Blooming,Peace,Lilies,In,Sunny,November

Blooming peace lilies in sunny November (Credit: Traveller70 on Shutterstock)

Active Living Wall Systems Cut Indoor Air Pollutants in Hours, Research Shows

In A Nutshell

  • Common houseplants mounted in an active living wall system can eliminate a cocktail of six indoor air pollutants: including formaldehyde, nitrogen dioxide, and sulfur dioxide, with reduction rates of 96 to 98 percent within 24 hours.
  • The peace lily outperformed all other tested species against nitrogen dioxide, reaching more than 90 percent differential reduction efficiency within 15 minutes, while the spider plant led the initial charge against formaldehyde.
  • Plants showed no drop-off in performance after three consecutive days of repeated pollution exposure — and some species actually improved, suggesting they may adapt to pollutants over time.
  • The system’s edge over a simple shelf of potted plants lies in its fan-driven airflow, which forces air through the vegetation panel rather than relying on passive drift, dramatically increasing the volume of air that contacts the plants.

Right now, in conference rooms and open-plan offices everywhere, people are breathing in a cocktail of invisible chemicals. Formaldehyde seeps from furniture. Nitrogen dioxide drifts in from traffic outside. Fumes waft off cleaning products. Most people don’t think twice about it. But researchers at the University of Seville asked themselves could a wall covered in common houseplants actually clean that air in real time?

According to their new study, the answer appears to be yes, and one plant in particular stood out as a superstar air purifier. When mounted in a living wall system with active air circulation, the peace lily reduced nitrogen dioxide by more than 90 percent efficiency within the first 15 minutes of exposure, far outpacing the other four species tested. That’s a startling figure for a plant commonly found at garden centers for a few dollars.

The study, published in the journal Atmospheric Environment tested five common houseplant species arranged in an active living wall, a vertical garden panel equipped with a fan system that pushes air through the plants rather than just letting it drift past. Researchers pumped a mix of six different pollutants into a sealed glass chamber and tracked how quickly the plants could bring those levels down, repeating the process over three consecutive days to see whether the plants lost steam. They didn’t.

How Researchers Built a Pollution Lab in a Glass Box

The research team set up their experiments in a basement laboratory at the University of Seville, where temperature and humidity could be tightly controlled and no natural light interfered with results. They built a rectangular glass chamber roughly the size of a large closet, about three feet wide, three feet tall, and six feet long, holding approximately 70 cubic feet of air. On one end, they attached a felt panel sewn into a grid of 49 pockets, each capable of holding a plant rooted in clay pellets. Eighteen plants of a single species were placed in the panel for each round of testing.

Five species were tested one at a time: the peace lily, wandering dude, heartleaf plant, creeping fig, and spider plant. These were chosen because they’re commonly used in indoor living walls and are already known for air-cleaning properties. Before any experiment began, each batch of plants spent at least three weeks outside the chamber adapting to their new growing conditions.

Rather than buying expensive compressed gas cylinders, the researchers developed a creative and low-cost method for generating pollutants. They heated liquid solvents, including formaldehyde solution, acetone, and two petroleum-based chemicals, in small glass tubes inside the chamber until they vaporized. For sulfur dioxide and nitrogen dioxide, they triggered chemical reactions between concentrated acids and metal powders. Small fans distributed the resulting pollution evenly throughout the chamber.

Each experiment ran for 72 hours. Pollutants were injected once per day, at the start and again at the 24- and 48-hour marks, creating three rounds of contamination per species. The entire experiment was then repeated three times on different weeks to ensure reliability. A portable air quality monitor tracked pollutant levels continuously. Between testing cycles, the living wall panels were moved to a clean room for at least four days to minimize any leftover contamination. The researchers also ran control experiments in the empty chamber with no plants so they could calculate exactly how much of the pollution reduction was due to the plants versus natural fading.

living wall
Scheme of the closed glass chamber with the air recirculation system. Location of the ALW and the equipment to introduce contaminants, sample and maintain the living wall. (1) pollutants generation system; (2) portable small fans; (3) air recirculation system; (4) tank with irrigation water; (5) submersible pump; (6) living wall; (7) LED grow lamp; (8) air quality monitor. (Credit: Rossini-Oliva, Fernández-Espinosa, et al. Atmospheric Environment, DOI: 10.1016/j.atmosenv.2026.121856)

What the Peace Lily and Spider Plant Actually Accomplished

The results were dramatic across the board. After 24 hours following each pollutant injection, all five species achieved pollutant reduction rates between 96 and 98 percent for combined airborne chemical compounds. But the differences between species and between pollutants told a more detailed story.

Formaldehyde, a known cancer-causing agent found in building materials and furniture, was the pollutant most rapidly eliminated. All five species brought formaldehyde concentrations to zero within about three hours, compared to eight hours in the plantless control chamber. The spider plant showed the fastest initial response, consistent with previous research identifying it as particularly efficient at breaking down formaldehyde. Scientists believe the plant converts the chemical into organic acids, sugars, and amino acids through its internal chemistry.

For nitrogen dioxide, a combustion byproduct that seeps indoors from vehicle exhaust and gas stoves, the peace lily dominated. Its differential reduction efficiency (a measure of how much faster the plant eliminated the gas compared to the control chamber with no plants) hit 92 percent at the moment of peak pollution and 94 percent within 15 minutes. No other species came close during that early window; the remaining four plants hovered between 32 and 51 percent at the 15-minute mark. The peace lily needed only about 11 minutes to cut the nitrogen dioxide concentration in half, while other species took considerably longer.

Sulfur dioxide proved the most stubborn pollutant, taking 8 to 12 hours for the plants to fully eliminate compared to just a few hours for formaldehyde. Still, every species performed significantly better than the empty control chamber. The peace lily again led the pack, needing only about 8 minutes to halve the sulfur dioxide concentration, while the heartleaf plant required 84 minutes for the same reduction.

For the combined airborne chemical compounds, all species achieved reductions of 24 to 40 percent within the first 15 minutes. The peace lily and heartleaf plant showed the strongest sustained removal over time, with the peace lily maintaining the highest efficiency through the end of each daily cycle.

spider plant
Spider plants showed the fastest initial response to formaldehyde. (Credit: fotosenukas on Shutterstock)

These Air-Cleaning Plants Didn’t Burn Out Over Three Days

One of the study’s most encouraging findings was that the plants’ air-cleaning ability didn’t fade with repeated exposure. Over three consecutive days of pollution injections, none of the five species showed a decline in performance. For some pollutants, including airborne chemical compounds, formaldehyde, and sulfur dioxide, certain species actually performed slightly better on the third day than the first. This suggests the plants may adapt to become more efficient pollutant removers with continued exposure.

This matters because real indoor environments don’t experience pollution as a one-time event. Chemicals are released continuously or on and off from furniture, cooking, cleaning, and outdoor sources. A plant system that loses effectiveness after a single exposure would have limited practical value.

The “active” part of the living wall is doing serious work here, too. Unlike a passive setup where air simply drifts past potted plants on a shelf, the system tested in this study used a fan to force air through the vegetation panel in programmed cycles of 30 minutes on and one hour off. This dramatically increases the volume of air that contacts the plants and their root systems, where soil microbes also help break down pollutants. Previous research has shown that active airflow drastically increases a living wall’s ability to capture airborne chemicals compared to passive setups. The current study adds evidence that this advantage extends to gas pollutants like nitrogen dioxide and sulfur dioxide as well.

The researchers acknowledged important limitations. The chamber, while not perfectly sealed (intentionally, to mimic a real room), was still far smaller than an actual office or home. The initial pollutant concentrations were higher than typical indoor levels. Each species was tested on different dates, meaning minor variations in conditions could partly explain some differences between species. And comparing results across studies remains difficult because experimental setups, plant sizes, air volumes, and methods vary widely.

Still, the core finding holds: a living wall system with forced air circulation and common houseplants can meaningfully reduce a cocktail of dangerous indoor air pollutants and keep doing it day after day. Among the five species tested, the peace lily earned its reputation as a pollution fighter, particularly against nitrogen dioxide, while the spider plant excelled at tackling formaldehyde. For anyone designing healthier indoor spaces, it might be worth giving plants a wall of their own.


Paper Notes

Limitations

The researchers noted several caveats. Species were assessed on different dates, so minor fluctuations in experimental conditions could partly explain observed differences between species. The chamber was smaller than a real room, and initial pollutant concentrations exceeded typical indoor levels, making direct application to real-world settings difficult. The air transfer rate due to chamber leakiness was not measured, though control experiments served as a reference. No direct measurements of pollutant release or decay of induced plant responses were performed during clean-air recovery periods between cycles. The team also noted that comparing results with other studies is challenging because experimental conditions, plant quantities, substrate types, air volumes, airflow methods, initial pollutant concentrations, and statistical indicators vary widely across the literature.

Funding and Disclosures

This research was funded by the Andalusian Plan of Research, Development and Innovation 2020 (grant number P18-TP-1657), through the 2018 call for research projects for universities and qualified public research entities as agents of the Andalusian Knowledge System (Junta de Andalucía, Spain). The authors declared no competing financial interests or personal relationships that could have influenced the work.

Publication Details

Title: “Volatile organic compounds, SO₂ and NO₂ capture by means of an indoor active living wall” | Authors: Antonio José Fernández-Espinosa, José Manuel Montiel-de La Cruz, Rafael Fernández-Cañero, Luis Pérez-Urrestarazu, and Sabina Rossini-Oliva | Affiliations: Department of Plant Biology and Ecology, University of Seville; Urban Greening and Biosystems Engineering Research Group, University of Seville; Department of Analytical Chemistry, University of Seville; Environmental Analytical Chemistry Research Group, University of Seville | Corresponding author: Sabina Rossini-Oliva ([email protected]) | Journal: Atmospheric Environment, Volume 371 (2026), Article 121856 | DOI: 10.1016/j.atmosenv.2026.121856 | Received: June 26, 2025; Accepted: February 3, 2026; Available online: February 4, 2026 | License: Open access under CC BY-NC-ND 4.0

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