Stephen J. Livesley’s research while affiliated with University of Melbourne and other places

What is this page?


This page lists works of an author who doesn't have a ResearchGate profile or hasn't added the works to their profile yet. It is automatically generated from public (personal) data to further our legitimate goal of comprehensive and accurate scientific recordkeeping. If you are this author and want this page removed, please let us know.

Publications (179)


Multi-perspective evaluation framework of three-dimensional cooling and energy saving potential of urban parks based on numerical simulation
  • Article

December 2024

·

14 Reads

Sustainable Cities and Society

·

·

·

[...]

·

Stephen J. Livesley

Correction to: Rapid root development in clay subsoils enhances the early growth of native grassland species
  • Article
  • Publisher preview available

November 2024

·

6 Reads

Plant and Soil

View access options

Root, shoot and total plant dry biomass (mg) of six grassland species grown in sand and clay subsoil harvested 12 weeks after the average date of seedling emergence for each species. Error bars indicate one standard deviation from the mean. Lower case letters indicate significant differences (p < 0.05) between capping substrates (Treatment) and within each species for each biomass category
Effect of substrate on root dry biomass (mg) according to species, treatment and rhizobox section. Rhizobox section corresponds to the following depths of growing media: Cap is the uppermost 80 mm (sand or subsoil cap). Upper is the top half (80–285 mm) and lower the bottom half of base substrates (285–490 mm). Error bars indicate one standard deviation from the mean. Lower case letters indicate significant differences (p < 0.05) between surface treatments, within each species and rhizobox section
Root length (m) according to species, treatment (sand or subsoil) and rhizobox section. Box section corresponds to the following depths of growing media: Cap is the uppermost 80 mm (sand or subsoil cap). Upper is the top half (80-285 mm) and lower the bottom half (285-490 mm) of base substrates. Error bars indicate one standard deviation from the mean. Lower case letters denote significant differences (p < 0.05) between treatments, within each species and box section
Root images converted to a binary format where black pixels indicate roots. Paired replicates for each species show plants sown in sand to the left and plants sown in clay subsoil to the right. All images are derived from the final photographs taken in the week of destructive harvest (twelve weeks after mean germination of each species, calculated across both substrates)
Visible root length over time for six species sown in sand (green) or clay subsoil (blue) capping substrates. Solid lines show the fitted linear regression model, with dashed lines indicating the standard error of the mean. Days elapsed since the day of sowing are indicated on the x axis. Stars indicate significant differences in the rate (mm/day) of visible root growth between treatments; p < 0.05 (*), p < 0.01 (**), p < 0.001 (***)

+1

Rapid root development in clay subsoils enhances the early growth of native grassland species

Plant and Soil

Background and aims Wildflower meadows are a low-maintenance landscape treatment that can improve urban biodiversity and achieve conservation outcomes, especially when designed to use plants from threatened grassy ecosystems. Cost-effective approaches to create meadows include direct seeding onto mined sand substrates that are placed onto site soils to supress weed competition and enhance sown plant establishment. However, waste subsoils diverted from landfill could provide a more sustainable alternative. This study compares a mined sand with a clay subsoil to understand the relative differences in sown plant establishment and root growth for a range of south-east Australian grassland species. Methods Germination, seedling emergence and root development were assessed for six species sown in an 80 mm deep cap of two low nutrient substrates (sand and clay subsoil) overlying a simulated site soil. Rhizoboxes were used to assess the rate at which plant roots could access soils beneath capping substrates. Results Sand and clay subsoil supported the establishment of the six sown species. Five species had significantly greater total root length, leaf area and aboveground biomass when sown in recycled subsoil, compared with sand. Conclusion Edaphic conditions affect the establishment of native grassland species in wildflower meadows. Compared to sand, recycled clay subsoils provide a more sustainable alternative for establishing designed wildflower meadows and can support rapid root and plant growth in south-east Australian grassland species.


Links between natural climate solutions (NCSs) in 12 ecosystems and Sustainable Development Goals (SDGs). Measures that promote the protection, restoration, or sustainable management of ecosystems (NCSs) represent opportunities to meet both climate objectives and sustainable development objectives through nature's contributions to people. The list of nature's contributions to people is not exhaustive. Pentagons marked with a “C” represent carbon stocks.
Schematic representation of indices. From top to bottom: (a) a bipartite network, (b) the modularity index (where M stands for module), (c) the nestedness index, and (d) the insurance index.
Relationships between ecosystem NCSs and SDGs. Bipartite network of the (a) negative links (trade‐offs) and (c) positive links (co‐benefits) between ecosystem NCS implementation and SDG target achievement. Edge (line) thickness is proportional to the number of targets. (b) Percentage of targets within each SDG that are positively (+) and negatively (–) linked to ecosystem NCS implementation, and the contribution of each ecosystem type. For (a) and (c): peatland (PTL), urban forest (UFO), forest (FOR), grassland (GRL), tidal marsh (TDM), mangrove (MGV), seagrass (SGR), macroalgae (MCA), seabed (SBD), pelagic (PEL), Antarctic (ANT), and mesopelagic (MES). Values along the vertical axis correspond to the SDG number (SDGs 1–16).
“Insurance” of SDG targets for positive links. The bars represent the number of ecosystems (y axis from 0 to 12) that contribute to achieving each target after ecosystem NCS implementation. Bar colors represent the type of ecosystem that promotes SDG target achievement. Red circles represent the number of times a given target is (as expected by chance) positively linked to an ecosystem (n = 6). Targets impacted less than randomly expected are vulnerable. Colored values at the end of each bar (along the outer circumference) indicate the target numbers of the 16 individual SDGs (depicted by the inner values within the circular plot).
“Insurance” of SDG targets for negative links. The bars represent the number of ecosystems (y axis from 0 to 12) that impede achievement of each target after ecosystem NCS implementation. Bar colors represent the type of ecosystem that inhibits SDG target achievement. Red circles represent the number of times a given target is (as expected by chance) negatively linked to an ecosystem (n = 6). Targets negatively impacted less than randomly expected are vulnerable. Targets impacted less than randomly expected are vulnerable. Colored values at the end of each bar (along the outer circumference) indicate the target numbers of the 16 individual SDGs (depicted by the inner values within the circular plot). SDG 13 (Climate action) is not represented as NCSs are supposed to only promote climate‐change mitigation.
Co‐benefits of and trade‐offs between natural climate solutions and Sustainable Development Goals

October 2024

·

535 Reads

·

1 Citation

Combating climate change and achieving the UN Sustainable Development Goals (SDGs) are two important challenges facing humanity. Natural climate solutions (NCSs) can contribute to the achievement of these two commitments but can also generate conflicting trade‐offs. Here, we reviewed the literature and drew on expert knowledge to assess the co‐benefits of and trade‐offs between 150 SDG targets and NCSs within 12 selected ecosystems. We demonstrate that terrestrial, coastal, and marine NCSs enable the attainment of different sets of SDG targets, with low redundancy. Implementing NCSs in various ecosystems would therefore maximize achievement of SDG targets but would also induce trade‐offs, particularly if best practices are not followed. Reliance on NCSs at large scales will require that these trade‐offs be taken into consideration to ensure the simultaneous realization of positive climate outcomes and multiple SDG targets for diverse stakeholders.



Interacting effects of sand, slugs and jute drive community composition in direct‐seeded urban wildflower meadows

September 2024

·

100 Reads

·

1 Citation

Wildflower meadows support biodiversity in urban environments, whilst providing low‐maintenance, amenity landscapes. By moving from international plant palettes to those that include species from threatened plant communities in meadows, we can reintroduce native species to urban landscapes and help achieve conservation objectives. Adapting horticultural techniques from Europe, we determined if such approaches could support the germination and establishment of grasses and wildflowers from critically endangered plant communities in Melbourne, Australia. Working in an urban park, we sowed seed of 27 species on soil capped with two depths of sand (10 and 80 mm) and site soil without sand to determine the impact of sand on weed emergence, slug grazing and growth of sown species. We quantified weed biomass and the time spent weeding unsown species from the emerging meadow. We also tested if covering the sites with a jute mesh enhanced sown species establishment. Twelve months after sowing, the percentage cover of sown species did not differ significantly among treatments. However, the cover of forb species was greater on plots without jute, whereas the cover of grasses was greater on plots with jute. Forb density and species richness were highest on 80 mm sand treatments without jute and lowest on 80 mm sand with jute. We attribute this to greater competition from grasses and higher slug abundance in the presence of jute, leading to the loss of forb species that are more palatable to slugs. Greater sand depths significantly reduced the time to weed and the biomass of weed species removed from the emerging meadow. Synthesis and applications. Using low‐nutrient substrates to cap and bury the weed seed bank, irrigation and direct seeding, we demonstrate it is possible to return plants from threatened grassy ecosystems to urban sites, creating a dense and species‐rich native understorey within 1 year whilst reducing labour requirements during meadow establishment.



Fig. 1. (a) Ground view and (b) bird-eye view of a plot. The experiment consisted of twelve identical plots (four treatments × three replicates). The four treatments were: unirrigated (U0), irrigated at 01:00 (N1), irrigated at 13:00 (D1), irrigated at 12:00, 13:48, 14:00 and 15:00 (D4). The daily total irrigation amount of the three irrigated plots was the same except that they were irrigated at different times of the day. Each plot was 6 m × 6 m and was enclosed by 1.8-m tall 70 % shade cloth (SOLARSHADE™). A climate station was installed at the centre of each plot, measuring soil temperature (-0.05 m), soil moisture content (-0.05 m), air temperature (1.1 m), vapour pressure (1.1 m), turf surface temperature (1.5 m), and incoming and outgoing shortwave and longwave radiation (1.5 m). A reference climate station was installed at the centre of the experimental site, measuring air temperature (1.1 m), vapour pressure (1.1 m), rainfall (2.0 m) and wind speed (2.0 m).
Fig. 2. Daily total rainfall, daily maximum, mean and minimum air temperatures, daily mean vapour pressure deficit, daily mean wind speed and daily mean incoming shortwave radiation of the study period from 2022 to 01-18 (Week 0) to 2022-03-06.
Fig. 6. Scatter plots of the afternoon (12:00-15:59) mean cooling effect of irrigation (Δ = irrigated -unirrigated) in air temperature against background (a) air temperature, (b) vapour pressure deficit, (c) wind speed and (d) incoming shortwave radiation. Linear regression models were used for background air temperature, vapour pressure and incoming shortwave radiation, and Gaussian regression models for wind speed. Only the models with a significant slope/parameter estimate were plotted.
Specifications of the microclimate and soil instruments used in this study and their installation height/depth.
Impacts of irrigation scheduling on urban green space cooling

April 2024

·

104 Reads

·

2 Citations

Landscape and Urban Planning

The increasing heat stress in cities due to climate change and urbanisation can prevent people from using urban green spaces. Irrigating vegetation is a promising strategy to cool urban green spaces in summer. Irrigation scheduling, such as daytime vs night-time irrigation and the frequency of irrigation in a day, may influence the cooling benefit of irrigation. This study aimed to investigate whether irrigation scheduling can be optimised to increase the cooling benefit and determine how the cooling benefit changes with weather conditions. A field experiment with twelve identical turfgrass plots (three replicates × four irrigation treatments) was set up to measure the afternoon cooling benefits of irrigation. The four treatments included: no irrigation, single night- time irrigation (4 mm d–1), single daytime irrigation (4 mm d–1) and multiple daytime irrigation (4 x 1 mm d–1). The cooling benefit was defined as the air temperature difference measured at 1.1 m above the turfgrass between the irrigated and unirrigated treatments (air temperature sensor accuracy ± 0.2 ◦C). The afternoon (12:00–15:59) mean cooling benefit of multiple daytime irrigation (–0.9 ◦C) which was significantly stronger than that of single night-time irrigation (–0.6 ◦C) and single daytime irrigation (–0.5 ◦C). Regardless of irrigation scheduling, the afternoon mean cooling benefits of irrigation were greater for days when background air temperature, vapour pressure deficit and incoming shortwave radiation were greater. The findings suggested that irrigation scheduling can be optimised to increase the cooling benefit of urban green space irrigation without increasing overall water use.


More than a canopy cover metric: Influence of canopy quality, water-use strategies and site climate on urban forest cooling potential

April 2024

·

361 Reads

·

11 Citations

Landscape and Urban Planning

Urban tree canopy cover is a promising solution for mitigating heat island. • Data-driven guidance on tree selection and planting locations is still limited. • Four research priorities are proposed, requiring a collaborative research effort. • Cross-climate morphological and physiological characteristics are desired. • Integration with atmospheric boundary layer models is suggested.


Fig. 2. Daily minimum, mean and maximum air temperatures and rainfall of the model evaluation period (2022-01-28 to 2022-03-06, 38 days).
Fig. 4. Comparison of modelled (first soil layer, 0-0.10 m below ground) and measured (0.05 m below ground) daily mean soil moisture content in the model evaluation period (2022-01-28 to 2022-03-06, 38 days). The turf was irrigated 2 mm d 1 from 202201-28 to 2022-02-07 and 4 mm d 1 from 202202-08 to 2022-03-06 at 13:00 local time. In the experiment, the 2-mm irrigation occurred from 13:00 to 13:11, and the 4-mm occurred from 13:00 to 13:23. In the simulation, both 2 and 4 mm were applied to the 13:00-13:59 time step.
Fig. 5. Model evaluation that compared the modelled differences between the irrigated and unirrigated scenarios (Δ = irrigated -unirrigated) and the measured differences between the irrigated and unirrigated plots in (a-d) air temperature, (e-h) vapour pressure (i-l) turf surface temperature, (m-p) soil temperature. The modelled and measured data were compared in terms of their average diurnal cycles (left column), daytime and nighttime daily means (middle column) and scatter plot of hourly means (right column). In the middle column, the broken lines were a time series split into daytime (10:00-16:59, white panels) and night-time (21:00-05:59, grey panels). The model evaluation period was from 202201-28 to 2022-03-06.
Fig. 9. Modelled impacts of different daily irrigation amount (2, 4, 6, 8, 15 and 30 mm) on (a) air temperature, (b) vapour pressure, (c) turf surface temperature, and (d) soil temperature. The impacts were calculated as the difference between the irrigated and unirrigated scenarios (Δ = irrigated -unirrigated). The circles represented the mean impacts in the simulation period. An open circle represented a significant impact (p < 0.05, t-test) while a closed circle an insignificant impact (p ≥ 0.05, t-test). The error bars represent the 95% confident intervals. The overlapping of two error bars is indicative of an insignificant difference (p ≥ 0.05) between the two means. The forcing data of the model evaluation period (2022-01-28 to 2022-03-06, 38 days) was used in this simulation.
Identifying the mechanisms by which irrigation can cool urban green spaces in summer

April 2024

·

62 Reads

·

1 Citation

Urban Climate

High temperatures in summer can prevent people from using urban green spaces. Irrigating urban green spaces is a promising strategy to reduce temperatures. In this study, we aimed to a) identify the proportional contribution of different irrigation cooling mechanisms and b) quantify the impacts of different irrigation amounts (from 2 to 30 mm d − 1) on the cooling effect of irrigating turfgrass in Melbourne, Australia. We first used a field experiment in Melbourne to provide empirical data to calibrate and verify the performance of an urban ecohydrological model, UT&C. Then, we used UT&C to predict the impacts of irrigating turfgrass on evapotranspiration, the energy balance and microclimate. UT&C predicted that irrigating turfgrass 4 mm d − 1 would increase the evaporation from grass canopy and soil surface by 0.2 and 0.6 mm d − 1 , respectively, whereas it would reduce transpiration by 0.6 mm d − 1 due to intercepted water covering part of the grass canopy following the irrigation. UT&C predicted that daytime (10:00-16:59) mean air temperature reductions would increase from 0.2 to 0.4 • C when the irrigation amount increased from 2 to 4 mm d − 1. However, increasing the irrigation amount beyond 4 mm d − 1 would not increase the cooling benefits.


Citations (67)


... Our analysis reveals reduction in the substrate heat storage as another mechanism that underlies the climate benefit of a green space. The wet-bulb equation can also be used for evaluation, using published data, of the net climate effect of other climate interventions, such as street trees 7,12 and urban irrigation 13 , on humid heat. ...

Reference:

Regulation of humid heat by urban green space across a climate wetness gradient
Impacts of irrigation scheduling on urban green space cooling

Landscape and Urban Planning

... Additionally, studies indicate that factors such as growth environment, water availability, pests, climate change, and human interference significantly affect canopy development and transpiration, thus influencing thermal comfort [86][87][88][89]. Plant physiological traits, such as stomatal conductance, photosynthesis, and water-use efficiency, play a key role in regulating transpiration rates and canopy cooling performance [59,90,91]. ...

More than a canopy cover metric: Influence of canopy quality, water-use strategies and site climate on urban forest cooling potential

Landscape and Urban Planning

... Forests, which cover roughly 30% of the Earth's land surface, serve as the largest carbon sink in terrestrial ecosystems, thereby playing a crucial role in human activities [1][2][3][4]. As vital components of terrestrial ecosystems, forests hold substantial implications for global carbon cycling, water cycling, biodiversity conservation, oxygen release, and climate regulation [5]. ...

Spatially analysed expansion of individual street tree crowns enables species-specific crown expansion predictions in different rainfall zones
  • Citing Article
  • February 2024

Urban Forestry & Urban Greening

... This conclusion rested on the assumptions that fire adaptation in deep time can be inferred, without fossils, from mapping one trait onto molecular phylogenies and that fire has always been the singular stimulus for the trait. Nevertheless, epicormic resprouting also expedites regenerative responses in eucalypts and other plants to nonfire disturbances (Burrows, 2013;Kenefick et al., 2024), all of which are applicable to early eucalypts, including mechanical injuries (landslides, wind, and herbivores), droughts, and lava flows. ...

A systematic review of resprouting in woody plants and potential implications for the management of urban plantings

... The need for infrastructural development was another significant factor leading to tree removal. As urban areas expand and new buildings, roads, and other infrastructure are constructed, trees are often removed to make way for these developments [15]. While this is sometimes unavoidable, it underscores the need for urban planning that integrates tree conservation and considers the ecological benefits of preserving mature trees. ...

Tree removals as socioecological experiments in cities

... Experts related that fruit trees, for example, are often divisive-with some residents demanding more fruit trees and others demanding their removal. Literature on this subject has found that though the typical narrative aligns with most people liking trees with aesthetic or food production traits more, this can vary, as relationships people form with trees can be deeply personal and reflect a range of values, including those informed by cultural identity and personal past experiences, and influence perceptions of services and disservices (Barona et al., 2023;Fernandes et al., 2019). Nonetheless, the selection of many diverse actions (such as many different species characteristics and pruning strategies) by participants indicate a potential diversity of pathways to foster stronger relationships between residents and street trees. ...

The role of diverse cultural identities in the perceived value of urban forests in Melbourne, Australia, and implications for urban ecosystem research and practice
  • Citing Article
  • January 2023

Ecology and Society

... A green façade is a coating system that uses vegetation on the façade of the building [41]. This architectural strategy can be implemented in different ways such as adhering the vegetation to a substrate, modular panels (direct green facades) or even suspending in auxiliary structures (indirect green facades) [42]. ...

Leaf trait plasticity means green facades are a flexible nature-based solution for vertical greening under full-sun and heavy shade conditions
  • Citing Article
  • July 2023

Nature-Based Solutions

... In light of this growing importance of trees, Ordóñez et al. (2023) highlights the vital role that urban trees play in shaping the human experience of urban nature in cities. The study found that people's perceptions of urban parks and its trees significantly diminished following the removal of these trees, with participants expressing decreased satisfaction and concerns about the loss of the natural beauty and shade. ...

Quantifying the importance of urban trees to people and nature through tree removal experiments

... Furthermore, it is known that trees have different strategies for water consumption. A tree with a higher transpiration rate may be more susceptible to drought stress than a species with more moderate transpiration performance [114]. Szota et al. [113] categorized 20 Australian tree species into three different groups: "risky", "balanced", and "conservative". ...

Water use strategy determines the effectiveness of internal water storage for trees growing in biofilters subject to repeated droughts
  • Citing Article
  • June 2023

The Science of The Total Environment

... The challenge is to find alternatives to peat whose physico-chemical properties remain relatively stable, both throughout the growing season and from year to year under the cultural practices applied under forest nursery conditions. Du et al. [19] tested the effects of compost tea applications on tree growth and root mycorrhizal colonization for five common urban tree species (Acer negundo, Corymbia maculata, Ficus platypoda, Hymenosporum flavum, Jacaranda mimosifolia) over six months. In another study, Asmara et al. [20] examined a mixture of woody and herbaceous plant species with the introduction of microsymbionts through inoculation, and the application of biochar amendments for accelerating the post-mining restoration. ...

The Use of Compost Tea in a Containerized Urban Tree Nursery Shows No Evident Benefits to Tree Growth or Mycorrhizal Colonization

Forests