Lemna valdiviana

Valdivia Duckweed

A tiny native Florida duckweed now identified as Valdivia Duckweed, this species has been introduced to the Freshwater Lake multiple times; its history is one of rapid consumption and repeated failed establishment in a nitrogen-limited closed system where grazers have consistently outpaced its growth.

Realm
Freshwater
Population
Extirpated
Primary biome
Freshwater Lake

Overview

Introduced to the Freshwater Lake multiple times over the history of miniBIOTA and identified as Lemna valdiviana, this small free-floating plant has repeatedly failed to establish. The last known surviving duckweed remained on the glass above the waterline and was identified as Valdivia Duckweed in September. On October 10, 2026, Josue reported that it had lost nearly all its color, judged it dead without a prospect of further budding or recovery, and recorded the species as extirpated. The actual death date and cause remain unknown.

Identity

  • Common name: Valdivia Duckweed
  • Alternate names: Valdivia's duckweed, forked duckweed, pale duckweed, water lentil, lemna, floating duckweed
  • Scientific name: Lemna valdiviana
  • Identification confidence: Species level
  • Uncertainty label: Observed

Taxonomy

  • Kingdom: Plantae
  • Phylum: Tracheophyta
  • Class: Liliopsida
  • Order: Alismatales
  • Family: Araceae
  • Genus: Lemna
  • Species: Lemna valdiviana

Natural History

Lemna valdiviana is a small free-floating aquatic monocot native to the Americas, with a range extending from the United States (including Florida) through Central and South America. Named after Valdivia, Chile, where it was first described, it is one of several Lemna species found in Florida's warm freshwater habitats: ponds, ditches, marshes, slow-moving rivers, and lake margins.

Each frond is 2 to 4 millimeters across, slightly elongated and asymmetrical compared to the rounder fronds of Lemna minor, with a single trailing rootlet. As with all Lemna species, reproduction occurs primarily through clonal vegetative budding: new fronds bud directly from the parent frond, separate, and form independent plants. Under optimal conditions of warm temperature, adequate light, and sufficient dissolved nitrogen, a population can double in two to four days.

Growth rate is strongly dependent on dissolved nitrogen availability. In nutrient-poor or cool systems, budding slows dramatically, and introduced biomass is typically consumed by grazers before the population can expand. This is the documented failure mechanism of prior Valdivia Duckweed introductions in miniBIOTA: the Freshwater Lake's nutrient limitation prevented the rapid budding needed to outpace grazing.

Ecological Role

In the Freshwater Lake, Valdivia Duckweed's potential ecological functions include primary production at the water surface, dissolved nitrogen and phosphorus uptake, surface shading to suppress phytoplankton and suspended algae, and food provision as high-protein floating plant biomass for invertebrate consumers.

Prior introduction attempts have not resulted in stable population establishment, due to a documented cycle of nutrient limitation slowing growth while grazers consume introduced biomass faster than it can expand. The June 30, 2026 reintroduction occurred under changed conditions: no fish were present to graze the plants, and the motivation is to evaluate floating plants as a nutrient management tool against persistent green water. On July 1, 2026, Slough Crayfish were confirmed climbing to the surface and feeding on the duckweed and other floating plants from below, one day after introduction, indicating that invertebrate grazing pressure remains a factor even without fish present.

miniBIOTA Evidence

### October 10, 2026 extirpation assessment

The remaining duckweed material was still on the glass but had lost nearly all its color. Josue judged the last known survivors dead, with no expected recovery or new budding, and the species is now considered extirpated. This is the date of the assessment, not a known death date; viability was not independently tested and the cause of the final loss was not established.

### September 10, 2026 observation

Josue identifies surviving Valdivia Duckweed on wet glass above the Freshwater Lake waterline, out of crayfish reach. This establishes positive presence, not establishment or the identity of every historical fragment.

Introduction context: Valdivia Duckweed has been introduced to the Freshwater Lake multiple times. The most recent prior introduction was a wild-collected sample on April 8, 2026, framed at the time as a temporary disruption rather than a stable solution. On June 30, 2026, the species was reintroduced alongside three other floating plant species (Lesser Duckweed, Dotted Duckweed, and Water Spangles) as a final evaluation of floating vegetation's ability to shift nutrient dynamics in the lake.

Observation timeline:

  • January 28, 2026: Last confirmed sighting from a prior introduction attempt, predating the April 8, 2026 field collection. No dedicated observation file exists for this date. Represents the end of a prior trial period.
  • April 8, 2026: Wild-collected from high-abundance natural sites and introduced to the Freshwater Lake. The observation record documents the reasoning: nutritional value as a food source for crayfish and shrimp, potential Daphnia alternative, and surface suppression of algae. The note explicitly acknowledges the history of failed introductions and frames this as an expected temporary disruption rather than a stable solution. Video evidence.
  • June 30, 2026: Reintroduced to the Freshwater Lake as part of a four-species floating plant trial alongside Lesser Duckweed, Dotted Duckweed, and Water Spangles. Identified to species level as Lemna valdiviana for the first time. Prompted by persistent green water; no fish were present to graze plants. Framed as a final evaluation of floating vegetation's ability to shift nutrient dynamics. Video evidence.
  • July 1, 2026: One day after introduction, Slough Crayfish observed climbing to the water surface and hanging beneath the floating mat to feed on the duckweed and other floating plants from below. The observer predicts the introduced plants may again be eliminated before establishing. Video evidence.
  • July 30, 2026: The four-species floating plant trial, of which Valdivia Duckweed is one, is reported at approximately 98% cover loss, effectively confirming the July 1, 2026 elimination prediction. Predation (consistent with the confirmed crayfish grazing), excessive light intensity, and possible low surface airflow are all proposed as contributing factors, none confirmed or ranked.
  • August 3, 2026: The trial is further reduced; the only duckweed still visible is a tiny fragment caught up on the glass against root structure, out of Slough Crayfish reach. Species is not distinguished among the three introduced duckweeds (Valdivia, Lesser, Dotted); whether this record's species is the survivor is unconfirmed.
  • September 10, 2026: Josue identified surviving Valdivia Duckweed on wet glass above the waterline, out of crayfish reach; this established presence without successful establishment.
  • October 10, 2026: The remaining glass duckweed had lost nearly all its color. Josue judged it dead and unable to recover or bud new growth, and the species is now considered extirpated. The actual death date and cause were not established.

Confirmed:

  • Presence in the Freshwater Lake at some point prior to January 28, 2026 (prior trial)
  • Wild-collected and introduced April 8, 2026 (video evidence)
  • Multiple prior failed introduction attempts; failure mechanism identified as nutrient limitation combined with grazing pressure
  • Reintroduced June 30, 2026 as a named, species-identified introduction (video evidence)
  • Species identity now resolved as Lemna valdiviana
  • Slough Crayfish confirmed feeding on the floating mat from below as of July 1, 2026, one day after reintroduction
  • The four-species floating plant trial reduced to approximately 98% cover loss as of July 30, 2026

Inferred:

  • All prior introductions consumed before population expansion could occur, consistent with the documented failure mechanism
  • April 2026 introduction likely followed the same pattern as prior failures
  • Nutrient limitation is the proximate driver of repeated establishment failure
  • Invertebrate grazing (crayfish) remains a limiting factor even without fish present, based on the rapid July 1, 2026 feeding response and the near-total loss confirmed July 30, 2026
  • Excessive light intensity and possible low surface airflow are also proposed as contributing factors to the July 30, 2026 near-total loss, alongside predation; none ranked or confirmed

Unknown:

  • Actual death date and cause of the last known glass survivors; October 10 is the assessment date.
  • Retrospective identity of the August 3, 2026 fragment before the September 10 identification; the earlier sighting did not distinguish Valdivia, Lesser or Dotted Duckweed.
  • Exact dates and outcomes of all prior introduction trials before April 2026
  • Which of predation, light intensity, or airflow is the dominant driver of the near-total loss; the August 3, 2026 detail that survivors are positioned out of crayfish reach favors grazing access as a meaningful factor