💧 Integral Project · San Gregorio Atlapulco, Xochimilco

Biofilter Network, Wetlands
and Solar Stations

Low-cost ecological infrastructure for water restoration in San Gregorio Atlapulco. Combining physical, chemical and biological processes with local mineral materials, solar energy and community participation.

BiofiltersWetlandsSolar energyCitizen science
Executive Summary

From filter to ecosystem

The Biofilter and Artificial Wetland Network of San Gregorio is a low-cost ecological infrastructure proposal to improve water quality in the agricultural systems and canals of Xochimilco, combining physical, chemical and biological processes.

The project originated in the Humedal San Gregorio 1, where biofilters were designed for ditches with modules built with wood and galvanized mesh, using mineral materials and adsorbents such as tezontle, tepojal and activated carbon.

The key question:

Not "how do we filter water?" but "how do we design the conditions for water to sustain life again?"

Objectives

Design, implement and document a Community Network of Biofilters and Artificial Wetlands using locally available mineral materials, low-cost technologies, solar energy and natural filtration, adsorption and biodegradation processes.

💧

Hydraulic

Reduce suspended solids load and other contaminants through prefiltration systems and granular media.

⚗️

Physicochemical

Use materials with different properties of filtration, adsorption, ionic exchange, particle retention and biofilm support.

🦠

Biological

Create conditions for the development of microorganisms, plants and aquatic communities.

☀️

Energy

Integrate pumping stations powered by solar energy.

🌱

Agricultural

Improve water conditions for chinampera production systems.

🦎

Ecological

Contribute to habitat recovery for native aquatic species.

📚

Educational

Create a model that any community can study, adapt and reproduce.

Current Network

Biofilters currently installed in Xochimilco, plus a pilot project using hair booms.

San Gregorio Atlapulco

~202 m

Network of ditches with multiple biofiltration points. Main section of 139 m with several modules distributed across the system.

19.2575, -99.0918

Cuemanco

105 m

Linear biofilter installed in the chinampera zone of Cuemanco.

19.2700, -99.1000

Laguna del Toro

80 m

Biofilter at Laguna del Toro, lacustrine zone of Xochimilco.

19.2800, -99.0800

Pilot Project: Hair Booms

Experimental project using hair booms to test their effectiveness in water decontamination. An innovative approach to explore natural absorbent materials for canal water treatment.

Scientific basis

How a trench biofilter works

A trench biofilter is essentially a subsurface flow artificial wetland. Imagine a ditch excavated in the soil, filled with gravel of different sizes and planted with the species we just saw. Wastewater enters at one end, flows slowly through the gravel and roots, and exits clean at the other end.

The water is never exposed to air; it always circulates below the surface. This has several advantages: it prevents bad odors, stops mosquito proliferation and, above all, protects the system from low temperatures, keeping root and microorganism activity even in winter.

Cleaning is not done by plants alone. A film of bacteria forms on the gravel that decomposes organic matter and transforms ammonia nitrogen into less polluting forms. Plant roots, like tule or carrizo, pump oxygen into this environment, helping those bacteria work better.

The combination of plants and microorganisms is what makes these systems so effective, achieving organic matter removal (BOD and COD) above 90% and nearly eliminating fecal coliforms.

>90%

BOD and COD removal

~100%

Fecal coliform elimination

Subsuperficial

Water flow

Subsurface flow

Water never exposed to air

Bacterial biofilm

Decomposes organic matter

Year-round active

Roots + microbes in winter

Scientific Mechanism

How a Wetland Really Cleans Water

The wetland is not just a "green pond". It is a reactive system where physics, chemistry and biology converge to remove contaminants through sedimentation, adsorption, ionic exchange, phytoremediation and microbial transformation.

Much of the initial cleaning occurs without direct plant intervention, through physicochemical processes acting on dissolved and suspended contaminants.

Sedimentation and Filtration

The wetland design slows water flow. This low velocity allows suspended solid particles to settle by gravity. Additionally, the dense root network and substrate itself act as a physical filter trapping these particles.

Adsorption and Ionic Exchange

This is one of the most important processes for retaining heavy metals and nutrients. The wetland substrate (gravel, sand, clay) and accumulated organic matter have electrically charged surfaces. Dissolved metal ions such as cadmium (Cd²⁺), lead (Pb²⁺) or copper (Cu²⁺) are electrostatically attracted and adhere to these surfaces. This process is known as adsorption.

Ionic Exchange with Zeolites

A particularly efficient case is ionic exchange. Materials such as zeolites (sometimes added to the substrate) have a porous structure with high cation exchange capacity. Contaminating metal ions are captured by the zeolite, which releases non-toxic ions such as sodium (Na⁺) or calcium (Ca²⁺) in exchange. Retention capacity by ionic exchange is strongly influenced by pH; generally, a higher pH (less acidic) favors metal precipitation and adsorption, while a low pH tends to keep them dissolved and mobile.

Precipitation and Coprecipitation

Contaminants can also be removed from water by forming insoluble solid compounds. For example, phosphorus, a key nutrient causing eutrophication, can precipitate by reacting with calcium, iron or aluminum ions present in the water or substrate, forming compounds that deposit at the bottom. Coprecipitation is a similar process where a contaminant ion incorporates into the crystalline structure of another mineral that is precipitating, thus becoming immobilized in the sediment.

💧 The Synergy in Action: The Wetland as a Whole

The artificial wetland functions as an integrated whole. Plants transport oxygen through their tissue (aerenchyma) to the roots, releasing it into the rhizosphere. This creates aerobic microzones that allow nitrifying bacteria activity. At the same time, oxygen-free (anoxic) zones in the substrate are the perfect habitat for denitrifying bacteria.

Contaminants are retained by the substrate (adsorption, precipitation), absorbed by plant roots (rhizofiltration, phytoextraction) and transformed by microorganisms (nitrification, denitrification). This combination of physical, chemical and biological pathways is what makes artificial wetlands such effective and sustainable treatment systems.

🪨

Substrate

Adsorption · Precipitation

🌱

Plants

Rhizofiltration · Phytoextraction

🦠

Microbes

Nitrification · Denitrification

System Architecture

The network is organized as a succession of modules. Not all systems need all layers — selection depends on water quality, flow and treatment goals.

Water treatment flow

Canal / ZanjaPrefiltroGrava gruesaRoca volcánica / TezontleTepojalZeolitaCarbón activadoZona de humedalVegetaciónBiofilm / MicroorganismosCámara de salidaAgua tratadaSistema agrícola / Humedal
B. Canal without biofilter

B. Canal without biofilter

Base cross-section of the canal before installation.

Module cross-section

Module cross-section

Structure with posts, galvanized mesh and filter layers.

Isometric view

Isometric view

Biofilter module in trench with water inlet and outlet.

Longitudinal section A-A'

Longitudinal section A-A'

Complete system: inlet, 4 biofilters, wetland and outlet (10 m).

Structure and materials

Structure and materials

Wooden posts .12×.12×2.5, galvanized wire mesh, 3" screws and oval washers.

Filter materials

Filter materials

Activated carbon, tepojal 1" and tezontle 5" layers in the module.

Measurement survey plan

Measurement survey plan

Total length: 202 m. Main section: 139 m. Ditches A-A', B-B', C, D, E and F.

Benefited ditches

Benefited ditches

Map of the biofilter network in San Gregorio: ditches A-A', B-B', C, D, E and F with biofiltration points.

Filter Media Catalog

12 technical sheets of filter materials. We distinguish between physical filtration, adsorption, ionic exchange, biological support and demonstrated removal.

🌿 How each plant cleans the water

Filtering Vegetation

Six aquatic plant species with documented phytoremediation capacity for heavy metals, nutrients and bacteria in constructed wetlands.

Filtering vegetation gallery

Cola de gato o tule

Typha latifolia

Typhaceae

Habitat

Wetlands, lake and river banks

How it cleans water

One of the most used plants in phytoremediation because its roots actively absorb heavy metal ions like cadmium, arsenic, lead and zinc. It releases oxygen through its roots, immobilizing metals in the substrate. It activates antioxidant enzymes in its leaves to tolerate and accumulate contaminants without dying.

Documented efficiency

Removals above 90% of ammonium and phosphates in wastewater. For iron, lead, copper and zinc, proven phytoremediation potential.

Placement in wetland

Tall species (2-3 m) at the wetland inlet, as a physical barrier and sediment trap.

Carrizo

Arundo donax

Poaceae

Habitat

Moist soils, riverbanks, disturbed areas

How it cleans water

Fast-growing, large plant that accumulates heavy metals in its tissues. Absorbs lead, cadmium and arsenic. For arsenic it can transform and release it as gas (phytovolatilization). Notable efficiency, with 94% to 98% metal removal in industrial waters.

Documented efficiency

94%-98% metal removal in industrial waters. Bioaccumulation factor >1 for lead.

Placement in wetland

Large species (4-6 m) in the subsurface flow zone. Ideal for removing large volumes of contaminants.

Malacote

Hydrocotyle ranunculoides

Araliaceae

Habitat

Freshwater environments, pond and stream edges

How it cleans water

Creeping plant with high absorption capacity for copper, manganese and aluminum. These metal ions accumulate mainly in its roots and leaves. So effective that copper removals of 98.9%, manganese 73% and aluminum 59.4% have been documented.

Documented efficiency

Copper 98.97%, manganese 73.01%, aluminum 59.40%. Phytoremediation capacity for mercury.

Placement in wetland

Creeping species forming dense surface cover. Surface flow zone or edges.

Lentejilla de agua

Lemna minor

Araceae

Habitat

Still waters, ponds, eutrophic lakes

How it cleans water

Pure ionic exchange mechanism. The plant acts as a chemical magnet: heavy metal ions like lead, cadmium, nickel or zinc are exchanged for benign ions already in its biomass, like potassium or calcium. Adsorption occurs in the cell wall and is very efficient for polishing water.

Documented efficiency

Zinc 78.69% in 7 days. Nickel removal at low concentrations. Copper phytoremediation in mining waters.

Placement in wetland

Floating species on polishing ponds or final wetland zone.

Cola de zorro acuática

Myriophyllum aquaticum

Haloragaceae

Habitat

Freshwaters, slow streams, ponds

How it cleans water

Cadmium hyperaccumulator. Its ionic action is dual: part of the metal enters by passive diffusion with transpired water (apoplastic pathway), and another part is actively absorbed via an energy-consuming process (cellular pathway). This combination makes it extremely efficient.

Documented efficiency

Chromium 99.6% in 80 hours. Copper 95.2%, lead 94.28%, mercury 99.19%, zinc 91.91%. >90% for coliforms, phosphate, iron and zinc.

Placement in wetland

Submerged-emergent species in the horizontal flow zone. Maximizes surface area for ionic absorption.

Alcatraz

Zantedeschia aethiopica

Araceae

Habitat

Wetlands, swamps, watercourse edges

How it cleans water

Accumulates metals like lead, copper and chromium in roots, stems, leaves and flowers. The process follows pseudo-second-order kinetics, meaning metal ion adsorption is fast and pH-dependent. Also very effective at reducing fecal bacteria load.

Documented efficiency

Total coliforms 92.12%. Total removal 37% in biodigester pool wastewater.

Placement in wetland

Ornamental species of medium height (0.8-1.2 m) at wetland edge zones.

Estación solar de filtrado
Off-Grid Technology

Solar Filtration Station

A solar-powered station installed directly in the field that filters, oxygenates and irrigates — all without conventional electricity.

1,800 L

every 4 hours of filtration

Oxygenation

of the canal system

Irrigation

solar irrigation station

Research Program

Each biofilter has a data sheet. We compare combinations of materials to discover what works best under the real conditions of Xochimilco.

Experimental filter media matrix

SystemGravaTezontleTepojalZeolitaCarbon
A✓✓✓——
B✓✓✓✓—
C✓✓—✓✓
D✓—✓✓✓

Parameters we measure

Turbidez
pH
Conductividad
Temperatura
Sólidos suspendidos
Nitrógeno
Fósforo
Otros parámetros disponibles

We transform simple mineral materials, solar energy and natural processes into accessible ecological infrastructure.

To recover water, agriculture and biodiversity.

Manual de construcción

Construction Manual

Step-by-step guide for building a biofilter module with locally available materials.

Join the Network

Four ways to support the restoration of water in Xochimilco.

Citizen Donation

Support the construction and maintenance of biofilters in Xochimilco.

Corporate Help

Companies can contribute with materials, funding or volunteer teams.

I am a chinampero

My water is contaminated. I want to apply for a biofilter on my chinampa.

Donate a biofilter

I would like to donate a biofilter to a chinampero.