Replanted Is Not Restored: Forest Succession Around Port Renfrew
Date prepared: 2026-06-03
Why this matters
When old forest is logged, the public is often told it will grow back. It does grow back as trees. It does not grow back as the same forest, not on any timescale that helps the people, fish, and animals alive today. Old-growth structure takes centuries to build. Managed second growth is usually cut again long before it gets there. So a cutblock that was old forest becomes a young plantation, then a stump, then a young plantation again. Under normal short-rotation management, it does not return to old forest.
This note lays out that argument, separates what is established science from what the local data shows, and records what we still cannot measure locally so it becomes a research and records target.
How to read the claims here:
- Established science: general, well-documented, cited.
- Screening fact: computed from official local data, real but not a legal or field-confirmed result.
- Local-data gap: something we cannot yet show locally, listed in
data/succession/research-backlog.csv. - Question: what the gap should make the public ask.
First, second, third growth: what the words mean
- First growth / old growth: forest that has never been industrially logged and has developed old-growth structure. On the wet B.C. coast the province treats stands as old growth at about 250 years. [Established science: BC Government, Old growth definitions and values.]
- Second growth: the stand that grows after the first harvest, usually replanted as an even-aged plantation.
- Third growth and beyond: what grows after the second stand is cut, and so on through each rotation.
The key point is in the ages. Coastal old growth is defined at roughly 250 years. Coastal second growth is typically logged at about 50 to 80 years. [Established science.] So under standard management the forest is re-cut three to five times before a single stand would ever be old enough to be called old growth again. The old forest does not come back. It is replaced by a cycle of young stands.
What is lost between generations
Old growth is not just older trees. It is a structure that takes centuries to assemble: large-diameter trees, standing dead trees (snags), large fallen logs and coarse woody debris, a layered canopy with gaps that let light reach a deep understory of ferns, shrubs, mosses, and lichens. [Established science: BC Government, Old growth definitions and values.] An even-aged plantation has none of these for a long time. It is dense, single-layered, and closed-canopy until it is thinned or cut.
Some of what depends on that structure:
- Wildlife habitat. The marbled murrelet, a seabird listed as Threatened under the federal Species at Risk Act, nests inland on the large mossy branches of old coniferous trees and almost nowhere else. COSEWIC and federal recovery planning estimate the species has lost more than 20 percent of its nesting habitat over three generations. Separately, an estimated 35 to 53 percent of British Columbia's coastal old-growth forest, much of it murrelet nesting habitat, had been lost to logging and development by the late 1990s. [Established science: BC Government, Marbled Murrelet; COSEWIC status report; federal Marbled Murrelet recovery strategy.] Young plantations do not have the large mossy branches murrelets need.
- Lumber quality. Slow-grown old-growth wood is tight-grained and largely clear of knots, which is why it is sought for specialty products. Faster-grown plantation wood harvested young contains more juvenile wood and grows under conditions that change the quality of the timber. [Established science: BC wood-quality research; sector descriptions.] Cutting old growth and replacing it with short-rotation plantations trades a one-time stock of high-grade wood for a lower-grade renewable crop.
- Fish habitat. Old streamside forest shades water, drops large wood that builds
pools and stable banks, and holds soil that would otherwise wash in as sediment. These
functions are documented in B.C.'s own riparian science. [Established science: BC
riparian areas science; see
how-forestry-affects-fish-habitat.md.] Young replanted stands take decades to provide them again. - Fire behaviour. Young dense stands and post-harvest slash change fuel structure
and exposure. In several well-studied forest systems, young plantations and clearcut
edges have burned at higher severity than older forest: an Oregon State analysis of the
2013 Douglas Complex Fire found industrial plantations burned more severely than older
public forest, and other peer-reviewed work links homogeneous young stands and logging
slash to elevated fire severity for a decade or more after harvest. [Established science:
Zald and Dunn 2018, Oregon State; see
slash-second-growth-wildfire-risk-explainer.md.] The Forest Practices Board's 2025 investigation found forestry in wildland-urban interface areas is not reaching its potential to reduce wildfire risk. [FPB, Help or Hinder.] These findings come mostly from drier systems; the Port Renfrew coast is wet temperate rainforest that historically burned rarely, but climate change is extending fire weather to the coast, and even Mosaic, the largest private Island manager, called the Island's 2026 fire season elevated-risk. Whether a given local stand is more or less flammable depends on many factors and is a local-data gap. The point is not that any block will burn; it is that converting old forest to short-rotation plantations creates decades of altered fuel, and the public pays to suppress fire while these records stay out of view.
What the local data shows
These come from official records already downloaded for the study area (San Juan,
Gordon, Fairy, Walbran, Harris, Lens, Caycuse, Renfrew, Sombrio). They are screening
facts. See scripts/build_succession_analysis.py and data/succession/.
The replanting is real, but it is plantation, not restoration. Of 1,074 RESULTS openings in the area, 1,008 (about 94 percent) have a planting record. So replanting is happening. But 1,002 of those openings (about 93 percent) used clearcut or clearcut-with-reserves systems, and of the 792 openings that record a prior stand age, 512 (about 65 percent) were 141 years or older before harvest, including 373 that were in the 251-plus age class. In plain terms, mature and old forest was clearcut and replaced with even-aged plantations.
Almost nothing logged has had time to recover. Across the recorded harvested footprint of about 32,764 hectares, 99.5 percent is regrowth less than 60 years old. Coastal old growth is defined at about 250 years. None of the logged area is close. A chronosequence study in B.C.'s Coastal Western Hemlock zone found that even at 80 to 100 years, second growth is only about 41 to 55 percent structurally similar to old growth. [Established science: chronosequence study, see Sources.] A stand clearcut today would not be old forest again until about the year 2275, roughly eight human generations from now. No one alive today, or their grandchildren, will see it return.
Old growth is still being cut while younger forest is available. Recorded harvest from 2010 onward overlaps about 518 hectares of mapped old growth (TAP old-forest, ancient-forest, and priority-deferral layers combined; 887 hectares across all recorded harvest). At the same time, the same watersheds hold about 15,915 hectares of second growth already 60 to 139 years old, which is at or past normal coastal harvest age, plus about 42,388 hectares of younger regrowth coming up behind it. [Screening fact.] This does not prove any specific block should not have been cut. It raises a clear question: why cut mapped old growth when second growth at harvestable age is far more abundant?
The cascade: fish, hunting, tourism
The argument does not end at the tree. The forest type drives the economy and the wildlife that depend on it.
- Salmon and sport fishing. Port Renfrew's economy has shifted toward sport fishing and old-growth tourism. [Context: Port Renfrew Chamber.] Riparian forest condition affects salmon habitat through shade, large wood, and sediment. The link between local stand age and local salmon returns is a local-data gap, not a proven local causation.
- Hunting. Forage for deer and elk peaks in early-seral openings, but thermal cover and winter range depend on older forest structure. Whether the current age mix can sustain ungulate populations locally is a local-data gap.
- Tourism. The ESSA Port Renfrew valuation found standing old growth carries
significant recreation and tourism value that a plantation does not replace. See
notes/essa-port-renfrew-economics-summary.md.
Carbon at stake (screening estimate)
Coastal old growth holds more carbon per hectare than almost any other forest type.
Published ranges for productive coastal sites run from roughly 500 to 1,300 tonnes of
carbon per hectare, and logging old growth releases an estimated 40 to 65 percent of
ecosystem carbon even after counting wood products. [Established science: Harmon, Ferrell
and Franklin 1990, Science 247:699-702; coastal carbon-density ranges per the Sources
below. Precise per-stand local values are a deep-research item, see
research/deep-research/07-carbon-oldgrowth-vs-secondgrowth.md.]
Applying those ranges to the local hectares is a screening estimate, not a measurement:
- The roughly 17,922 hectares of 250-plus old forest remaining in these watersheds hold on the order of 33 to 85 million tonnes of CO2.
- The roughly 518 hectares of old growth cut since 2010 represent on the order of 0.4 to 1.6 million tonnes of CO2 released.
These are wide screening ranges meant to show the order of magnitude of the climate
stake, not a precise figure. See data/succession/carbon-screening-estimate.csv.
What the public received for that carbon is small by comparison. Coastal old growth carries very high timber volume, on the order of 1,000 to 1,800 cubic metres per hectare (second growth is roughly a third of that). [Established science: industry and CBC/AFA figures.] The roughly 518 hectares of old growth cut since 2010 therefore held very roughly 0.5 to 0.9 million cubic metres of timber. At the area's average public stumpage of about $6.55 per cubic metre (ESSA 2021), the public's direct cash take from that timber was on the order of $3 to $6 million. The carbon released from the same cutting is valued at roughly $30 to $274 million at the federal carbon price (screening). Even at the most conservative ends, the carbon cost is several times the public's cash return. [Screening estimate; combines our carbon screening with ESSA stumpage and published volume ranges.]
What this does not prove
- It does not prove any specific harvest was illegal or that any rule was broken.
- It does not prove a local wildlife population, salmon run, or fire was caused by local logging. Those need data we do not have.
- The harvest-over-old-growth overlap is a screening number computed on simplified geometry, not a field-confirmed audit.
The honest claim is narrower and still strong: replanting restores tree cover, not old forest, and the public should be able to see why old growth is cut when younger forest is available, and what is being given up in habitat, fish, fire resilience, and wood quality.
Related angles worth pursuing (brainstorm)
- Carbon debt. Old growth stores large, stable carbon; a clearcut releases it and a young stand takes decades to repay the debt. Pair with the carbon line in the full-cost work.
- Timber-supply falldown. The known drop from high old-growth volumes to lower managed second-growth yields. It reframes old-growth logging as drawing down a stock, not a steady harvest.
- Soil and productivity over rotations. Whether successive short rotations reduce site productivity over time.
- Cumulative watershed and hydrology recovery. How long peak-flow and sediment effects persist as a watershed fills with young stands.
- Connectivity and edge effects. Fragmented old growth loses interior-forest value even where patches remain.
- Climate resilience. Whether old, structurally complex stands buffer drought, heat, and fire better than even-aged plantations.
- At-risk-species legal triggers. Murrelet habitat thresholds and the December 2021 Crown-land retention order as a concrete accountability hook.
- Cedar and cultural values. Large old cedar for cultural use is not replaced by a short-rotation plantation.
- A public story scene. "Replanted is not restored," built from the numbers above, as a future addition to the story page.
Methods and caveats
- Growth-stage areas come from the VRI age-class summary in
data/public-data-audit/watershed-harvest-stand-age-summary.csv. VRI age is a screening signal, not a legal old-growth determination. - Harvest-over-old-growth overlap dissolves cutblocks and the TAP old-growth layers and intersects them, on geometry simplified to about 40 metres for speed. Treat the hectares as screening estimates.
- Reforestation figures come from RESULTS openings
(
data/historical-change/results-openings.geojson). Prior age class uses the standard B.C. age-class codes; a full code decode is a backlog item. - Time-since-harvest uses cutblock
HARVEST_START_YEAR_CALENDARagainst 2026.
Sources
- BC Government, Old growth definitions and values: https://www2.gov.bc.ca/gov/content/industry/forestry/managing-our-forest-resources/old-growth-forests/old-growth-values
- BC Government, Marbled Murrelet: https://www2.gov.bc.ca/gov/content/environment/plants-animals-ecosystems/species-ecosystems-at-risk/implementation/conservation-projects-partnerships/marbled-murrelet
- COSEWIC status report, Marbled Murrelet: https://www.canada.ca/en/environment-climate-change/services/species-risk-public-registry/cosewic-assessments-status-reports/marbled-murrelet-2012.html
- Forest Practices Board, Help or Hinder? Aligning forestry with wildfire risk reduction: https://www.bcfpb.ca/release-publications/releases/help-or-hinder/
- Federal Marbled Murrelet recovery strategy: https://www.canada.ca/en/environment-climate-change/services/species-risk-public-registry/recovery-strategies/marbled-murrelet-2014-proposed.html
- Coastal old-growth carbon density (productive coastal sites store on the order of 500-1,300 tonnes C/ha; among the most carbon-dense forests outside the tropics): https://phys.org/news/2021-06-temperate-old-growth-rainforest-key-sustainable.html ; BC Coastal Old-Growth Dynamics project: https://www2.gov.bc.ca/gov/content/environment/plants-animals-ecosystems/ecosystems/ecosystem-and-landscape-ecology-research-and-classification/coastal-old-growth-dynamics-ogd-project
- Carbon released when old growth is logged (about 40 to 65 percent of ecosystem carbon, even after wood products): Harmon, Ferrell and Franklin 1990, Science 247(4943):699-702, https://doi.org/10.1126/science.247.4943.699
- Coastal old-growth timber volume (about 1,000-1,800 m3/ha; second growth about a third): https://www.cbc.ca/news/canada/british-columbia/old-growth-trees-british-columbia-1.6045289 ; Ancient Forest Alliance FAQ (advocacy): https://ancientforestalliance.org/ancient-forests/common-questions-answers-bc-old-growth-forests/
- Plantation and slash fire severity: Zald, H.S.J. & Dunn, C.J. 2018, Ecological Applications 28(4): 1068-1080: https://doi.org/10.1002/eap.1710
- BC wildfire suppression cost (about $1.1B in 2023): https://www.cbc.ca/news/canada/british-columbia/bc-wildfires-aug-13-2024-1.7293428
- ESSA 2021 Port Renfrew old-growth valuation: https://www.essa.com/what-is-the-economic-value-of-old-growth-forests-if-they-are-kept-standing/
- BC riparian areas science (see
data/source-inventory.md). - Full source register for these claims:
data/source-register-analysis.csv. Canonical figures:notes/canonical-figures.md. - Old-growth structural recovery time (second growth at 80-100 yr is only 41-55% similar to old growth): chronosequence study, Coastal Western Hemlock zone, https://cdnsciencepub.com/doi/10.1139/x11-079
- Riparian old growth and salmon habitat (large wood, shade): WDFW riparian science; Helfield and Naiman 2001, Ecology 82(9):2403-2409.
- Old-forest-dependent species (northern goshawk, marbled murrelet, and others): BC Government Northern Goshawk: https://www2.gov.bc.ca/gov/content/environment/plants-animals-ecosystems/species-ecosystems-at-risk/implementation/conservation-projects-partnerships/northern-goshawk
- Timber-supply falldown (second growth yields less; southern Vancouver Island AAC cut ~5.5%): https://www2.gov.bc.ca/gov/content/industry/forestry/managing-our-forest-resources/timber-supply-review-and-allowable-annual-cut
- Deeper research syntheses with citations:
research/deep-research/(notes 01, 02, 03, 05, 06, 07, 08). - Local analysis:
scripts/build_succession_analysis.py,data/succession/.