Planted in Practice

In the discourse of contaminated landscapes, phytoremediation expands how remediation can be understood, designed, and implemented across multiple scales. Rather than relying solely on mechanical or chemical interventions, phytoremediation reframes pollution as a condition that can be mediated through living systems. By using plants to absorb, stabilize, or transform contaminants, remediation becomes a spatial and ecological process rather than a purely technical one. This shift is particularly relevant for designers and planners working within urban and regional landscapes where contamination intersects with habitation and the public realm.

Phytoremediation operates through a range of biological mechanisms that mobilize contaminants within plant and soil systems. These processes include the uptake and storage of pollutants in plant tissues, the stabilization of contaminants within root zones, and the breakdown of toxic compounds through microbial activity associated with plant roots. Rather than treating pollution as something to be excavated and removed, phytoremediation emphasizes containment, transformation, and long-term mitigation. As a result, remediation becomes embedded within landscape systems that continue to function ecologically and socially.

Figure 2.1 Adopted from Kennen and Kirkwood, 2015

From a landscape architecture perspective, phytoremediation is notable for its adaptability and economic viability. Compared to conventional remediation methods, it is significantly less costly and can be deployed incrementally over time. Its effectiveness, however, depends heavily on site-specific design decisions, including plant selection, soil conditions, contaminant type, and climate. Fast-growing, locally adapted species, particularly grasses and aquatic plants, tend to outperform slower woody vegetation reinforcing the important of regional ecological knowledge in remediation design. Despite its advantages, phytoremediation is not without limitations. The process is generally slower than conventional cleanup methods and is not effective for all contaminants, particularly those that cannot be readily transported through plant vascular systems. Additionally, most existing studies focus on short-term outcomes, leaving questions about long-term performance, maintenance, and ecological resilience. These uncertainties highlight the need for standardized protocols, long-term monitoring, and interdisciplinary frameworks that integrate science, design, and policy.

Figure 2.2 Adopted from Kennen and Kirkwood, 2015

If phytoremediation is understood not as a universal solution but as a landscape strategy, its value becomes clearer. It operates best when contamination is addressed as a spatial condition rather than isolated technical problem. By integrating remediation into living systems, phytoremediation expands the role of landscape architecture in managing polluted sites, particularly in regions such as British Columbia where industrial, agricultural, and ecological landscapes are deeply intertwined. Under this lens, remediation becomes an ongoing process of car, adaptation, and design rather than a finite act of cleanup.

 

Case Study

Petroleum-contaminated sites represent one of the most prevalent and persistent forms of brownfields within urban and industrial landscapes. Hydrocarbons from fuel storage, transportation corridors, refineries, and former industrial uses often migrate through soil and groundwater, creating long-term ecological and public health risks. Conventional remediation methods typically rely on excavation or chemical treatment, approaches that are disruptive, costly, and spatially extractive. Phytoremediation reframes petroleum contamination as a condition that can be managed in situ, allowing remediation to occur without removing soil or displacing surrounding landscape systems.

Figure 2.3 Adopted from Kennen and Kirkwood, 2015

In petroleum-impacted soils, phytoremediation functions primarily through rhizodegradation and phytodegradation processes. Rather than absorbing hydrocarbons directly into plant tissues, plants stimulate microbial communicates in the rhizosphere that metabolize petroleum conditions, accelerating microbial activity and enhancing the breakdown of petroleum hydrocarbons such as oils, fuels, and other organic contaminants. This indirect mechanism makes phytoremediation particularly effective for petroleum wastes, which are often resistant to physical removal but biologically degradable under appropriate conditions.

Figure 2.4 Plant selection for petroleum remediation


Comprehensive Plant List

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