An Urban Environment

Introduction
Urban Climate
Urban soils
Waterproof ground surfaces
Water quality
Impact of urban development on streams
Flooding and other concerns
Air pollution
Noise

Introduction

Kedron Brook flows through a largely urbanised catchment. Here human activities and land use dominate and affect all aspects of the physical and biotic environment. Human populations are currently growing at a faster rate than ever before. Population growth in the Kedron Brook catchment is no exception.

The ecological processes occurring in an urban catchment differ from natural and rural areas. Resources for wildlife are often limited. There are many hazards (pollution of all types, motor vehicles and human interference etc).

Natural areas in an urban landscape are fragmented; that is, small remnants are isolated from one another.

Development of land in the Kedron Brook catchment has almost reached its limits. Only in the upper catchment is further housing development occurring.

Habitat within the older suburbs has stabilised and in recent years, ecological qualities have been improved through the activities of Bushcare groups.

Consequences of human land use on an urban catchment that apply to Kedron Brook are outlined below.

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Urban Climate

The climate in urban areas is often 3-4ºC warmer than surrounding rural or natural areas.

This arises from

  • high absorption of heat by building materials and paved surfaces
  • loss of shady tree and other vegetation cover on the ground surface
  • reduction of moisture reaching (and therefore cooling) air due to transpiration

Urban temperature changes can be important in temperature sensitive species of plants and animals. Temperature may stimulate flowering in some plants and affect growth rates of plants and invertebrates.

In urban areas wind speeds are reduced due to building roughness. However, wind tunnels can form when the wind direction aligns with straight roadways or other built features.

When compared with surrounding rural land, urban areas tend to have

  • a lower relative humidity
  • more chance of fog
  • and a mini “greenhouse effect” on the immediate surroundings (warmer and elevated carbon-dioxide)

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Urban soils

Urban soils are modified from natural soils due to the action of

  • construction and related disturbance
  • mixing and movement of soils within the landscape

Often in developed areas, the rich topsoil has been removed or mixed with subsoils during construction. Even when topsoils is stockpiled and respread on the land it takes time for a functional soil profile to develop.

Urban soils are often compacted. This leads to poor drainage and limited aeration (oxygen) in the soil. Plants and soil micro-organisms require oxygen within the soil to grow and function properly.

Nutrients become depleted in urban soils. Leaf litter and other organic debris are important contributors to nutrient addition in natural soils. When there is no vegetation cover, there is little replenishment of the nutrients leached by rainfall from the soil profile.

It is difficult for plants to establish in many urban soils due to

  • the low soil oxygen levels
  • inadequate drainage
  • low nutrient levels

These conditions are also harmful to soil micro-organisms.

Micro-organisms in the soil have an important role in the breaking down of organic material to the component nutrients that are used by plants.

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Waterproof ground surfaces

Development results in construction of many surfaces (roads, roof tops, concrete and parking areas). These form a barrier to rainfall penetrating the soil. These surfaces are described as impervious.

The high number of impervious surfaces has a major impact on the hydrology (water flows) within the urban catchment.

  • less water reaches the watertable leading to a decline in water table levels over time
    large areas of impervious surfaces lead to an increase in water run off; this can increase erosion, both on cleared land and within drainage channels
  • stream flow is more variable in urban areas. As the watertable is not recharged, there is less percolation of water from the watertable into the stream during dry periods.
  • Increased runoff increases flow during rainfall events in urban areas

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Water quality

Water flowing from urban areas often contains particles and pollutants that impact on waterways. These are described in more detail in Stream characteristics.

These include

  • toxic materials
  • additional nutrients (commonly nitrogen and phosphorous)
  • sediments

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Impact of urban development on streams.

General impacts of urban development on streams include:

  • muddier streambeds due to fine sediment entering the stream
  • increased turbidity (cloudiness) of the water. This is a consequence of suspended
  • sediments coming from erosion of exposed soil surfaces.
  • increased erosion of the streambank. This is a consequence of more water moving through the waterway at a higher velocity.
  • streambank abrasion increase due to suspended sediments
  • pollution in the form of toxic heavy metals, fertilisers and pesticides
  • toxic heavy metals such as lead, cadmium and mercury. These pollutants can come from tyre wear and vehicle emissions as well as commercial or industrial operations.
    fertilisers. Excess nutrients in waterways often arise from intensively managed parklands, gardens, golf courses, bowling greens, sports fields and animal husbandry activities. The increase in nitrogen and phosphorous can lead to algal blooms.
    pesticide. These chemicals can accumulate in the food chain and affect species far removed from the source.

Water temperatures in urban streams are higher than that of natural counterparts due to:

  • heat which is absorbed by impervious surfaces and transferred to runoff water
  • removal of riparian vegetation which allows more light to reach and warm water in the stream

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Flooding and other concerns

To quickly remove the excess runoff in developed areas streams are often channelised.

This practice was more widespread in the past and involves:

  • removal of the riparian vegetation
  • straightening of the stream
  • concreting of the channel

Examples of channelisation are evident in different sections of Kedron Brook.

A 4 km section of the Kedron Brook downstream from the Webster Road Bridge was channelised following the 1974 floods.

The lower reaches of Kedron Brook were channelised into Schultz Canal during the redevelopment of the Brisbane airport in the 1980’s.

Concrete channels were constructed on some of the tributaries of Kedron Brook including Sandy Creek and the Colac Street channel.

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Air pollution

Visible particles of dust, smoke and exhaust materials from vehicles and other forms of fossil fuel consumption concentrate around urban areas. Eventually, many of these particles settle. They are washed by rainfall into the stormwater systems and eventually reach local streams.

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Noise

Urban areas have a background of noise. The effect on wildlife is poorly known. Some species will thrive despite noise, such as the raptors that roost and nest in the vicinity of the Brisbane Airport. Birds and other animals that rely on acoustic communication may be more disturbed if the noise prevents communication for finding mates or food.

Wildlife can also be responsible for uncomfortable levels of noise to humans. Gatherings of crows cause early morning disturbances when calling.

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CI 08/07/2008
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