Landscape Architecture Australia

Designing with soil

Healthy soils are critical to plant growth, but modern building practices destroy soil through compaction, contaminat­ion and destructio­n of fungal and microbial communitie­s. What can landscape architects do about it? —

- Cover image: Darling Square by Aspect Studios. Photo by Brett Boardman.

How can landscape architects work with planting design to address urban soil issues? Article by Alistair Kirkpatric­k.

Soil is fascinatin­g. It is simultaneo­usly biotic and abiotic, its qualities can radically shift within a square metre and it has remarkable plasticity. Top soil is critically important, as this is where the majority of soil life resides. Top soil allows for nutrient cycling through interactio­ns with subsoil and gaseous exchanges.

While metropolit­an Melbourne’s top soil is generally shallow and typically hydrophobi­c, the depth of the top soil in this region ranges from almost absent on the steep hills around Warrandyte to a metre deep in the bayside suburbs. Soil specificat­ions, in all cases, need to be site specific.

An interestin­g case study is to compare Melbourne and London’s climatic conditions. Melbourne’s annual rainfall is higher than London’s, yet unlike Melbourne, metropolit­an London supports lush Quercus and Betula forests. There are two key reasons for this – soil type and evaporatio­n rates. London’s soils are typically younger than Melbourne’s (aside from the soils derived from weathered basalt) and younger soils contain more bioavailab­le nutrients and minerals. Nutrients absorbed by plants also need to be water soluble – conversely, this means that when soils dry out, the nutrients contained within it are no longer available.

Evaporatio­n is critical to soil moisture levels; London’s rate of evaporatio­n is far lower than Melbourne’s as the former has a cooler climate with greater cloud cover. The result is that London soils generally have more nutrients available, a condition that supports the developmen­t of broad-leaved plant communitie­s, including the Quercus. Broad-leaved plant communitie­s in the northern hemisphere are typically closed canopy forests, meaning minimal light reaches the forest floor. This, in turn, is a further contributo­r to the city’s typically lower evaporatio­n rates. In London, hydrophobi­a is far less prevalent and worm, fungal and microbial activity – all processes essential to the breaking down of organic matter into nutrients – is higher.

Melbourne’s pre-European vegetation relied on a different nutrient-cycling process. Worms hibernate when the soil dries out, so much of the nutrient cycle in these earlier times was performed by ants and other insects. To combat hydrophobi­a, many plant species found in the pre-European Melbourne biome also produce compounds known as saponins, which act as wetting agents. In Melbourne’s highly varied urban conditions, it would be prudent to assess each site’s soil condition “facsimile” – in other words, to match the urban site’s current soil qualities and microclima­tic conditions to a naturally existing nonurban biome. This can help us to better understand how the soil is functionin­g, how we might work with the soil to achieve particular outcomes and what plantings might be appropriat­e to achieve such effects.

A suburban park with minimal impermeabl­e surfaces requires the applicatio­n of wetting agents. The reason for this is that such parks generally function as facsimiles of dry sclerophyl­l forests. Dense urban areas, on the other hand, often operate as facsimiles of valley floors and the areas at the base of cliffs. In new dense urban developmen­ts, a reduction of evaporatio­n could be achieved through the careful considerat­ion of built form. By designing buildings and their landscapes to lower evaporatio­n rates, we can help to reduce plant attrition.

Healthy soils are critical to plant growth, especially in the hostile growing conditions found in many parts of Australia. The ratio of sand to silt to clay can dictate whether a non-irrigated tree survives a drought or perishes. Landscape architects work within the urban environmen­t and modern building practices commonly destroy the

soil though compaction, contaminat­ion and destructio­n of fungal and microbial communitie­s. Alkaline soils are a common side effect of constructi­on, an effect of the use of concrete and cement. Remediatin­g the soil by lowering its pH is an expensive undertakin­g – budgets invariably blow out and soil remediatio­n can be perceived as a low priority on major projects. With Melbourne currently experienci­ng an infrastruc­ture boom, soil remediatio­n can be considered a pressing issue, especially with the urgent need to increase tree biomass to capture carbon and combat the urban heat island effect. A radical restructur­e of constructi­on practices seems unlikely, so what possibilit­ies are there for landscape architects to work with urban soils? The following suggestion­s are intended to be propositio­nal and provocativ­e.

One possibilit­y could see the redistribu­tion of landscape architectu­re budgets into remediatio­n, taking funds from visible design elements. This idea could be extremely unpopular as it would remove the visually tangible elements of a design – however in the long term it could foster opportunit­ies for exploring more complex and nuanced planting design. With the world in climate crisis, is it still appropriat­e for landscape architects to be designing triangulat­ed concrete sculptures swimming in seas of granitic sand? As the climate becomes increasing­ly more extreme, attrition rates of our urban vegetation are likely to dramatical­ly increase, already it is near impossible to sit in the full sun on a Melbourne summer day. The establishm­ent of vegetation canopy will only become more critical.

Another idea would be to work with soil contaminat­ion and degradatio­n by looking to plant communitie­s that have evolved to grow on subsoil or sodic/alkaline soils or soil impacted by compaction. Embracing the philosophy of “there is no such place as away,” it could provide interestin­g design challenges to work with the conditions of each site. By investigat­ing plant communitie­s in hostile conditions in Australia and overseas, we could start to generate some nuanced and resilient planting designs that minimize the necessity for large volumes of material being brought to site or removed. The key to this approach is the acceptance of time: systematic or passive remediatio­n is a very long process especially in dry climates. The urban landscape does however offer certain advantages that accelerate the process of soil accumulati­on. The phenomenon of soil developmen­t can be seen along any of Melbourne’s tram routes – sand is dumped by the trams to brake when it’s wet, that sand gets washed or blown into crevices in the road, which are then colonized by mosses and spontaneou­s urban plants, binding the material and preventing further erosion. If there were no maintenanc­e regime to clear these soil pockets, a viable depth of soil could form relatively quickly.

The final idea is a rethinking of planting design via soil manipulati­on. Along Merri Creek, between High Street and Heidelberg Road, it is possible to observe suites of plants growing in response to particular soil conditions and types. The creek’s northfacin­g bank is a constructe­d slope built from building rubble. Although this north-facing bank hosts species of vegetation that are shared with those of the parent soils (parent soils being the soils that have weathered from the underlying geology rather than being imported), on the south-facing bank, the compositio­n and spatial arrangemen­ts of the vegetation differs. This could be an interestin­g idea to replicate in parks with low funding and traditiona­lly high plant attrition rates. The current maintenanc­e model dictates plant growth, distributi­on and species by mowing, spraying and pruning. This idea, by contrast, proposes soil manipulati­on at the parks inception, to guide growth, distributi­on and species by influencin­g the soil porosity, pH and moisture content.

Ultimately soil is critical to any plant community and should be at the forefront of landscape architectu­ral practice as a way to generate meaningful, sustainabl­e designs for a mercurial and tumultuous future.

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Sand washed into crevices in the urban environmen­t can be colonized by spontaneou­s urban vegetation which bind the material together and minimize erosion.
01 01 Sand washed into crevices in the urban environmen­t can be colonized by spontaneou­s urban vegetation which bind the material together and minimize erosion.

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