E.C. Denman, P.B. May, G.M. Moore
University of Melbourne

This paper has been presented previously at the Urban Trees Research Conference, “Trees, people and the built environment”, 13 & 14 April 2011, Birmingham, UK and the ISA Annual Conference, 25 – 27 April 2011, Sydney.

Abstract

Sustainable stormwater management presents unique challenges and opportunities in the urban built environment. The disposal of stormwater directly from impervious urban surfaces into surrounding waterways is detrimental to the aquatic environment. In response to this, processes such as evapotranspiration and soil and groundwater recharge are increasingly being used so that hydrological patterns of urban areas more closely mimic natural areas. Vegetation, including urban trees, affects many of these processes and is an important component of stormwater management.

An experiment was conducted in Melbourne, Australia to assess the potential role of street trees in urban biofiltration systems. Four tree species, Eucalyptus polyanthemos (Red Box), Lophostemon confertus (Brush Box), Callistemon salignus (Willow Bottlebrush) and Platanus orientalis (Oriental Plane) were grown in three different constructed soil profiles, including one chosen for its low, and potentially growth limiting drainage rate. The plants were irrigated with tapwater (potable) or a model stormwater solution. In general, tree growth, in all soils, was increased when the irrigation was with the model stormwater solution.

Compared to unplanted controls, the presence of trees in the biofiltration system resulted in significant reductions of the soluble nitrogen and phosphorus concentrations of the stormwater. In general, biofiltration systems effectively reduced the filterable reactive phosphorus (FRP) concentration of stormwater. The treatment of nitrate plus nitrite (NOx) concentration of stormwater was more variable from planted systems with reductions achieved during cooler months while NOx was generated during warmer months.

Species selection did not appear to be an important element in terms of system success. Profile planted with the deciduous species performed similarly in terms of nutrient removal to the systems with evergreen species, although there was some seasonal variation. Incorporating street tree plantings as stormwater treatment measures offers an exciting opportunity to create multi-functional landscapes.

Keywords: trees, stormwater, biofiltration

Introduction

Urbanisation changes many attributes of the land that is developed. One of these is a reduction in the permeability of surfaces that can lead to modified patterns of runoff and increased loads of pollutants entering downstream waterways. The degree of impervious surfaces or perhaps more importantly, the nature of the pathway between where the stormwater is generated and where it flows into the receiving waters, can be important predictors of the extent of disturbance to the health of aquatic ecosystems (Taylor et al., 2004, Walsh, 2004, Hatt et al., 2004). Approaches that are used to offset this disturbance are known by various names that include water-sensitive urban design (WSUD) (Australia), sustainable urban drainage systems (SUDS) (UK) and low impact development (LID) (USA). Urban trees are an important component of these more sustainable approaches to stormwater management.

Biofiltration systems, also known are raingardens or biofilters, are one of the strategies used as part of WSUD to improve the quality and reduce the quantity of urban stormwater runoff. Biofiltration systems direct stormwater runoff into a treatment area that has plants growing in a moderately permeable soil. The run-off percolates through the system and a combination of physical, chemical and biological processes reduces the nutrient and sediment load of the runoff. The volume and speed of delivery of run-off directed into waterways is also reduced if stormwater is retained within the systems. Most biofilters use herbaceous species (grasses, sedges and rushes are common) but in highly urbanised locations, such as streets, trees may be more suitable vegetation. While an extensive literature exists that discusses the performance of predominantly herbaceous biofiltration systems (Davis et al., 2006, Blecken et al., 2007, Henderson et al.,

2007, Bratieres et al., 2008, Read et al., 2008) systems using large, woody vegetation are less well documented.

This paper examines existing literature on the performance of woody plants in stormwater management systems and also reports on an experiment that investigated the use of four street tree species (Eucalyptus polyanthemos, Lophostemon confertus, Callistemon salignus and Platanus orientalis) in model infiltration systems. All of these species are used as street trees in south-eastern Australia.

The use of woody plants in stormwater management systems

Urban trees can contribute to stormwater management in a number of ways. Stormwater run-off can be reduced by the evaporation of rainfall intercepted by the canopy and transpiration losses, while stormwater quality can be improved by retention of pollutants in soil and plant uptake (Stovin et al. 2008).

Stormwater quantity

Rainfall interception in canopy

The volume of runoff is reduced by the evaporation of rainfall from leaf surfaces within the tree canopy. Rainfall interception by trees in the parks and streets of a Californian city equated to 1.6% of total precipitation and a saving of $3.80 per tree on expenditure for stormwater management (Xiao and McPherson, 2002). Rainfall interception is maximised with large, evergreen tree species (Xiao and McPherson, 2002).

Increased infiltration of rainfall and soil water storage

Trees can increase the rate or amount of soil water infiltration and subsequently increase soil and groundwater recharge. A proportion of the rainfall temporarily held on the canopy will flow down the stem and trunk (Xiao et al. 2000). In highly impervious areas this trunk flow increases the likelihood that rainfall is directed into soil at the base of the tree rather than onto surrounding impervious surfaces.

Tree pits can be designed to maximise water storage. The use of structural soil under pavement areas such as carparks and footpaths to retain stormwater is an example of this. By providing increased rooting volumes through the use of structural soils, these systems should support larger-sized trees and will further mitigate stormwater by rainfall interception and retention within the soil (Day et al., 2008). Fraxinus pennsylvanica and Quercus bicolor grew successfully in structural soil planting pits that were designed to retain stormwater (Bartens et al., 2009).

The percolation of stormwater through compacted soil layers can also be increased by tree root growth. The saturated hydraulic conductivity (SHC) of a compacted subsoil layer under structural soil was
mm hr-1 (27-fold higher) with Fraxinus pennsylvanica (green ash) than in unplanted systems (Bartens et al., 2008). Acer rubrum (red maple) and Quercus velutina (black oak) increased the saturated hydraulic conductivity of compacted clay soil in less than 12 weeks after planting (Bartens et al., 2008).

Stormwater quality

Pollutant removal

In addition to reducing the quantity of urban run-off, vegetation and its associated soil can play an important role in removing nutrients and heavy metals from stormwater (Davis et al., 2001, Henderson et al., 2007, Read et al., 2008) To date there has been limited research of the performance of individual plant species in biofiltration systems, with two notable exceptions, Read et al. (2008) and Bratieres et al. (2008). These two studies investigated a range of plant species, varying in size from rushes to large shrubs or small trees, indigenous to south-eastern Australia.

This research

The seasonal performance of street tree species in biofiltration systems is largely unknown. A study was designed to assess the combined performance of street trees and tree soils as part on an integrated urban stormwater treatment system. The proposed treatment system could be retrofitted into most urban streets, either at the time of tree replacement, or to amend an existing planting. Stormwater from the road and footpath is directed along the gutter and into the biofiltration system. The soil surface is set at a designed depth below the surrounding surfaces, referred to as the extended detention depth, allowing stormwater to fill this space during rain events. The systems are designed so that if the detention depth is filled, additional stormwater is bypassed into the conventional stormwater management systems to avoid flooding.

Methods

The experiment was designed to evaluate both tree growth responses and also the efficacy of nutrient removal of these biofiltration systems. Trees were grown outdoors in experimental biofiltration systems, constructed with 240 mm diameter columns, cut into 600 mm lengths. The constructed soil profiles were 500 mm deep with 10% (v:v) composted green waste added to the surface 200 mm. The three soils used were sands with saturated hydraulic conductivities (SHC) of 4, 95 and 170 mm h-1 and the soils are referred to as low, medium and high SHC soil respectively. The hydraulic conductivity of the slowest draining soil was below the range 20-1000 mm h-1 stipulated in the Australian Standard AS4419 ‘Soils for landscaping and garden use’ (Standards Australia, 2003).

The four species selected are common in urban landscapes in southern Australia (Frank et al., 2006) and three are Australian species. The tree species chosen come from a range of climates and environments and were chosen in part to investigate innate differences in response to the regular inundation that would be expected in biofiltration systems. The evergreen trees were planted in late March to early April 2003 and the deciduous trees in June 2003. The application of simulated run-off commenced in September of the same year.

The trees were irrigated using tapwater or a model stormwater solution and compared to unplanted, control profiles. The profiles received weekly applications of approximately 100 mm depth of either tapwater or stormwater. The chemical composition of the simulated stormwater was adapted from one devised by Davis et al. (2001) and included 2 mg L-1 NO –N, 4 mg L-1 organic-N and 0.6 mg L-1 phosphate-P as well as a heavy metal (copper) and dissolved solids (sodium chloride and magnesium chloride). As suspended solids were not included in the synthetic stormwater the implications of surface clogging and changes in hydraulic performance over time were not investigated.

The model soil profiles were raised off the ground, allowing collection of leachate following simulated run- off events. An irrigation system was used to deliver the simulated runoff events. All profiles received a volume of tapwater via a microspray within a 500 mL plastic food container, and the addition of stormwater concentrate in this container prior to the system running created the simulated stormwater solution.

Data collected during the experiment included final above-ground plant biomass as well as soluble nitrogen and phosphorus concentration of the leachate over time. For above-ground biomass measurements all trees were harvested at the completion of the experiment, oven dried (70oC for 48 hours) and weighed. Sampling of leachate from the constructed profiles for nutrient analysis was undertaken from December 2003 until December 2004. On 10 occasions during the 13-month period the leachate was collected from the base of the systems for two hours after a simulated runoff event. Filtered (0.45 µm) samples were analysed for NOx and FRP using colorimetric methods and an Alpkem (Perstorp Analytical) segmented flow autoanalyser. In some instances, typically in higher evaporative demand months towards the end of the experiment, all of the applied water was retained within the soil and no leachate drained from the profiles. The concentration was recorded as a missing value.

Analysis of variance (ANOVA) was used to make overall comparison between treatment means and differences were recorded as significant at the five per cent level (p<0.05). Paired comparisons were made using the least significant difference (LSD). For the vegetation growth data n=8 and for the nutrient concentration of leachate from the biofiltration systems data n=3.

Results

Tree growth

All four tree species grew well in all three soils, including one chosen for its low, and potentially growth limiting drainage rate. Above-ground growth of C. salignus, L. confertus and P. orientalis was increased when the irrigation was with the model stormwater solution rather than tapwater (Table 1). E. polyanthemos growth was similar with tapwater water and stormwater applications in the low and high SHC soils.

Table 1: Above-ground dry weight (g): species, soil and water quality interaction
 

Species

 

yzSoil and water quality

 

Low SHC

 

Medium SHC

 

High SHC

 

Tap water

 

Storm water

 

Tap water

Storm water  

Tap water

 

Storm water

 

C. salignus

 

136

 

b

 

265

 

fg

 

168

 

cd

 

266

 

fg

 

133

 

b

 

233

 

fg

 

E. polyanthemos

 

174

 

cd

 

177

 

cd

 

149

 

bcd

 

243

 

fg

 

131

 

b

 

159

 

bcd

 

L. confertus

 

147

 

bcd

 

273

 

g

 

155

 

bcd

 

255

 

fg

 

129

 

b

 

219

 

ef

 

P. orientalis

 

86

 

a

 

182

 

de

 

85

 

a

 

150

 

bcd

 

89

 

a

 

143

 

bc

 

y means followed by the same letter down the column and across the row are not significantly (p<0.05) different

z means are back log  transformed

While successful tree growth has been confirmed, the systems must also treat stormwater to successfully function in terms of biofiltration. This study focused on nutrient removal, a component of stormwater treatment.

Nutrient removal

Compared to unplanted controls, the presence of trees resulted in significant reductions of soluble nitrogen and phosphorus concentration of leachate. The pattern of FRP concentration of leachate over time was similar between the unplanted and planted profiles (Figure 1). The leachate concentration of FRP was  higher during the warmer months and in particular early in the experiment. The unplanted low SHC soil profiles were very effective in reducing the FRP concentration of stormwater. Conversely, FRP seemed to be generated within the unplanted, medium and high SHC soil profiles with higher concentrations of the leachate than the input stormwater during most events (Figure 1).

The effectiveness of planted profiles at reducing the FRP concentration of stormwater was variable. The low SHC soil planted profiles greatly reduced the FRP concentration of stormwater input for all events (Figure   1). The medium and high SHC soil planted profiles had little effect at the start of the experiment, with leachate FRP concentrations similar to the input stormwater. However, following the first summer, good reductions of FRP concentrations were achieved from profiles with these two soils (Figure 1). .

Figure 1: FRP concentration (mg P L-1) of leachate over time from planted and unplanted profiles receiving stormwater. The dashed, horizontal line indicates the stormwater input concentration.

During the first few months of the experiment the leachate FRP concentration was high from systems planted with all four species (Figure 2). During winter (June to August) the FRP concentration of leachate from the profiles with the deciduous species was relatively similar to the leachate from those planted with evergreen species. The spike of FRP in late spring (November 2004, Figure 1) was due to high concentrations in leachate from P. orientalis profiles (Figure 2).

Figure 2 The effect of species on FRP concentration (mg P L-1) of leachate from medium SHC soil profiles receiving stormwater. The horizontal dashed line represents the stormwater input concentration.

The pattern of NOx concentration of leachate over time was generally similar in both the unplanted and planted profiles (Figure 3). The leachate concentration of NOx was typically higher during the warmer months. The spike observed in July is most likely an artefact of soil core sampling undertaken prior to leachate sampling.

The NOx concentration of leachate from the planted profiles was less than from unplanted profiles (Figure 3). NOx was consistently generated in the unplanted profiles with the leachate having higher concentrations than the stormwater input during all events. The effectiveness of planted profiles in reducing the NOx concentration of stormwater was variable. On all occasions, the planted, low SHC soil profiles had lower concentrations of NOx in leachate than the stormwater input. The performance of the planted, medium and high SHC soil profiles was less consistent, with NOx being produced during late spring and summer (Figure  3). During the cooler months the concentration of NOx in stormwater was reduced by biofiltration through the planted, medium and high SHC soil systems.

Figure 3: NOx-N concentration (mg N L-1) of output leachate over time from profiles receiving stormwater over time. The dashed horizontal line represents the stormwater input concentration. * The spike observed in July is most likely due to an artefact of the experimental (soil cores were taken prior for root and soil analysis).

The effect of species on the NOx concentration of leachate during the experiment was not large (Figure 4, high SHC soil profiles shown).

Figure 4: The effect of species on NOx-N concentration (mg N L-1) of output leachate from high SHC soil profiles receiving stormwater. The dashed horizontal line represents the stormwater concentration. *The spike observed in July is most likely due to an experimental artefact (soil cores were taken prior for root and soil analysis).

Discussion

Tree growth

The trees grew well in this experiment and soil selection was not critical for plant growth with regular exposure to small sized run-off events. The low saturated hydraulic conductivity of the low SHC soil used in the experiment would not meet AS 4419-2003 guidelines and these soils may have been expected to have poor aeration. The trees grown in the low SHC soil performed well. However further field evaluation is required to confirm that such soils would be suitable for tree growth. The rate of water infiltration into, and percolation through, the constructed profiles was variable and not necessarily reflective of the different saturated hydraulic conductivity of the three experimental soils (data not shown). The low SHC soil profiles did drain more slowly than the medium and high SHC soil profiles.

As a growing medium for trees, the coarse textured soils used in biofiltration systems inherently have low levels of available nutrients and water. The addition of organic matter to similar sandy soils is common practice in constructing designed tree soils. Greater growth of the trees that received stormwater than tapwater confirms that the systems studied had low levels of nutrition.

NOx concentration of leachate

The NOx concentration of leachate from planted systems was higher in warmer months. A positive correlation between NOx concentration of leachate from biofiltration systems and temperature has been reported (Blecken et al., 2010). Averaged over time, the experimental street tree biofiltration systems reduced the NOx concentration of stormwater by 2 to 78% for the various filtration media. Street trees grown in the two faster draining soils were not effective at reducing N concentration, however load removal was adequate (data not shown). This reduction in NOx concentration is within reported ranges (Davis et al., 2006, Henderson et al., 2007, Read et al., 2008, Bratieres et al., 2008). Permanently saturated zones designed at the base of biofiltration systems can promote denitrification and increase nitrogen removal performance (Kim et al. 2003).

FRP concentration of leachate

The FRP concentration of stormwater was reduced by an average of 70 to 96% following biofiltration through street tree systems with various filtration media. These reductions are similar to those reported in the literature (Bratieres et al., 2008, Read et al., 2008).

Seasonal patterns of nutrient concentration of leachate

Seasonal patterns of nutrient uptake capacity have been reported for some trees, with maximum rates typically coinciding with active growth periods (Roy and Gardner, 1945, Muñoz et al., 1993, Weinbaum et al., 1978). It was therefore anticipated that nutrient removal performance would be low during winter while the trees were dormant or growing slowly. The peaks in nutrient concentration of leachate from planted profiles occurred during summer and often corresponded to periods when higher water volumes were retained in the biofiltration systems (data not shown), suggesting that the soil was dry. This seasonal pattern of NOx and FRP concentration was also observed in the unplanted profiles with considerable leaching of nutrients during summer. This suggests that the soil may be behaving as a larger source of nutrients during these times. That is, the mineralisation of organic matter is higher during the summer in response to higher temperatures (Gessler et al., 1998) or possibly increased soil drying and wetting.

Organic amendment of biofiltration media

Substantial leaching of nitrogen and phosphorus from unplanted soil profiles was found for the duration of this experiment. Despite the potential increase in cation exchange capacity, caution is required if biofiltration media are to be amended with organic matter. In response to high levels of nutrient leaching from organic matter amended soils, Bratieres et al. (2008) recommended that biofiltration soils are not amended. Further field testing is required to ascertain the impact of this recommendation on the long term growth of street trees and stormwater treatment performance.

Species selection for biofiltration systems

Four street tree species with different waterlogging tolerances were evaluated in this study to determine differences in nutrient removal performance. Species selection was not essential to maximise nutrient removal performance of biofiltration systems. The evergreen and deciduous species performed similarly during winter, when the latter had lost leaves. This raises interesting questions about root function and nutrient uptake in dormant trees. P. orientalis was less effective at reducing the phosphorus concentration of leachate during the final months of the experiment, although phosphorus load reduction was adequate (data not shown). This reduced performance is possibly related to stresses caused by more severe drying of soil columns in late spring and summer. Further field evaluation is required to investigate the effect of  water stress on stormwater treatment performance and the likelihood of it occurring in practice. The ability of trees to withstand drought may be an important selection criterion which requires further evaluation.

Biodiversity of vegetation within our cities is important and street tree selection should not be based on a single criterion. Therefore it is a positive finding that under these experimental conditions the differences in nutrient removal performance between the four species were not large and the planting of any one particular species is not recommended. However, it is acknowledged that the lack of differences reported in this study may reflect the regime of simulated run-off events applied in this study, which may not have   been sufficiently large to impose significant deoxygenation stress on the trees.

While the tree species studied behaved similarly it is important to reiterate that for removing nutrients from stormwater, vegetation is a critical component of these systems. Newly planted biofiltration systems will initially behave largely as unvegetated systems, until the root systems have developed sufficiently to colonise large proportions of the filtration medium. Nitrogen and phosphorus leaching, in terms of concentration, was still occurring in the experimental systems nine months after planting and so these systems will take some time to perform effectively. Good post planting practices are important to ensure rapid tree establishment in these systems. As with traditional street tree planting, irrigation is most likely the most critical aspect of post planting maintenance. To avoid water deficit stress, additional irrigation may be required until the tree root systems have established. To optimise tree establishment, the scheduling of irrigation should be proactive rather than reactive (Harris, 1998). The frequency of irrigation post planting is more important than the volume applied (Gilman et al., 1998) due to the small root ball volume and the low water holding capacity of fast draining biofiltration media. To minimise any nutrient leaching from these newly established systems, care must be taken to apply irrigation volumes which can be fully retained within the soil profile.

Conclusion

Trees in urban built areas can contribute in many ways to sustainable stormwater management. The novel use of structural soils to form a stormwater reservoir for urban tree plantings shows promise (Bartens et al., 2009). In the model biofiltration systems used in this research, four common street tree species grew well. Species selection did not appear to be an important element in terms of system success. The one deciduous species behaved similarly to evergreen species, in terms of soluble nitrogen and phosphorus removal,  during their dormant period. After the initial summer, the biofiltration systems were successful in reducing FRP concentration. The performance of the systems in reducing NOx concentration was more variable and during the warmer months NOx was generated in the medium and high SHC soil profiles. This work shows that street trees have the potential to be effective elements in urban biofiltration systems and that field- level evaluation of these systems is required to further elucidate the role of such systems in urban stormwater treatment. Design modifications may be required howeve,r if consistent reductions in NOx concentration are required.

References

  • BARTENS, J., DAY, S. D., HARRIS, J. R., DOVE, J. S. & WYNN, T. M. (2008) Can urban tree roots improve infiltration through compacted subsoils for stormwater management? Journal of Environmental Quality, 372048-2057.
  • BARTENS, J., DAY, S. D., HARRIS, J. R., WYNN, T. M. & DOVE, J. E. (2009) Transpiration and root development of urban trees in structural soil stormwater reservoirs. Environmental management, 44, 646-657.
  • BLECKEN, G.-T., ZINGER, Y., DELETIC, A., FLETCHER, T. D., HEDSTRÖM, A. & VIKLANDER, M. (2010) Laboratory study on stormwater biofiltration: Nutrient and sediment removal in cold temperatures. Journal of Hydrology, 394, 507-514.
  • BLECKEN, G.-T., ZINGER, Y., MUTHANNA, T. M., DELETIC, A., FLETCHER, T. D. & VIKLANDER, M. (2007) The influence of temperature on nutrient treatment efficiency in stormwater biofilter systems. Water Science and Technology, 56, 83-91.
  • BRATIERES, K., FLETCHER, T. D., DELETIC, A. & ZINGER, Y. (2008) Nutrient and sediment removal by stormwater biofilters: a large-scale design optimisation study. Water Research, 42, 3930-3940.
  • DAVIS, A. P., SHOKOUHIAN, M., SHARMA, H. & MINAMI, C. (2001) Laboratory study of biological retention for urban stormwater management. Water Environment Research, 73, 5-14.
  • DAVIS, A. P., SHOKOUHIAN, M., SHARMA, H. & MINAMI, C. (2006) Water quality improvement through bioretention media: nitrogen and phosphorus removal. Water Environment Research, 78, 284-293.
  • DAY, S. D., DOVE, J. E., BARTENS, J. & HARRIS, J. R. (2008) Stormwater management that combines paved surfaces and urban trees. Geotechnical special publication, 1129-1136.
  • FRANK, S., WATERS, G., BEER, R. & MAY, P. (2006) An analysis of the street tree population of Greater Melbourne at the beginning of the 21st century. Arboriculture & Urban Forestry, 32, 155-163.
  • GESSLER, A., SCHNEIDER, S., VON SENGBUSCH, D., WEBER, P., HANEMANN, U., HUBER, C., ROTHE, A., KREUTZER, K. & RENNENBERG, H. (1998) Field and laboratory experiments on net uptake of nitrate and ammonium by the roots of spruce (Picea abies) and beech (Fagus sylvatica) trees. New Phytologist, 138, 275-285.
  • GILMAN, E. F., BLACK, R. J. & DEHGAN, B. (1998) Irrigation volume and frequency and tree size affect establishment rate. Journal of Arboriculture 24, 1-9.
  • HARRIS, R. (1998) Irrigation of newly planted street trees. IN NEELY, D. & WATSON, G. (Eds.) The Landscape Below Ground II. San Francisco, California, International Society of Arboriculture.
  • HATT, B. E., FLETCHER, T. D., WALSH, C. J. & TAYLOR, S. L. (2004) The influence of urban density and drainage infrastructure on the concentrations and loads of pollutants in small streams. Environmental Management, 34, 112-124.
  • HENDERSON, C., GREENWAY, M. & PHILLIPS, I. (2007) Removal of dissolved nitrogen, phosphorus and carbon from stormwater by biofiltration mesocosms. Water Science and Technology, 55, 183-191.
  • KIM, H., SEAGREN, E. A. & DAVIS, A. P. (2003) Engineered bioretention for removal of nitrate from stormwater runoff. Water Science and Technology, 75, 355-367.
  • MUÑOZ, N., GUERRI, J., LEGAZ, F. & PRIMO-MILLO, E. (1993) Seasonal uptake of 15N-nitrate and distribution of absorbed nitrogen in peach trees. Plant and Soil, 150, 263-269.
  • READ, J., WEVILL, T., FLETCHER, T. & DELETIC, A. (2008) Variation among plant species in pollutant removal from stormwater in biofiltration systems. Water Research, 42, 893-902.
  • ROY, W. R. & GARDNER, F. E. (1945) Seasonal absorption of nutrient ions by orange trees in sand culture. Proceedings of the Florida State Horticultural Society, 58, 25-36.
  • STANDARDS AUSTRALIA (2003) Australian Standard: Soils for landscaping and garden use AS 4419-2003. Homebush, NSW.
  • STOVIN, V. R., JORGENSEN, A. & CLAYDEN, A. (2008) Street trees and stormwater management. Arboricultural Journal, 30, 297-310.
  • TAYLOR, S. L., ROBERTS, S. C., WALSH, C. J. & HATT, B. E. (2004) Catchment urbanisation and increased benthic algal biomass in streams: linking mechanisms to management. Freshwater Biology, 49, 835-851.
  • WALSH, C. J. (2004) Protection of in-stream biota from urban impacts: minimise catchment imperviousness or improve drainage design? Marine and Freshwater Research, 55, 317-326.
  • WEINBAUM, S. A., MERWIN, M. L. & MURAOKA, T. T. (1978) Seasonal variation in nitrate uptake efficiency and distribution of absorbed nitrogen in non-bearing prune trees. Journal of the American Society for Horticultural Science, 103, 516-519.
  • XIAO, Q., McPHERSON, E. G., USTIN, S. L., GRISMER, M. E. & SIMPSON, J. R. (2000) Winter rainfall interception by two mature open-grown trees in Davis, California. Hydrological Processes, 14, 763-784.
  • XIAO, Q. & MCPHERSON, E. G. (2002) Rainfall interception by Santa Monica's municipal urban forest. Urban Ecosystems, 6, 291-302.