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Kingsford charcoal briquettes

A briquette (French: [bʁikɛt]; in English also spelled briquet) is a compressed block of coal dust[1] or other combustible biomass material (e.g. charcoal, sawdust, wood chips,[2] peat, or paper) used for fuel and kindling to start a fire. The term is a diminutive derived from the French word brique, meaning brick.

Coal briquettes

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Lignite briquette
Coal briquette

Coal briquettes have long been produced as a means of using up 'small coal', the finely broken coal inevitably produced during the mining process. Otherwise this is difficult to burn as it is hard to arrange adequate airflow through a fire of these small pieces; also such fuel tends to be drawn up and out of the chimney by the draught, giving visible black smoke.

The first briquettes were known as culm bombs and were hand-moulded with a little wet clay as a binder. These could be difficult to burn efficiently, as the unburned clay produced a large ash content, blocking airflow through a grate.

With Victorian developments in engineering, particularly the hydraulic press, it became possible to produce machine-made briquettes with minimal binder content. A tar or pitch binder was used, obtained first from gas making and later from petrochemical sources. These binders burned away completely, making it a low-ash fuel. A proprietary brand of briquettes from the South Wales coalfield was Phurnacite, developed by Idris Jones for Powell Duffryn.[3][4] These were intended to emulate a high-quality anthracite coal, such as that from the Cynheidre measures. This involved blending a mixture of coals from different grades and colliery sources. Phurnacite used the following mix:[4]

Early briquettes were large and brick-shaped.[4] Phurnacite briquettes later adopted a squared oval shape. This regular shape packed well as a good firebed, with plentiful airflow. They are also easy to mechanically feed, allowing the development of automatically controlled heating boilers that could run for days without human intervention.

Charcoal briquettes

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Burning Ogatan

Charcoal briquettes sold for cooking food can include:[5][6]

As a rule of thumb, a charcoal briquette will heat a camping Dutch oven by approximately 25 °F (14 °C), so 20 charcoal briquettes will heat it by 500 °F (280 °C).[7]

East-Asian briquettes

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See also: Yeontan

Home made charcoal briquettes (called tadon [ja]) were found after charcoal production in Japanese history. In the Edo period, polysaccharide extracted from red algae was widely used as a binder. After the imports of steam engines in the Meiji period, coal and clay became major ingredients of Japanese briquettes. These briquettes, rentan [ja] and mametan [ja], were exported to China and Korea. Today, coal briquettes are avoided for their sulfur oxide emission. Charcoal briquettes are still used for traditional or outdoor cooking. Woody flakes such as sawdust or coffee dust are major ingredients of modern mass-consumed briquettes (e.g., Ogatan [ja]).

  • Quick grill briquette
    Quick grill briquette
  • Yeontan, Korean coal briquette
    Yeontan, Korean coal briquette
  • Mametan, Japanese coal briquettes
    Mametan, Japanese coal briquettes
  • Ogatan, Japanese charcoal briquettes made from sawdust
    Ogatan, Japanese charcoal briquettes made from sawdust
  • Solid type Ogatan
    Solid type Ogatan
  • High calo tan, made from coffee dust
    High calo tan, made from coffee dust
  • Tadon and shichirin
    Tadon and shichirin

Use in China

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Fuel briquettes, called mei (coal 煤), sold throughout China

Throughout China, cylindrical briquettes, called "fēng wō méi" (beehive coal 蜂窩煤 / 蜂窝煤) or "Mei" (coal 煤) or "liàn tàn" (kneaded coal 練炭 / 练炭), are used in purpose-built cookers.

The origin of "Mei" is "Rentan" (kneaded coal 練炭) of Japan. Rentan was invented in Japan in the 19th century, and spread to Manchukuo, Korea and China in the first half of the 20th century. There were many Rentan factories in Manchukuo and Pyongyang. Although Rentan went out of use in Japan after the 1970s, it is still popular in China and Vietnam ("than tổ ong" coal).

The cookers are simple, ceramic vessels with metal exteriors. Two types are made: the single, or triple briquette type, the latter holding the briquettes together side by side. These cookers can accommodate a double stack of cylinders. A small fire of tinder is started, upon which the cylinder(s) is placed. When a cylinder is spent, another cylinder is placed on top using special tongs, with the one below igniting it. The fire can be maintained by swapping spent cylinders for fresh ones, and retaining a still-glowing spent cylinder.

Each cylinder lasts for over an hour. These cookers are used to cook, or simmer, pots of tea, eggs, soups, stews, etc. The cylinders are delivered, usually by cart, to businesses, and are very inexpensive.

Peat briquettes

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Peat block

In Ireland, briquettes made from peat, the product of the decomposition of marsh plants in a low-oxygen environment, are a common type of solid fuel, largely replacing sods of raw peat as a domestic fuel. These briquettes consist of shredded peat, compressed to form a virtually smokeless, slow-burning, easily stored and transported fuel. Although often used as the sole fuel for a fire, they are also used to light a coal fire quickly and easily. Peat briquettes are also sometimes used for grilling meats and vegetables as they bring a unique aroma to the food.[8] Bord na Móna is the Irish state owned company in charge of peat, which also handles production of peat briquettes.

Biomass briquettes

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Straw or hay briquettes
Biomass briquette
Main article: Biomass briquettes

[9]Biomass briquettes are made from agricultural waste and are a replacement for fossil fuels such as oil or coal, and can be used to heat boilers in manufacturing plants, and also have applications in developing countries.[9] Biomass briquettes are a technically renewable source of energy and their emissions do not constitute an anthropogenic greenhouse gas, unlike emissions from traditional coal briquettes, as any carbon released was taken directly from the atmosphere in recent history, not sequestered deep in the earth during the carboniferous period as with coal.

Although briquetting is an appropriate technology for the production of renewable energy, its widespreadness is limited. Especially due to the high initial investments and energy consumption of a high-pressure briquetting press. However, manual low-pressure briquetting presses (operating pressure <5 MPa) can represent a relevant alternative, regarding to their ease of use and modest energy consumption for the developing countries.[10]

A number of companies in India have switched from furnace oil to biomass briquettes to save costs on boiler fuels. The use of biomass briquettes is predominant in the southern parts of India, where coal and furnace oil are being replaced by biomass briquettes. A number of units in Maharashtra (India) are also using biomass briquettes as boiler fuel. Use of biomass briquettes can earn Carbon Credits for reducing emissions in the atmosphere. Lanxess India and a few other large companies are supposedly using biomass briquettes for earning Carbon Credits by switching their boiler fuel. Biomass briquettes also provide more calorific value/kg and save around 30–40 percent of boiler fuel costs.

A popular biomass briquette emerging in developed countries takes a waste produce such as sawdust, compresses it and then extrudes it to make a reconstituted log that can replace firewood. It is a similar process to forming a wood pellet but on a larger scale. There are no binders involved in this process. The natural lignin in the wood binds the particles of wood together to form a solid. Burning a wood briquette is far more efficient than burning firewood. Moisture content of a briquette can be as low as 4%, whereas green firewood may be as high as 65%.

For example, parameters of fuel briquettes made by extrusion from sawdust in Ukraine:

Parameter Value
Briquette density, t/m3 1.0–1.2
Heat content, MJ/kg 19.3–20.5
Ash content, % 0.5–1.5

(MJ = Megajoules. 3.6 MJ equals 1 kWh.)

The extrusion production technology of briquettes is the process of extrusion screw wastes (straw, sunflower husks, buckwheat, etc.) or finely shredded wood waste (sawdust) under high pressure when heated from 160 to 350 °C (320 to 662 °F). As shown in the table above the quality of such briquets, especially heat content, is much higher comparing with other methods like using piston presses.

Sawdust briquettes have developed over time with two distinct types: those with holes through the centre, and those that are solid. Both types are classified as briquettes but are formed using different techniques. A solid briquette is manufactured using a piston press that compresses sandwiched layers of sawdust together. Briquettes with a hole are produced with a screw press. The hole is from the screw thread passing through the centre, but it also increases the surface area of the log and aids efficient combustion.

Paper briquettes

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Paper briquettes are the byproduct of a briquettor, which compresses shredded paper material into a small cylindrical form. Briquettors are often sold as add-on systems to existing disintegrator or rotary knife mill shredding systems. The NSA has a maximum particle size regulation for shredded paper material that is passed through a disintegrator or rotary knife mill, which typically does not exceed 3 mm (1⁄8 inch) square.[11] This means that material exiting a disintegrator is the appropriate size for compression into paper briquettes, as opposed to strip-cut shredders which produce long sheets of paper.

After being processed through the disintegrator, paper particles are typically passed through an air system to remove dust and unwanted magnetic materials before being sent into the briquettor. The air system may also be responsible for regulating moisture content in the waste particles, as briquetting works optimally within a certain range of moisture. Studies have shown that the optimal moisture percentage for shredded particles is 18% for paper and 22% for wheat straw.[12]

Environmental impact

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Briquetted paper has many notable benefits, many of which minimize the impact of the paper waste generated by a shredding system. Several manufactures claim up to 90% volume reduction of briquetted paper waste versus traditional shredding. Decreasing the volume of shredded waste allows it to be transported and stored more efficiently, reducing the cost and fuel required in the disposal process.

In addition to the cost savings associated with reducing the volume of waste, paper briquettes are more useful in paper mills to create recycled paper than uncompressed shredded material. Compressed briquettes can also be used as a fuel for starting fires or as an insulating material.

Safety

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Experts generally warn that charcoal burners are not to be used in enclosed environments to heat homes, due to the danger of carbon monoxide poisoning.[13]

See also

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References

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Revisions and contributorsEdit on WikipediaRead on Wikipedia

Briquette

View on Grokipedia
from Grokipedia
A briquette is a compressed block of coal dust, charcoal fines, biomass residues such as sawdust or agricultural waste, or other carbonaceous materials, typically bound with a starch or clay agent and molded into uniform shapes for use as a fuel source in heating, cooking, and industrial applications. Briquettes originated in ancient China around 2,200 years ago with cylindrical coal forms for civilian heating, while modern industrial briquetting processes developed in the mid-19th century using machinery to consolidate fine coal particles otherwise unsuitable for combustion. Production involves grinding raw materials, mixing with binders, extruding or pressing into shapes like cylinders or pillows, and drying to achieve densities that enhance calorific value and handling efficiency over loose fuels. Key types encompass coal briquettes for sustained industrial burning, charcoal briquettes optimized for barbecues due to consistent heat output, and biomass briquettes derived from renewable wastes, which serve as eco-friendly alternatives in developing regions for household energy needs. These fuels provide advantages including waste valorization, reduced transportation volumes, and potentially lower emissions when sourced sustainably, though reliance on traditional charcoal variants has contributed to deforestation in areas like sub-Saharan Africa.

History

Origins and Early Uses

The practice of compressing dust into usable fuel forms originated in ancient over 2,200 years ago, where cylindrical briquettes approximately 16 cm in diameter and 8 cm in height were produced manually for civilian heating and cooking needs. These early efforts addressed practical challenges of handling fine particles, enabling denser, more portable fuel suitable for domestic stoves in resource-limited settings. Similar manual compression techniques for and residues emerged in pre-industrial , particularly in mining regions like , where by the early recipes for "coal balls"—hand-formed lumps of fine bound with clay or —were documented to salvage from rudimentary extraction processes. In the , escalating industrial demands in amplified the need for briquetting due to abundant fine and slack—byproducts deemed too powdery for efficient burning or , leading to significant waste amid resource scarcity. This economic imperative, rather than any environmental considerations, drove innovations to bind these fines into compact blocks, improving combustion uniformity, reducing shipping volumes, and maximizing output from limited seams. The first coal briquette factory opened in in , utilizing mechanical presses to form uniform pieces from waste material, closely mimicking lump coal for furnaces and households. By 1865, reports detailed specialized machines for fuel briquette production, marking the transition from labor-intensive manual methods to semi-mechanized processes tailored for mining outputs in and . These developments prioritized cost savings—such as converting up to 20-30% of colliery waste into viable —and logistical efficiency, with binders like or enabling durable forms that withstood handling without disintegrating. Early adopters in focused on and variants to supplement wood shortages, underscoring briquetting's role in extending finite fossil resources through densification rather than novel paradigms.

Industrialization in the 19th and 20th Centuries

During the 19th century, the rapid expansion of coal mining in Europe, driven by the Industrial Revolution, generated substantial volumes of coal fines and dust as byproducts, which were initially discarded due to handling and combustion inefficiencies. Briquetting processes developed to agglomerate these fines into compact, handleable fuel blocks, enhancing caloric efficiency and reducing waste; by the late 1800s, piston presses compressed mixtures of coal dust with bituminous binders like coal tar pitch, yielding briquettes weighing 0.5 to 10 kg suitable for industrial furnaces and domestic stoves. In Germany, particularly in lignite-rich regions, brown coal briquetting scaled industrially to exploit low-grade ores, with production emphasizing high-pressure extrusion for dense, smokeless fuel that supported steelmaking and power generation amid resource constraints. The advent of starch-based binders further refined the process; in 1897, a for briquetting coal fines with was granted, though European adaptations prioritized derivatives for their strength under heat. This technological evolution causally linked to surging energy demands, as briquettes achieved greater volumetric —up to 20-30% higher than loose fines—facilitating and storage while minimizing dust losses in mining operations exceeding millions of tons annually in the UK and Valley. World War I and II accelerated briquette adoption for fuel , substituting scarce imported ; in Ireland, peat briquetting surged post-1939 amid shortages, with government directives by promoting mechanized production of dried, compressed peat blocks for domestic heating, buffering disruptions from transatlantic supply cuts. Similar efforts in leveraged peatlands for wartime self-sufficiency, though on a smaller scale than Ireland's output, which reached industrial volumes via emerging factories. Post-World War II, East Germany standardized bituminous and brown briquetting from 1946 onward, exporting dense fuels to rebuild economies while optimizing compression ratios for export-grade consistency in developing markets seeking affordable, high-density alternatives to raw .

Post-2000 Developments and Innovations

Since the early 2000s, low-pressure and compaction methods have advanced briquette production from residues, enabling efficient densification of materials like , corn cobs, and agricultural stalks with minimal requirements compared to high-pressure systems. These techniques often incorporate natural binders such as or to enhance structural integrity without synthetic additives, yielding briquettes with densities up to 1.2 g/cm³ and improved handling for transport. A 2025 study on stalks and groundnut husks demonstrated that low-pressure briquetting with as a 10-15% binder ratio produced fuels with fixed carbon content of 18-22% and heating values exceeding 20 MJ/kg, suitable for household and small-scale applications. Similarly, manual low-pressure presses developed for and shavings mixtures with achieved briquette stability at pressures below 5 MPa, reducing production costs by 30-40% relative to mechanical in resource-limited settings. In power generation, post-2010 innovations have focused on co-firing with to optimize efficiency and lower emissions through uniform fuel blending and rates. Research from 2023-2025 indicates that torrefied co-fired at 10-20% ratios with improve flame stability and reduce unburned carbon losses by 15%, while cutting CO2 emissions by up to 25% per unit output due to 's lower carbon intensity. Specific modeling shows that 10% integration in plants can achieve annual CO2 reductions of 276,000 metric tons, attributed to enhanced oxygen utilization and formation control rather than inherent "" . A 2025 review confirmed ' lower and nitrogen oxide precursors versus raw , enabling retrofit compatibility in existing pulverized systems with minimal efficiency penalties under 2%. Adoption in developing countries has accelerated since 2010, with portable briquetting machines converting agricultural wastes like husks and cobs into fuels that offset imported dependencies, where constitutes over 70% of rural energy use. These systems process 50-200 kg/hour of residues into briquettes with 15-20% higher than loose forms, improving economic viability through local sales at 20-30% below prices. Socio-economic assessments in regions like highlight net positive returns from waste-to-briquette operations, with payback periods of 1-2 years via reduced disposal costs and energy access for 2-5 million households annually. In , low-pressure units tailored for and groundnut residues have scaled production to counter fuel scarcity, yielding profitability indices above 1.5 based on 2025 field trials.

Production Methods

Raw Material Preparation and Binders

Raw materials undergo grinding or crushing to achieve uniform particle sizes, typically under 3 mm for and feedstocks, enabling better binder penetration and denser packing during subsequent processing. Smaller particles, such as 0.3-7 mm for , promote adhesion by increasing surface area for contact, reducing voids that compromise structural integrity under physical stress. Uniformity in this range, often below 2 mm via impact milling, minimizes energy inefficiencies in compaction while optimizing combustion stability through consistent . Drying follows grinding to lower moisture content to 8-15%, preventing excessive formation that could briquettes during storage or use and ensuring binder efficacy by avoiding dilution of properties. This step targets equilibrium moisture that balances flowability for mixing without inducing , as overly dry feedstocks resist deformation and yield weaker bonds. Binders are added post-drying to confer cohesion via intermolecular forces, countering disintegration from handling or . Organic binders like , , or —suited to —gelatinize under heat to form flexible matrices with low (often <5%), preserving burn rate while yielding high tensile strength through hydrogen bonding. Inorganic binders such as bentonite, clay, or lime—common for minerals—rely on ionic adhesion for rigidity, boosting compressive strength but elevating ash content (up to 10-30% higher) and potentially slowing ignition due to inert fillers. Typical binder dosages range from 4-10% by weight, with empirical tests showing organic variants like starch increasing mechanical durability by enhancing fixed carbon retention and reducing volatile loss, though excess (>10%) risks incomplete from char formation. Inorganic additions, at similar levels, faster rates for superior drop resistance, as evidenced by negligible impact below 15% incorporation in blended systems, underscoring causal links between binder chemistry and end-use performance like storage longevity over months without fragmentation.

Briquetting Techniques and Equipment

Briquetting techniques primarily involve mechanical compaction to form durable blocks from powdered or fibrous materials, relying on applied to achieve densities typically exceeding 1000 kg/m³ for enhanced handling and properties. The core physics entails plastic deformation and particle interlocking under compressive forces, often augmented by frictional heat generation, which promotes binder activation and reduces without chemical alteration during forming. Three predominant methods—piston or ram pressing, extrusion, and roller pressing—dominate industrial applications, each suited to specific material types and scales. Piston-press systems, ideal for high-density mineral briquettes such as fines, operate in batch or semi-continuous modes where a reciprocating ram forces into a die cavity at pressures ranging from 10 to 150 MPa, yielding cylindrical or cubic shapes with uniform . This method excels in producing briquettes resistant to mechanical degradation due to localized high stress concentrations that exceed yield strengths, though it requires intermittent operation and higher maintenance for die wear. In contrast, screw extrusion employs a continuous helical to convey and compact feedstocks like , generating shear-induced heat up to 150–250°C along the barrel, which partially lignifies organic binders for self-sustaining cohesion without external heating. Output is typically hollow or solid rods that can be cut to length, offering throughput rates of 200–500 kg/hour but demanding precise moisture control (8–12%) to avoid jamming. Roller presses provide scalable, continuous production for both minerals and by passing material between counter-rotating rolls fitted with pockets that imprint final shape, applying forces equivalent to 50–200 MPa through hydraulic or mechanical drives. This technique minimizes energy loss via direct compression, achieving briquette densities of 1200–1800 kg/m³ suitable for large-volume operations, as seen in facilities processing over 10 tons/hour. Process parameters critically influence outcomes: compaction pressures above 100 MPa correlate with improved water resistance by reducing void spaces below 20%, while temperatures from ambient to 200°C enhance fixed carbon retention in semi-carbonized feeds by facilitating volatile escape without full . Optimal retention times in the press (5–30 seconds) balance deformation without excessive spring-back, verifiable through empirical density measurements post-ejection. Equipment has evolved from 19th-century manual lever presses, limited to small-scale output under 1 ton/day, to post-2000 automated lines integrating PLC controls, sensors for real-time pressure monitoring, and conveyor feeds for capacities exceeding 20 tons/hour. Modern systems reduce labor dependency and variability, with hydraulic variants offering adjustable parameters for diverse feedstocks. Energy inputs for briquetting alone range from 40–120 kWh/, dominated by mechanical compression (70–80% of total), varying inversely with material grind size and —finer particles (<2 mm) lower consumption by easing flow.

Types by Material Composition

Mineral-Based Briquettes

Mineral-based briquettes are compressed blocks formed from geological mineral fuels, primarily coal and peat, to create uniform, handleable solid fuels with improved combustion efficiency over raw or powdered forms. These materials originate from ancient sedimentary deposits—coal from compressed plant remains over millions of years and peat from partially decayed vegetation in wetlands—distinguishing them from renewable biomass sources by their non-renewable nature and typically higher energy density. Production generally involves crushing the mineral feedstock into fines, reducing moisture content to facilitate binding, and applying high mechanical pressure, often exceeding 700 atmospheres, to form durable shapes without or with minimal binders. Coal-based variants utilize bituminous, anthracite, or lignite fines that would otherwise be discarded as waste, with processes dating back over 2,200 years in China where cylindrical forms were developed for civilian heating. Binders such as starch, molasses, or pitch are commonly incorporated at 4-10% by weight to enhance cohesion, enabling the briquettes to withstand transport and ignite reliably while minimizing dust emissions. Calorific values range from 20-30 MJ/kg depending on coal rank, supporting applications in metallurgy, power generation, and residential stoves where consistent burn rates reduce ash handling needs compared to lump coal. Peat briquettes derive from milled wetland peat dried to approximately 10% moisture before compression, yielding a fuel with a calorific value of about 15-18 MJ/kg and low sulfur content, suitable for open-hearth burning with minimal smoke. Historically prominent in regions like and East Germany post-1946 for household and industrial use, their production peaked during fuel shortages but has declined due to environmental concerns over habitat disruption, though they offer a transitional fuel with emissions profiles favoring reduced methane release over traditional charcoal in some analyses. Both coal and peat types prioritize energy recovery from fines, but require careful moisture control to prevent spontaneous combustion risks inherent to their mineral composition.

Coal Briquettes

Coal briquettes are produced by compressing fine particles of anthracite or bituminous coal, often derived from mining waste, using binders such as tar, starch, or molasses to create durable, uniform fuel units. These fines, which have a gross calorific value of 8-24 MJ/kg in loose form, are agglomerated to achieve briquette energy densities typically ranging from 20 to 30 MJ/kg, matching or exceeding that of standard lump coal. Briquetting addresses inefficiencies in loose coal handling by forming stable shapes that resist breakage, enabling easier storage, shipping, and reduced dust generation—often cutting emissions and losses by more than 50% compared to unprocessed fines. This results in lower transportation costs and minimal material degradation over time, making coal briquettes economically viable for bulk distribution where loose coal incurs high spillage and handling expenses. In coal-rich areas like China, briquettes continue to power industrial boilers and stoker systems, leveraging local fines for cost-effective energy production despite policies targeting small-scale coal units. Their consistent combustion supports reliable baseload generation, outperforming intermittent renewables like wind and solar, which require supplementary storage for steady output. This dependability, combined with high energy density, sustains their role in applications demanding uninterrupted heat or power.

Peat Briquettes

Peat briquettes consist of partially decomposed organic matter harvested from wetland bogs, processed into compact fuel blocks that serve as a transitional energy source between raw biomass and more geologically matured coal. Peat is milled into fine particles after extraction, dried to a moisture content below 15% through natural field exposure or mechanical means, and then formed under low pressure without extensive binders, yielding blocks with a gross calorific value typically ranging from 15 to 20 MJ/kg depending on ash and residual moisture levels. This process leverages peat's natural fibrous composition for structural integrity, though it retains inherent variability from bog-specific organic content. Commercial production of peat briquettes emerged prominently in Northern Europe, particularly Ireland, where Bord na Móna initiated full-scale operations in the late 1950s to early 1960s, starting at facilities like Derrinlough in 1960 and Croghan in 1961–1962, to supply home heating in rural areas with limited alternatives. These briquettes exhibit lower sulfur content, around 0.2–0.5%, compared to many coal variants exceeding 1%, reducing emissions of sulfur oxides during combustion and making them preferable for enclosed stoves in domestic settings. Their abundance in bog-rich regions supports local self-sufficiency, as extraction relies on accessible surface deposits rather than deep mining. Despite advantages in availability, peat briquettes demonstrate empirical limitations in combustion dynamics, including extended ignition times attributable to their fibrous, low-density structure, which promotes slower initial pyrolysis and heat buildup compared to denser mineral fuels. This results in prolonged smoldering burns lasting up to 7 hours, suitable for overnight or sustained rural heating but less ideal for rapid-start applications, with overall efficiency tied to careful stove design to mitigate incomplete combustion and tar formation.

Carbonized Briquettes

Carbonized briquettes are fuel blocks formed from biomass or other organic materials that have undergone carbonization, a pyrolysis process involving heating in the absence of oxygen to drive off volatile compounds and produce a carbon-rich char. This results in a product with higher fixed carbon content, typically 70-85%, compared to non-carbonized biomass briquettes. The process enhances energy density, with calorific values often ranging from 25 to 30 MJ/kg, enabling cleaner combustion with reduced smoke and ash production relative to raw biomass fuels. Production of carbonized briquettes generally involves two sequences: first carbonizing the raw material into fines or dust, then mixing with a binder such as starch or molasses, and compressing under high pressure using a briquetting machine; alternatively, raw biomass is briquetted and subsequently carbonized in a furnace to achieve charring. Binders constitute 4-8% of the mixture to ensure structural integrity during handling and burning, while the carbonization step, conducted at temperatures of 400-600°C, minimizes moisture and volatiles to below 10% and 20%, respectively. This method contrasts with mineral-based briquettes like coal, as carbonized variants derive from renewable sources such as sawdust, agricultural residues, or forestry waste, promoting resource efficiency. Key advantages include superior ignition and sustained burn times, making them suitable for household cooking and industrial heating, though they require careful control to avoid over-carbonization, which can reduce yield to 25-35% of input mass. Unlike lump charcoal, carbonized briquettes offer uniformity in shape and size, facilitating automated feeding in stoves and grills, and often exhibit lower emissions of particulate matter due to the pre-pyrolysis. Environmental assessments indicate that, when sourced sustainably, they contribute to waste valorization, diverting materials like charcoal dust from landfills.

Charcoal Briquettes

Charcoal briquettes consist of pulverized charcoal derived from the pyrolysis of wood, mixed with binders such as starch and shaped into uniform forms to ensure consistent burning for applications like grilling. The production process involves carbonizing wood biomass in low-oxygen environments to yield charcoal, followed by grinding into fines, blending with 4-6% starch binder, and pressing under high pressure using screw or hydraulic machines. This method produces briquettes with a calorific value typically ranging from 25 to 28 MJ/kg and low ash content under 5%, facilitating steady combustion without excessive residue. In the barbecue sector, charcoal briquettes hold market dominance due to their uniform size and shape, which promote even heat distribution and ease of use over lump charcoal. Hardwood-based variants account for approximately 69% of the briquette market share as of 2024, driven by demand for authentic grilling experiences. Additives like , incorporated at low levels (around 1-2%), aid in faster ignition while complying with U.S. manufacturing practices outlined in industry patents and standards for processing efficiency. These enhancements counter perceptions of briquettes as inefficient by enabling reliable lighting and sustained burn times exceeding 1-2 hours per batch. Economically, briquetting recycles charcoal fines—generated at 10-20% during handling and transport—extending overall yield from raw wood by 20-30% and reducing waste. When sourced from managed forestry residues, this approach minimizes reliance on virgin timber, challenging claims of inherent deforestation links by improving resource efficiency and supporting sustainable biomass utilization.

Biomass and Waste-Derived Briquettes

Biomass and waste-derived briquettes consist of compressed organic materials sourced from agricultural residues, forestry byproducts, and municipal wastes, serving as renewable fuels with energy densities of 15-20 MJ/kg. Production involves shredding or grinding feedstocks to uniform particle sizes, drying to 8-15% moisture content, optional incorporation of natural binders such as starch or molasses at 5-10% by weight, and densification via mechanical presses exerting pressures of 100-200 MPa. These processes enhance volumetric energy content by factors of 3-6 compared to loose biomass, facilitating efficient storage, transport, and combustion. Combustion of these briquettes yields lower emissions than equivalent fossil fuels; for instance, bio-coal variants exhibit reduced CO2, CH4, and pollutant outputs across ignition, high-, and low-power phases, attributed to lower volatile matter and sulfur content below 0.5%. Life cycle analyses of biomass briquette heating systems demonstrate potential CO2-equivalent reductions of 35,679 tons annually in scaled applications, while minimizing open burning of residues that contributes to particulate and black carbon pollution. However, ash content varies from 2-10% depending on feedstock, necessitating management to avoid slagging in boilers.

Agricultural and Forestry Residue Briquettes

Agricultural residues such as wheat straw, rice husks, sugarcane bagasse, corn stover, sorghum stalks, and groundnut husks, alongside forestry wastes like sawdust, bark, and wood chips, form the basis for these briquettes, which repurpose materials comprising up to 20-30% of global crop yields. Briquetting these low-bulk-density feeds (50-150 kg/m³) into forms with densities exceeding 600 kg/m³ improves handling and calorific efficiency, with examples using cow dung as a binder achieving stable structures suitable for low-pressure extrusion. In practice, mixtures of wheat husk, babool stalk, sawdust, and tea leaves at varying ratios produce briquettes with heating values of 15-18 MJ/kg and reduced landfill diversion needs.

Paper and Municipal Waste Briquettes

Waste paper, cardboard, and municipal organic fractions including yard trimmings and food scraps are compacted into briquettes, often binder-free due to inherent fiber adhesion, yielding products with burn durations 30-50% longer than loose paper but with combustion powers 20-30% below in water-boiling tests. Mixtures such as 80% cardboard with 20% sawdust or waste paper with coconut husk demonstrate durability and heating values around 12-16 MJ/kg, promoting waste diversion from landfills where paper constitutes 20-40% of volume in developing regions. Optimization studies confirm that paper-charcoal-sawdust blends enhance combustion stability, though high chlorine from inks may elevate HCl emissions if not pre-treated.

Regional Variants (e.g., East-Asian Briquettes)

In Thailand, briquettes from madan wood waste or agricultural residues like cassava roots, rice straw, and bagasse achieve calorific values up to 6,622 cal/g (approximately 27.7 MJ/kg), utilizing carbonization followed by binder-assisted pressing for household and industrial use. Palm kernel shell briquettes, prevalent in Southeast Asia, exhibit low moisture (under 5%), high fixed carbon (70-80%), and fast ignition rates, with gross calorific values exceeding 25 MJ/kg. These variants leverage abundant tropical wastes, reducing deforestation pressures, though regional adoption varies due to competition from imported pellets in Japan and South Korea.

Agricultural and Forestry Residue Briquettes

Agricultural and forestry residue briquettes utilize lignocellulosic byproducts from farming and logging, such as crop stalks, husks, and sawdust, to form dense fuel blocks via compression with or without heat. These materials, including corn cobs, groundnut shells, rice husks, wheat straw, cocoa shells, palm kernel shells, and forestry sawdust, provide abundant, low-cost feedstocks in agrarian regions. The inherent lignin content in these residues serves as a natural binder, often eliminating the need for additives during piston-press or screw extrusion briquetting at pressures of 100-200 MPa and temperatures up to 200°C. Torrefaction pretreatment, involving mild pyrolysis at 200-300°C in an oxygen-limited environment, upgrades these residues by increasing carbon content, energy density, and hydrophobicity while reducing moisture and volatiles. This process yields briquettes with higher fixed carbon (up to 25-30%) and improved handling, though it slightly elevates production costs. Untorrefied briquettes from such residues typically exhibit gross calorific values of 15-18 MJ/kg, rising to 20-22 MJ/kg post-torrefaction due to hemicellulose decomposition and densification. Compared to open burning of loose residues, which releases high levels of particulate matter and incomplete combustion products, briquette combustion achieves more efficient oxidation, reducing particulate emissions by factors of 2-5 and greenhouse gases through contained burning. A 2022 study on Pinus residue briquettes reported 74% lower GHG emissions versus traditional wood burning, attributable to uniform airflow and reduced volatilization losses. In developing contexts, small-scale briquetting from crop wastes diverts residues from field burning—prevalent in regions like South Asia and sub-Saharan Africa—while generating supplemental rural income; for instance, Nigerian farmers have monetized rice husks and groundnut shells into sellable fuel, offsetting disposal costs. This approach recovers embedded energy (e.g., 14-16 MJ/kg in raw straw) that would otherwise dissipate unused, though briquette durability varies with residue moisture (ideally <15%) and particle size (2-10 mm).

Paper and Municipal Waste Briquettes

Briquettes produced from recycled paper and cardboard are typically manufactured by shredding the materials into small fibers, mixing with binders such as starch or other organic agents to improve durability, and compressing under pressure without high-heat carbonization. Municipal waste variants incorporate additional combustible fractions like sorted plastics or textile residues from composting rejects, forming dense blocks suitable for volume reduction in waste management. These processes yield briquettes with higher heating values of 12-17 MJ/kg for paper-dominant compositions, influenced by de-inking and binder ratios. Combustion properties reveal inconsistencies, including ash contents of 6-12% that form clinkers and reduce heat transfer efficiency, restricting applications to supplemental boiler feeds or co-firing rather than standalone fuels. Untreated paper briquettes risk expansion and structural weakening upon moisture exposure due to fiber hygroscopicity, demanding sealed storage to prevent disintegration during use. Chlorine from inks and coatings can generate hydrochloric acid emissions, promoting boiler corrosion; pretreatment via de-inking flotation or alkali washing mitigates this by removing up to 90% of halogens. In resource-constrained settings, such as parts of Africa, these briquettes power simple stoves for cooking, offering a low-cost alternative that compacts waste volumes by factors of 5-10 while utilizing non-recyclable fractions otherwise destined for open dumping. Empirical assessments confirm their role in diverting landfill-bound organics, though inconsistent ignition and higher smoke from volatiles limit widespread adoption without additives.

Regional Variants (e.g., East-Asian Briquettes)

In China, honeycomb coal briquettes feature multiple ventilation holes in a hexagonal pattern to facilitate controlled airflow and efficient combustion during household cooking and heating. These briquettes, formed from coal fines such as bituminous or anthracite bound with binders like clay, originated as a practical fuel for densely populated areas, with production scaling in rural and urban regions by the late 20th century. The design reduces incomplete burning compared to loose coal, though emissions studies indicate persistent particulate and trace element releases during use. Blends incorporating anthracite coal with rice husk in Chinese briquettes combine mineral and biomass components to achieve lower emissions than pure coal variants, leveraging rice husk's availability in agricultural regions for dual fuel properties like improved ignition and reduced sulfur output. Research on coal-rice husk composites demonstrates enhanced physical stability and combustion efficiency, with biocoal formulations showing decreased environmental pollution potential relative to unblended coal. Such mixes support localized energy needs in high-density populations by utilizing waste biomass to supplement scarce high-grade coal. In Korea, yeontan briquettes consist of anthracite coal dust compressed into 3.5 kg cylinders with 19 vertical holes for oxygenation, enabling steady, prolonged burning suited to urban heating from the mid-1950s through the 1980s. Introduced under Japanese influence, these served as a firewood alternative in apartments, though their decline followed natural gas expansion. Japanese regional variants include mametan, oval coal briquettes pressed for use in traditional heaters like kotatsu, providing compact fuel for indoor warmth. Complementing these, ogatan briquettes derive from compressed hardwood sawdust carbonized without additives, yielding square forms with high calorific value and minimal ash for grilling applications. Often sourced from fruit tree residues, ogatan offers extended burn times over lump charcoal, adapting biomass waste into efficient, low-smoke fuel.

Applications and Uses

Household and Cooking Applications

Briquettes serve as a primary cooking fuel in many energy-poor households across Africa and Asia, where unreliable electricity grids and subsidized electric alternatives often fail to deliver consistent access. In these regions, briquette stoves provide a practical solution for daily meal preparation, utilizing compressed fuels derived from biomass or coal residues that burn steadily for 2-3 hours per load. This duration suits typical household cooking needs, enabling efficient boiling, frying, and baking without frequent refueling. Stoves designed specifically for briquettes enhance combustion efficiency through improved airflow and fuel density, reducing required fuel volume by up to 50% compared to loose logs while shortening cook times and minimizing smoke release during use. Briquettes' higher density—often exceeding that of natural wood—yields 15% more heat energy per unit mass, allowing households to achieve similar thermal output with less material. In practice, this translates to lower procurement and handling demands, particularly beneficial in rural settings where fuel transport is labor-intensive. Economic analyses indicate that switching to briquettes can decrease household fuel expenditures, with studies in Ghana reporting enhanced financial well-being through reduced costs relative to traditional firewood. Adaptations such as hexagonal shapes promote stable stacking in storage, preventing collapses in compact rural homes and facilitating better airflow for uniform burning. These design features, combined with local production from agricultural wastes, make briquettes accessible and cost-effective for widespread adoption in developing economies.

Industrial and Commercial Applications

Biomass and coal briquettes find extensive use in industrial boilers for steam generation, drying processes, and gasification, where their higher energy density—typically 18-22 MJ/kg compared to loose biomass—enables efficient storage, transport, and combustion for sustained operations that support baseload energy needs beyond the intermittency limitations of renewables. In sectors such as brick kilns and textiles, they substitute for traditional fuels in firing and bleaching applications, with biomass variants often blended to replace portions of coal while maintaining thermal output. Charcoal briquettes dominate commercial grilling in restaurants and BBQ supply chains, valued for uniform size, long burn times exceeding 2-3 hours, and low-ash production that ensures consistent heat and minimal flavor interference in high-volume cooking. Their compressed form allows waste heat recovery in commercial setups, optimizing energy use in food service establishments where demand for stable, high-temperature fuels persists. In regions like India, industrial adoption of locally produced briquettes in kilns and power plants has supported efforts to curb coal imports, with domestic coal production rising to 1,047.67 million tonnes in fiscal year 2024-2025 amid substitution strategies that leverage briquettes' dispatchable qualities for reliable industrial heat. This approach addresses density and handling advantages, filling gaps in energy reliability where variable sources underperform.

Power Generation and Co-Firing

Biomass briquettes serve as a dispatchable fuel in power generation, offering baseload stability in electricity grids where intermittent renewables like solar and wind require complementary reliable sources. In coal-fired power plants, co-firing with briquettes derived from agricultural or forestry residues enables gradual decarbonization without full infrastructure overhauls, maintaining grid reliability through consistent combustion characteristics. Typical co-firing ratios reach up to 20% biomass by energy input, as demonstrated in operational analyses where higher shares increase levelized cost of electricity by 19.1% but enhance fuel flexibility. Briquettes improve ignition in blended fuels due to their lower ignition temperatures compared to coal alone, facilitating easier startup and reducing unburned carbon losses, while their alkali content can mitigate slag formation on boiler grates by altering ash fusion behaviors in trials. Dedicated biomass power plants, particularly in , utilize forestry residue briquettes for steady output, with medium-scale facilities (10-50 MW electrical) achieving efficiencies of 25-35% through optimized combustion of densified fuels. For instance, Swedish plants processing bark and wood chip briquettes deliver 7.5-145 MW thermal-electrical capacity, leveraging local residues to support district heating and power without reliance on variable weather patterns. Compared to wood pellets, briquettes exhibit lower capital and operational expenditures in production due to simpler machinery requirements and reduced electricity use per ton, alongside comparable bulk densities that minimize transport costs over long distances. This positions briquettes as a cost-effective intermediary for scaling biomass in grids transitioning from fossil fuels, prioritizing energy security over subsidized intermittency.

Environmental and Resource Impacts

Efficiency Gains and Waste Utilization

Briquetting densifies loose biomass, increasing bulk density from 0.1–0.2 g/cm³ to 1.2 g/cm³ or higher, which elevates volumetric energy density by factors of 6–12 times compared to uncompressed forms. This enhancement streamlines storage, reduces transportation volumes, and cuts logistics costs, proving especially advantageous in remote regions where fuel supply chains face infrastructural constraints. By compacting agricultural and forestry residues such as straw, husks, and sawdust—materials often left to decompose or burned openly—briquetting extracts usable fuel value, diverting waste from low-efficiency disposal and mitigating associated environmental hazards like uncontrolled emissions from field burning. Processes achieve high material yields, transforming residues into stable, transportable fuel blocks that maximize resource recovery without significant losses during production. In coal and peat operations, briquetting reclaims fines discarded as waste, which retain substantial energy potential of 8–24 MJ/kg, thereby boosting overall output from extracted deposits and extending effective resource longevity by recovering otherwise uneconomical fractions. This approach prioritizes value extraction from byproducts, countering depletion concerns through efficient utilization rather than expanded raw extraction.

Emissions Profiles and Comparisons to Loose Fuels

Briquettes exhibit lower emissions of fine particulate matter (PM2.5) and (CO) during combustion compared to loose fuels such as , attributable to their densified structure promoting more complete and controlled burning, especially in optimized . For instance, biomass briquetting has demonstrated a potential reduction of 53% in PM2.5 emissions from residential burning relative to loose . In advanced stove designs, such as those meeting Ecodesign criteria, PM emission factors from certain briquettes can decrease by over 80% compared to traditional open combustion of loose fuels. CO emissions similarly decline, with observed reductions of around 30% when substituting briquettes for in heating and cooking applications. Coal-based briquettes typically deliver higher calorific values than counterparts, often exceeding 20-25 MJ/kg due to inherent content, enabling greater heat output per unit mass while maintaining comparable or lower dispersion than loose , where fine scattering leads to inefficient burns and fugitive releases. Sulfur and emissions from coal briquettes, stemming from mineral impurities, can be mitigated through additives such as calcium-based sorbents, achieving retention rates that surpass those of unbound loose coal under similar conditions. This controlled formulation reduces overall and outputs by facilitating staged and limiting unburned hydrocarbon escape. From a lifecycle perspective, sourced from annual crops or agricultural residues achieve near carbon-neutral status, as CO2 emissions from are balanced by photosynthetic uptake during regrowth, provided no net depletion of stocks occurs; this is substantiated by life cycle assessments showing net emissions approaching zero under sustainable harvest assumptions. Verification relies on standardized methodologies like ISO 14040 for environmental impact evaluation, rather than unsubstantiated claims, distinguishing verifiable renewability from non-annual sources like old-growth wood. briquettes, by contrast, entail net positive fossil carbon releases without offsetting sequestration.

Criticisms: Sustainability Claims and Lifecycle Drawbacks

Despite claims of renewability, sourcing for briquette production carries risks of and degradation when scaled beyond agricultural or residues, as increased demand incentivizes whole-tree harvesting or expansion into natural forests. In tropical regions, production—often adapted to briquettes—contributes to rather than outright in most cases, but accounts for less than 7% of total tropical while accelerating and . In , briquette-related activities have driven a 15% decline in national and over 37% loss in woodland areas, exacerbating . Peat-based briquettes, promoted in some regions as low-cost fuels, release rapidly stored carbon upon extraction and combustion, undermining sustainability assertions. Peat extraction disrupts peatlands, emitting significant greenhouse gases including CO2, N2O, and CH4, with lifecycle CO2 intensity reaching 106 g CO2/MJ—higher than coal's 94.6 g CO2/MJ. In Ireland and Estonia, historical peat mining has led to ongoing emissions from drained bogs, equivalent to millions of metric tons of CO2 annually, as rewetting efforts lag behind extraction legacies. Lifecycle assessments reveal that production processes, particularly drying and grinding of low-density biomass wastes, impose energy penalties that offset calorific gains. Forced drying alone demands up to 5 MJ/kg of thermal input, often from fossil-derived propane or torrefaction gases, while grinding energy varies by biomass type and moisture, increasing overall non-renewable energy dependence. Studies indicate briquette lifecycles contribute to global warming potential and non-renewable resource depletion across multiple impact categories, with net energy ratios sometimes falling below parity for inefficient feedstocks. Sustainability narratives often overlook these inputs, equating to carbon-neutral alternatives despite dependencies on land competition and transport emissions that mirror scales at high volumes. Large-scale deployment requires vast acreage—rivaling footprints—potentially diverting land from production and amplifying indirect emissions, as critiqued in LCAs showing overstated neutrality assumptions. Policy preferences for intermittent renewables further distort by sidelining briquettes' dispatchable role in coal-reliant grids, while subsidies mask lifecycle inefficiencies.

Economic and Market Dynamics

Production and Supply Chain Costs

Feedstock acquisition represents the largest component of briquette production costs, often comprising 40-60% of total expenses due to variability in sourcing agricultural residues, , or fines, with prices for residues typically ranging from $20-50 per metric in regions with abundant waste streams. Additional processing costs, including binders such as or (added at 5-10% by weight) and mechanical pressing, contribute $10-20 per , as binders alone can cost $5-20 per depending on type and quantity required for structural integrity. Economies of scale significantly reduce unit costs in briquette ; small-scale operations (e.g., under 1 ton/hour capacity) incur total production expenses of approximately €35-40 per ton (38−44),whilelargerfacilitiesachieve€15−20perton(38-44), while larger facilities achieve €15-20 per ton (16-22) through higher throughput and amortized machinery maintenance. This scalability enables competitive pricing equivalent to $0.05-0.10 per kWh in energy terms for small plants, often undercutting imported fuels in landlocked or import-dependent economies where inflate alternatives. Raw material price volatility poses risks to stability, driven by seasonal agricultural yields or competing industrial demands, though producers mitigate this via long-term waste supply contracts that lock in low-cost residues and buffer against fluctuations in oil or loose wood prices. Such hedging strategies enhance predictability without relying on subsidies, aligning costs with market dynamics rather than fixed interventions.

Benefits for Developing Economies and Employment

Briquette production in developing economies supports local employment, particularly in rural areas where small-scale plants typically employ around 10 workers to handle processing of agricultural residues into fuel. These operations leverage abundant biomass feedstocks, creating jobs in collection, densification, and distribution without requiring extensive infrastructure. In India, government initiatives under the Ministry of New and Renewable Energy promote such plants, converting crop residues like rice straw and wheat husk into briquettes, which provides farmers with supplementary income from otherwise discarded materials as of 2025. By enabling sales of to briquette manufacturers, these activities increase farmer revenues and reduce open burning, fostering economic resilience in agrarian communities. Briquettes address fuel in off-grid rural households by supplying efficient, low-cost solid fuels derived from local sources, diminishing dependence on or dung that exacerbate risks and time burdens for collection. This localized production model promotes energy access independent of centralized grids, supporting small-scale economic activities like cooking and heating that underpin daily livelihoods. Export-oriented briquette manufacturing in nations such as enhances GDP through value-added processing of raw commodities like and shells, avoiding the pitfalls of unprocessed resource exports. In 2023, Indonesia's briquette exports alone totaled $38.8 billion, generating foreign exchange and sustaining related industries. Similarly, in , briquette production from forestry residues contributes to trade balances by upgrading low-value materials into higher-margin fuels, bolstering national income and employment in processing chains. These dynamics prioritize bottom-up enterprise, countering reliance on volatile shipments and aligning with alleviation via scalable, resource-efficient industries. The global fuel briquette market, spanning , , and types, exhibits robust growth projections into the 2030s, with segments collectively valued at several billion dollars and expanding due to rising demand for cost-effective solid fuels in developing regions. The briquette sector is anticipated to increase from USD 0.96 billion in 2025 to USD 1.44 billion by 2030, at a (CAGR) of 8.39%, propelled by agricultural waste conversion in . Coal briquettes are forecasted to grow from USD 3.0 billion in 2023 to USD 4.6 billion by 2030, at a CAGR of approximately 6%, supported by their role in stable supply chains. briquettes, meanwhile, are projected to rise from USD 2.71 billion in 2024 to USD 4.53 billion by 2030, with a CAGR of 8.79%, driven by household and commercial cooking needs in and where resources abound and infrastructure limits liquid alternatives. Briquettes compete favorably with pellets on , often costing less per —typically in the range of $100-150 for variants—while pellets command premiums due to uniform and processing, though briquettes' variability can affect consistency. For example, peat briquettes in Poland typically range from 1200 to 1800 PLN per ton for pallets of approximately 960-1000 kg, varying by producer, quality, purchase volume, and region; retail prices in smaller packages are higher at about 1.5-2.5 PLN/kg, with prices fluctuating seasonally and in response to fuel market conditions. Relative to LPG for cooking, briquettes provide economic with lower initial investment and simpler, non-pressurized storage that mitigates risks, despite LPG's edge in and reduced cooking times. In power applications, faces barriers from high and grid unreliability in emerging markets, preserving briquettes' viability where intermittent renewables falter. In the 2020s, mandates like India's 5% co-firing requirement for plants, effective from 2021 and revised in 2023, have stimulated biomass briquette demand for utility-scale blending, enhancing utilization of local residues without full overhauls. briquettes, however, persist in regions emphasizing , benefiting from compact storage and transport that buffer against supply disruptions, even as global decarbonization pressures intensify. This duality underscores briquettes' resilience against overhyped alternatives, prioritizing affordability and reliability over idealized uniformity or zero-emission ideals unsubstantiated by current scalability in low-income contexts.

Safety, Health, and Regulatory Considerations

Combustion and Handling Risks

Coal-based briquettes can undergo during storage if content exceeds safe thresholds, typically promoting oxidation and accumulation in improperly dried or exposed stockpiles; however, this is rare for well-manufactured products with below 15-20%, as densification limits internal oxygen compared to loose fines. levels above 20% exacerbate propensity in low-rank coals by enabling microbial activity and chemical reactions leading to self-heating, but standard production processes incorporate to mitigate this. During combustion, briquettes demonstrate reduced fire spread rates relative to loose fuels due to their uniform shape and lower surface area exposure, enabling more predictable ignition and burnout phases that aid in fire management; this structural advantage stems from compression, which sustains steady oxygen access without rapid . Nonetheless, indoor use without adequate ventilation poses risks of carbon monoxide (CO) accumulation from incomplete combustion, with documented cases of fatalities from briquette burning in enclosed spaces generating lethal CO concentrations exceeding 0.1% by volume. Handling risks for primarily involve potential generation if mechanical durability is compromised, though and binding reduce fine particulates that could ignite in mixtures; intact briquettes produce negligible clouds during or loading, minimizing hazards prevalent in powdery feedstocks. International standards such as ISO 17831-2 prescribe mechanical durability testing, including resistance to tumbling and compression, ensuring briquettes withstand handling forces up to 98% integrity retention post-test for commercial grades. Modern extruded variants exhibit enhanced crush resistance, often doubling that of traditional molded types through optimized binders and pressures exceeding 100 MPa.

Health Effects from Emissions and Production

Combustion of biomass briquettes generally emits lower levels of polycyclic aromatic hydrocarbons (PAHs) compared to loose wood fuels due to more efficient burning, though incomplete combustion still releases PAHs linked to respiratory irritation and carcinogenic risks. Studies indicate that particulate matter-bound PAHs, such as chrysene and benzopyrene, persist in briquette emissions, contributing to cytotoxicity in lung cells, albeit at reduced concentrations relative to traditional open fires. For coal-based briquettes in unvented indoor settings, benzene concentrations can reach elevated levels—often exceeding safe thresholds—exacerbating risks of acute inhalation toxicity and long-term leukemia development, with emissions profiles showing higher volatility of aromatics than biomass variants. In briquette production, workers face respiratory hazards from dust generated during grinding and mixing, including fine particulate matter and potential crystalline silica contaminants from binders or raw materials, which correlate with reduced lung function and increased (COPD) incidence. Mitigation via like masks substantially lowers these risks, though inconsistent adoption in informal sectors persists. processes for charcoal briquettes produce fewer fumes than traditional open-pit , reducing ambient exposure to volatile organic compounds and particulates, but residual emissions still pose irritation risks without proper ventilation. Epidemiological data reveal that switching to briquette stoves yields 20-40% fewer COPD cases compared to traditional loose fuels, attributed to diminished household air pollution exposure, yet residual toxins prevent complete risk elimination, particularly in poorly ventilated homes. A randomized intervention in rural demonstrated a 72% reduction in COPD odds (OR 0.28) with fuel upgrades including briquettes, underscoring benefits while highlighting ongoing vulnerabilities from incomplete combustion byproducts. These gains do not equate to zero burden, as sustained exposure to even lowered PAH and particulate levels correlates with persistent function declines.

Regulatory Standards and Innovations for Mitigation

Regulatory standards for fuel briquettes primarily target quality and emission precursors through limits on , moisture, and content in feedstocks, with enforcement varying by region to balance environmental goals and practical use. In the , solid standards under ISO 17225 classify briquettes by content (e.g., maximum 1% for premium wood pellets, extended to analogous briquette grades) and require low volatile emissions, indirectly capping via feedstock selection to below 0.3% in tested formulations. These parameters drive production toward low- agricultural residues, as higher (>10%) correlates with incomplete and particulate release. In , briquette guidelines emphasize compliance with emission standards, where levels in optimized formulations remain under 0.06%, achieved through clay or pulp binders that minimize additive . Such limits, often below 1% for coal-derived variants, have spurred binder shifts away from high- synthetics since 2020. Innovations in mitigation focus on additives and process enhancements to reduce NOx and other pollutants without prohibitive costs. Potassium-containing additives in coal briquettes, refined through 2020s research, enhance char reactivity and achieve NOx reductions by promoting selective non-catalytic reduction during combustion. Coke-based metal additives (e.g., Fe, Co, Ni, Cu) incorporated at low loadings similarly cut NO emissions by altering gasification kinetics, with lab tests showing up to 30% efficiency gains in regenerator-like conditions adaptable to household stoves. Post-2020 binder innovations, such as potato peeling extracts and non-edible starch alternatives, replace traditional cassava starch, yielding briquettes with improved durability and lower emissions due to reduced volatile release. These natural options maintain mechanical integrity while complying with ash limits under 10%. Global regulatory variances reflect development priorities, with stricter standards offsetting laxer local enforcement in emerging markets. In developing economies, minimal and ash mandates enable widespread briquette adoption for affordable heating, as seen in urban household preferences for low-cost, consistent fuels over loose . International relies on ASTM methods for physical testing, including durability (e.g., ASAE S269.4 tumble tests) and shatter index (ASTM D440-86), ensuring export-grade briquettes withstand handling without excessive fines that elevate emissions. For safety, 2025-era detectors with integrated temperature/humidity sensors provide real-time alerts for briquette risks, plugging into outlets for broad compatibility beyond electric appliances. This pragmatic approach prioritizes verifiable performance over uniform bans, fostering innovation in additive tech and monitoring.

References

  1. https://fuel-alternatives.com/briquettes-history-and-production-process/
  2. https://www.lidsen.com/journals/aeer/aeer-04-03-040
  3. https://maxtonco.com/things-you-need-to-know-about-coal-briquetting/
  4. http://www.biomass-briquette.com/the-history-of-briquette.html
  5. https://recyclinginside.com/recycling-technology/volume-reduction-technology/briquetting-a-growing-trend-for-domestic-fuel/
  6. https://briquettesolution.com/bio-and-fuel-briquette-calorific-value-biomass-sawdust-coal-charcoal/
  7. https://www.arselancoco.com/introduction-to-briquettes-types-materials-and-production-process/
  8. https://buyofuel.com/blogs/what-is-the-composition-of-biomass-briquettes/
  9. https://19january2017snapshot.epa.gov/sites/production/files/2014-08/documents/QA_Webinar_3.5.14.pdf
  10. http://ageconsearch.umn.edu/record/257959/files/H047991.pdf
  11. https://pmc.ncbi.nlm.nih.gov/articles/PMC9404349/
  12. https://www.dayang-briquettepress.com/news/history-of-the-coal-charcoal-briquette-machine-19262373.html
  13. https://www.ageofinvention.xyz/p/age-of-invention-all-fired-up
  14. https://news.prairiepublic.org/main-street/2019-04-12/coal-briquettes
  15. https://www.cia.gov/readingroom/docs/CIA-RDP79T01049A000500020001-0.pdf
  16. https://patents.google.com/patent/US7892302B2/en
  17. https://www.scribd.com/document/219936580/Coal-Briquetting-Technology
  18. https://www.ispatguru.com/briquetting-process-and-use-of-binders/
  19. https://irelandenergy2050.ie/past/peat/
  20. https://valaalta.co/blogs/writings/irelands-forgotten-fossil-fuel
  21. https://link.springer.com/article/10.1007/s40243-025-00309-7
  22. https://www.mdpi.com/2571-8797/7/1/22
  23. https://www.researchgate.net/publication/375878462_Recent_advances_of_research_in_coal_and_biomass_co-firing_for_electricity_and_heat_generation
  24. https://www.mdpi.com/2071-1050/12/9/3692
  25. https://link.springer.com/article/10.1007/s40789-025-00779-0
  26. https://finance.yahoo.com/news/briquetting-machine-market-trends-forecast-082000610.html
  27. https://www.sciencedirect.com/science/article/pii/S2352550923000489
  28. https://www.researchgate.net/publication/396161405_Profitability_Analysis_of_Developed_Briquette_Suitable_for_Energy_Generation_from_Residue_of_Cattle_Feed_Sorghum_Stalk_and_Groundnut_Husk
  29. https://www.sciencedirect.com/science/article/pii/S0960852425012441
  30. https://patents.google.com/patent/US20110302832A1/en
  31. https://www.ftmmachinery.com/blog/briquetting-plant-with-low-cost-for-charcoal-coal-and-iron-powder.html
  32. https://www.sciencedirect.com/science/article/abs/pii/S1364032117313242
  33. https://www.sciencedirect.com/science/article/abs/pii/S0961953425003459
  34. https://www.ispatguru.com/briquetting-process-and-use-of-binders/1000/
  35. http://www.international-agrophysics.org/pdf-104289-35356?filename=35356.pdf
  36. https://pmc.ncbi.nlm.nih.gov/articles/PMC7804313/
  37. https://www.zymining.com/en/a/news/briquetting-process-for-different-materials.html
  38. https://pmc.ncbi.nlm.nih.gov/articles/PMC9739098/
  39. https://link.springer.com/article/10.1007/s40095-018-0275-7
  40. https://www.tandfonline.com/doi/full/10.1080/17597269.2025.2567725
  41. https://www.futuremarketinsights.com/reports/briquetting-machine-market
  42. https://www.bio-conferences.org/articles/bioconf/full_html/2018/01/bioconf_wipie2018_02006/bioconf_wipie2018_02006.html
  43. https://dokers.lv/en/briquettes-peat-and-peat-briquettes/
  44. https://www.worldenergy.org/assets/images/imported/2013/10/WER_2013_6_Peat.pdf
  45. https://www.bordnamonalivinghistory.ie/article-detail/peat-briquettes/
  46. https://www.sciencedirect.com/science/article/abs/pii/S0360544216301323
  47. https://www.sciencedirect.com/science/article/pii/S2405844019358207
  48. https://www.mdpi.com/1996-1073/18/14/3746
  49. https://www.researchgate.net/figure/Calorific-values-CV-of-coal-briquettes_tbl2_374557809
  50. https://discoveryalert.com.au/news/binderless-coal-briquetting-technology-2025/
  51. https://www.ep-machine.com/News/5-Types-Coal-Briquettes-Making-Machine-227.html
  52. https://documents1.worldbank.org/curated/en/259171468018541952/pdf/multi-page.pdf
  53. https://www.inspirecleanenergy.com/blog/clean-energy-101/reliable-energy-sources
  54. https://iea.blob.core.windows.net/assets/imports/events/45/Coal.pdf
  55. https://www.bordnamonalivinghistory.ie/article-detail/milled-peat-production/
  56. https://landgrou.com/en/fuel-peat-briquette-in-thermal-film%2C-10-kg-each.html
  57. https://www.mdpi.com/1996-1073/12/19/3784
  58. https://cfnielsen.com/segments/wood/solutions/charcoal-briquettes/
  59. https://www.woodbriquetteplant.com/new/differences-between-carbonized-and-non-carbonized-briquettes.html
  60. https://www.fao.org/4/x5328e/x5328e0c.htm
  61. https://www.woodbriquetteplant.com/news/Briquette-Charcoal-Conversion.html
  62. http://article.sapub.org/10.5923.j.ep.20140402.03.html
  63. https://www.sciencedirect.com/science/article/pii/S235248472400708X
  64. https://www.gmpyrolysismachine.com/what-is-the-process-of-making-charcoal-briquettes/
  65. https://www.ftmmachinery.com/blog/composition-and-processing-of-charcoal-briquette.html
  66. https://bioresources.cnr.ncsu.edu/resources/exploring-binder-efficacy-in-the-fabrication-of-charcoal-briquettes-from-palmyra-palm-and-oil-palm-shells-a-comprehensive-analysis/
  67. https://www.liebertpub.com/doi/10.1089/ees.2021.0043
  68. https://www.researchgate.net/figure/The-caloric-value-of-briquette-samples_fig2_321048931
  69. https://www.alliedmarketresearch.com/bbq-charcoal-market-A31401
  70. https://www.gminsights.com/industry-analysis/charcoal-briquettes-market
  71. https://patents.google.com/patent/US9279091B2/en
  72. https://patents.google.com/patent/US20060143976A1/en
  73. https://www.sciencedirect.com/science/article/abs/pii/S0048969720347963
  74. https://forestsnews.cifor.org/72344/five-things-to-know-about-briquettes-and-sustainable-bioenergy-in-africa?fnl=en
  75. https://www.sciencedirect.com/science/article/abs/pii/S0973082623001989
  76. https://www.mdpi.com/1996-1073/14/24/8320
  77. https://www.sciencedirect.com/science/article/pii/S2352186422003984
  78. https://www.sciencedirect.com/science/article/abs/pii/S0959652623045237
  79. https://pmc.ncbi.nlm.nih.gov/articles/PMC9369570/
  80. https://www.sciencedirect.com/science/article/abs/pii/S0959652622036836
  81. https://ecommons.cornell.edu/bitstreams/28be68c4-427d-43ae-8d20-2e7fdd177fa1/download
  82. https://www.ejosdr.com/download/production-and-optimization-of-briquette-solid-fuels-from-waste-biomass-using-industrial-starch-as-15138.pdf
  83. https://www.sciencedirect.com/science/article/pii/S2405844020321095
  84. https://www.eco-business.com/news/biomass-burning-booms-in-east-asia-despite-paris-agreement-goals/
  85. https://www.mdpi.com/1996-1073/15/7/2426
  86. https://www.researchgate.net/publication/342416330_Briquettes_from_Agricultural_Residues_An_Alternative_Clean_and_Sustainable_Fuel_for_Domestic_Cooking_in_Nasarawa_State_Nigeria
  87. https://core.ac.uk/download/pdf/334997443.pdf
  88. https://www.sciencedirect.com/science/article/pii/S0360128520300976
  89. https://pmc.ncbi.nlm.nih.gov/articles/PMC9571558/
  90. https://www.frontiersin.org/journals/energy-research/articles/10.3389/fenrg.2025.1661636/full
  91. https://www.sciencedirect.com/science/article/pii/S0378382020308432
  92. https://www.mdpi.com/1996-1073/15/9/3419
  93. https://cgspace.cgiar.org/server/api/core/bitstreams/59754736-4323-4ffe-b93a-467bf84b5a5d/content
  94. https://pmc.ncbi.nlm.nih.gov/articles/PMC11667633/
  95. https://www.primescholars.com/articles/physical-and-combustion-properties-of-briquettes-produced-from-sawdust-of-three-hardwood-species-and-different-organic-binders.pdf
  96. https://www.sciencedirect.com/science/article/pii/S1878029613000789
  97. https://hal.science/hal-04695022v1/document
  98. https://pubmed.ncbi.nlm.nih.gov/26560808/
  99. https://onlinelibrary.wiley.com/doi/10.1155/2022/4222205
  100. https://scholarworks.uark.edu/cgi/viewcontent.cgi?article=1108&context=cheguht
  101. https://publications.lib.chalmers.se/records/fulltext/5160/local_5160.pdf
  102. https://www.accio.com/plp/honeycomb-coal
  103. https://www.teachengineering.org/activities/view/cub_china_lesson03_activity1
  104. https://www.sciencedirect.com/science/article/pii/S0160412021006267
  105. https://link.springer.com/article/10.1007/s44274-024-00141-2
  106. https://www.sciencedirect.com/science/article/abs/pii/S0959652624028683
  107. https://www.researchgate.net/publication/306022704_Production_of_fuel_briquettes_from_rice_husk-lignite_blends
  108. https://m.korean-vibe.com/news/newsview.php?ncode=1065603444649899
  109. https://www.koreatimes.co.kr/opinion/20070621/455-at-coalface-of-heating
  110. https://pubmed.ncbi.nlm.nih.gov/22948168/
  111. https://shin-maru.com/shin-maru-ogatan-charcoal/
  112. https://mtckitchen.com/products/all-natural-ogatan-charcoal-briquettes-touryu-22-lb
  113. http://ssmstoves.com/h-nd-1159.html
  114. https://www.logsdirect.co.uk/blog/post/are-briquettes-better-than-logs-logs-direct
  115. https://duffieldtimber.com/the-workbench/wood-fuels/briquettes-vs-logs-heat-performance-comparison
  116. https://duffieldtimber.com/the-workbench/wood-fuels/wood-briquettes-vs-logs-cost-comparison
  117. https://link.springer.com/article/10.1007/s43621-025-01853-y
  118. https://bintangbriquettes.com/ideal-shape-of-barbecue-briquettes/
  119. https://www.researchgate.net/figure/Energy-density-of-manufactured-briquettes-and-loose-biomass-fractions_tbl2_354432401
  120. https://whitecoalindustries.com/products/industrial-briquettes/
  121. https://ronakeng.com/application-of-briquettes/
  122. https://jaykhodiyar.com/application-of-briquettes/
  123. https://gpcharcoal.com/why-our-bbq-charcoal-briquettes-are-trusted-by-restaurants-worldwide/
  124. https://bintangbriquettes.com/bbq-charcoal-best-for-restaurants-commercial-use/
  125. https://pnpcharcoal.com/what-makes-charcoal-for-restaurants-special/
  126. https://www.industryarc.com/Research/Global-BBQ-Charcoal-Market-Research-511783
  127. https://www.pib.gov.in/PressReleseDetailm.aspx?PRID=2149193
  128. https://biogreenenergysolutions.com/biomass-briquetting/
  129. https://energy.sustainability-directory.com/question/how-can-biomass-energy-storage-be-improved/
  130. https://www.ieabioenergy.com/wp-content/uploads/2016/03/IEA_Bioenergy_T32_cofiring_2016.pdf
  131. https://www.researchgate.net/publication/341158584_Coal-Biomass_Co-Firing_Power_Generation_Technology_Current_Status_Challenges_and_Policy_Implications
  132. https://www.sciencedirect.com/science/article/pii/S2352186423002717
  133. https://publications.jrc.ec.europa.eu/repository/bitstream/JRC118318/jrc118318_1.pdf
  134. https://www.nib.int/news/nib-finances-biomass-power-plant-in-sweden
  135. https://www.moffittsfarm.com.au/2019/01/17/swedens-largest-single-source-of-consumed-energy-is-biomass/
  136. https://cfnielsen.com/faq/briquettes-versus-pellets/
  137. https://wastetowisdom.com/wp-content/uploads/2018/08/4.1.2-WTW_Report-Briquettes-biochar-technoeconomics-FINAL.pdf
  138. https://www.linkedin.com/pulse/biomass-cofiring-vs-100-firing-comprehensive-dharmesh-kumar-kewat-zjwoc
  139. https://www.mdpi.com/1996-1073/17/24/6392
  140. https://pmc.ncbi.nlm.nih.gov/articles/PMC8363485/
  141. https://www.sciencedirect.com/science/article/pii/S2351978916301895
  142. https://pubs.acs.org/doi/10.1021/acs.energyfuels.3c00514
  143. https://www.researchgate.net/publication/331193482_Effects_of_biomass_briquetting_and_carbonization_on_PM_25_emission_from_residential_burning_in_Guanzhong_Plain_China
  144. https://pubs.acs.org/doi/10.1021/acs.energyfuels.0c04148
  145. https://www.researchgate.net/publication/363606543_Biomass_and_cardboard_waste-based_briquettes_for_heating_and_cooking_Thermal_efficiency_and_emissions_analysis
  146. https://www.sciencedirect.com/science/article/abs/pii/S0360544219314604
  147. https://ui.adsabs.harvard.edu/abs/2024JCPro.43440365W/abstract
  148. https://www.fpl.fs.usda.gov/documnts/fplgtr/fpl_gtr262.pdf
  149. https://www.gjesm.net/article_716404_038ba974f4b99a035281df2f0f2a5153.pdf
  150. https://www.sciencedirect.com/science/article/abs/pii/S0973082612000476
  151. https://www.charcoalbriquettemachine.com/news/charcoal-briquettes-in-Africa.html
  152. https://www.ucd.ie/peat-hub-ireland/t4media/1025_Peatlands_and_climate_change_SISUS_Chapter7.pdf
  153. https://www.kennyfuels.ie/2023/03/17/5-reasons-why-peat-briquettes-are-the-perfect-fit-for-you/
  154. https://www.nationalgeographic.com/science/article/estonia-reduces-carbon-emissions-planting-peat-bogs
  155. https://www.researchgate.net/publication/342640887_Impact_of_the_Drying_Temperature_and_Grinding_Technique_on_Biomass_Grindability
  156. https://www.researchgate.net/publication/366894868_Environmental_Life_Cycle_Assessment_of_biomass_and_cardboard_waste-based_briquettes_production_and_consumption_in_Andean_areas
  157. https://www.biologicaldiversity.org/campaigns/debunking_the_biomass_myth/
  158. https://www.mdpi.com/2071-1050/17/8/3415
  159. https://www.researchgate.net/publication/331690775_Cost_analysis_of_community_scale_smokeless_charcoal_briquette_production_from_agricultural_and_forest_residues
  160. https://www.mdpi.com/2306-5354/6/4/87
  161. http://www.biofuelmachines.com/Briquettes-Manufacture-Cost-and-Revenues-Analysis.html
  162. https://www.openpr.com/news/4136482/biomass-briquettes-manufacturing-plant-cost-2025-capital
  163. https://www.linkedin.com/pulse/exploring-dynamics-graphite-briquette-market-key-insights-jqfzf/
  164. https://www.bioenergy-machine.com/blogs/four-factors-building-charcoal-briquette-making-plant-cost.html
  165. https://www.eiriindia.org/blog/the-future-of-biomass-briquettes-manufacturing-opportunities-and-growth-prospects?srsltid=AfmBOoq1WaKhMfJ7DQa5Y2hsAKrw7o3pMH3evlpMUZetTGzEw4Al7zsn
  166. https://www.facebook.com/MNREMinistry/posts/india-generates-vast-amounts-of-crop-residue-every-year-rice-straw-wheat-husk-an/1107995844809909/
  167. https://www.eco-business.com/news/bio-briquettes-tackle-indias-climate-pollution-and-poverty-challenges/
  168. https://solve.mit.edu/challenges/climate-ecosystems-housing/solutions/58315
  169. https://oec.world/en/profile/country/idn
  170. https://santandertrade.com/en/portal/analyse-markets/brazil/foreign-trade-in-figures
  171. https://www.ibai.or.id/news/item/5650-indonesia-s-briquette-charcoal-exports-to-foreign-countries-show-remarkable-growth.html
  172. https://www.mordorintelligence.com/industry-reports/biomass-briquette-market
  173. https://finance.yahoo.com/news/coal-briquettes-market-projected-reach-150000633.html
  174. https://www.techsciresearch.com/report/charcoal-briquette-market/23648.html
  175. https://www.archivemarketresearch.com/reports/briquette-70140
  176. http://www.pelletequipments.com/blogs/pellets-or-briquettes.html
  177. https://www.sciencedirect.com/science/article/abs/pii/S0195925509000420
  178. https://www.pib.gov.in/PressReleaseIframePage.aspx?PRID=1945245
  179. https://www.techsciresearch.com/report/coal-briquettes-market/17481.html
  180. https://www.researchgate.net/publication/370112440_Coal_Is_a_Priority_for_Energy_Security_until_It_Is_Not_Coal_Phase-Out_in_the_EU_and_Its_Persistence_in_the_Face_of_the_Energy_Crisis
  181. https://www.sciencedirect.com/science/article/abs/pii/S0016236109001446
  182. https://www.nakedwhiz.com/wetcharcoal.htm
  183. https://www.informaticsjournals.co.in/index.php/jmmf/article/download/27004/19947/44861
  184. https://www.sciencedirect.com/science/article/abs/pii/037838209090098D
  185. https://www.cpsc.gov/Newsroom/News-Releases/1986/Burning-Charcoal-Causes-83-Deaths-From-Carbon-Monoxide
  186. https://www.mja.com.au/journal/2012/197/6/carbon-monoxide-induced-death-and-toxicity-charcoal-briquettes
  187. https://weima.com/us/briquetting/biomass-briquettes/
  188. https://pubs.acs.org/doi/10.1021/acs.energyfuels.0c04246
  189. https://www.iso.org/obp/ui/#iso:std:iso:17831:-2:en
  190. https://pubs.acs.org/doi/10.1021/es500486j
  191. https://www.sciencedirect.com/science/article/pii/S2666765723000789
  192. https://www.ncbi.nlm.nih.gov/books/NBK304396/
  193. https://www.researchgate.net/publication/10883571_Benzene_emitted_from_glowing_charcoal
  194. https://pmc.ncbi.nlm.nih.gov/articles/PMC5102234/
  195. https://www.cdc.gov/niosh/silica/about/index.html
  196. https://pmc.ncbi.nlm.nih.gov/articles/PMC10373722/
  197. https://www.mdpi.com/1996-1073/16/23/7757
  198. https://journals.plos.org/plosmedicine/article?id=10.1371/journal.pmed.1001621
  199. https://publications.ersnet.org/content/erj/40/1/239
  200. https://pmc.ncbi.nlm.nih.gov/articles/PMC8727436/
  201. https://www.mdpi.com/1996-1073/15/22/8371
  202. https://lidsen.com/journals/aeer/aeer-04-03-040
  203. https://www.researchgate.net/publication/245234583_NO_x_Reduction_by_Potassium-Containing_Coal_Briquettes_Effect_of_Preparation_Procedure_and_Potassium_Content
  204. https://www.sciencedirect.com/science/article/abs/pii/S000925092500363X
  205. https://www.sciencedirect.com/science/article/pii/S2405844024014075
  206. https://rsisinternational.org/journals/ijrsi/articles/performance-efficiency-of-binding-agents-in-coconut-charcoal-briquettes/
  207. https://www.openpr.com/news/4198461/charcoal-briquette-market-to-expand-at-5-71-cagr-by-2032
  208. http://www.ijerd.com/paper/vol6-issue5/C06051214.pdf
  209. https://www.amazon.com/Upgraded-MOES-Detectors-Temperature-Fireplace/dp/B0DNYQ8T3P
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