A new constructed wetland system combining biochar and pyrite minerals removed 89.74% of ammonia nitrogen and 90.36% of nitrate nitrogen from wastewater in laboratory tests, according to Gram Research analysis. The biochar prevented the mineral surface from becoming clogged while promoting beneficial bacteria that break down nitrogen pollution, offering a sustainable solution for treating contaminated water without adding carbon.

Scientists created a new type of constructed wetland—a natural water-cleaning system—that removes nitrogen pollution much better than traditional methods. The system combines biochar (a charcoal-like material) with pyrite (a mineral containing iron and sulfur) to clean wastewater that has low amounts of carbon. According to Gram Research analysis, the new system removed nearly 90% of ammonia and nitrate nitrogen without creating harmful byproducts. The breakthrough involved understanding how specific bacteria and minerals work together to break down nitrogen pollution, offering a sustainable solution for treating contaminated water.

Key Statistics

A 2026 laboratory study published in Bioresource Technology found that a biochar-pyrite constructed wetland system achieved 89.74% ammonia nitrogen removal and 90.36% nitrate nitrogen removal from low-carbon wastewater under controlled conditions.

Research showed that denitrification genes in the biochar-pyrite system increased dramatically, with narG genes increasing 2.7-fold and nirS genes increasing 4.5-fold, enabling efficient nitrogen breakdown by Thiobacillus bacteria.

The biochar-pyrite system prevented toxic nitrite accumulation while achieving nitrogen removal rates substantially exceeding traditional constructed wetlands, which typically achieve 60-80% removal under similar conditions.

The Quick Take

  • What they studied: Whether adding biochar and pyrite minerals to constructed wetlands could improve nitrogen removal from wastewater that doesn’t have much carbon in it
  • Who participated: Laboratory-scale constructed wetland systems (not human subjects); the study tested one optimized system configuration under controlled conditions
  • Key finding: The biochar-pyrite system removed 89.74% of ammonia nitrogen and 90.36% of nitrate nitrogen—significantly higher than traditional wetland systems—while preventing toxic nitrite buildup
  • What it means for you: This technology could lead to better, more affordable wastewater treatment at municipal facilities and industrial sites, potentially improving water quality in communities. However, this is early-stage research tested in laboratory conditions, so real-world performance at full scale still needs verification

The Research Details

Researchers built a vertical constructed wetland system—essentially a tall tank filled with layers of soil and special materials that filter water naturally. They added two key ingredients: biochar (a porous carbon material made from burned plant material) and pyrite (an iron-sulfur mineral). The system was tested under specific conditions: water stayed in the system for 24 hours, temperature was kept at 20°C (68°F), and the incoming wastewater had 15 mg/L of total nitrogen.

The researchers measured how well the system removed different forms of nitrogen (ammonia and nitrate) and analyzed what was happening at the microscopic level. They used electron microscopy to see the surfaces of the materials and examined the bacterial communities using genetic sequencing to understand which microorganisms were doing the nitrogen removal work.

This approach allowed them to connect the physical and chemical changes in the system with the biological activity of the bacteria, revealing how all the pieces work together.

Understanding the mechanisms—the ‘how’ and ‘why’—behind nitrogen removal is crucial because it allows engineers to design better systems. By identifying that biochar prevents the pyrite surface from getting clogged (passivation) and that specific bacteria are responsible for the nitrogen removal, future systems can be optimized. This knowledge also helps predict how the system will perform under different conditions and scales.

This is a controlled laboratory study published in a peer-reviewed journal (Bioresource Technology), which means the work was evaluated by other experts. The researchers used multiple analytical methods (microscopy, genetic analysis, chemical testing) to verify their findings, which strengthens confidence in the results. However, because this is a laboratory-scale study, results may differ when scaled up to real wastewater treatment plants. The study doesn’t specify sample size for biological replicates, which is a minor limitation.

What the Results Show

The biochar-pyrite system achieved exceptional nitrogen removal rates: 89.74% for ammonia nitrogen (NH4+-N) and 90.36% for nitrate nitrogen (NO3–N). Importantly, the system did not accumulate nitrite, a toxic intermediate compound that sometimes forms during nitrogen removal. These removal rates are substantially higher than traditional constructed wetlands, which typically achieve 60-80% removal under similar conditions.

The researchers discovered that biochar played a critical protective role. By buffering pH changes and helping move reaction byproducts away from the mineral surfaces, biochar prevented the pyrite from becoming ‘passivated’—a process where mineral surfaces get coated and stop working. This was a major breakthrough because passivation is a common problem that limits the performance of pyrite-based systems.

Genetic analysis revealed that a specific bacterium called Thiobacillus became dominant in the system. This chemolithoautotrophic bacterium (meaning it gets energy from chemicals rather than organic matter) was responsible for the nitrogen removal. The genes responsible for denitrification—the process that converts nitrate to harmless nitrogen gas—increased dramatically: narG genes increased 2.7-fold and nirS genes increased 4.5-fold.

The study found that biochar functioned as an electron mediator, facilitating direct interspecies electron transfer (DIET) between different microorganisms. This means the biochar acted like a bridge, allowing bacteria to exchange electrons and work together more efficiently. The system also demonstrated that slow-release iron-sulfur minerals from the pyrite provided a sustained energy source for the autotrophic denitrification process, meaning the bacteria could break down nitrogen without needing added organic carbon.

Traditional constructed wetlands often struggle with low carbon-to-nitrogen wastewater because bacteria need carbon as an energy source. This study advances the field by showing that mineral-based energy sources (from pyrite) combined with biochar can overcome this limitation. Previous research identified passivation as a major problem with pyrite systems; this study is novel in demonstrating that biochar effectively prevents this problem. The nitrogen removal rates achieved here (>89%) exceed most published results for similar wastewater types.

This research was conducted at laboratory scale in controlled conditions (constant 20°C, 24-hour retention time, specific nitrogen concentration). Real wastewater treatment plants experience temperature fluctuations, variable flow rates, and changing influent composition, which could affect performance. The study doesn’t specify how long the system maintained these high removal rates or whether performance declined over extended operation. Additionally, the study doesn’t include cost analysis or comparison with other advanced treatment technologies, so practical feasibility for widespread adoption remains unclear. The exact sample size and number of replicates for biological analyses are not specified in the abstract.

The Bottom Line

For wastewater treatment facilities treating low-carbon nitrogen-rich wastewater: This technology shows strong promise and warrants pilot-scale testing before full implementation. The evidence is solid for laboratory conditions (high confidence), but real-world performance needs verification (moderate confidence). For environmental engineers: Consider this approach as a potential solution for treating specific wastewater streams, particularly industrial effluent with high nitrogen and low carbon content.

Municipal wastewater treatment plants, industrial facilities treating nitrogen-rich wastewater (food processing, chemical manufacturing, pharmaceutical production), and environmental engineers designing treatment systems. This is particularly relevant for regions with strict nitrogen discharge regulations. General public should care because better wastewater treatment means cleaner rivers and groundwater.

In laboratory conditions, the system achieved optimal performance within the 24-hour retention time tested. For real-world implementation, pilot studies would likely take 6-12 months to evaluate performance across seasons and varying conditions. Full-scale deployment would require 1-2 years of planning and construction.

Frequently Asked Questions

How does biochar help remove nitrogen from wastewater?

Biochar acts as a protective buffer and electron mediator in the system. It prevents the pyrite mineral surface from becoming clogged (passivated) by stabilizing pH and moving waste products away. It also helps bacteria exchange electrons more efficiently, enabling them to break down nitrogen compounds faster.

What bacteria does the biochar-pyrite system use to remove nitrogen?

The system relies on Thiobacillus, a chemolithoautotrophic bacterium that gets energy from iron-sulfur minerals rather than organic carbon. This bacterium produces enzymes (narG and nirS) that convert ammonia and nitrate into harmless nitrogen gas through denitrification.

Can this wastewater treatment system work in real cities and factories?

This research shows strong laboratory results, but real-world performance still needs testing. The system was tested under controlled conditions (constant temperature, steady flow). Pilot studies at actual treatment facilities would be needed to confirm it works with variable conditions before widespread adoption.

Why is this better than regular constructed wetlands?

Traditional wetlands struggle with wastewater that has high nitrogen but low carbon because bacteria need carbon for energy. This system uses minerals (pyrite) as an energy source instead, achieving 89-90% nitrogen removal compared to typical 60-80% removal rates, without producing toxic byproducts.

How long does water need to stay in the system to be cleaned?

In laboratory tests, water stayed in the system for 24 hours and achieved optimal nitrogen removal. Real-world systems might need different retention times depending on wastewater composition and temperature, which would require additional testing.

Want to Apply This Research?

  • For wastewater treatment operators: Track daily nitrogen removal efficiency (% of ammonia and nitrate removed), system temperature, and water retention time. Set alerts if removal efficiency drops below 85%, which could indicate passivation or other problems.
  • Operators could use an app to log daily influent and effluent nitrogen concentrations, automatically calculate removal percentages, and receive alerts when performance deviates from expected ranges. This enables proactive maintenance before problems develop.
  • Implement weekly trend analysis of removal efficiency, monthly microscopic inspection of biochar-pyrite surfaces, and quarterly genetic analysis of bacterial communities to ensure the system maintains optimal microbial composition and physical condition.

This research represents laboratory-scale findings under controlled conditions and has not yet been tested at full-scale wastewater treatment facilities. Results may differ significantly in real-world applications with variable temperatures, flow rates, and wastewater composition. This technology should not be implemented at municipal or industrial facilities without pilot-scale testing and consultation with qualified environmental engineers. Always consult with water quality professionals and regulatory agencies before adopting new treatment methods. This summary is for informational purposes and does not constitute professional engineering or environmental advice.

This research translation is published by Gram Research, the science division of Gram, an AI-powered nutrition tracking app.

Source: Deep nitrogen removal in biochar-coupled pyrite constructed wetlands driven by targeted microbial succession: anti-passivation and electron transfer mechanisms.Bioresource technology (2026). PubMed 42379323 | DOI