Start with the failure mechanism

Site Assessment & Restoration Planning

Turn a difficult site into a practical restoration pathway with clear treatment selection, specifications and field support.

Site Assessment & Restoration Planning field example

What may be happening

Diagnose before prescribing

The visible symptom is not always the cause. Erosion may be driven by concentrated runoff, seepage, compaction, lost root strength, an over-steepened landform or a biological filter that prevents natural recruitment. A generic treatment can spend money without changing that process.

We review the site history and conditions before recommending work. The scope may be a short written recommendation or include drawings, material guidance, field direction and monitoring. We identify where other disciplines or permits need to be part of the project.

Methods that may fit

Treatment follows site conditions

Projects

Compare similar sites and long-term outcomes.

Resources

Read the papers and field notes behind the recommendations.

Field evidence

See the method in context

Projects by problem

Use completed field examples to compare settings, treatments and recovery.

View the evidence →

David Polster's research legacy

Follow the papers and practical ideas that shaped the approach.

View the evidence →

Read the source material

PES starts with a practical question: what is stopping this site from recovering? The treatment should address that limiting condition and support the next stage of succession.

Where this service fits

Common site types and project needs

These are starting points, not a substitute for assessment. A project may combine several service areas.

  • Early feasibility and treatment selection
  • Restoration concepts and specifications
  • Construction or installation field support
  • Monitoring criteria and adaptive recommendations

From first look to field follow-through

A practical four-part path

Assess

Review the site, disturbance history, forces, constraints and desired outcome.

Select

Match methods, species, materials and timing to the limiting process.

Support

Provide specifications, installation guidance and field decisions where required.

Learn

Monitor trajectory and adjust when field evidence shows a better path.

Questions clients ask

Assessment & Planning FAQ

What should I send before an assessment?

A location, several current photos, a short site history, the observed problem, known constraints and the outcome you need are enough to begin the conversation.

Can PES work with engineers and other consultants?

Yes. Soil bioengineering often sits within a larger geotechnical, hydrological, environmental or regulatory scope. Roles and interfaces should be clear from the outset.

Will the assessment recommend one standard detail?

Not automatically. The purpose is to identify the limiting process and choose a treatment suited to the site, including where soil bioengineering is not the right tool.

Bring the site problem into focus

Send the location, current photographs, known history and the outcome you need. PES will help identify the right next step.

Native plant gardens as a recovery pathway

A native plant garden can be the visible first stage of ecological recovery, not just an ornamental planting.

We start with water, soil, exposure, compaction, existing vegetation, and the process that is holding the site back. Locally appropriate pioneering plants can occupy safe sites, slow surface flow, hold soil with roots, add organic matter, and create conditions that help later species establish. The garden is designed to change with the site rather than freeze it at installation day.

Explore planting examples and monitoring guidance

The 2003 Somenos Garry Oak ecosystem plan treated restoration as a sequence of site-specific work, monitoring, and adjustment. It separated implementation, effectiveness, and validation monitoring, then called for repeated plots and photo points to track change. The plan supports the monitoring framework below. The public field image documents monitoring equipment in use, but it is not proof that every proposed treatment was completed or successful.

A separate David Polster field record at the Battle Lake former gas plant shows the same logic in a different setting: after remediation and rough-and-loose preparation, willow, balsam poplar, and red-osier dogwood cuttings were installed and observed as woody cover and later species developed. It is a historical example, not a standard recipe for every garden.

David's Honeymoon Bay Ecological Reserve record shows why recovery can depend on hydrology, not only on a planting list. The source links Pink Fawn Lily habitat to periodic floodplain flooding that removed maple leaves and seeds and deposited fine silt, creating conditions that favoured bulb-forming species. It also records down-cutting and bank loss after a bridge constriction changed flow, and discusses restoring flood conveyance and annual overbank conditions. This is a historical ecological record, not a current project assessment or a prescription to plant lilies.

David Polster's Faro Mine succession record adds a second recovery lesson: native and locally appropriate pioneering plants need the right microsites before they can do the work of succession. The source describes willow seedlings establishing in wet pockets, pioneering herbs on disturbed ground, and later spruce appearing beneath willow cover as vegetation and soil conditions changed. For a garden or reclamation site, that supports designing for water, roughness, and safe establishment sites rather than promising that a fixed plant list will produce the same outcome everywhere. This is a historical mine-reclamation example, not a current PES project assessment.

Established woody vegetation from pocket planting along the Seaton River, British Columbia
Documented field record: established woody vegetation after pocket planting on the Seaton River, 2002 to 2014. View the full planting record.
Young willow stems leafing out among coarse rocks and mine substrate at Brenda Mine
Documented field record: young willow growth among coarse rock at Brenda Mine, May 18, 2015. View the Brenda Mine field record.
Young leafy plant growing between rounded cobbles on the Sandy Pools gravel bar
Sandy Pools field detail: a young leafy plant occupying a protected gap among rounded gravel-bar cobbles, September 17, 2016. This close view illustrates a safe-site condition; it is not a measured treatment result, and the species is not identified here.

David Polster's Sandy Pools restoration plan also shows why plant choice belongs inside the site process. At the Cowichan River bank, live staking using primarily Balsam Poplar was intended to rebuild a dense root complex and re-establish a species that had been lost from the post-logging conifer stand. Live gravel-bar staking was planned to slow flow and encourage sediment accumulation. This historical plan describes site-specific living stabilization, not a universal planting prescription or a measured outcome for every native garden.

Somenos field monitoring plot in a native grass and forb meadow with a quadrat and transect tape
Somenos monitoring record: a quadrat and transect tape in a native grass and forb meadow from David Polster's archive. This frame documents how recovery can be measured; it is not a before-and-after result, and species identification is not asserted.
SSI Conservancy stream edge with woody vegetation and living branch structures, March 30, 2019
SSI Conservancy field record: a stream edge with woody vegetation and living branch structures, March 30, 2019. This historical course-site frame illustrates how living materials and planted vegetation can work together during recovery; it is not a fixed-view before-and-after result or a claim about current site condition.

Assess the site

Find the constraint first: runoff, seepage, compaction, browse, invasive pressure, or missing soil structure.

Create safe sites

Use roughness, small terraces, woody debris, mulch, or living structures where planting needs protection before it can take hold.

Plant for sequence

Match locally appropriate pioneers to moisture and exposure, then plan for later shrubs, trees, and ground-layer species.

Protect and learn

Plan for establishment care, browse protection, invasive control, and monitoring so the next decision follows field evidence.

Questions to ask before planting

Can native planting solve an active slope failure?

Not by itself. Deep-seated movement, active seepage, concentrated runoff, or a failing landform may need structural, drainage, or soil-bioengineering measures selected through a site assessment.

How do you choose the plants?

We match locally appropriate species to moisture, exposure, soil, browse pressure, access, and the role each plant can play in succession. A native species is not automatically suitable for every site.

Is a native garden maintenance-free?

No. Establishment care, browse protection, invasive control, monitoring, and occasional replanting should be planned around the site's conditions and the recovery trajectory.

How should progress be shown?

Use a same-project, date-labelled sequence when the source and image permission are verified. Otherwise, label a single field image as historical or illustrative and describe only what can be observed.

A native plant garden does not replace structural treatment for a deep-seated failure, active seepage, or a site that needs a different intervention. Planting, soil preparation, drainage, and bioengineering should be selected together when the assessment calls for it.