigated grass shall not have tight corners or be steeper than 1:6; Mowing obstructions shall be positioned to allow the easy

manoeuvring of ride-on equipment (a minimum clearance of 2.7 metres shall be allowed in most areas, with a 2 metre clearance

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allowed in tight developments where smaller machinery is acceptable);

Where shrub and tree planting (including low branches) does not allow clearance for mowing equipment, it is preferable to incorporate planting into a mulched bed (self-seeding trees may be a problem in these locations);

Paths or barriers to partition off narrow sections of grass are not

desirable but paths can be positioned to define the edge of irrigated grass;

Hard surfaces, mulch, granite or shade tolerant ground covers

are preferred for shaded areas.

1.3.7.2 Dryland Grass

Dryland grass shall be used in areas low usage or where aesthetics are not a top priority. The surface shall be level and smooth. Grass shall not be sown on slopes greater than 1:4, areas with less than a 3 metre clearance, acute corners or in other difficult to mow areas. Obstructions in dryland grass shall be spaced far enough apart for mowing by 2 metre wide equipment. Bitumen and straw mulch shall be used to assist in the establishment of grass and reduce erosion on sloping surfaces.

1.3.7.3 Native Grass

The use or retention of native grass and herb species is encouraged. Native grass plantings that are mulched shall be maintained with mulch at a depth of 50–100 mm. All bare areas should be covered and finished level with or below the level of adjacent footpaths, roads and kerbs.

1.3.7.4 Edge Treatment

Grass edges shall be stable and able to withstand traffic by maintenance vehicles. They must also be able to withstand mechanical grass cutters. Curved edging is desirable in most circumstances. Serrated paving, metal and small section timber materials are not desirable materials to use as edging.

1.3.8 Plants Plant species shall be chosen carefully to suit the intended purpose; otherwise the trees can become a detraction from the space or even not survive.

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Trees can provide screening from prevailing environmental conditions such as high winds and also from roads or buildings. Careful consideration shall be given to the selection of species and its appropriateness for providing a screen. Selection of species shall also take into account the surrounding tree species, so that the trees blend into the surrounding environment when mature. Screen planting for future developments shall be carried out several years before construction of the development so that the trees have time to mature to fulfil their screening role. Correctly designed planting can fulfil the following functions within a landscape: Provide shade; Introduce visual interest; Screening and wind breaks; Divide the space into a series of spaces; Provide habitat for wildlife; Add scale to an open space. 1.3.8.1 Plant Selection

Plant species for use in UOW grounds shall be chosen carefully. Designers shall consider the site conditions, maintenance requirements and design intent when selecting plants. Plants shall be predominantly Australian Native species. The following shall be considered when selecting plants:

Selection of an appropriate species for its intended purpose; The mature height and crown spread of the tree. The following shall be considered when designing planted areas for a new landscape: The tree spacing. Different types of tree planting have different

spacing requirements, especially in areas of dense planting such as wind breaks, screening and forward tree planting;

Clearances from above and below ground services, as well as new and proposed buildings;

Sight lines for both pedestrian and vehicular traffic; Access for mowing and other maintenance vehicles.

1.3.8.2 Protection of Surrounding Infrastructure

The use of root barriers provides protection to the surrounding infrastructure against disruption from tree roots, with minimal impact on the tree. Properly installed root barriers protect pavement,

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footings and kerbs from cracking and lifting caused by certain tree species. Root barriers shall be installed vertically in a continuous length in a narrow trench dug on the tree side of the pavement or kerb with the top edge flush with the finished ground surface. If a ribbed root barrier material is used, then the root barrier shall be positioned so that the ribs run vertically. The trench should be backfilled and tamped sufficiently to avoid later subsidence. The barrier should not be torn or pierced.

1.3.9 Shrub Beds

Shrub beds form an integral part in the development of landscapes. If properly designed and maintained they provide amenity and quality to the area. Shrub beds provide spatial definition, visual interest, treatment of slopes, cohesion in the space and a setting for buildings. The designer shall consider the following when designing shrub beds: Irrigation of shrub beds beneath eaves or other overhangs; Shrubs shall be spaced at a distance approximately three-quarters of their

mature width unless forming a screen, in which case they shall be planted closer;

Shrub beds are ideal on steep slopes that are otherwise unsuitable for grass cover and in heavily shaded areas or areas that are difficult to mow;

Shrub beds reduce erosion caused by storm water; Shrub beds require adequate surface fall to drain excess water; Avoid placing beds in low-lying areas where water cannot easily be

removed; Avoid creation of areas that may encourage undesirable activities such as

hiding and loitering; Future vehicular access for mowing, litter removal, tree surgery, pest

control and other maintenance. Large shrub beds require relatively high levels of maintenance; Avoid the use of spiky shrubs near pedestrian areas, child care areas and

high litter areas; Shrub plantings next to paths, buildings, lawns and fences shall have a

minimum clearance equal to their mature drip-line radius; Shrub beds can provide windbreaks where winds are likely to make the

area unpleasant; Avoid obstruction of access to manholes, valves etc.

1.3.10 Paving

Hard paving surfaces form part of the landscape features for UOW. Paving materials shall be selected to ensure aesthetics and quality is consistent across the UOW campus.

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Permeable paving is useful where a hard surface is required to be installed near trees. Structural soils and permeable paving, used together, allow water to filter through the paving surface to the soil layers below, providing water and nutrients to the plant’s root system while still providing a hard wearing, trafficable surface. The permeable paving may be pavers with porous material between, special pavers or gravel stabilised with epoxy resin or other bonding agents. Permeable pavers are similar to normal clay and concrete pavers but contain a series of drainage holes in the surface of the pavement. After installation the drainage holes shall be filled with a freely draining material. Adequate drainage shall be installed with permeable paving.

1.3.11 Mulching The type of mulching material to be used for planting areas shall be selected on the basis of its general purpose and location of the bed within the environment. When applying mulch to newly constructed shrub beds, it shall be applied so its settled depth is 75–100 mm. This will prevent most seed germination in the soil. Fine mulch shall not be used as it is prone to being either blown or washed away and decompose too rapidly. Common mulching materials include but are not limited to: 1.3.11.1 Pine Flake

Pine flake is a commonly used mulching material for shrub beds. This mulch shall be used to cover both non-irrigated and irrigated planting areas. It is especially useful on sloping sites as the mulch binds to itself and near buildings because it will not cause damage when thrown.

1.3.11.2 Pine Bark

Pine bark is more expensive than pine flake and comes in a variety of sizes. Its attractive appearance suits its use in prestige areas.

1.3.11.3 Decomposed Granite

Decomposed granite has a relatively high cost. It shall be used in low maintenance areas where some pedestrian traffic across the shrub beds is expected. Decomposed granite shall not be used as mulch on sloping sites greater than 1:30 or in areas where loose material can spill onto pathways.

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1.3.12 Special Areas 1.3.12.1 Roads and Carparks

Trees and plants planted along roadsides and in carparks often suffer stress from lack of water and air. When trees do grow well, the road or carpark surface is often damaged by the root system. Providing more space around the tree shall reduce this problem. The designer shall consider the following when designing landscaped areas for roads and carparks: Fast growing, large trees have the most potential to disrupt

hard surfaces; Trees with nuisance litter drop such as fruit or sap are not

suited to roadside or carpark planting; Ensure that plants have access to adequate moisture and air.

The area shall be ventilated properly with air and moisture pipes. Permeable paving and structured soils can be used to help achieve this;

Ensure that a root barrier is installed when trees are planted close to hard surfaces;

Avoid the use of hard surfaces too close to the trunk, which may cause girdling as the tree grows.

1.3.12.3 Streams & Ponds

The designer shall consider the following when designing streams and ponds: Ponds and streams shall not create environmental hazards; Ponds and streams shall not be located where they will prevent

Utility Authorities from gaining access to their mains or services;

Ponds and streams shall not be located where they will obstruct vehicular or pedestrian access. Where necessary, bridges shall be designed to provide access.

The maximum depth shall not exceed 3.0 m because of the increased risk of temperature stratification beyond this depth.

The designer shall consider the following when selecting plants for use in ponds and streams: The proposed plants shall be able to establish and grow; Plants shall be unlikely to colonise outside the proposed area; The maximum height of the plants shall be consistent with

maintaining desirable visual characteristics around the pond or stream;

The over-wintering form of a plant shall not cause degradation of the aesthetics of the area;

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Plants shall not grow to a density that would provide habitats suitable for mosquito breeding.

1.3.12.4 Child Care Areas

Child care areas form part of UOW's commitment to providing quality childcare facilities. A child’s entitlement to play should be recognised and reflected in the range of experiences made available to them. Where appropriate, a playground and equipment shall be accessible to all persons (i.e. including people with disabilities).

1.4 STANDARDS

The design shall comply with the latest versions of all relevant codes and standards in force at the time of specification. Table 11.1 below contains a list of the relevant codes and standards.

Issuing Body Document Number Title

Australian Building Codes Board BCA 2006 Building Code of Australia

Standards Australia AS 1428.1 Design for access and mobility

Standards Australia AS 4373 Pruning of Amenity Trees

Standards Australia AS 1924 Playground Equipment for Parks, Schools and Domestic Use.

UOW OHS064 OH&S Consideration for Design (http://staff.uow.edu.au/workingsafely/design/OHS064-OHS_Design_Guidelines.pdf)

Table 1.1 - Codes and Standards 1.5 LIFE CYCLE COSTING

The designer shall prepare life cycle costing as part of the conceptual design process. Due to the varying cost of undertaking landscaping works and the significant difference in cost between elements it is important that the designer prepare individual life cycle costs for each of the following major group elements: a. Civil Works; b. Flora and Fauna; c. Landscape Furniture.

As landscaping can last for any nominated period, depending on the maintenance undertaken, the period of financial interest should be determined by the projected life of each element.

These costs will include: a. Materials; b. Initial construction; c. Regular and reactive maintenance.

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1.6 LANDSCAPE ELEMENTS

1.6.1 Drawings

The following landscape elements shall be designed and constructed in accordance with drawings:

01 Typical paving detail

02 Typical path plan

03 Brick paving detail – curved edging.

04 Brick surround to stormwater grate

05 Trench drain detail – paving

06 Brick infilled pit cover

07 Grated trench drain

08 Tree planter in paving

09 Brick steps

10 Freestanding seat wall

11 Retaining seat wall

12 Kerb and gutter detail

13 Planter box / retaining wall detail

14 Tree grate to existing tree

15 Typical planting detail

16 Typical bench seat detail – 1

17 Typical bench seat detail – 2

18 Lawn turfing detail

19 Garbage bin detail with paving below

20 Timber bollards

21 Sandpit

22 Freestanding bicycle rack

23 Inverted ‘U’ leaning rail

24 Timber edge to mass planting

Refer to Appendix A.

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Appendix A

Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

Hardwood

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

Perforated metal litter bins now in use. Please refer to Street Furniture Australia LB2 80L http://streetfurniture.com/au/products/waste-bins/rim-bin/ Subsurface and paver requirements still apply

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.

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Drawing is not to scale. Refer to original PDF for scaled drawing.