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A review of the effects of formaldehyde release from endodontic materials

  • University of Queensland Dental School


Formaldehyde is present in most living cells and the environment. In dentistry, patients may be exposed to formaldehyde through the use of several endodontic materials (e.g. AH 26) and during formocresol pulpotomies. This review outlines how the human body reacts to formaldehyde exposure, how recent data has re-looked at the issue of carcinogenicity and leukaemia associated with formaldehyde, and whether it is possible to quantify the amount of formaldehyde produced by endodontic cements. The review analyses the way formaldehyde is produced from epoxy resins and addresses the question of whether the amount of formaldehyde from endodontic cements is large enough to override the body's ability to deal with its own endogenous levels of formaldehyde and should the amount of formaldehyde produced be a concern.This article is protected by copyright. All rights reserved.
A review of the effects of formaldehyde release
from endodontic materials
B. Athanassiadis
, G. A. George
, P. V. Abbott
& L. J. Wash
Private Practice, Brisbane, Qld;
School of Chemistry, Physics and Mechanical Engineering, Queensland University of
Technology, Brisbane, Qld;
School of Dentistry, University of Western Australia, Perth, WA; and
School of Dentistry,
University of Queensland, Brisbane, Qld, Australia
Athanassiadis B, George GA, Abbott PV, Wash LJ.
A review of the effects of formaldehyde release from
endodontic materials. International Endodontic Journal,48,
829838, 2015.
Formaldehyde is present in most living cells and the
environment. In dentistry, patients may be exposed to
formaldehyde through the use of several endodontic
materials (e.g. AH 26) and during formocresol pulpot-
omies. This review outlines how the human body
reacts to formaldehyde exposure, how recent data has
relooked at the issue of carcinogenicity and leukaemia
associated with formaldehyde, and whether it is possi-
ble to quantify the amount of formaldehyde produced
by endodontic cements. The review analyses the way
formaldehyde is produced from epoxy resins and
addresses the question of whether the amount of form-
aldehyde from endodontic cements is large enough to
override the body’s ability to deal with its own endoge-
nous levels of formaldehyde and should the amount of
formaldehyde produced be a concern.
Keywords: AH 26, carcinogen, endogenous levels,
formaldehyde release, safety.
Received 29 May 2014; accepted 30 September 2014
The release of formaldehyde is a widely known effect
that occurs with many materials used in dentistry.
Some typical examples are methacrylate and urethane
dimethacrylate (base plates used in orthodontics and
prosthetics), composite resin for restorations, epoxy
resins used in root canal treatment and formocresol
in pulpotomies (Santerre et al. 2001, Kopperud et al.
2011). Formaldehyde has been used in the manufac-
ture of particle board, plywood, glues and foam insu-
lation. Approximately 80% of its use is for plastic and
resin manufacture. The remaining 20% is used in
agriculture (seed treatment), reagents in laboratories
and preservatives in cosmetics (Restani & Gali 1991).
It is important to understand the difference between
formaldehyde gas and formaldehyde solution in order
to avoid confusion. Formaldehyde is a flammable gas
with a pungent, strong odour (at greater than 0.3
parts per million [ppm]). It is highly soluble in water
(up to 55%), acetone, benzene, chloroform and etha-
nol. Most formaldehyde is sold as aqueous solutions,
known as formalin, containing 3050% formaldehyde
with methanol as a stabilizer to prevent it polymeriz-
ing into a solid form. Formaldehyde solution is a clear
colourless liquid also with a pungent and irritating
odour (Lewis & Chestner 1981, Budavari 2001,
Sweetman 2011). The chemical formula of formalde-
hyde is HCHO (or CH
O), and it is the simplest
aldehyde being a mono-aldehyde compared to
the di-aldehyde of glutaraldehyde. It is a gas that dis-
solves easily in water to form methylene hydrate
-OH). Methylene hydrate molecules react with
one another, combining to form polymers with
most of the formaldehyde existing as low polymers
-H. Higher polymers
Correspondence: Basil Athanassiadis, 268 Ipswich Rd cnr
Cornwall Street, Annerley, 4103 Brisbane, Qld, Australia
International Endodontic Journal,48, 829–838, 2015©2014 International Endodontic Journal. Published by John Wiley & Sons Ltd
(nup to 100), which are insoluble, are white powders,
and these are called paraformaldehyde (Kiernan
2000). Paraformaldehyde has a formaldehyde compo-
nent of 9199%, and in liquid phase, the powder and
the water vaporize at room temperature to release
formaldehyde (Lewis & Chestner 1981). Formocresol
was introduced into dentistry as a pulpotomy agent by
Buckley in 1904 and consists of 35% tricresol, 19%
formaldehyde, 15% glycerine and water. Variations
include the use of a diluted formula (1 : 5) and of the
mixing of the formocresol into a zinc-oxide eugenol
base instead of applying the solution to the pulp on a
cotton pellet (Kahl et al. 2008, Balaprasanna 2011).
In endodontic practice, there are materials that
contain formaldehyde and/or paraformaldehyde
such as N2 paste (Indrag-Agsa, Losone, Switzerland),
Endomethasone (Septodont, Paris, France), Riebler’s
paste (Amubarut; Wera Karl, Biesingen, Germany)
and SPAD (Trailement, Quetigny, France) which
have paraformaldehyde levels between 4 and 8%
(Bonsor & Pearson 2013). Other materials such as
the epoxy resin cements, for example AH26 (De Trey
Dentsply, Konstanz, Germany) and AH Plus (De Trey
Dentsply), do not contain formaldehyde as an ingredi-
ent, but they release minimal levels of formaldehyde
during their setting reaction. The formaldehyde
release peaks after 2 days and then slowly decreases
for a maximum period of 2 weeks (Lewis & Chestner
1981, Koch 1999).
The American Association of Endodontists issued a
position paper on the use of formaldehyde- and para-
formaldehyde-containing materials in which they rec-
ommended that they should not be used during
endodontic treatment due to their toxicity and carcin-
ogenicity (AAE 2013).
An electronic search was conducted using PubMed
and Google Scholar search engines to identify appro-
priate articles written in the English language. The
following keywords were used: formaldehyde, carcino-
gen, toxicity, formocresol, endodontics, epoxy resins,
AH26, AHPlus. Textbooks such as Merck Index and
Martindales were also examined for relevant informa-
tion. Government agency websites in the USA, Austra-
lia and United Kingdom related to formaldehyde were
examined. The reference lists of the identified publica-
tions were also examined for additional articles.
Sources of formaldehyde
The possible routes of exposure to formaldehyde are
by ingestion, inhalation, dermal absorption and blood
exchange. Once absorbed, formaldehyde is very
quickly broken down. Almost every tissue in the body
has the ability to breakdown formaldehyde. It is usu-
ally converted to a nontoxic chemical called formate,
which is excreted in the urine. Formaldehyde can also
be converted to carbon dioxide and breathed out of
the body. Formaldehyde is irritating to tissues when it
comes into direct contact with them. The most com-
mon symptoms include irritation of the eyes, nose
and throat, along with increased tearing, which
occurs at air concentrations of 0.43 ppm (ATSDR
1999, Golden 2011).
Humans are exposed to formaldehyde on a daily
basis from various sources related to lifestyle and
diet. Some of these sources are foods such as shiitake
mushrooms (40380 ppm), fresh seafoods (mackerel,
squid, scallop, octopus at 2 ppm), fruit and vegeta-
bles (322 ppm). Inhalation of trace amounts of
formaldehyde can easily occur from multiple sources,
such as the decomposition of plant residues, automo-
tive exhaust, cigarette smoke, outgassing of furniture
and joinery items manufactured from chipboard or
plywood, insulating materials used in construction,
workplace use of various synthetic resins and glues,
fabrics, cosmetics and hair straightening products.
Combining these various sources, the World Health
Organization (WHO) estimated daily intake of
formaldehyde for an adult is about 10.55 mg day
comprising 9.4 mg day
from food, 1 mg day
from inhalation and 0.15 mg day
from water
(Restani & Gali 1991, WHO 2001, Tang et al.
Formaldehyde is present in virtually all cells in the
human body as a by-product of the metabolism of ser-
ine, glycine, methionine and various other amino
acids. Endogenous levels of metabolically produced
formaldehyde range from 3 to 12 ng g
of tissue
(WHO 2001, Kahl et al. 2008). Formaldehyde can be
readily detected in human plasma with typical con-
centrations of 2.5 ppm (Restani & Gali 1991, Leh-
man-McKeeman 2010, Golden 2011, Checkoway
et al. 2012). No increase in formaldehyde concentra-
tion was seen in the blood of humans, rats and mon-
keys following exposure to concentrations of 1.9 ppm
(2.3 mg m
), 6 ppm (7.2 mg m
) and 14.4 ppm
(17.3 mg m
) gaseous formaldehyde, respectively
(IPCS 2002). This has been attributed to the deposi-
tion of formaldehyde principally in the respiratory
tract and its rapid metabolism (Heck et al. 1985,
Casanova et al. 1988). Exogenous formaldehyde does
not accumulate in the body as it has a biological
Formaldehyde, controversy, risks, quantification Athanassiadis et al.
©2014 International Endodontic Journal. Published by John Wiley & Sons LtdInternational Endodontic Journal,48, 829–838, 2015
half-life of only 11.5 min, and it is quickly cleared
from human plasma. Such rapid metabolism would
inhibit the systemic distribution of formaldehyde
(Restani & Gali 1991, NICNAS 2006).
Formaldehyde is present in low concentrations
(<0.2%) in a wide variety of consumer products. It is
used as a preservative for the control of bacteria and
fungae in water-based solutions in both industrial
and consumer products including dishwashing liq-
uids, disinfectants, fabric conditioners, shampoos,
conditioners and shower gels. Many of these products
are released directly into wastewater streams during
their use and hence, they are a source of formalde-
hyde levels in water (NICNAS 2006). Some common
formaldehyde-releasing preservatives include DMDM
Hydantoin (1,3-dihydroxymethyl-5, 5-dimethyl hyd-
antoin) and imidazolidinyl urea. The free formalde-
hyde content in DMDM Hydantoin is usually up to
2%. Any bacterial activity consumes the free formal-
dehyde which is then replenished from the parent
compound. Over a period of time, all formaldehyde
from the donor molecule is used up in preserving the
product against microbes (NICNAS 2006).
Antimicrobial actions
Formaldehyde solution is bactericidal, sporicidal and
virucidal, but it works more slowly than glutaralde-
hyde. Formaldehyde is an extremely reactive chemical
that interacts with protein, DNA and RNA. When
applied to unbroken skin, formaldehyde solution hard-
ens the epidermis, renders it tough and white, and
produces a local anaesthetic effect. Formaldehyde
prevents tissue autolysis as it binds to protein and
prevents enzymatic degradation of proteins (Kurji
2009). Diluted formaldehyde solution containing
0.75% formaldehyde w/w has been used to treat
warts on hands and feet (McDonnell & Russell 1999,
Kiernan 2000, Sweetman 2011).
Root canal cements that produce formaldehyde on
setting may allow the material to exert some anti-
microbial action to counter the effects of any resid-
ual bacteria left in the root canal system at the
time of root filling. Formaldehyde is a relatively
nonspecific bactericidal agent, affecting the growth
and viability of most gram-positive and gram-nega-
tive bacteria as well as fungi (Sweetman 2011).
Formaldehyde gas has very little penetrative power
as it readily condenses on surfaces and polymerizes.
Its effectiveness as an antimicrobial agent requires a
high relative humidity of 8090%. Formaldehyde
gas is used for disinfection of rooms and cabinets,
and it can be used with low temperature steam for
sterilization of heat sensitive items (Sweetman
Some epoxy resin endodontic cements (e.g. AH 26)
contain hexamethylenetetramine (HMT- also known
as hexamine, methenamine or urotropine), which
itself exerts antibacterial actions, and was first used
as an antiseptic agent (urotropine) in 1894 (Grayson
2010). HMT is a white powder which is freely solu-
ble in water and soluble in alcohol with an alkaline
pH, but the hippurate and mandelate salts of HMT
have a pH of 4 when in solution. HMT owes its anti-
bacterial action to the release of formaldehyde which
is slowly liberated by hydrolysis at acidic pH (<5.5).
The hippurate or mandelate salts are also used for
long-term suppression of chronic or recurrent lower
urinary tract infections. It is only active in acidic
urine when formaldehyde is released (Sweetman
2011). Almost no hydrolysis of HMT occurs at physi-
ological Ph, and it is therefore virtually inactive in
the body at neutral pH (Scott & Wolf 1962, Sweet-
man 2011). The half-life is approximately 4 h, and it
is rapidly and almost completely eliminated in the
urine (Sweetman 2011). In humans, no harmful
reactions or complications have been observed in
patients receiving HMT as an antiseptic at dose levels
of 46 g day
for weeks (Restani & Gali 1991).
HMT continues to be used as an antibacterial agent,
most commonly as a food preservative because of its
antimicrobial activity and its lack of taste and odour
(Restani & Gali 1991). HMT is also used widely in
the manufacturing of particle board, plywood and
foam insulation.
Hexamine, N
, liberates formaldehyde under
acidic hydrolysis. This hydrolysis is accelerated by
heating and decreasing the pH (Dreyfors et al. 1989,
Grayson 2010). Such conditions would be uncommon
following the use of root canal medicaments, but it
may occur if instrumentation and root canal filling
were done in one appointment and periapical inflam-
mation was present. Therefore, the amount of formal-
dehyde produced when hexamine is used in a root
canal filling and following a period of medicament
use would most likely be inconsequential.
The chemical formula for the breakdown of HMT is
as follows:
(HMT) +6 H2O ?4NH
nia) +6CH
O (formaldehyde)
The key ingredient is the requirement of an acidic
pH (<pH 5.5) (Scott & Wolf 1962, Sweetman 2011).
Athanassiadis et al. Formaldehyde, controversy, risks, quantification
International Endodontic Journal,48, 829–838, 2015©2014 International Endodontic Journal. Published by John Wiley & Sons Ltd 831
The controversy of formaldehyde being a
Concerns regarding formaldehyde release are based
on its known properties as an irritant as well as con-
cerns that it may be a carcinogen. There is contro-
versy as to the risk that formaldehyde presents as a
carcinogen, and the possibility that it is a human car-
cinogen is impossible to exclude formally (Sweetman
2011) even though formaldehyde is not a direct
genotoxic agent at sites distant to the portal of entry
(nose, oral cavity) (Checkoway et al. 2012, Gentry
et al. 2013). A substantial body of new evidence has
appeared in the literature between 2010 and 2012,
which shows no increased incidence of nasopharyn-
geal cancer in humans who have a mean formalde-
hyde exposure level of <1 ppm, up to peak levels of
4 ppm (Bolt & Morfeld 2013).
A major issue with assessing the possible carcinoge-
nicity of formaldehyde is that it is present at relatively
constant levels in the blood of humans. These back-
ground levels of formaldehyde create an analytical
problem in differentiating altered or damaged DNA
(adducts) that result from endogenously generated
formaldehyde from those that are directly related to
any exogenous chemical exposure. Various regulatory
bodies have set exposure limits to formaldehyde in air
(Table 1). The International Agency for Research in
Cancer (IARC) has classified formaldehyde as ‘carcino-
genic to humans’ (Cogliano et al. 2005), although
Marsh et al. (2010) later showed that some of the
studies on which this IARC classification was based
had incomplete data sets and striking discrepancies
and presented misleading evidence. The US Occupa-
tional Safety and Health Administration (OSHA) and
the Australian National Industrial Chemicals Notifica-
tion and Assessment Scheme (NICNAS) both regard
formaldehyde as a possible human carcinogen and
consider that it can cause cancer in animals at high
levels that are not found in the majority of workplaces.
Duhayon et al. (2008) stated that the most recent
epidemiological studies indicate that the statement
‘formaldehyde is carcinogenic to humans’ is probably
too strongly worded. In a review of all cohort studies
published to February 2007 (Bosetti et al. 2008)
noted that industry workers and professionals exposed
to formaldehyde showed no appreciable excess risk of
cancers of the oral cavity, pharynx, sinus, nasal cav-
ity and lungs.
Logically, one would expect a site-exposure rela-
tionship with malignancies related to the tissues most
exposed to formaldehyde from inhalation or ingestion.
In cases of high exogenous exposure to formaldehyde,
DNA effects are limited to the respiratory tract, and
lesions have not been observed beyond the point of
contact from inhalation exposure to formaldehyde
(Lehman-McKeeman 2010) nor are levels of adducts
different in remote sites. In other words, exogenous
formaldehyde can cause DNA adducts in nasal epithe-
lial DNA from direct inhalation exposure but not in
bone marrow and other distant sites. The concept
that inhaled formaldehyde could cause leukaemia or
influence myeloid progenitor cells or other bone
marrow cells have been formally excluded (Bolt &
Morfeld 2013). A recent review (Gentry et al. 2013)
concluded that there is no association between form-
aldehyde exposure and myeloid or lymphoid malig-
nancies. Likewise, there is no consistent evidence of
genotoxicity in the bone marrow following exogenous
formaldehyde exposure (Checkoway et al. 2012). The
Table 1 Formaldehyde gas exposure limits from different regulatory bodies
Legal exposure limits
Threshold limit value (TLV) 0.3 ppm 0.2 ppm N/A N/A
Permissible exposure level (PEL)
Limit (PEL) over an 8-h workshift
0.751.00 ppm 0.2 ppm 2.0 ppm 0.3 ppm
Short-term exposure limit (STEL)-over 15-min period 2.0 ppm 0.4 ppm 2.0 ppm 0.6 ppm
Immediately dangerous to life and health (IDLH) >20 ppm N/A N/A N/A
Data derived from Bolt & Morfeld 2013, Duhayon et al. 2008, and regulatory body websites. OHSA, US Occupational Safety and
Health Administration; NIOSH, US National Institute of Occupational Safety and Health; NICNAS, Australian National Industrial
Chemicals Notification and Assessment Scheme; HESIS, Californian Hazard Evaluation System and Information Service;
EU-SCOEL, European Union-Scientific Committee on Occupational Exposure Limits for formaldehyde; UK-HSE, United Kingdom-
Health and Safety Executive; TLV, FA concentration should not exceed this value at any time; N/A, not available. 1 ppm =1 part
of formaldehyde gas per million parts of air. Conversion factors (in air): 1 ppm =1.25 mg m
, 1 mg m
=0.8 ppm (at 20 °C and
1013 hPa) (WHO 2001, Arts et al. 2006).
Formaldehyde, controversy, risks, quantification Athanassiadis et al.
©2014 International Endodontic Journal. Published by John Wiley & Sons LtdInternational Endodontic Journal,48, 829–838, 2015
extensive metabolic capability of humans and the
findings that no inhaled formaldehyde gets past nasal
epithelium into the systemic circulation strongly sug-
gest that formaldehyde should be more appropriately
characterized as a chemical with adverse effects
rather than as a carcinogen (Golden 2011).
Exposure limits
Formaldehyde affects humans when breathing its
vapours or touching the liquid. It reacts quickly with
body tissues and affects the site of direct contact (e.g.
eyes, nose, throat and skin). Formaldehyde can
destroy the skin’s protective oils causing dryness,
cracking and dermatitis. High levels (530 ppm) can
severely irritate the lungs causing chest pain and
shortness of breath (HESIS 2011). In humans, odour
perception of formaldehyde (0.51.0 ppm) precedes
sensory irritation (>2.0 ppm) of the nose, throat and
eyes, with eye irritation accepted as the most sensitive
end-point. Short-term exposure (<1 h) to formalde-
hyde below 2 ppm produces no toxicological effects
on the eyes or upper respiratory tract. Moderate eye,
nose and throat irritation occurs at 23 ppm. A form-
aldehyde concentration of 0.1 ppm is unlikely to
result in any irritant effects for individuals, including
children, asthmatics and the elderly. Adverse effects
occur only at the point of contact after the concentra-
tion achieved is in excess of endogenous levels, and it
exceeds the body’s ability to maintain homoeostasis
(Golden 2011). Formaldehyde vapour is irritant to
the nose, eyes and upper respiratory tract and may
cause coughing, spasm and oedema of the larynx,
bronchitis and pneumonia with asthma-like symp-
toms with repeated exposure (Sweetman 2011).
The minimum risk level (MRL) is an estimate of the
daily human exposure to a hazardous substance that
is likely to be without appreciable risk of adverse, non-
cancer health effects over a specified duration of expo-
sure. For oral exposure to formaldehyde, an MRL of
0.3 mg kg
has been derived for intermediate-
duration exposure, and an MRL of 0.2 mg kg
has been derived for chronic-duration exposure
(ATSDR 1999).
In the blood, the mean formaldehyde concentra-
tion is reported as 2.24 mg 0.07 mg kg
(Restani & Gali 1991). WHO estimates that an adult
is exposed to 10.55 mg formaldehyde day
food, air and water. There are fairly constant endog-
enous levels of 2.5 ppm formaldehyde in blood
(Golden 2011). Szarvas et al. (1986) determined the
endogenous level of formaldehyde in blood at an
average of 0.5 lgmL
of blood. With approxi-
mately 5 L of blood volume in humans, this equates
to 2.5 mg of endogenous formaldehyde circulating at
any one time. Endogenous turnover of formaldehyde
was estimated to be approximately 878
1310 mg kg
body weight per day, assuming a
half-life of 11.5 min (EFSA 2014).
Quantification of formaldehyde
There are several methods used to assess formalde-
hyde release from endodontic materials, and each has
its advantages and disadvantages (Table 2). The
direct instrumental methods of GC-MS (Sp
et al. 1993) and direct spectrophotometry in the
infrared or ultraviolet ranges (Leonardo et al.1999)
can detect formaldehyde but cannot give absolute
concentrations. The remaining methods involve an
initial reaction with colorimetric reagents to form
formaldehyde adducts which are then analyzed by
their ultraviolet absorption spectra, generally after
removing other components by HPLC (Cohen et al.
1998, Koch 1999, Koch et al. 2001). Current meth-
ods include direct instrumental analysis (e.g. gas
phase spectroscopy using a tunable diode laser) and
derivatization methods involving subsequent chroma-
tography and ultraviolet detection, as well as more
sensitive methods using fluorescence (Li et al. 2005).
The biggest challenge with fluorescence assay meth-
ods is to avoid false positives due to the presence of
contaminants or nonspecific reactions (Compton &
Purdy 1980). Nevertheless, the fluorescence method
when compared with the derivatization/HPLC method
has been found to give statistically comparable results
as well as having high sensitivity (Pinheiro et al.
In order to determine the amount of formaldehyde
produced in a typical root canal filling, the mass of
resin deposited has to be calculated. Results from
three studies were used to determine the average sur-
face area found in a prepared molar root canal (Peters
et al. 2001, 2003, H
ubscher et al. 2003). The aver-
age from the three studies for the total surface area of
a prepared maxillary molar was 74.68 mm
. Average
film thickness determined from two studies (Weis
et al. 2004, Jung et al. 2005), was used to determine
the volume of resin and found the average film
thickness was 18.0 lm. This was used in the calcula-
tion below. AH 26 was used as an example in the
calculations below as this material produces the high-
Athanassiadis et al. Formaldehyde, controversy, risks, quantification
International Endodontic Journal,48, 829–838, 2015©2014 International Endodontic Journal. Published by John Wiley & Sons Ltd 833
est formaldehyde release from the epoxy resin
cements. Epoxy resins such as AH 26 and AH Plus
release their maximum amount of formaldehyde after
2 days. There is then a gradual decline to zero with
no further release after 2 weeks.
The density of AH 26 powder, based on the above
composition is 7.06 g cm
(taking the density of
bismuth trioxide as 8.5 g cm
and that of hexa-
methylenetetramine as 1.33 g cm
). This powder
is then mixed with AH26 epoxy resin (density
1.16 g cm
) at a recommended ratio of 2 : 1. The
manufacturer’s instructions imply measurement by
volume as this is the usual mode of measurement in
the dental surgery setting. Mixing to this specifica-
tion gives a composition of 75% powder and 25%
resin by weight and thus an average density of
5.59 g cm
The volume of cement will be equal to the surface
area of the root canal multiplied by the thickness of the
cement. Therefore, based on the above findings, the
volume of cement used in a typical molar root canal
filling is 74.68 mm
90.018 mm =1.34 mm
The density is equal to the mass divided by the vol-
ume. Hence, the mass of sealer used is 7.5 milligrams
(mg) in a typical root canal filling.
Cohen et al. (1998) used 5 g of AH 26, previously
cured for 1 h and mixed it with 100 mL distilled
water. This was adjusted to a pH of 5.0 to maximize
the amount of formaldehyde released from the sealer.
They reported that 1347 ppm was released. Unfortu-
nately, this result cannot be converted to an amount
that could be used to work out the formaldehyde
levels per mg of material.
Koch et al. (2001) reported that the mean formal-
dehyde release from AH 26 was 6.6 lgmg
. This
material was stored dry for 6 months before ground
samples were taken and analyzed. Therefore, for a
typical root canal filling, the amount of formaldehyde
released would be 7.5 mg 96.6 lg formalde-
hyde mg
cement =49.5 lg formaldehyde. Unfortu-
nately, the length of time and the storage conditions
mean the result is of limited value.
In another study, Koch (1999) determined that
8 mg of formaldehyde was produced per gram of
Table 2 Laboratory studies of formaldehyde release from endodontic materials
Reference Method and materials Results Comment
et al. (1993)
GC-MS after mixing and after 100%
RH exposure of AH 26 and N2
Relative FA levels from MS ion
intensities. No [FA] possible
but N2 level was ~1000 times that
of AH 26
Method has limited quantification
and easily saturated at high
[FA]. Cannot be converted
to ppm
Cohen et al.
DNPH reaction with FA then HPLC
following method EPA8315. AH
26, AH Plus and EZ-Fill sonicated
in pH 5 buffer at 40 °C for 60 min
with DNPH
AH 26: 1347 ppm
AH Plus: 3.9 ppm
EZ-Fill: 540 ppm
(based on mass of resin)
No standard deviation given
No indication of cure time before
buffer immersion. Extensive
workup required before HPLC
separation and detection.
Sensitivity 0.25 ppm
et al. (1999)
Direct UVvis and IR
spectrophotometry of AH 26,
AH Plus, Top Seal and
Endomethasone. Cured 72 h
FA detected in AH 26 and
Endomethasone but not
quantified. No FA detected
from AH Plus and Top Seal
Simple UV spectrophotometry
without formaldehyde
derivatization is subject to
interferences. IR
spectrophotometry was not
Koch (1999) Colorimetric analysis of FA with
acetylacetone and ammonia using
Visible spectra at 412 nm, for
AH 26, Amubarut and N2.
Specificity confirmed with HPLC.
Effect of mix ratio, storage time and
surface to volume ratio on
[FA] reported
Highest [FA] initially after mixing:
AH 26: 8000 1800 ppm
Amubarut: 70000 5000 ppm
N2: 17 000 2700 ppm
After 48 h reduced by 94%
(AH 26); 61% (Amubarut) and
74% (N2)
Accepted analytical method
(Hantzsch reaction).
Sensitivity ~20 ppm
Koch et al. (2001) FA reaction with dimedone
followed by HPLC of adduct
detected at 260 nm. AH 26,
Amubarut and N2 analysed after
6 months storage, with grinding
before analysis
AH 26: 6600 2600 ppm
Amubarut: 8300 1000 ppm
N2: 300 100 ppm
Method previously used by
Ruyter (1980). Variability in
results may reflect sample more
than method
Formaldehyde, controversy, risks, quantification Athanassiadis et al.
©2014 International Endodontic Journal. Published by John Wiley & Sons LtdInternational Endodontic Journal,48, 829–838, 2015
AH 26 immediately after mixing and this then
reduced to <1mgg
after 48 h. Utilizing the high-
est formaldehyde release (8 mg formaldehyde g
the amount of formaldehyde released in a typical root
canal filling with 7.5 mg sealer would be 0.06 mg of
formaldehyde, which is 1/40 of the normal endoge-
nous levels in all humans and 1/175 of the WHO
(2001) daily intake value. The formaldehyde amount
falls to zero after 2 weeks as discussed earlier. The
amount of 0.06 mg of formaldehyde is comparable to
the daily formaldehyde intake for individuals in
homes with people who smoke, which has been esti-
mated to be 0.030.067 mg (Nazaroff & Singer
When performing a pulptomy, the mean dose of
formocresol has been determined to be 0.013 mg per
pellet, but the actual dose that interacts with the pulp
is probably smaller than this (Kahl et al. 2008, Milnes
2008). This amount is 1/810 of the 10.55 mg day
of formaldehyde that occurs in our daily intake from
food, water and air (WHO 2001).
How formaldehyde is generated in the
curing of epoxy resins
Epoxy resins are thermosetting polymers formed by a
step polymerization with a suitable cross-linking agent
such as a diamine. Because of their industrial impor-
tance, the mechanism of curing for epoxy resins has
been studied in great detail to achieve optimum
mechanical properties and environmental durability
(Halley & George 2009). The properties achieved
depend on the chemical structure of the original resin
and curing agent, and the number of crosslinks per
unit volume (the crosslink density) achieved in the
curing process.
The curing process is a chemical reaction in which
the terminal epoxide groups in epoxy resin react with
a curing agent to form a cross-linked three-dimen-
sional network. The epoxy resin cement AH26 was
introduced to dentistry for root canal fillings over
50 years ago, and an unusual feature of this resin was
the choice of HMT as the curing agent. HMT is a ter-
tiary amine that, to the authors’ knowledge, had not
previously been in use for epoxy resin curing, but it
was a key ingredient in the curing of phenolic resin
precursors and in rubber vulcanization (Dreyfors et al.
1989). In phenolic resins, the curing reaction relies on
the liberation of formaldehyde in the presence of acid.
In contrast to its use in phenolic resins, the curing
reaction of hexamine with epoxy resins does not
require the liberation of formaldehyde but rather the
attribute of the HMT molecule as a tertiary amine.
There is no other industrial application of epoxy res-
ins that uses HMT as a curing agent (Dreyfors
et al.1989), possibly because of the slow curing reac-
tion and the likely liberation of formaldehyde if expo-
sure to acid subsequently occurs.
It has been reported (Oliver & Abbott 1991) that
moisture is required for the polymerization of AH26
(i.e. DGEBA epoxy resin cured with HMT). This is an
interesting result as epoxy resin cure does not usually
require the presence of moisture (Halley & George
2009) although trace amounts could potentially cata-
lyze the reaction through a process of hydrogen bond-
ing. The liberation of formaldehyde and ammonia by
the hydrolysis of HMT is not required for it to function
as a tertiary amine for catalysis of the polymerization
of DGEBA epoxy resin in AH26. It is possible that an
intermediate in the hydrolysis of hexamine is a pri-
mary amine, and this may accelerate the reaction so
that the effect is a secondary one and not a require-
ment for the reaction to occur. What is important is
that the HMT is a catalyst, so it is not consumed in
the anhydrous curing reaction. If the cure is truly cat-
alytic, then all HMT added to the resin is expected to
be present at the end of the curing reaction.
In summary, there should be no production of
formaldehyde from epoxy resins when cured with
agents other than HMT. The production of formalde-
hyde from HMT is a consequence of subsequent
hydrolysis and not the curing process of the epoxy
resin in AH26.
Evaluation of the risks posed by
formaldehyde release from root canal
Block et al. (1980) filled dogs teeth with N2 paste
containing 6.5% paraformaldehyde and measured the
amount of
C-labelled paraformaldehyde released
into the circulation after 28 days. They showed that
the maximum level was reached after 1 day and it
was spread systemically, but there was no quantifica-
tion of the amounts. In another study (
et al. 1981), using 15% w/v formaldehyde placed in
extracted human teeth, the amount of formaldehyde
released through dentine and cementum into distilled
water was determined. Formaldehyde penetrated read-
ily through the apical third of roots within 60 s, par-
ticularly in roots derived from young patients. Values
of 80120 lg per 3 h were obtained after insertion of
Athanassiadis et al. Formaldehyde, controversy, risks, quantification
International Endodontic Journal,48, 829–838, 2015©2014 International Endodontic Journal. Published by John Wiley & Sons Ltd 835
between 5 and 10 lL into the root canal (
made et al. 1981). Taken together, these studies
showed that formaldehyde permeates through dentine
and cementum quickly, and formaldehyde could enter
adjacent tissues and the systemic circulation.
However, these materials are no longer used in con-
temporary endodontic practice, and their high con-
centrations of formaldehyde do not reflect the amount
of formaldehyde that would be present in the systemic
circulation when formaldehyde is released from epoxy
resins (e.g. AH26, AH Plus). It is known that formal-
dehyde is rapidly metabolized in the human body,
and this was highlighted in a study by (Kahl et al.
2008) involving 30 children aged 26 years age who
underwent 85 pulpotomies (15 per child). A cotton
pellet with 0.013 mg of formocresol was placed in the
pulp chamber for 5 min for each pulpotomy per-
formed. Blood samples were taken before and after
the pulpotomies, yielding a total of 312 blood sam-
ples. There was no detectable formaldehyde above
normal baseline physiologic concentrations in any of
the blood samples.
In pulpotomies, formocresol is positioned in the
base of the pulp chamber in a fixed area which is in
direct contact with pulp tissue (for a period of 5 min).
In a root canal filling, the path for formaldehyde
release is more complex as the formaldehyde is pro-
duced from the epoxy resin cement which is spread
throughout the entire root canal (coronal to apical).
The formaldehyde has to be released and it then has
to diffuse through the dentine and cementum or via
the apical foramen and into the blood supply.
Systemic absorption is of no importance since after
formocresol is placed and formaldehyde is produced, it
vaporizes quickly and is rapidly eliminated in the
urine. Vaporization and dissolution of formaldehyde
in exudate minimizes the potential toxicity of root
canal medication (Gutierrez et al.1991).
Appraisals of risk from formaldehyde
The authors of two older articles (Lewis & Chestner
1981, Lewis 1998) have presented a view on formal-
dehyde which is not consistent with the more recent
reports of measured formaldehyde release from dental
materials used in vitro. These earlier articles discussed
chronic exposure of high levels of formaldehyde
rather than the short-term exposures used for formoc-
resol pulpotomies (i.e. minutes), and the doses from
epoxy resins in root canal fillings that are at least
40-fold lower than those normally ingested or present
in the circulation. There is no current evidence of
harm in humans from the latter (Sue Seale 2010).
This same confusion is evident in a paper from the
same author (Lewis 2010) which claims that
‘recently formaldehyde was strongly associated with
leukaemia whilst generally accepted as a direct cause
of nasopharyngeal cancer’. The research on formalde-
hyde referred to in that paper has for the most part
been discredited or updated, primarily because newer
and more rigorous methodologies have been used to
investigate formaldehyde (Milnes 2008).
In conclusion, it appears that the amount of form-
aldehyde released during pulpotomies with formocre-
sol and from resin-based root canal fillings are at
least 1/40 less than the normal endogenous levels in
humans, and they do not pose any health risks.
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Formaldehyde, controversy, risks, quantification Athanassiadis et al.
©2014 International Endodontic Journal. Published by John Wiley & Sons LtdInternational Endodontic Journal,48, 829–838, 2015
... Formaldehyde (HCHO) is a colorless, flammable, strong-smelling organic compound [1,2] and is an important chemical feedstock as a precursor to many widely used materials and chemical compounds in manufactural industry [1,2]. Large quantities of formaldehyde (over millions of tons) are used each year in the production of household supplies, such as shampoo, lipstick, toothpaste, vaccines, disinfectants, paper product coatings, permanent-press clothing, and liquid coatings [1]. ...
... Formaldehyde (HCHO) is a colorless, flammable, strong-smelling organic compound [1,2] and is an important chemical feedstock as a precursor to many widely used materials and chemical compounds in manufactural industry [1,2]. Large quantities of formaldehyde (over millions of tons) are used each year in the production of household supplies, such as shampoo, lipstick, toothpaste, vaccines, disinfectants, paper product coatings, permanent-press clothing, and liquid coatings [1]. ...
... Formaldehyde is mainly used in the production of industrial resins [3], which are widely used in various materials for furniture manufacturing and the construction industry, including insulation materials, glues and adhesives, particleboards, plywoods, and fiberboards [4]. Due to its high volatility, significant amounts of formaldehyde are released into the air from furniture and building materials, with the pressed-wood products (particleboards, plywoods, and fiberboards) being the main sources of indoor air pollution [2,5]. HCHO is highly toxic to human beings and animals [1]. ...
Full-text available
Tungsten carbide (WC) nanostructures were prepared by carbothermal reduction (CR) of tungsten-impregnated pinewood-derived activated carbon (AC) at 1000 °C under an inert atmosphere. Brunauer–Emmet–Teller (BET) surface area, pore structures of the AC, and catalyst samples were evaluated by N2 adsorption–desorption experiments. The structures of the catalysts were characterized using X-ray powder diffraction (XRD). The morphologies and particle structures of the synthesized WC nanoparticles were investigated by field emission scanning electron microscopy (FESEM) and high-resolution transmission electron microscopy (HRTEM). The WC/AC material was used as support of the platinum catalysts for catalytic oxidation of formaldehyde (HCHO) from interior sources. Pt-WC/AC catalysts with different platinum loadings were assessed for the catalytic oxidation of HCHO at low temperature. The catalytic performance was found to be significantly influenced by reaction temperature, initial formaldehyde concentration, relative humidity, and space velocity. The testing results demonstrated that HCHO can be totally oxidized by the 1 wt% Pt-WC/AC catalyst in the gas hourly space velocity (GHSV) = 50,000 h−1 at 30 °C with a relative humidity (RH) of 40%.
... Polymethyl methacrylate (MMA) resin has been widely used to manufacture many dental materials for a long time [2]. On the contrary, many research studies have shown that heat-polymerized acrylates have many advantages over cold-polymerized materials due to almost complete polymerization and better biological properties [3,4]. One of the significant concerns about using MMA resins for denture base fabrication is the release of byproducts such as formaldehyde and monomer into the oral environment [5]. ...
... Some studies have shown the lack of biocompatibility and cytotoxicity of this material [11,12]. MMA monomer is an allergen and a contributing factor in the sick building syndrome (SBS), and even some studies of humans have suggested that MMA exposure is linked with certain types of cancers [4]. Long-term exposure to this substance causes a headache, burning eyes, and mutational consequence respiratory system irritation [2,3,5,8]. ...
... Long-term exposure to this substance causes a headache, burning eyes, and mutational consequence respiratory system irritation [2,3,5,8]. According to the International Agency for Research on Cancer, formaldehyde has been introduced as a potential carcinogen for animals, but the carcinogenic effect of formaldehyde on humans is controversial [4]. However, the toxicity effects of formaldehyde on man and animals in some studies have been reported [13,14]. ...
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Background/Purpose. The biocompatibility and cytotoxicity of formaldehyde and monomer are essential in resin-based denture’s byproducts. This present study was performed to compare the release of formaldehyde and monomer and biocompatibility of three brands of heat-curing acrylic resins, including Ivoclar, Bayer, and Acropars, with different mixing properties and the same processing methods. Materials and Methods. In this experimental in vitro study, 18 samples were fabricated from Ivoclar, Bayer, and Acropars heat-curing acrylic resins (each group consisting of 6 samples). The released formaldehyde and monomer level were measured and registered for 1, 7, and 30 days. Also, methyl methacrylate release from samples was used to test cell cytotoxicity using L-929 murine fibroblast. The data were analyzed with repeated measures, one-way ANOVA, and Kruskal–Wallis tests. Results. For formaldehyde release of 1 day, Ivoclar acrylic resin showed the lowest level, followed by Bayer and Acropars acrylic resins (P<0.05). On 7 and 30 days, Bayer acrylic resin released the lowest formaldehyde, followed by Ivoclar and Acropars acrylic resins (P<0.05). Acropars showed the weakest and most significant results regarding biocompatibility and monomer release in all three points of time, respectively (P<0.05). Conclusion. Acropars acrylic resin showed the most significant formaldehyde and monomer release and least biocompatibility compared to Bayer and Ivoclar for 1, 7, and 30 days; however, after 30 days, all three resins displayed the same amount of formaldehyde release.
... Inhalation exposure to formaldehyde commonly occurred in industries [4]. This chemical irritates the eye, nose, throat, and respiratory systems [5]. ...
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Formaldehyde as a mass-produced chemical is used in many contexts. The genotoxicity and mutagenicity of formaldehyde are observed in different human body organs, such as buccal and white blood cells. The purpose of this study is to evaluate the lower confidence interval of benchmark dose (BMDL) for genotoxic damage of formaldehyde in the workplace, according to published studies. Studies from occupational genotoxic damage of formaldehyde were retrieved using search in databases such as Google Scholar, Web of Science, and PubMed until April 2020. The search strategy was established based on the words-formaldehyde‖,-genotoxicity‖,-carcinogenicity‖,-DNA damage,‖ and-occupational exposure‖. Based on dose-response data from three studies, benchmark dose (BMD) analysis was performed using EPA-BMD Software. Finally, five studies were included in the final BMDL conclusion. Polynomial and Hill models were used for BMDL evaluation in three studies, and BMD of formaldehyde was estimated between 0.062 to 0.26 ppm. The lowest level of BMDL (0.028 ppm) in five studies was considered the basic value for genotoxicity risk assessment. The estimated BMDL is approximated to the time
... The direct antimicrobial effects for epoxy resin-based cements, seem to be slightly lower as compared with those based on zinc oxide-eugenol [13]. In addition, higher cytotoxicity has been found towards fibroblasts as compared with other types of cements, along with a genotoxic effect for AH-26 due to the release of formaldehyde, which has not been found for AH Plus [14]; however, biocompatibility is higher than in zinc oxide-eugenol-based cements [15]. ...
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Objectives The purpose of this systematic review of the literature is to investigate which of the epoxy-based cements and those based on Tricalciumsilicate (MTA, Bioceramic) have the best sealing capacity through the analysis of studies that have provided a survey model in vitro of bacteria leakage. Source The articles were identified using electronic databases such as PubMed, Scopus, the search was conducted between 8.12.2020 and 31.12.2020 and a last search was conducted on 2.12.2021. Study selection 678 records were identified and after removing the duplicates we obtain 481 records, with the first phase of screening and selection of records we reached 204 and with the application of the inclusion and exclusion criteria we selected 31 articles, only 9 studies made a direct comparison between the two endodontic cement categories and presented data that could be included in the metaanalysis. Data The meta-analysis of first outcome shows an odds ratio of 2.70 C.I.(Confidence Interval) [1.54, 4.73], the test for overall effect has a p value = 0.0005 with a heterogeneity index of I 2 of 9%; The second outcome meta-analysis shows an Odds Ratio of 1.50 C.I. (Confidence Interval) [0.92, 2.46] with a p value of 0.10 with an I 2 of 79%. Conclusion the sealing ability is higher for epoxy resins than for tricalcium silicate-based cements, for observation periods longer than 90 days. Clinical relevance The knowledge of the cement that determines the best sealing ability and resistance to microbial leakage, can be of help for the dentist who has to face clinical situations such as endodontic retreatments whose failure is determined by the persistence of bacteria in the endodontic canals
... AH-26 releasing formaldehyde while setting and how it could possibly be of carcinogenic effect. However, one paper has found that the amount of formaldehyde released during pulpotomies with formocresol and from resin-based root canal fillings are at least 1/40 less than the normal endogenous levels in humans, and they do not pose any health risks (Athanassiadis et. al, 2015). AH Plus (Dentsply DeTrey, Konstanz, Germany), an epoxy-amine resin-based sealer, is the modified formulation of AH-26, and does not release formaldehyde like it's previous version. When comparing the sealing ability and apical leakage of AH-26 and AH Plus, there was no statistically significant differences (De Moor et al., 2004). Moreo ...
Introduction: The ideal endodontic sealer should be biocompatible, dimensionally stable, and have proper bond strength to dentin. The aim of this study was to apply a hoop stress to sectioned teeth discs which have been obturated with AH Plus sealer with no gutta percha, EndoSequence Bioceramic Sealer (BC Sealer) with no gutta percha, and Tetranite® with no gutta percha until fracture occurred and then compared the failure stresses. Methods: Teeth were divided into three groups based on the sealer type used. The teeth were sectioned into 2 mm thick discs and load was applied using a piston until fracture took place. The stress generated by the sealer on the dentinal wall was then calculated using a hoop stress formula. One – way ANOVA with a 95% multiple range test was used to compare hoop stresses at failure for all groups (SPSS, TBM). Tukey HSD multiple comparisons test was also implemented to compare values of each group. Linear regression was used to examine failure load versus dentin wall thickness (SigmaPlot 13.0, Systa Software). Results: Fracture loads forces exerted by the various sealers on the internal tooth wall, demonstrated significant differences amongst all three groups (p < 0.0001). The mean and standard deviation values for failure stress loads were 499.80±120.5555 MPa, 622.3125± 83.7154 MPa, and 708.2357± 68.2772 MPa for the AH Plus sealer with no gutta-percha group, BC sealer with no gutta-percha group, and Tetranite® group respectively. Multiple comparisons showed significant differences between the AH Plus sealer group and BC sealer group (p < 0.002), AH Plus sealer group and Tetranite® group (p < 0.0001), and BC sealer group and Tetranite® group (p < 0.042). Conclusions: Implementing the hoop stress introduces a novel method for the field of endodontics, of testing sealers and their influence on dentin strength. The current knowledge gap in endodontics lacks a specific method or test application for sealers to potentially enhance dentin strength. The use of piston drive hoop stress test in conjugation with the MTS 858 Mini Bionix® II Biomaterials Testing System is able to provide a method for testing failure stress loads on obturated sectioned teeth. Tetranite® significantly increased fracture stress compared to AH Plus sealer and Endosequence BC sealer. The novel Tetranite group enhanced dentin strength in this study
... However, during its setting reaction, minimal levels of 3.9 ppm formaldehyde were detected in one study [72]. Such a low level of formaldehyde is similar to its endogenous concentration in human plasma [73][74][75][76][77] and several dozen times lower than the bactericidal level against E. faecalis [78]. ...
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Dental materials used in root canal treatment have undergone substantial improvements over the past decade. However, one area that still remains to be addressed is the ability of root canal fillings to effectively entomb, kill bacteria, and prevent the formation of a biofilm, all of which will prevent reinfection of the root canal system. Thus far, no published review has analysed the literature on antimicrobial additives to root canal sealers and their influence on physicochemical properties. The aim of this paper was to systematically review the current literature on antimicrobial additives in root canal sealers, their anti-fouling effects, and influence on physicochemical properties. A systematic search was performed in two databases (PubMed and Scopus) to identify studies that investigated the effect of antimicrobial additives in epoxy resin-based root canal sealers. The nature of additives, their antimicrobial effects, methods of antimicrobial testing are critically discussed. The effects on sealer properties have also been reviewed. A total of 31 research papers were reviewed in this work. A variety of antimicrobial agents have been evaluated as additives to epoxy resin-based sealers, including quaternary ammonium compounds, chlorhexidine, calcium hydroxide, iodoform, natural extracts, antibiotics, antifungal drugs, and antimicrobial agent-functionalised nanoparticles. Antimicrobial additives generally improved the antimicrobial effect of epoxy resin-based sealers mainly without deteriorating the physicochemical properties, which mostly remained in accordance with ISO and ANSI/ADA specifications.
Aims: The aim of this study was to evaluate the biocompatibility of resinous root canal sealers: Sealer 26, AH plus, and SK Seal Root Canal Sealer in the subcutaneous tissue of rats. Subjects and methods: Twenty-four Wistar rats received polyethylene tubes containing the sealers and empty tubes as control (n = 6). After 7, 15, 30, and 60 days, animals were killed and polyethylene tubes were removed with the surrounding tissues. The specimens were embedded in paraffin, processed for hematoxylin-eosin and immunohistochemistry assessed for fibronectin (FN) and tenascin (TN). Statistical analysis used: Data were tabulated and analyzed via Kruskal-Wallis and Dunn's test (P < 0.05). Results: All groups induced a moderate inflammatory reaction after 7 and 15 days (P > 0.05); after 30 days, a mild inflammatory infiltrate was observed in control groups, and moderate in sealers groups (P > 0.05); all groups showed mild inflammatory infiltrate at 60 days (P > 0.05). Overall, the fibrous capsule was considered thick only on the 7th day and became thin over time. All groups had expression for FN and TN in all analyzed periods, with high immunolabeling in sealers groups when comparing with the control group (P < 0.05). Conclusion: All sealers demonstrated biocompatibility and induced FN and TN expression.
Sealing the therapeutic agents in the root canal is considered to be an essential step in root canal therapy. The lyotropic liquid crystalline precursor (LLCP) incorporated with chlorhexidine (CHX) and silver nanoparticles (Ag-NPs) has been confirmed as a promising candidate for root canal therapy in the previous study. Importantly, the stability of the LLCP system was a significant determinant for its therapeutic effect and further application. The objective of this study was to comprehensively investigate the stability of the LLCP incorporated with CHX and Ag-NPs. The oil-water partition coefficient of CHX and Ag-NPs was measured. The water absorption and the physical stability of drug-loaded LLCP solution were studied. Stability under high temperature, high humidity, and strong light irradiation was also investigated. The results demonstrated that CHX and Ag-NPs could be entrapped in the water channel of LLCP, indicating the low tendency of drugs leakage. The drug-loaded LLCP was a pseudoplastic fluid and it showed an excellent physical stability with a sedimentation rate of 0.981 and a settling time of 26~28 h. The payload of LLCP was confirmed to weaken the water absorption behavior, which facilitated its transformation to cubic liquid crystal. The stress testing under high temperature, high humidity, and strong light irradiation also manifested that the LLCP was stable when stored under moisture-proof condition. In conclusion, the developed LLCP incorporated with CHX and Ag-NPs was highly stable during storage and qualified for further application.
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Bahan tambahan pangan (BTP) adalah bahan yang ditambahkan ke dalam pangan untuk mempengaruhi sifat dan atau bentuk pangan. Formaldehid merupakan salah satu substansi yang sering digunakan sebagai BTP. Penelitian ini bertujuan untuk mengetahui kadar formaldehid dalam bahan pangan mentah yang dijual di pasar tradisional Kota Yogyakarta. Sampel yang digunakan dalam penelitian ini adalah tahu putih, mie basah, ikan pindang, dan ikan asin. Teknik sampling yang digunakan adalah stratified random sampling. Analisis kualitatif dan kuantitatif dilakukan di Laboratorium Biologi UAD menggunakan formalin test-kit dan spektrofotometer. Sampel positif formaldehid dengan pengujian test-kit dianalisis lebih lanjut dengan SPSS. Persamaan regresi linier yang digunakan adalah linier y = 5E-06x – 0,0028 dengan R2 sebesar 0,9977. Data menunjukkan bahwa terdapat 10 sampel dari total 92 sampel yang positif mengandung formaldehid dengan konsentrasi 4358, 8441, 30310, 11436, 9348, 16154, 7624, dan 9348 ppm. Konsentrasi ini kemudian diuji secara statistic menggunakan One-sample T Test dan didapatkan hasil p value < 0,05. Berdasarkan hasil tersebut, disimpulkan bahwa konsentrasi formaldehid pada sampel ikan asin secara signifikan lebih tinggi dibandingkan dengan kadar formaldehid yang dapat ditolerir oleh tubuh, yaitu 108 mg/kg berat badan. Kata kunci: formaldehid, bahan pangan mentah, pasar tradisional, analisis kuantitatif
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In the United States, 48 million adults smoke 3.5-5 x 10(11) cigarettes/year. Many cigarettes are smoked in private residences, causing regular environmental tobacco smoke (ETS) exposure to roughly 31 million nonsmokers (11% of the US population), including 16 million juveniles. (Upper bound estimates are 53 million exposed nonsmokers including 28 million juveniles.) ETS contains many chemical species whose industrial emissions are regulated by the US federal government as hazardous air pollutants (HAPs). In this paper, average daily residential exposures to and intakes of 16 HAPs in ETS are estimated for US nonsmokers who live with smokers. The evaluation is based on material-balance modeling; utilizes published data on smoking habits, demographics, and housing; and incorporates newly reported exposure-relevant emission factors. The ratio of estimated average exposure concentrations to reference concentrations is close to or greater than one for acrolein, acetaldehyde, 1,3-butadiene, and formaldehyde, indicating potential for concern regarding noncancer health effects from chronic exposures. In addition, lifetime cancer risks from residential ETS exposure are estimated to be substantial ( approximately 2-500 per million) for each of five known or probable human carcinogens: acetaldehyde, formaldehyde, benzene, acrylonitrile, and 1,3-butadiene. Cumulative population intakes from residential ETS are compared for six key compounds against ambient sources of exposure. ETS is found to be a dominant source of environmental inhalation intake for acrylonitrile and 1,3-butadiene. It is an important cause of intake for acetaldehyde, acrolein, and formaldehyde, and a significant contributor to intake for benzene.
Technical Report
The FEEDAP Panel received a request to deliver a scientific opinion on the safety and efficacy of formaldehyde used in feed for all animal species based on dossiers submitted by applicants. In parallel, the ANS Panel evaluated the safety of formaldehyde formed from endogenous production and from dietary sources of methanol, including aspartame. In order to support both evaluations, assistance was requested to the SCER unit to evaluate the oral internal dose of formaldehyde in humans from endogenous production, food-derived from target animals exposed to formaldehyde-treated feed and formaldehyde generated from dietary sources of methanol, including from food additives such as aspartame. Endogenous turnover of formaldehyde was estimated to be approximately 0.61-0.91 mg/kg bw per minute and 878-1310 mg/kg bw per day assuming a half life of 1 1.5 min. Compared with formaldehyde turnover and the background levels of formaldehyde from food sources (1.7-1.4 mg/kg b. w per day for a 60-70 kg person), including from dietary methanol, the relative contribution of exogenous formaldehyde from consumption of animal products (milk, meat) from target animals exposed to formaldehyde-treated feed was negligible (<0.001 %). Oral exposure to formaldehyde from aspartame involves metabolism to methanol and further oxidation to formaldehyde. At the current ADI of 40 mg/kg bw per day for aspartame, formaldehyde would be approximately 4 mg/kg bw per day and represent only 0.3-0.4 % of the endogenous turnover of formaldehyde.