June 25, 2026

Natural Regeneration of a Century-Old Paperbark Maple (Acer griseum)

Location: The Bradley Estate (The Trustees of Reservations), Canton, MA (Zone 7a)
Parent Tree Metrics: CBH: 72" | DBH: 22.92" | Estimated Age: 103–115 years old
Conservation Status: Globally Endangered (IUCN Red List)

During a recent survey at the Bradley Estate, I documented 25 naturally established volunteer saplings growing from a single, historic parent paperbark maple (Acer griseum). Finding natural volunteers on this scale is an extraordinary anomaly. Acer griseum suffers from notorious biological reproduction barriers: it has extreme seed sterility (frequently <5% embryo viability due to hollow seeds) and requires a grueling two-year double seed dormancy cycle to germinate in the wild.

Data Breakdown


The 25 recovered volunteers are scattered up to 87.42 feet away from the parent tree, spanning 1 to 5 years of age. Looking at the data by age group reveals a the following population structure:
  • Age 1 (6 saplings): Avg Height: 4.8" | Mean Dispersal Distance: 45.4 ft | Germinated 2025
  • Age 2 (5 saplings): Avg Height: 11.0" | Mean Dispersal Distance: 34.9 ft | Germinated 2024
  • Age 3 (10 saplings): Avg Height: 21.4" | Mean Dispersal Distance: 31.8 ft | Germinated 2023 (40% of population)
  • Age 4 (2 saplings): Avg Height: 30.5" | Mean Dispersal Distance: 31.2 ft | Germinated 2022
  • Age 5 (3 saplings): Avg Height: 42.3" | Mean Dispersal Distance: 34.6 ft | Germinated 2021

Why now?

The parent tree is a century-old, likely a direct genetic descendant of Ernest Henry Wilson’s 1907 seed collection for the Arnold Arboretum. It was planted in the late 1940s by Eleanor Cabot Bradley alongside other Asian species, e.g. a dawn redwood (Metasequoia glyptostroboides).
Despite dropping millions of seeds over its lifespan, there are zero saplings older than 5 years. This sharp demographic cutoff reveals that a century-long reproductive bottleneck was recently broken by two major environmental events:

  1. The Structural Catalyst (Canopy Gap): I discovered a cut-down tree stump directly West-Southwest (WSW) of the parent tree. The stump appeared to be about 5 years old. Removing this tree reduced intense subterranean root competition and flooded the sloped forest edge with increased lighting, giving the young seedlings the energy required to survive past infancy.
  2. The Climate Trigger (The Age 3 Spike): 40% of the volunteer seedlings are exactly 3 years old. Weather data from the Blue Hill Observatory (right down the street) reveals a multi-year weather sequence that perfectly aligned with the species' 2-year seed cycle:
    • Winter 2021–2022: Heavy snow insulation and an intense cold snap (0°F) successfully cracked the seeds' dense woody outer hulls.
    • Summer 2022: An extreme regional drought (8th driest summer on record) kept the dormant seeds safe from rotting in the ground.
    • Spring/Summer 2023: Just as the seeds emerged, the drought broke with a historic deluge (7th wettest summer on record), providing continuous moisture for the fragile new root taps.

Ground Cover Habitat

The saplings show a strict preference for specific ground cover:

  • The Survival Mat: 24 out of 25 saplings are rooted exclusively in a shaded, sloped hillside carpeted by lesser periwinkle (Vinca minor) and Eastern poison ivy. The loose Vinca weave keeps the soil surface humid and perfectly cradles the seeds through their multi-year dormancy.
  • The Exclusion Barrier: Zero saplings were found in the adjacent patch of dense Japanese pachysandra. Pachysandra's thick, interlocking rhizome mat acts as an absolute physical barrier that prevents maple seed establishment.
  • Animal Dispersal?: While gravity and slope carry seeds down into the 25–45 ft core zone, the furthest outlier (Seedling #25) was found 87.42 feet away across a stone wall in a wetland. This is possible evidence of zoochory?
Posted on June 25, 2026 12:41 PM by rkillam | 11 observations | 3 comments | Leave a comment

April 30, 2026

June 25, 2025

State-Listed Invasives Found at Broadmoor Wildlife Sanctuary

Ongoing inventory of the occurrence and status of Massachusetts Invasive Plant Advisory Group (MIPAG) state-listed invasive, likely invasive, and potentially invasive vascular plant species observed at Broadmoor Wildlife Sanctuary. These observations are part of ongoing stewardship and ecological monitoring efforts to better manage invasive species and protect native biodiversity at this site.

To assess long-term patterns in invasive species presence at Broadmoor, I am referencing historical flora surveys conducted by:

  • Bruce Lund (1970s–1980s)
  • Lisa Standley (2008–2009)

This comparison provides a baseline for evaluating:

  • Persistent Species: Invasives found by Lund, Standley, and myself, indicating long-term establishment.
  • Emergent Species: Invasives found by Standley and myself, but not Lund, suggesting mid-to-late 20th century introductions that have persisted or expanded.
  • Reintroduced Species: Invasives found by Lund and myself, but not Standley, indicating species that have returned.
  • New Arrivals: Invasives found only in recent surveys by myself, absent from both prior records, indicating recent establishment or detection.

Summary of State-Listed Invasive Species Observed

Persistent Invasive Species

Scientific Name Common Name Status
Acer platanoides Norway maple INVASIVE
Berberis thunbergii Japanese barberry INVASIVE
Celastrus orbiculatus oriental bittersweet INVASIVE
Elaeagnus umbellata autumn olive INVASIVE
Euonymus alatus winged euonymus INVASIVE
Frangula alnus glossy buckthorn INVASIVE
Iris pseudacorus yellow iris INVASIVE
Lythrum salicaria purple loosestrife INVASIVE
Phalaris arundinacea reed canary-grass INVASIVE
Phragmites australis common reed INVASIVE
Rhamnus cathartica common buckthorn INVASIVE
Rosa multiflora multiflora rose INVASIVE
Vincetoxicum nigrum black swallow-wort INVASIVE
Berberis vulgaris European barberry LIKELY

Emergent Invasive Species

Scientific Name Common Name Status
Alliaria petiolata garlic mustard INVASIVE
Fallopia japonica Japanese knotweed INVASIVE
Lonicera morrowii Morrow's honeysuckle INVASIVE
Lysimachia nummularia creeping Jenny INVASIVE
Robinia pseudoacacia black locust INVASIVE
Vincetoxicum rossicum European swallow-wort LIKELY
Lonicera maackii Amur honeysuckle POTENTIAL

Reintroduced Invasive Species

Scientific Name Common Name Status
Lonicera tatarica Tatarian honeysuckle LIKELY

New Invasive Species

Scientific Name Common Name Status
Alnus glutinosa European alder INVASIVE
Cabomba caroliniana Carolina fanwort INVASIVE
Ficaria verna lesser celandine INVASIVE
Hesperis matronalis dame’s rocket INVASIVE
Lonicera japonica Japanese honeysuckle INVASIVE
Salix atrocinerea rusty willow INVASIVE
Trapa natans water chestnut INVASIVE
Actinidia arguta hardy kiwifruit LIKELY
Ampelopsis glandulosa porcelain berry LIKELY
Cardamine impatiens narrow-leaved bittercress LIKELY
Ligustrum obtusifolium border privet LIKELY
Phellodendron amurense Amur corktree LIKELY
Pyrus calleryana Callery pear LIKELY
Rhodotypos scandens jetbead LIKELY
Rubus phoenicolasius wineberry LIKELY
Posted on June 25, 2025 05:13 PM by rkillam | 0 comments | Leave a comment

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