The Kedron Brook
A field report evaluating the challenge of managing urban encroachment along the Kedron Brook.
List of Figures:
Figure 3
Figure 4
Figure 10
Water Turbidity Test Results
Figure 12
Water Nitrate Test Results
Figure 13
Rates of Dissolved Oxygen
Introduction
The Kedron Brook is a natural water body which flows from the D'Aguilar Range through the northern suburbs of Brisbane, before emptying into the Schulz Canal at Nudgee Beach. Descending over 220 metres throughout its 29km length, the Kedron Brook is an essential component of the local environment, sustaining a diverse and critical ecosystem. Additionally, it holds a unique status to local traditional landowners, who have been actively involved in its conservation for thousands of years. Over the past 20 years, growth in population and urbanisation paired with the escalating effects of anthropogenic climate change have induced a manifold of geographic challenges to the land cover of the Kedron Brook.
Kedron Brook
The section of the brook which runs through the Northern suburbs of Brisbane has been impacted extensively by high rates of urban development over recent years. Efforts to reduce the rates of water erosion along the banks have been coordinated by community groups, landholders and the local council.
Site A - (Kedron State High School)
Located on the mid-lower section of the catchment, the section of the Brook bordering Kedron State High School is highly urbanized and prone to various biophysical and anthropogenic challenges as a result.
Site B - Nudgee Beach
Notably includes the end of the catchment which flows into Moreton Bay. Despite being a region of extensive conservation zoning and management, the wider Moreton Bay area has undergone sizable urban development in recent years, such as a major airport expansion and the construction of a waste management facility.
Methodology
The primary focus of this investigation is to evaluate the anthropogenic and biophysical impacts of urban development on the Kedron Brook. In particular, a focus will be drawn on the increased vulnerability of the site to erosion, and how the consequences of urbanization will entail future anthropogenic and biophysical effects. Quantitative data will be collected through samples assessing water quality, while qualitative data will be collected in the form of visual assessments made on local ecosystem populations, water erosion, and pollution. As majority of the quantitative data yielded ideal results, this report will focus on the qualitative data to identify how the lack of riparian vegetation (as a consequence of urban encroachment) resulted in increased erosion. It is important to note that the primary data will be collected in ideal conditions in specific locations, although recent flooding may have impacted the results (Figure 1).
Figure 1: Aerial extent of flooding along the Kedron Brook (Youtube, 2022)
Secondary data was incorporated into this investigation for the purpose of evaluating long-term impacts. Notable instances of this include the use of ArcGIS WayBack imagery, statistics from landcare organizations and federal databases, and diagrams.
Land Transformations
"Land-use change, particularly the reduction in riparian vegetation, was identified in the 1990s as a major driver of declining water quality and ecosystem health, particularly in South East Queensland rivers." - Kaitlyn O'Mara, Australian Rivers Institute
Figure 2: Land Transformation at the Kedron State High Site 1958 - 2022 (QImagery, 2022)
Figure 2 Notable Observations:
1958
Majority of the brook is covered in extensive forest and riparan zone.
1972
Land clearing for expansion of school oval and sporting grounds.
1978
Commercial zones begin to develop along Gympie Road, paired with increase in housing density.
1991
Extensive reduction in trees and Riparian zone surrounding the banks of the Brook. This area is replaced by bike paths and bridges.
2002
Forest and green space renewal around newly developed sporting facilities.
2014
Emergency Services precinct undergoes major expansion, correlating with further infastructure developments such as bridges, pathways and car parks. Additionally, Gympie road undergoes a major modernization and expansion.
2022
Kedron State High School undergoes major expansion, likely to accomodate for further population growth. Minor increase in Riperian zone observed, likely due to revegetation efforts.
Figure 3: Site A Land Use map (ArcGIS, 2022)
Land use at Sites A and B:
Legend for Figures 3 & 4
The most important change observed in Figure 3 was the removal of the Riparian vegetation to make way for hard surface development. . This coincides with the created land use map, which suggests urban encroachment has resulted in Site A consisting primarily of LR Low and MR Medium density residential land use (Figure 3). The various infrastructure expansions observed impact the local ecosystem in various ways, such as motorways increasing air pollution, residential expansion displacing wildlife populations, and chemicals being released into the environment via urban runoff.
Figure 4: Site B Land Use map (ArcGIS, 2022)
Land change in Site B consists of a major airport expansion initiated in 2015. This development is displayed in both the swipe map below (Figure 5) and in the Site B land use map (Figure 4). This expansion resulted in both mangrove area clearance and the Schultz canal having to be manually diverted.
Figure 5: Development of the Nudgee Beach Site 2014 - 2022 (ArcGIS Wayback, 2022)
Figure 6: Kedron - Gordon Park Population and Housing Type (Australian Bureau of Statistics, 2017)
The Kedron – Gordon Park area population has undergone an accelerated period of growth since 2007 (Figure 6). Figure 5 also indicates an increase in semi-detached housing and apartments to accommodate for this population growth. This replacement of low-density housing with high-density housing indicates urban consolidation, which further contributes to erosion and urban runoff.
Loss of Riparian Vegetation
Figure 7: Biophysical role of the Riparian Zone (Victorian Department of Environment, Land, Water, and Planning, 2005)
The principal consequence of these land transformations was the mass clearing of riparian vegetation along the banks of the Kedron Brook. The Riparian zone plays a critical role in the local ecosystem, preserving waterway health through biophysical processes such as infiltration, soil profile stability, and providing shade (Figure 7).
There was extensive damage to the Riparian zone at Site 1, primarily due to flooding and heavy urban development. However, thanks to directed conservation efforts through zoning, the mangrove areas at Nudgee Beach were largely intact.
Construction of Bike tracks
Impervious, developed surfaces such as bike paths drastically increase the rate of flow during rainfall and flooding, therefore increasing the severity of urban runoff. This is due to the lack of natural vegetation to slow and filter this flow. Furthermore, the construction of these bike paths has greatly impeded the riparian zone, reducing its length from 14.2m to 9.3m (Figure 8).
Figure 8: Measurements of Riparian Zone 1978 - 2022 (QImagery, 2022)
Catchment Flooding
The low elevation of the Brook riverbed, paired with the removal of vegetation has transformed it into a major floodplain. The Brisbane City Council's Flood Awareness Map (Figure 9) reports that the immediate area of the Kedron brook is at a High Likelihood (5.0% Annual Chance) of flooding annually. Thus, flooding occurs both more frequently and at higher severities within the Brook catchment, as was directly observed during the 2022 Brisbane floods.
Additionally, urbanisation is a primary contributor to anthroprogenic climate change, which subsequently increases the severity of current and future flooding.
Topsoil Loss
As is evident in Image 1, the loss of riparian vegetation has also correlated with a loss in topsoil. Due to both flooding and urban encroachment, the topsoil and hummus layers were observed to be completely destroyed along the banks of Site A. This vulnerability exacerbates the process of erosion as well as making it increasingly difficult for the Riparian vegetation to recover.
Weed outbreak
Many sections of the brook that suffered damage to the Riparian zone were observed to have renewed weed growth. Through reducing local soil moisture, these weeds create difficult conditions for native vegetation recovery. Despite this, these weeds do partially replenish the role of the Riparian zone, mitigating the effects of further water erosion.
The loss of Riparian Vegetation entails a plethora of anthropogenic and biophysical effects. Through the introduction of hard surfaces, disrupting the natural process of infiltration, and the destruction of water bank soil profiles, the site's vulnerability to flooding will increase exponentially as the Riparian zone is cleared further.
As flooding becomes more severe as a result, nearby residential areas will be placed under threat. Furthermore, it will become progressively more difficult for ecosystems to recover from the effects of erosion and pollution, causing issues within the local and wider food chain.
Erosion, Sedimentation and Nutrient Loading
The Kedron Brook Catchment Network has recorded the effects of erosion and sedimentation occurring since as far back as the 1960’s.
Image 4: Water erosion at Nudgee Beach (Site B)
Whilst erosion is a natural, biophysical process that occurs both with or without anthropogenic land change, the rate and extent of erosion observed at both sites was extensively affected by increasing urbanization.
As the local area is developed under both commercial and residential zoning, the natural riparian zone which preserves the local soil profile is threatened, subsequently resulting in large amounts of water-borne sedimentation, or turbidity.
Water Turbidity
Water sedimentation tests revealed that turbidity levels were noticeably higher at the Nudgee Beach site (Figure 10). It is highly probable that increased turbidity is a consequence of upstream erosion at the Kedron High Site.
Nutrient Loading
Nutrient Loading, to contrast, is a completely anthropogenic process which consists of water-borne nitrate and phosphate pollution, primarily through fertilizers. These nutrients are released into waterways via unfiltered stormwater and urban runoff (Figure 11). Riparian infiltration is the only process protecting waterways from such pollution, thus tying waterway health to the riparian zone.
Urban runoff
By replacing the riparian zone with hard-surfaced bike tracks, this process of natural infiltration was disrupted. Urban runoff transmits fertilizers from nearby residential areas into the Kedron Brook, with this process being exacerbated by recent flooding. Consequentially, tests at Site A revealed that waterway nitrate levels reached over 5ppm (Figure 12), creating ideal conditions for an algae bloom.
Low Dissolved Oxygen
Dissolved oxygen is essential for the survival of aquatic food chains, however high levels of algae force other organisms to compete for limited dissolved oxygen supply. Both sites reported 'Very Poor' dissolved oxygen results of 23.3% saturation and 30.3% saturation (Figure 13) respectively.
Biodiversity loss
The Invertebrate animal’s observation at Site A provided even stronger indication of this correlation. There was interestingly only a single observed species (Caddisfly Nymph) that could be considered ‘sensitive’, with every other observed invertebrate being highly adapted to a hostile living environment.
Variables such as low rates of dissolved oxygen, high levels of algae and water turbidity all contribute towards harsh conditions for local flora and fauna. This correlation provides an indication of overall poor ecosystem health, all as a direct consequence of urbanization and erosion.
Impact on Fisheries:
Increasing water turbidity at the Nudgee Beach site is particularly alarming, as the site is a major estuary and critical fish breeding ground. Mangroves and seagrass provide the ideal conditions for fish nesting, and thus water quality at the Nudgee Beach site is essential for sustainment of the ecosystem.
In 2018, Queensland fisheries returned over $300 million dollars in production value (Figure 14). Furthermore, trends indicate that previous flooding such as the 2011 floods contribute strongly to past downturns in fisheries production value.
Figure 14: Fisheries and Aquaculture Production value ($'000) (QLD Department of Agriculture and Fisheries, 2021)
Should pollution render the Nudgee Beach estuary unsuitable for nesting, it would become difficult for local fish species to replenish themselves, thus leading to a reduction in species population.
A lapse in supply would present devastating impacts on both local and wider economy. Employment and food security would be put under considerable risk.
Recommendations:
In order to produce a feasible and sustainable solution, three key priorities have been selected to mitigate the effects of urban encroachment along the Kedron Brook:
- Containing Erosion
- Preventing further Riparian loss
- Managing urban runoff
Highly coordinated Landcare transformation plans have been undertaken on other regional waterways to address similar issues, most notably at Oxley Creek. The Oxley Creek plan targets specific variables that contribute to poor waterway health, erosion, and vulnerability to flooding.
Considering the success observed at Oxley Creek by a coordinated transformation plan, it is therefore recommended that a similar plan be orchestrated for the Kedron Brook.
Overview of the Oxley Creek Plan:
Figure 15: Oxley Creek Transformation Overview (Brisbane City Council, 2021)
The Oxley Creek plan identifies key priority areas to direct land care efforts. Landcare methods consist of a diverse mix of riparian zone regeneration, stormwater treatment, and waterway stabilization (Figure 15).
Displayed below is the aspects of the Oxley Creek transformation deemed viable to replicate at the Kedron Brook:
Riperian Zone Regeneration:
Targeted maintenance and restoration of bank vegetation is critical in combating erosion. Through manual replanting of riparian vegetation and the replacement of lost soil, the natural and sustainable process of infiltration is restored, thus mitigating urban runoff. Additionally, through restoring the local soil profile, the bank vegetation becomes more resilient towards future flooding.
Water Stabilization:
Image 6: Rock seawalls and riffles at Site A and B
Waterway stabilization efforts were undertaken at both Site A and Nudgee Beach, such as the construction of rock seawalls to prevent erosion (Image 6). By preventing water flow stagnation, artificial riffles at Site A contributed by increasing rates of dissolved oxygen. Considering the existing success of these measures, it is recommended that further seawalls and riffles are constructed along the brook in order to further mitigate the effects of erosion.
Stormwater Treatment through Biorentation Basin:
Stormwater was a major source of runoff pollution observed at both Site A and B. By treating and filtering this runoff, the toxic nutrient load released into the waterway via stormwater can be mitigated.
Targeted Stormwater Treatment
The introduction of Biorentation Basins in highly urbanized areas allows for a simple, safe and efficient method of controlling urban runoff and sedimentation.
Through amplifying biophysical processes, the Biorentation Basin presents a particularly sustainible solution (Gold Coast Council, 2007).
Operation of a Biorentation Basin
Through landscaped depressions, stormwater is directed into the basin and processed with various physical, chemical and biological processes.
Waterway nitrate, petroleum, hydrocarbon, sedimentation and heavy metal levels are drastically reduced as a result.
How will this improve Site A and B?
The shallow ponding area of a Biorentation Basin facilitates a natural process for reducing water turbidity. Additionally, the vegetation and underdrain system reduces excess pollutants such as nitrates through nutrient cycling.
These reductions in water pollution will assist Site A in recovering waterborne dissolved oxygen. Site B will benefit greatly from these reduced toxicity and sedimentation levels, with fish nesting grounds returning to ideal conditions.
Conclusion:
The effects of erosion and urbanization were observed as playing a key role in land transformations along the Kedron Brook. These changes were then observed to have increasingly damaging anthropogenic and biophysical effects. Despite this, there is an opportunity for restoration and innovation in the face of compounding ecological challenges, and for a more sustainable future for the brook.