This article is about the chemical series. For other uses, see Halogen (disambiguation).
The halogens () are a group in the periodic table consisting of five chemically related elements: fluorine (F), chlorine (Cl), bromine (Br), iodine (I), and astatine (At). The artificially created element 117 (tennessine, Ts) may also be a halogen. In the modern IUPAC nomenclature, this group is known as group 17. The symbol X is often used generically to refer to any halogen.
The name "halogen" means "salt-producing". When halogens react with metals they produce a wide range of salts, including calcium fluoride, sodium chloride (common table salt), silver bromide and potassium iodide.
The group of halogens is the only periodic table group that contains elements in all three main states of matter at standard temperature and pressure. All of the halogens form acids when bonded to hydrogen. Most halogens are typically produced from minerals or salts. The middle halogens, that is chlorine, bromine and iodine, are often used as disinfectants. Organobromides are the most important class of flame retardants. Elemental halogens are dangerous and can potentially be lethally toxic.
The fluorine mineral fluorospar was known as early as 1529. Early chemists realized that fluorine compounds contain an undiscovered element, but were unable to isolate it. In 1860, George Gore, an English chemist, ran a current of electricity through hydrofluoric acid and probably produced fluorine, but he was unable to prove his results at the time. In 1886, Henri Moissan, a chemist in Paris, performed electrolysis on potassium bifluoride dissolved in anhydrous hydrogen fluoride, and successfully isolated fluorine.
Hydrochloric acid was known to alchemists and early chemists. However, elemental chlorine was not produced until 1774, when Carl Wilhelm Scheele heated hydrochloric acid with manganese dioxide. Scheele called the element "dephlogisticated muriatic acid", which is how chlorine was known for 33 years. In 1807, Humphry Davy investigated chlorine and discovered that it is an actual element. Chlorine was used as a poison gas during World War I.
Bromine was discovered in the 1820s by Antoine-Jérôme Balard. Balard discovered bromine by passing chlorine gas through a sample of brine. He originally proposed the name muride for the new element, but the French Academy changed the element's name to bromine.
Iodine was discovered by Bernard Courtois, who was using seaweed ash as part of a process for saltpeter manufacture. Courtois typically boiled the seaweed ash with water to generate potassium chloride. However, in 1811, Courtois added sulfuric acid to his process, and found that his process produced purple fumes that condensed into black crystals. Suspecting that these crystals were a new element, Courtois sent samples to other chemists for investigation. Iodine was proven to be a new element by Joseph Gay-Lussac.
In 1931, Fred Allison claimed to have discovered element 85 with a magneto-optical machine, and named the element Alabamine, but was mistaken. In 1937, Rajendralal De claimed to have discovered element 85 in minerals, and called the element dakine, but he was also mistaken. An attempt at discovering element 85 in 1939 by Horia Hulubei and Yvette Cauchois via spectroscopy was also unsuccessful, as was an attempt in the same year by Walter Minder, who discovered an iodine-like element resulting from beta decay of polonium. Element 85, now named astatine, was produced successfully in 1940 by Dale R. Corson, K.R. Mackenzie, and Emilio G. Segrè, who bombarded bismuth with alpha particles.
In 1811, the German chemist Johann Salomo Christoph Schweigger proposed that the name "halogen" – meaning "salt producer", from αλς [als] "salt" and γενειν [genein] "to beget" – replace the name "chlorine", which had been proposed by the English chemist Humphry Davy. Davy's name for the element prevailed. However, in 1826, the Swedishchemist Baron Jöns Jakob Berzelius proposed the term "halogen" for the elements fluorine, chlorine, and iodine, which produce a sea-salt-like substance when they form a compound with an alkaline metal.
Fluorine's name comes from the Latin word fluere, meaning "to flow", because it was derived from the mineral fluorospar, which was used as a flux in metal working. Chlorine's name comes from the Greek word chloros, meaning "greenish-yellow". Bromine's name comes from the Greek word bromos, meaning "stench". Iodine's name comes from the Greek word iodes, meaning "violet". Astatine's name comes from the Greek word astatos, meaning "unstable". Tennessine is named after the US state of Tennessee.
The halogens show trends in chemical bond energy moving from top to bottom of the periodic table column with fluorine deviating slightly. (It follows trend in having the highest bond energy in compounds with other atoms, but it has very weak bonds within the diatomic F2 molecule.) This means, as you go down the periodic table, the reactivity of the element will decrease because of the increasing size of the atoms.
Halogens are highly reactive, and as such can be harmful or lethal to biological organisms in sufficient quantities. This high reactivity is due to the high electronegativity of the atoms due to their high effective nuclear charge. Because the halogens have seven valence electrons in their outermost energy level, they can gain an electron by reacting with atoms of other elements to satisfy the octet rule. Fluorine is one of the most reactive elements, attacking otherwise-inert materials such as glass, and forming compounds with the usually inert noble gases. It is a corrosive and highly toxic gas. The reactivity of fluorine is such that, if used or stored in laboratory glassware, it can react with glass in the presence of small amounts of water to form silicon tetrafluoride (SiF4). Thus, fluorine must be handled with substances such as Teflon (which is itself an organofluorine compound), extremely dry glass, or metals such as copper or steel, which form a protective layer of fluoride on their surface.
The high reactivity of fluorine allows paradoxically some of the strongest bonds possible, especially to carbon. For example, Teflon is fluorine bonded with carbon and is extremely resistant to thermal and chemical attack and has a high melting point.
Diatomic halogen molecules
The halogens form homonucleardiatomicmolecules (not proven for astatine). Due to relatively weak intermolecular forces, chlorine and fluorine form part of the group known as "elemental gases".
The elements become less reactive and have higher melting points as the atomic number increases. The higher melting points are caused by stronger London dispersion forces resulting from more electrons.
All of the halogens have been observed to react with hydrogen to form hydrogen halides. For fluorine, chlorine, and bromine, this reaction is in the form of:
- H2 + X2 → 2HX
However, hydrogen iodide and hydrogen astatide can split back into their constituent elements.
The hydrogen-halogen reactions get gradually less reactive toward the heavier halogens. A fluorine-hydrogen reaction is explosive even when it is dark and cold. A chlorine-hydrogen reaction is also explosive, but only in the presence of light and heat. A bromine-hydrogen reaction is even less explosive; it is explosive only when exposed to flames. Iodine and astatine only partially react with hydrogen, forming equilibria.
All halogens form binary compounds with hydrogen known as the hydrogen halides: hydrogen fluoride (HF), hydrogen chloride (HCl), hydrogen bromide (HBr), hydrogen iodide (HI), and hydrogen astatide (HAt). All of these compounds form acids when mixed with water. Hydrogen fluoride is the only hydrogen halide that forms hydrogen bonds. Hydrochloric acid, hydrobromic acid, hydroiodic acid, and hydroastatic acid are all strong acids, but hydrofluoric acid is a weak acid.
All of the hydrogen halides are irritants. Hydrogen fluoride and hydrogen chloride are highly acidic. Hydrogen fluoride is used as an industrial chemical, and is highly toxic, causing pulmonary edema and damaging cells. Hydrogen chloride is also a dangerous chemical. Breathing in gas with more than fifty parts per million of hydrogen chloride can cause death in humans. Hydrogen bromide is even more toxic and irritating than hydrogen chloride. Breathing in gas with more than thirty parts per million of hydrogen bromide can be lethal to humans. Hydrogen iodide, like other hydrogen halides, is toxic.
Main article: Metal halides
All the halogens are known to react with sodium to form sodium fluoride, sodium chloride, sodium bromide, sodium iodide, and sodium astatide. Heated sodium's reaction with halogens produces bright-orange flames. Sodium's reaction with chlorine is in the form of:
- 2Na + Cl2 → 2NaCl
Iron reacts with fluorine, chlorine, and bromine to form Iron(III) halides. These reactions are in the form of:
- 2Fe + 3X2 → 2FeX3
However, when iron reacts with iodine, it forms only iron(II) iodide.
Iron wool can react rapidly with fluorine to form the white compound iron(III) fluoride even in cold temperatures. When chlorine comes into contact with heated iron, they react to form the black iron (III) chloride. However, if the reaction conditions are moist, this reaction will instead result in a reddish-brown product. Iron can also react with bromine to form iron(III) bromide. This compound is reddish-brown in dry conditions. Iron's reaction with bromine is less reactive than its reaction with fluorine or chlorine. Hot iron can also react with iodine, but it forms iron(II) iodide. This compound may be gray, but the reaction is always contaminated with excess iodine, so it is not known for sure. Iron's reaction with iodine is less vigorous than its reaction with the lighter halogens.
Main article: Interhalogen
Interhalogen compounds are in the form of XYn where X and Y are halogens and n is one, three, five, or seven. Interhalogen compounds contain at most two different halogens. Large interhalogens, such as ClF3 can be produced by a reaction of a pure halogen with a smaller interhalogen such as ClF. All interhalogens except IF7 can be produced by directly combining pure halogens in various conditions.
Interhalogens are typically more reactive than all diatomic halogen molecules except F2 because interhalogen bonds are weaker. However, the chemical properties of interhalogens are still roughly the same as those of diatomic halogens. Many interhalogens consist of one or more atoms of fluorine bonding to a heavier halogen. Chlorine can bond with up to 3 fluorine atoms, bromine can bond with up to five fluorine atoms, and iodine can bond with up to seven fluorine atoms. Most interhalogen compounds are covalent gases. However, there are some interhalogens that are liquids, such as BrF3, and many iodine-containing interhalogens are solids.
Many synthetic organic compounds such as plasticpolymers, and a few natural ones, contain halogen atoms; these are known as halogenated compounds or organic halides. Chlorine is by far the most abundant of the halogens in seawater, and the only one needed in relatively large amounts (as chloride ions) by humans. For example, chloride ions play a key role in brain function by mediating the action of the inhibitory transmitter GABA and are also used by the body to produce stomach acid. Iodine is needed in trace amounts for the production of thyroid hormones such as thyroxine. Organohalogens are also synthesized through the nucleophilic abstraction reaction.
Polyhalogenated compounds are industrially created compounds substituted with multiple halogens. Many of them are very toxic and bioaccumulate in humans, and have a very wide application range. They include PCBs, PBDEs, and perfluorinated compounds (PFCs), as well as numerous other compounds.
Reactions with water
Fluorine reacts vigorously with water to produce oxygen (O2) and hydrogen fluoride (HF):
- 2 F2(g) + 2 H2O(l) → O2(g) + 4 HF(aq)
Chlorine has maximum solubility of ca. 7.1 g Cl2 per kg of water at ambient temperature (21 °C). Dissolved chlorine reacts to form hydrochloric acid (HCl) and hypochlorous acid, a solution that can be used as a disinfectant or bleach:
- Cl2(g) + H2O(l) → HCl(aq) + HClO(aq)
Bromine has a solubility of 3.41 g per 100 g of water, but it slowly reacts to form hydrogen bromide (HBr) and hypobromous acid (HBrO):
- Br2(g) + H2O(l) → HBr(aq) + HBrO(aq)
Iodine, however, is minimally soluble in water (0.03 g/100 g water at 20 °C) and does not react with it. However, iodine will form an aqueous solution in the presence of iodide ion, such as by addition of potassium iodide (KI), because the triiodide ion is formed.
Physical and atomic
The table below is a summary of the key physical and atomic properties of the halogens. Data marked with question marks are either uncertain or are estimations partially based on periodic trends rather than observations.
Fluorine has one stable and naturally occurring isotope, fluorine-19. However, there are trace amounts in nature of the radioactive isotope fluorine-23, which occurs via cluster decay of protactinium-231. A total of eighteen isotopes of fluorine have been discovered, with atomic masses ranging from 14 to 31. Chlorine has two stable and naturally occurring isotopes, chlorine-35 and chlorine-37. However, there are trace amounts in nature of the isotope chlorine-36, which occurs via spallation of argon-36. A total of 24 isotopes of chlorine have been discovered, with atomic masses ranging from 28 to 51.
There are two stable and naturally occurring isotopes of bromine, bromine-79 and bromine-81. A total of 32 isotopes of bromine have been discovered, with atomic masses ranging 67 to 98. There is one stable and naturally occurring isotope of iodine, iodine-127. However, there are trace amounts in nature of the radioactive isotope iodine-129, which occurs via spallation and from the radioactive decay of uranium in ores. Several other radioactive isotopes of iodine have also been created naturally via the decay of uranium. A total of 38 isotopes of iodine have been discovered, with atomic masses ranging from 108 to 145.
There are no stable isotopes of astatine. However, there are three naturally occurring radioactive isotopes of astatine produced via radioactive decay of uranium, neptunium, and plutonium. These isotopes are astatine-215, astatine-217, and astatine-219. A total of 31 isotopes of astatine have been discovered, with atomic masses ranging from 193 to 223.
Approximately six million metric tons of the fluorine mineral fluorite are produced each year. Four hundred-thousand metric tons of hydrofluoric acid are made each year. Fluorine gas is made from hydrofluoric acid produced as a by-product in phosphoric acid manufacture. Approximately 15,000 metric tons of fluorine gas are made per year.
The mineral halite is the mineral that is most commonly mined for chlorine, but the minerals carnallite and sylvite are also mined for chlorine. Forty million metric tons of chlorine are produced each year by the electrolysis of brine.
Approximately 450,000 metric tons of bromine are produced each year. Fifty percent of all bromine produced is produced in the United States, 35% in Israel, and most of the remainder in China. Historically, bromine was produced by adding sulfuric acid and bleaching powder to natural brine. However, in modern times, bromine is produced by electrolysis, a method invented by Herbert Dow. It is also possible to produce bromine by passing chlorine through seawater and then passing air through the seawater.
In 2003, 22,000 metric tons of iodine were produced. Chile produces 40% of all iodine produced, Japan produces 30%, and smaller amounts are produced in Russia and the United States. Until the 1950s, iodine was extracted from kelp. However, in modern times, iodine is produced in other ways. One way that iodine is produced is by mixing sulfur dioxide with nitrate ores, which contain some iodates. Iodine is also extracted from natural gas fields.
Even though astatine is naturally occurring, it is usually produced by bombarding bismuth with alpha particles.
Both chlorine and bromine are used as disinfectants for drinking water, swimming pools, fresh wounds, spas, dishes, and surfaces. They kill bacteria and other potentially harmful microorganisms through a process known as sterilization. Their reactivity is also put to use in bleaching. Sodium hypochlorite, which is produced from chlorine, is the active ingredient of most fabric bleaches, and chlorine-derived bleaches are used in the production of some paper products. Chlorine also reacts with sodium to create sodium chloride, which is table salt.
Halogen lamps are a type of incandescent lamp using a tungsten filament in bulbs that have a small amounts of a halogen, such as iodine or bromine added. This enables the production of lamps that are much smaller than non-halogen incandescent lightbulbs at the same wattage. The gas reduces the thinning of the filament and blackening of the inside of the bulb resulting in a bulb that has a much greater life. Halogen lamps glow at a higher temperature (2800 to 3400 kelvins) with a whiter color than other incandescent bulbs. However, this requires bulbs to be manufactured from fused quartz rather than silica glass to reduce breakage.
In drug discovery, the incorporation of halogen atoms into a lead drug candidate results in analogues that are usually more lipophilic and less water-soluble. As a consequence, halogen atoms are used to improve penetration through lipid membranes and tissues. It follows that there is a tendency for some halogenated drugs to accumulate in adipose tissue.
The chemical reactivity of halogen atoms depends on both their point of attachment to the lead and the nature of the halogen. Aromatic halogen groups are far less reactive than aliphatic halogen groups, which can exhibit considerable chemical reactivity. For aliphatic carbon-halogen bonds, the C-F bond is the strongest and usually less chemically reactive than aliphatic C-H bonds. The other aliphatic-halogen bonds are weaker, their reactivity increasing down the periodic table. They are usually more chemically reactive than aliphatic C-H bonds. As a consequence, the most common halogen substitutions are the less reactive aromatic fluorine and chlorine groups.
Fluoride anions are found in ivory, bones, teeth, blood, eggs, urine, and hair of organisms. Fluoride anions in very small amounts may be essential for humans. There are 0.5 milligrams of fluorine per liter of human blood. Human bones contain 0.2 to 1.2% fluorine. Human tissue contains approximately 50 parts per billion of fluorine. A typical 70-kilogram human contains 3 to 6 grams of fluorine.
Chloride anions are essential to a large number of species, humans included. The concentration of chlorine in the dry weight of cereals is 10 to 20 parts per million, while in potatoes the concentration of chloride is 0.5%. Plant growth is adversely affected by chloride levels in the soil falling below 2 parts per million. Human blood contains an average of 0.3% chlorine. Human bone typically contains 900 parts per million of chlorine. Human tissue contains approximately 0.2 to 0.5% chlorine. There is a total of 95 grams of chlorine in a typical 70-kilogram human.
Some bromine in the form of the bromide anion is present in all organisms. A biological role for bromine in humans has not been proven, but some organisms contain organobromine compounds. Humans typically consume 1 to 20 milligrams of bromine per day. There are typically 5 parts per million of bromine in human blood, 7 parts per million of bromine in human bones, and 7 parts per million of bromine in human tissue. A typical 70-kilogram human contains 260 milligrams of bromine.
Humans typically consume less than 100 micrograms of iodine per day. Iodine deficiency can cause intellectual disability. Organoiodine compounds occur in humans in some of the glands, especially the thyroid gland, as well as the stomach, epidermis, and immune system. Foods containing iodine include cod, oysters, shrimp, herring, lobsters, sunflower seeds, seaweed, and mushrooms. However, iodine is not known to have a biological role in plants. There are typically 0.06 milligrams per liter of iodine in human blood, 300 parts per billion of iodine in human bones, and 50 to 700 parts per billion of iodine in human tissue. There are 10 to 20 milligrams of iodine in a typical 70-kilogram human.
Astatine has no biological role.
The halogens tend to decrease in toxicity towards the heavier halogens.
Fluorine gas is extremely toxic; breathing in fluorine at a concentration of 25 parts per million is potentially lethal. Hydrofluoric acid is also toxic, being able to penetrate skin and cause highly painful burns. In addition, fluoride anions are toxic, but not as toxic as pure fluorine. Fluoride can be lethal in amounts of 5 to 10 grams. Prolonged consumption of fluoride above concentrations of 1.5 mg/L is associated with a risk of dental fluorosis, an aesthetic condition of the teeth. At concentrations above 4 mg/L, there is an increased risk of developing skeletal fluorosis, a condition in which bone fractures become more common due to the hardening of bones. Current recommended levels in water fluoridation, a way to prevent dental caries, range from 0.7 to 1.2 mg/L to avoid the detrimental effects of fluoride while at the same time reaping the benefits. People with levels between normal levels and those required for skeletal fluorosis tend to have symptoms similar to arthritis.
Chlorine gas is highly toxic. Breathing in chlorine at a concentration of 3 parts per million can rapidly cause a toxic reaction. Breathing in chlorine at a concentration of 50 parts per million is highly dangerous. Breathing in chlorine at a concentration of 500 parts per million for a few minutes is lethal. Breathing in chlorine gas is highly painful.Hydrochloric acid is a dangerous chemical.
Pure bromine is somewhat toxic, but less toxic than fluorine and chlorine. One hundred milligrams of bromine is lethal. Bromide anions are also toxic, but less so than bromine. Bromide has a lethal dose of 30 grams.
Iodine is somewhat toxic, being able to irritate the lungs and eyes, with a safety limit of 1 milligram per cubic meter. When taken orally, 3 grams of iodine can be lethal. Iodide anions are mostly nontoxic, but these can also be deadly if ingested in large amounts.
Astatine is very radioactive and thus highly dangerous, but it has not been produced in macroscopic quantities and hence it is most unlikely that its toxicity will be of much relevance to the average individual.
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With halogen-containing substances in the public eye -- due to scrutiny by the European Union (EU) and various non-governmental organizations (NGO) -- as possible additions to the list of substances banned from electronics, many manufacturers are asking how this materials restriction will affect them and their processes. Having just overcome the hurdle of RoHS, they want to know what halogens and halides are, and what changes they should be prepared for if required to stop using them. John Vivari, Nordson EFD, explains what these elements are and why they matter, as well as where halogens and halides appear in the electronics manufacturing bill of materials.
Halide-free materials are not new. Some segments of the electronics industry have been sensitive to halides for decades. This article provides a working knowledge of halogens and halides. Armed with this education, the reader will be able to make informed decisions when required to use halogen-free materials, either because regulations dictate it or social pressure makes acceptance preferable to resistance.
What are Halogens and Halides?
At their most basic level, halogens are the electronegative elements in column 17 of the periodic table,
Figure 1. Columns 14 through 18 of the Periodic Table of Elements.including fluorine (F), chlorine (Cl), bromine (Br), iodine (I), and astatine (At). In electronics applications, iodine and astatine are rarely if ever used.
A halide is a chemical compound that contains a halogen. A host of halides, including a wide variety of salts and acids, are essential to human life.
Where are Halogens Found in Electronics Assemblies?
Chlorine, as found in circuit boards, is primarily in the form of residual materials left over from production of non-brominated epoxy resins used in board assembly. It is difficult to remove all the chlorinated compounds produced in epoxy resin, and minor quantities of sodium chloride (NaCl) and other chlorides can be found. Concentrations are typically below 100 ppm.
Bromine in electronics is most commonly bound to brominated flame retardants (BFRs). Brominated flame retardants have been in common and effective usage for the last few decades to combat fire risk (and resultant property damage). BFR use is not limited to electronics; it is also used in furniture, construction materials, and textiles.
Other sources of halogens in circuit boards include fiberglass sizing, epoxy curing agents and accelerators, resin wetting and de-foaming agents, flux residues, and contamination from handling. In the broader category of “electronics,” many plastics, papers, coatings, sealants, lubricants, and adhesives can be added to the list of sources.
Why are Halogens of Concern?
There are both known and suspected risks associated with halogens in electronics. Hundreds of studies have been performed to determine the immediate and long-term effects of various halogenated compounds in both laboratory and outdoor environments. Both the groups supporting a ban on halogens and those opposing such a ban reference specific studies as proof their point of view is correct.
The most widely publicized risk is associated with byproducts of uncontrolled disposal by incineration, which produces dioxins and furans. Modern incineration technology, compared to uncontrolled burning, has virtually eliminated concerns over dioxin and furan production from waste disposal in modern facilities. Given the global waste disposal economy, proponents of halogen elimination point to the fact that it is impossible to predict where or how an electronic product will be treated at end of life (EOL).
Dioxins are naturally occurring materials. Everyone has some dioxins in them, which enter the body primarily through food.
Common usage of the term “dioxin” refers to halogenated dibenzo compounds, including polychlorinated dibenzo-dioxins (PCDDs), polychlorinated dibenzo-furans (PCDFs), polybrominated dibenzo-dioxins (PBDDs), and polybrominated dibenzo-furans (PBDFs). There are 210 known dioxin and furan family compounds. Of those 210, 7 dioxins and 10 furans are tracked by the U.S. Environmental Protection Agency (EPA) for computation of total dioxin contribution to the environment.
Dioxin sources include a wide variety of combustion and chemical processing methods, along with natural sources such as forest fires. In 2008, the EPA estimated dioxin and furan production from human-associated sources in the United States was roughly equivalent to the estimated dioxin and furan production from documented wild fires in the United States over the same period.
Figure 2. 2,3,7,8 tetrachlorodibenzo-p-dioxin (TCDD).
Both dibenzo-dioxins and dibenzo-furans have 8 bond sites to which chlorine and bromine can attach. The number and position of attached Cl or Br atoms determine whether the dioxin has any toxic properties. Dioxins that enter the body are poorly metabolized and accumulate in fatty tissue and the liver. The most toxic dioxin is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), for which there is no known safe exposure level. Several dibenzo-dioxins are established carcinogens, and dibenzo-furan testing classifies furans as predictably carcinogenic.
Figure 3. 2,3,7,8 tetrachlorodibenzo-p-furan (TCDF).
Brominated Flame Retardants (BFRs)
Brominated flame retardants come in many compositions. The only property some have in common is a single bromine atom. Surveys of water samples, animals, and humans have found the presence of BFRs. Some BFRs are persistent in the environment. Some do bio-accumulate, but are also rapidly eliminated, so that a substantial, extended source of exposure is required for adverse effects to be realized. Grouping all BFRs together is no more appropriate than generalizing all 210 dioxins and furans. A collection of studies over 10 years was assessed by the EU in 2007. The conclusion was that the continued use of DecaBDE and TBBPA, which represent over 95% of BFR in electronics, do not pose human or environmental risks.
Despite the European studies, there remains a constituency lobbying against those BFRs that are persistent, due to concern over long-term impacts on humans and animals. Testing particular BFRs in pure form in laboratory environments has produced measureable effects given prolonged exposure of sufficiently high dosage. Testing of other BFRs suggest that some are benign. Assessment of the effects on humans and creatures in the wild is less well understood. Individual BFRs, such as polybrominated biphenyls (PBBs), that have established toxic properties are either no longer manufactured or in the process of being discontinued.
How Will Halogen-free Materials Be Different?
The “green” social movement has created an environment in which it can be to a company’s financial advantage to be halogen-free as a demonstration of corporate social responsibility (CSR). It is left to the technologists to figure out how to supply safe, high-quality products that meet corporate environmental goals. Research into halogen-free materials for PCB manufacture started in the 1990s in Europe as companies began to address halogen concerns. Depending on what materials you are using, there may be no difference in your process because you may already be “halide free.”
The governing document defining “halide free” in Europe is IEC 61249-2, Specification for Non-Halogenated Epoxide/Woven E-glass Laminates for Defined Flammability. This specification defines both the term “non-halogenated” and flammability performance requirements. The definition of non-halogenated in this document is 1500ppm, with a maximum chlorine content of 900ppm and a maximum bromine content of 900ppm.
IPC-J-STD-004a defines halide-free fluxes as a flux containing <500ppm chlorine (bromine and fluorine converted to chlorine equivalent by molecular weight.)
The primary replacements for BFRs are phosphorous-based materials. These materials are typically more hydrophilic, so moisture sensitivity ratings are lower. In most cases, significantly more halogen-free material is required by mass to achieve the same level of flammability resistance. Side effects include shorter shelf life, greater PCB stiffness, and lower coefficient of thermal expansion (CTE).
Of potential benefit, some halogen-free laminate systems have greater thermal stability than traditional FR-4. Phosphorous-based chemistries are currently more costly and the majority are supplied from Europe and Asia. The process window for successful board manufacture is smaller than with FR-4, requiring close cooperation between material vendors and board fabricators.
Halide-free fluxes are typically less active than their halogenated predecessors. A consequence is that many do not wet as well and have a smaller profile process window. Component lead solderability has a greater effect on joint quality. In addition to changes in the reflow process, migration to halide-free reflow may necessitate other material changes to accommodate the limitations of halide-free flux chemistry.
The decision to produce a halogen-free electronic product is not based on existing regulation. Those halogenated compounds that have established risks have already been removed from the market. The key drivers for the major multinational players with halogen-free implementation plans are a combination of public perception of environmental sensitivity and a choice on the side of caution to avoid the cost of a last-minute shift when facing possible future legislation.
Currently available halogen-free materials are not identical in performance to their halogenated counterparts and require more attention to detail to accommodate their smaller process windows. Their long-term performance is less well understood.
Development of halogen-free materials continues to advance. As the desirable properties of halogen-free materials increase relative to their undesirable properties, their acceptance will increase. Whole new avenues of research into inherently flame-resistant materials promise profound changes in how flammability risk is balanced against environmental concerns. Until those potentials are realized, it is left to technologists to make the best of what materials are available.
John Vivari, senior application engineer, Nordson EFD, can be reached at firstname.lastname@example.org or (401) 431-7004; www.nordsonefd.com.
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