ChapterPDF Available

SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT AND HUMAN BEINGS ENVIRONMENT AND SOCIETY

Authors:
  • Babasaheb Bhimrao Ambedkar University, Lucknow

Abstract and Figures

Paints generally include pigment (the colour), carried by a resin and/or binder, a solvent to assist the paint application, and a dryer. Some will include formaldehyde, arsenic, thinners, and foamers. Every year we wish to paint our home, furniture, etc. for adornment, protection, identification, sanitation, but we forget the impact of paint on our surroundings. Volatile organic compounds (VOCs) in paints are very harmful for the environment and particularly for the painters and paint industry workers who work with them regularly. The most important environmental impact from paints is that they release volatile organic compounds (VOCs) during the drying process after the coating is applied. Virtually everything but the solids during a typical paint formulation is released to the air. Once in the atmosphere, VOCs participate within the formation of ozone. This can cause some serious hazardous effect on our body like headaches, trigger allergies, asthmatic reactions, irritate skin, eyes, and put increased stress on vital organs such as the heart and not only paint but also its by-products and hence paints features a dangerous impact on human beings and our surroundings too. Hence this study aims to explore the effect of solvent based paints and analyse the impact of them on the environment and painters. This review also covers the chemical as well as the biological concerns about toxicological profile of solvents used in paint manufacturing systems. Additionally, the challenges and future prospects of injurious effect are discussed which may provide better understanding and new insights into ongoing and future research in this field.
Content may be subject to copyright.
SOLVENT BASED PAINT AND ITS IMPACT ON
ENVIRONMENT AND HUMAN BEINGS
Padmini Pandey* and U.V Kiran
Department of Human Development & Family Studies
School for Home Sciences, BBA Central University, Lucknow (U.P.)
*Corresponding author: dolly15pandey@gmail.com
ENVIRONMENT AND SOCIETY
pp: 198-207; Year: 2020
ABSTRACT
Paints generally include pigment (the colour), carried by a resin and/or binder, a solvent to assist the
paint application, and a dryer. Some will include formaldehyde, arsenic, thinners, and foamers. Every
year we wish to paint our home, furniture, etc. for adornment, protection, identification, sanitation,
but we forget the impact of paint on our surroundings. Volatile organic compounds (VOCs) in paints
are very harmful for the environment and particularly for the painters and paint industry workers who
work with them regularly. The most important environmental impact from paints is that they release
volatile organic compounds (VOCs) during the drying process after the coating is applied. Virtually
everything but the solids during a typical paint formulation is released to the air. Once in the
atmosphere, VOCs participate within the formation of ozone. This can cause some serious hazardous
effect on our body like headaches, trigger allergies, asthmatic reactions, irritate skin, eyes, and put
increased stress on vital organs such as the heart and not only paint but also its by-products and hence
paints features a dangerous impact on human beings and our surroundings too. Hence this study aims
to explore the effect of solvent based paints and analyse the impact of them on the environment and
painters. This review also covers the chemical as well as the biological concerns about toxicological
profile of solvents used in paint manufacturing systems. Additionally, the challenges and future
prospects of injurious effect are discussed which may provide better understanding and new insights
into ongoing and future research in this field.
Keywords: Sanitation, Vital organs, Allergies.
INTRODUCTION
In the period of development, environmental
pollution is one of the most serious issues due
to which humankind and other life getting
affected. Environmental pollution is defined as
“the contamination of the physical and organic
parts of the earth/atmosphere system to such a
degree that ordinary environmental processes
are adversely influenced” (Muralikrishna &
Manickam, 2017). Any natural substance or
chemical, can be considered sullies when got
abundance nature.
Chief Editor: Dr. A. K. Verma
ISBN: 978-81-931262-3-3
Copyright©Author
Pub.: Government P.G. College Saidabad, Prayagraj (U.P.)
198
SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT.....
199
SOLVENT-BORNE PAINTS
Liquefying agents are the main components of
the solvent based paints, due to which it's also
called oil based paint. Liquefying agents get
evaporated when chemical reaction occurs
with oxygen. Oil based paints, is a composition
of various organic solvents as the diluent,
including aliphatic, aromatics, alcohols,
ketones and white spirit (From Wikipedia,
2020). It contain up to 80% of solid
constituents in the form of binders, pigments
and additives which dispersed in the organic
solvent(Kopeliovich, 2020). Solvent-borne
paints dry fast due to containing a wide range of
binders. The main disadvantages of the
solvent-borne paints are their toxicity and
instability.
COMPONENTS OF SOLVENT-
BORNE PAINTS
1. Binder: Binders are the glue that holds the
pigments together and responsible for good
(i). Aliphatic Hydrocarbon Solvents
Aliphatic hydrocarbon solvents are mixtures of
either immersed, long straight chain (normal-
paraffin) or iso-paraffin or cyclic paraffins.
They do not contain a benzene ring. These
solvents are manufactured by refining of crude
oil by the appropriate boiling point range
fraction, and then are treated to improve shades
and odour (Anonymous, 2020).
(ii) Aromatic hydrocarbons solvents
Aromatic hydrocarbons comprise of closed
rings of carbon atoms. Cellulose thinner is
another name of it, is usually a mixture of
adhesion of the coating to the substrate. The
binder holds the pigment particles distributed
throughout the paint coating. The binder in
solvents based paint is dispersed in organic
solvents. Binders that commonly used in paint
are alkyd resins, acrylic resins, latex, phenolic
resins, polyurethane and epoxy resins etc.
(Kopeliovich, 2020).
2. Solvents:In paints formulation solvents
play important role to dissolve various
components used such as pigments, and also
making itof desired consistency for the
application. After applying the paints, the
solvent evaporates due to its good evaporation
rate and allowing binders and pigment particles
to produce a coat.The use of solvents in paints
provides a variety of effective choices among
durable and decorative coatings and glossy
paints for indoor and outdoor uses.
solvents able to dissolve a number of different
resins or plastics used in modern lacquer.
(iii) Oxygenated hydrocarbon solvents
(a) Ketones:
Commonly the process of oxidation of
hydrocarbons is responsible for the synthesis of
ketones. Ketones have a carbonyl group
bonded to two other carbon atoms. They have
very strong solvency, a high range of
ev ap or ation ra te s an d furthe rm or e an
extremely, strong odour. Acetone, methyl
ethyl ketone, methyl isobutyl ketone and
Table 1: Hydrocarbon Solvents used for Solvent Based Paint Formulation.
Hydrocarbon Solvents Commonly used in Paint
Aliphatic compounds Hexanes, Heptane, Naphtha, White spirit.
Aromatic compounds Benzene, Toluene, Mixed xylenes, Ethyl benzene (BTEX).
Oxygenated Solvents Ketones, Esters, Alcohols, Glycol ethers, Glycol ether esters
(Active Solvents)
Padmini Pandey and U.V Kiran
200
isophorone are the usually used ketones in
paints and coatings (Anonymous, 2020).
(b) Esters:
Esters are typically derived from an inorganic
acid or organic acid where there is at least one
hydroxyl (-OH) group replaced by an alkyl
(alkoxy) group and most commonly from
carboxylic acids and alcohols. Esters as
solvents are alkyl acetates and propionates and
glycol ether acetates. Their volatility is
equivalent to ketones. They have strong
solvency however more fragile than ketones of
an equivalent volatility(Anonymous, 2020).
(c) Alcohols:
Alcohol sometimes referred to by the chemical
name ethanol. Alcohol can be utilized as a
thinner for paint material, this gives a little
better control over the glare. On using enamel
or lacquer, any water in the thinner will ruin
paint matters.
(d) Glycol ethers:
Glycol Ethers commonly used in paints and
cleaners, are a group of solvents based on alkyl
ethers of ethylene glycol and they typically
have both ether and alcohol functionality.
These compounds were utilized broadly in
coatings until concerns emerged about their
safety risks. They are being supplanted with
pr op ylene glycol eth ers i n n um erous
applications. These compounds have strong
solvency combined with moderate evaporation
rate and higher boiling points(Anonymous,
2020).
3. Pigments:
Pigments are solid materials that are dispersed
and dissolved in paint solvents to provide
specific quality to the paint, as colour,
durability, strength, and protection of wall
surfaces. Pigments classified into organic
pigments and inorganic pigments.
4. Additives:
Additives are the important components of
paint which is used to impart additional
attribute and features to the paint. It can be
defined as low-level ingredients that provide
specific paint properties such as mildew
inhibiting property, increase the flowing
capacity, improvement in appearance, coating
durability etc. At the time of manufacturing,
paints forms foams and bubbles due to which
paints are not properly mixed, by the use of
additives bubbles can be broken and provide a
smooth and equal texture to the paints.
Fig. 1: Composition of Solvent-borne Paints.
Table 2: Different Colours Used in Paints and its Pigments.
Colours Pigments
White Titanium dioxide, Zinc oxide.
Black Carbon black, Black iron oxide, Aniline black
Brown Iron oxides brown, Benzimidazolone
Yellow Lead chromate, Yellow iron oxide
Red Cadmium red, Red iron oxide, Metallized Azo Red, Perylene
Blue Ferric potassium ferrocyanide, Cobalt blue Copper, Phthalocyanine
Green Chrome green, Chromium oxide, Hydrated chromium oxide, Copper
Phthalocyanine Green
(Youssef et al, 2019)
SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT.....
201
HARMFUL EFFECTS OF PAINTS
On the most basic level, paint is pigment that's
dissolved in a liquid called the solvent. It can
then be applied to walls or other surfaces. We
like to decorate our houses every year to make
it durable by painting our home, furniture, etc.
Paints are used for decoration, protection,
identification and for the sanitation purpose,
but we forget the harmful impact of paint on our
environments and our health.
Paint pollutant can cause serious hazardous
effect on our body like headaches, trigger
allergies, asthmatic reactions, irritate skin,
eyes, and put increased stress on vital organs
which could be temporary or may be
permanents. The oil based paint uses organic
solvents like volatile organic compounds. In
vinyl and acrylic paints they will also include
plastics compounds. Some will include
formaldehyde, arsenic, thinners, and foamers.
On the other hand Lead falls in this category as
it is responsible for lead poisoning and has been
banned since 1976. It has been replaced by
titanium that gives brightness and intensity to
the paints (FPS Public health, 2020). Lead is a
poi son ous me t al , ca n d a ma g e n erv e
connections and cause blood and brain
disorders (From Wikipedia, 2020).
Paint and Coating manufacturing facilities
emit pollutants such as hazardous air pollutants
(HAPs), volatile organic compounds (VOC),
and particle pollution (dust) by which paint
creates are also more dangerous to us and our
environment. These pollutants can contribute
to health problems that may affect facility
employees, their families, and the community
(EPA, 2020).
The World Health Organization (WHO)
estimated that about a quarter of the diseases
faced by mankind today occur due to prolonged
exposure to environmental pollution. The
World Health Organization (WHO) has
reported a 20%-40% increased risk of certain
types of cancer (in particular lung cancer) for
those who come into regular contact with, or
work with paint(Stratford, 2019)
EFFECTS OF VARIOUS COMPONENTS
1). VOLATILE ORGANIC
COMPOUNDS (VOC):
Volatile organic compounds are used mainly in
solvent based paints. When coating is applied
on a wall the drying process starts and during
this period generally paints release the volatile
organic comp ounds (VOCs) . The solid
particles released to the air during paint
formulation and begin participating in the
Table 3: Different Additives and their Applications.
Additives name Application Feature
UNIFLOW-TN-1500 Emulsion paint, water based Strong Thickening and
paint, emulsion adhesive good levelling
Good adhesiveness for
elastic paint
UNIFLOW-TN-1009 Emulsion paint, water based Good thermo-sensitive
paint, emulsion adhesive Viscosity and pattern can
be controlled
UNIFLOW DAPPO Acryl, Alkyd paint, Very strong deforming property
SERIES Oil based paint
UNIFLOW DF -504 Acryl, Alkyd paint, Stoving Very strong defoaming property
paint, Oil based paint Good adhesiveness for
elastic paint
(J&C Global tech, picture content retrieved on April 12, 2020)
202
formation of ozone by reacting with oxygen in
the presence of nitrogen oxides (NOx) and
sunlight. Ozone, the most toxic component and
it is called secondary pollutant, commonly
known as smog. Ozone attacks lung tissue, and
is very injurious, even in extremely minimum
exposure. Volatile organic compounds are
majorly present in the form of oil distillates,
Chl ori nat e d A l ip hati c H ydro car b on s,
Aromatic hydrocarbons etc.
Oil distillates are hydrocarbon solvents
delivered from raw petroleum. These solvents
incorporate mineral spirits, kerosene, white
spirits, naphtha, and Stoddard solvent. The low
surface pressure of many of these solvents
permits them to penetrate and clean little
spaces. They are usually used at or near room
temperature due to combustible properties.
Additionally they are found as the solvent
portion of some semi aqueous solutions.
Petroleum distillates are volatile organic
compounds (VOCs) and may be regulated in
areas. Toxicity levels are considered low;
however fluctuate with the particular materials
like kerosene. These solvents can be recycled
by distillation.
The process of chlorination of hydrocarbons is
responsible for the production of chlorinated
aliphatic hydrocarbons, by the addition of
chlorine or hydrogen chloride to unsaturated
compounds, by the reaction between hydrogen
chloride or chlorinated lime and alcohols,
aldehydes or ketones, and exceptionally by
chlorination of carbon disulphide (Encyclo-
paedia, 2020). It may cause dizziness,
giddiness, sickness and migraines, irritation to
skin and eyes, and unconsciousness by the
momentary exposure to these solvents. Long-
term impacts include muscular weakness,
obscured vision, headache, exhaustion, and
numbness, damage to lungs and skin, and
neurological issue(Anonymous, 2020).
The Aromatic hydrocarbons solvents benzene,
toluene, mixed xylenes, ethyl benzene, and
aromatic naphtha's are most widely used in
paint. Short-term exposure of Aromatic
hydrocarbons solvents from inhalation can
bring about bothering to the upper respiratory
tract and eyes, also dizziness, exhaustion and
headaches. Long-term impacts may cause
disorders in blood, cardiovascular and kidney
effects, unconsciousness, dysfunction of the
CNS(Anonymous, 2020).
Table 4: Paints Product and their Potential Health Effects.
Product Type Harmful Ingredients Potential Health Hazards
Furniture polish Petroleum distillates (or) Highly ignitable; toxic in nature; carcinogen;
irritate skin, eyes, nose, throat and lungs
Paint thinner Chlorinated aliphatic hydrocarbons Toxic in nature; cause digestive and
urinary system damage
Esters Toxic in nature; irritate eyes, nose and throat
Alcohols Ignitable; cause nervous system
damage; irritate eyes, nose and throat
Ketones Ignitable; toxic in nature; respiratory
system damage
Paints Aromatic hydrocarbon thinners Ignitable; toxic in nature; carcinogenic;
irritates skin, eyes, nose and throat;
respiratory system damage
Mineral spirits Highly ignitable; toxic in nature; irritates skin,
eyes, nose and throat; respiratory system
damage
mineral spirits
(Source: Babu & Reddy, 2014)
Padmini Pandey and U.V Kiran
SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT.....
203
2) NANOPARTICLES:
Nanoparticles are expected to surpass the
current properties of paints such as hardening,
U.V radiation absorption quality etc. because
of their particular structural characteristics
such as size, shape and greater surface area
(Van Broekhuizen et al., 2009). The foremost
pertinent nanomaterials for the paint industry
are titanium oxide, silicon dioxide, and
Nanosilver. Nanoparticles are used as pigment
materials in paints.
According to a studywithin the lungs and
circulatory system, inflammation is the
primary issue in atherothrombosis, asthma,
TOXICITY OF NANOPARTICLES
(a). Titanium Dioxide (TiO ):
2
Among all the nanoparticles, titanium dioxide
(TiO NPs) is one among the foremost highly
2
manufactured and widely used (Shah et al,
2017) pigments accounting for 70% of the
entir e produ ction volume of pi gment s
worldwide. Their large surface area high
embod ie d energ y e missi on s duri ng
manufacture may negatively impact the
environment and therefore human health. TiO2
NPs enter the human body through several
ways, including inhalation, ingestion, through
skin lesions, and medical injections (Migdal et
al, 2010)and may be distributed to different
body organs through cardiovascular system.
The unique characteristic of titanium dioxide
nanoparticles is its small size and therefore the
chronic obstructive lung disease, pulmonary
fibrosis and cancer (Donaldson & Tran 2002)
majorly effected by the particles, so that the
inflammation are often seen as a serious
property of particles. One among the important
findings was nanoparticles have a more
pronounced effect on inflammation, cell
damage and cell stimulation than normal
particles (Donaldson et al. 2000).
Smulders et al, 2012 examined the different
nanoparticles by different physical method
transmission electron microscope analysis
(TEM):
large area. Nanoparticles when enter the
human body they impose potential health risk
on human welfare due to high reactivity of NPs
(Warheit, 2007 and Oberdorster et.al.,, 2005).
TiO particles size is extremely ultrafine which
2
makesthem able to undergo the cell membranes
to nuclear membranes and then create a
disruption within the structure of cell and
damage it (Moss and Wong, 2006, Moller et al,
2002). Linhua et al, 2009, studies confirmed
the toxic proof of the TiO2 NPs. Exposure of it
results in adverse effects in aquatic organisms
(Linhua et al, 2009)
Health Effects: TiO nanoparticles can cause
2
inflammation, pulmonary damage, fibrosis,
and lung tumors and cancer to humans.
Table 4: Nanoparticle Characteristics.
Materials Nanotitanium dioxide Nanosilica dioxide Nanosilver
Function Colour strength Biocide Scratch resistance
Primary particle size and 25 nm (spherical) to
morphology (TEM) 80 – 90 nm (rods) 15nm 19 nm
Shape Some spherical, Spherical Spherical
others rods
(Source: Smulders et al, 2012)
204
b) Silicon Dioxide (SiO )
2
The addition of nanosilicon dioxide to paints
can improve the macro- and micro-hardness,
abrasion, scratch and weather resistance.
Adding nanosilicon dioxide to polymeric
resins creates paints with excellent abrasion
properties. People can experience adverse
effects of silicon dioxide after inhaling the fine
particles. Long-term exposure to silica dust
may pose a significant risk to health.
Health Effects:Nano-SiO by inhalation can
2
devel op p ulmonar y and cardiovasc ular
damage such as pulmonary inflammation,
myocardial ischemic damage, atrio-ventricular
blockag e, and increase s in fib rinogen
concentration and blood viscosity (Chen,
2008).
c) Silver nanoparticle
Silver Nano-particles (SNPs) are one of the
fo rem os t a vai la ble and co mme rc ial ly
distributed nanomaterials round the world.
Although silver nanoparticles are less toxic
than others nanoparticles but the respiratory
and gastrointestinal systems, as well as the
skin, are the main routes of SNPs penetration
into the body. Recent studies have investigated
the consequences of silver nanoparticles
exposure to humans from the increased use of
Ag NP-enhanced products may lead to rise in
toxic levels of environment.At work, it is
exposed which as using wall and spray paints,
paint strippers, adhesives. It is exposed to them
who are working at a manufacturing facility,
solvents and paint industries.
Health Effects: It can cau se l oss of
consciousness, low blood pressure, respiratory
issues and damage to the central nervous
sy st em . Chronic e xposure m ay cause
inflammation of the eye, headaches, insomnia,
stomach problem, visual and dermatitis. Short-
term exposure to cause difficulty breathing,
lack of coordination, blurred vision, dermatitis,
headache, dizziness, insomnia, confusion,
nausea, stomach problems and weakness, leg
cramps. It causes damage to liver, kidney and
eye disorder.
3) Lead
Lead is a toxic metal which is naturally found in
the Earth's crust. It is widely used metal that is
harmful to human health and the environment.
The sources of lead in the environment are lead
pa int s, E w as te- rec ycl in g a nd was te
incineration, smelting mining etc. Lead is used
in paints as additives and the enhancer.
Children and adults are at risk especially
pregnant women and workers in industries that
use lead paint. Lead is particularly dangerous to
children because their growing bodies absorb
4-5 times more lead than adults. Every year
approximately 600000 childre n develop
intellectual disability because of the exposure
to lead because lead poisoning has been shown
to affect various systems but the main that has
been studies most is the central nervous system.
Workers and people may be exposed to lead by
breathing lead dust during renovations or repair
work and also may be due to eating or drinking
food or water contaminated with lead, so the
users are not even aware of what they can be
exposed to. The presence of lead within the
body especially as a result of chronic poisoning
is going to affect the mental ability.
In the manufacturing of paints lead is used at
huge scale to maintain its appearance and
accelerate drying process. According to the
report of WHO, Its widespread use has resulted
in extensive environmental contamination,
human exposure and significant public health
problems in many parts of the world (WHO,
2017). According to WHO lead exposure
accounted for nearly 1.06 million deaths and
24.4 million years of healthy life lost
(disability-adjusted life years (DALYs))
worldwide in 2017 because of long-term
impact on wellbeing (WHO, 2017).
In the interior parts of houses like window
frames, doors, skirting boards, kitchen and
bathroom cupboards, exterior walls, gutters,
metal surfaces lead paint is mostly used. It can
likewise be found on inside walls, roofs and
territories with enamel paint. Pink and red
Padmini Pandey and U.V Kiran
SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT.....
205
primers contain high concentrations of lead
(Porwal.T, 2015).
CONCLUSION
This review article has revealed that painting
and coating are played important role in the
protection and decoration of a building.Paint
composed mainly of four substances, binders
which bind all the paint components, such as;
epoxy, polyurethane, cellulose, and nitro-
cellulose. Solvent isthe second component;
which used to dissolve all components of paint.
Other components used such as pigment which
give the paint its colour and the most important
and the last component is some additives such
as thickeners, dryers, anti-foaming agents,
which can enhanced the property of paints.
This review also revealed about the serious
hazardous impact due to the use of various
toxic solvents, additives (nanomaterials), and
other heavy metals such as lead and chromium
which leads to the chronic and acute impact on
human lives and on environment.Exposure of
the toxic substances, both by inhalation and via
skin contact, occurs specifically in operations
that involve during preparation of the paint,
during thinning, tinting and shading, during
filling operations, and during the filtering of
varnishes.
By taking some precautions we can reduce
some of the toxic effects on human and
environment.
lFor the prevention of such harm water
based products should be used instead of
oil based paint and thinner.
lThe methods for the product synthesis
should be designed to use and generate
which contain little or no toxicity to the
human health and environment.
lLo w vola ti le org an ic com po und s
containing paint which includes latex
(water-paint), recycled latex (water-
based) and acrylic paint should be in use.
lProper care and some prel iminary
pr eca ut ions must be ta ke n w hen
renovating or doing maintenance to avoid
exposing people and surroundings.
REFERENCES
1. Ali Shah,N.S, Shah, Z., Hussain, M. and
Muzaffa (2017). Hazardous Effects of
Tit anium Di oxi de Nanoparticles i n
Ecosystem Retrieved at April 9, 2020 from
https://doi.org/10.1155/2017 /4101735
2. Babu, S.N. & Reddy, M.S. (2014) Impact
of solvents leading to environmental
pollution. Journal of Chemical and
Pharmaceutical Sciences, 49. Retrieved
from www.jchps.com
3. Chen Z, Meng H, Xing G, Yuan H, Zhao
F, et al. (2008) Age-related differences in
pulmonary and cardiovascular responses
to SiO n anop arti cle i nha l ati o n:
2
nanotoxicity has susceptible population.
Environ SciTechnol 42: 8985–8992.
4. Donaldson, K. & Tran, C. L. (2002).
Inflammation caused by particles and
fibers. Inhal. Toxicol. 14, 5–27. (doi:10.
1080/089583701753338613).
5. Donaldson, K., Stone, V., Gilmour, P.
S., Brown, D. M. & MacNee, W. (2000)
Ultrafine particles: mechanisms of lung
injury. 358, 2741–2749. (doi:10.1098/
rsta.2000.0681
6. Effect of paints on the environment and
health. (January 4, 2020), FPS Public
Health R etrieved Apri l 12 , 20 20 ,
fromhttps://www.health.belgium.be/en/e
ffect-paints-environment-and-health
7. Environmental impact of paint
Wik ipe dia. Last edited (April 13,
202 0) Ret ri eve d Ap ri l 1 5, 20 2 0,
fromhttps://en.wikipedia.org/wiki/Envir
onmental_impact_of_paint
8. H y d r o ca rb ons, Al ipha t i c an d
Hal oge nat ed. (A u gus t 3 , 20 11) .
R e t r i e v e d A p r i l 1 5 , 2 0 2 0 ,
f r o m h t t p s : / / w w w . i l o e n c y -
206
clopaedia.org/part-xviii-10978/guide-to-
ch emicals /i tem/1 05 0- hydro ca rb ons-
aliphatic-and-halogenated
9. Kopeliovich. D, (2020), Composition of
Paints, SubsTech, Retrieved April 10,
2020, from https://www.substech.com/
dokuwiki/doku.php?id=composition_of_
paints
10. Kopeliovich. D, (2020), Solvent-borne
paints, SubsTech, Retrieved April 10,
2020, fromhttps://ww w.substech.com
/ d o k u w i k i / d o k u . p h p ? i d = s o l v e n t -
borne_paints
11. Le ad pai nt ht tps://en.wikipedi a. or g/
wiki/Lead_paint).
12. Linhua H, Zhenyu W, Baoshan X.
(2009). Effect of sub-acute exposure to
TiO nanoparticles on oxidative stress and
2
histopathological changes in Juvenile
Carp (Cyprinuscarpio). J Environ Sci. 21:
1459-1466.
13. Migdal, C., Rahal, R., Rubod. A et al.
(2010), Internalisation of hybrid titanium
dio x ide /pa ra-a m ino be nzoi c ac id
nanoparticles in human dendritic cells did
not induce toxicity and changes in their
fun ctions, Toxicology Lett ers, 199,
34–42,
14. Moss O.R., Wong V.A. (2006).When
nanoparticles get in the way: impact of
projected area on in vivo and in vitro
ma cro pha ge fu nct ion .I nha lTo xi col
18(10): 711-716.
15. Moller W, Hofer T, Ziesenis A, Karg E,
Heyder J. (2002). Ultrafine particles
cause cyt oskel etal dysf uncti ons in
ma cr op hages.T ox ic ol Ap plPharm co l.
182(3): 197-207.
16. Muralikrishna, V. I. & Manickam. V.
(2017) Environm ental Managemen t
(book), Elsevier.
17. Ob erdor ster G, Ob er dor st er E,
Oberdorster J. (2005). Nanotoxicology:
An emerging discipline evolving from
studies of ultrafine particles. Environ
Health Perspect. 113(7): 823-839.
18. Outdoor Air - Industry, Business, and
H o m e : P a i n t a n d C o a t i n g
M a nu f ac t ur i ng - A d di t io n al
Information. (2016, February 21).U.S.
En viron me ntal Prote ct ion Agency
Ret rie ved Apr i l 1 5, 2020 , fr om
https://archive.epa.gov/airquality/commun
ity/web/html/paint_manuf_addl_info.html
19. Paint. Last edited (2020, April 13).
Retrieved April 15, 2020, fromhttps://
en.wikipedia.org/wiki/Paint
20. Porwal,T. (20 15 ). P ai nt pollution
harmful effects on environment, Social
Issues and Environmental Problems.
International Journal of Research
GRANTHAALAYAH Retrieved at April
1 1 , 2 0 2 0 f r o m H t t p : / / w w w .
granthaalayah.com
21. Pa i nt an d co at i ng so lve nts ai r
monitoring application, Retrieved April
3 , 2 0 2 0 f ro m h ttp s : / /w ww . s i g
maaldrich.com/ technical documents/
articles/analyti cal/applicati ons/paints-
a n d -c oa t i ng s- s o l ve nt s - ai r- m o n i
toring.html).
22. Smulders S, Kaiser, J.P. Zuin S, Van
L a nd u yt , K .L , G ol a ns k i , L.
V a n oi rb e e k , J . et a l ( 20 1 2 ) .
Contaminati on of nan oparticl es by
endotoxin: evaluation of different test
methods. Part. Fibre Toxicol. 9 41).
23. Stratford. H, (2019 ). How Pai nt
Pollu tion Effe cts the Env ironm ent
Updated at Nov 1, 2019, Retrieved April
15, 2020, fromhttp://www.pollution
is sue s.c o. uk/ ho w- pai nt- po llu tio n-
effects-environment.html
Padmini Pandey and U.V Kiran
SOLVENT BASED PAINT AND ITS IMPACT ON ENVIRONMENT.....
207
24. The E dito rs of E n cyc lo p aedi a
Britannicahttps://www.britannica.com/sc
ience/ester-chemical-compound
25. V a n Bro e k h u i z e n F . A . et a l .
(2009).FIEC-EFBWW Report 20 09:
Na not echno log y in the Euro pe an
Construction Industry - State of the art.
Retrieved at April 7, 2020
26. Warheit D.B., Hoke R.A., Finlay C,
Donner E.M., Reed K.L., Sayes, C.M.
(2007). Development of a base of toxicity
tests using ultrafine TiO particles as a
2
comp on ent o f n an o par ti c le r i sk
management. Toxicol Lett. 171: 99-110.
27. WHO, lead poisoning and h ealth,
(20 1 7). h ttp s :/ / www . who . int / new s -
room/fact-sheets/detail/lead-poisoning-
and-health).
28. Youssef, A.M.R.A and Azab, H.M
(2019). Paints Industry: Raw materials &
uni t o per ati ons & Equ ipm ent &
M anufact ur in g & Q ua li t y tests
Ret rived April 14, 2020fromh ttps:/
/w ww. re sea rc hga te .ne t/ pub li catio n/
335 172 2 52_ Pai n ts _Ind ust r y_R aw_
materials_unit_operations_Equipment_
Ma nufac tu ring_ Qu ali ty _t est s DOI:
10.13140/RG.2.2.22793.60007
Article
Due to an increasing awareness of environmental protection, waterborne coatings have replaced solvent-borne ones. The waterborne styrene-acrylate dispersion was successfully synthesized using emulsion polymerization. In this work, the emulsion was composed of Butyl Acrylate (BA) and Styrene (Sty) at different ratios. FTIR spectra confirmed the successful copolymerization of BA and Sty. Additionally, it was observed that all emulsions exhibited a consistent hydrodynamic diameter (120 nm to 140 nm), polydispersity index (between 0.030 and 0.050), and zeta potential (-40 mV to -60 mV). Thus, the BA/St ratio did not impact particle growth during emulsion polymerization. Furthermore, an increase in Sty concentration raised the glass transition temperature (Tg) of the films from 10.8 °C to 30.8 °C. This is attributed to Sty being a high Tg polymer, contributing to a rigid monomer that could enhance rigidity and restrict the movement of polymer chains. Additionally, the tensile strength of the dispersion films increased with the increase in Sty concentration, from 3.01 MPa to 5.88 MPa. Interestingly, the elongation at break did not significantly change as the St concentration increased, dropping by 15%. The investigation to aid in establishing relationships between the monomer concentration and mechanical properties of styrene-acrylate films.
Article
A comparative study on three types of fireproofing coatings (namely, cementitious, sodium silicate, and epoxy) was made to determine their effectiveness in protecting steel structures. The effects of these coatings on the external protection of steel were structurally, thermally, and mechanically studied. The prepared cementitious coatings endured the heat until 1200 oC for 1 hour showing dimensions stability without deformation nor cracking during firing. Both crushing strength (CS) and bulk density measurements decreased from 69 to 18 kg/cm2 and from 1.62 to 1.00 g/cm3 'respectively' with increasing both perlite and vermiculite percentages. Six of the prepared 48 sodium silicate and epoxy coatings succeeded in bearing heat until 900 oC for 3.5 hours sustaining the steel substrates' temperature below 60 oC following the Underwriters Laboratory-94 (UL-94) standard. This protective effect was due to the formation of a hard glassy phase on the steel surface isolating it from the heat by the action of the applied constituents. Thermogravimetric analysis (TGA) and differential scanning calorimetry (DSC) thermograms for these succeeded samples revealed that they gave a high residual weight ranging from 63 to 88% when tested from room temperature up to 900 °C. Performing the scanning electron microscopy (SEM) test revealed that physical blending between both the binder and additives (other coating ingredients’) has occurred. The results concluded that the used ingredients, which have low prices, compared to the imported ones, and are locally available, are recommended for the fire protection of steel.
Article
Epoxy-acrylate (EA) core–shell nanoparticles have gained significant attention recently due to their dual unique properties as heterogeneous materials, particularly in coating applications. However, the effect of epoxy (EP) concentration in core layer on mechanical properties is still limited, and the mechanism of how it affects the film's performance is not well understood. In this study, we investigate the effect of varying EP concentration in the core layer on the mechanical properties of nanostructured films containing EA core–shell nanoparticles. The core–shell nanoparticles were synthesized through multistage seeded emulsion polymerization. The transmission electron microscopy (TEM) images revealed similar particle morphology and size in all EA nanoparticles. Differential scanning calorimetry (DSC) analysis confirmed the successful synthesis of core–shell particle morphology with two glass transition temperature (Tg) values (~12 °C and ~ 60 °C) observed for the core and shell layers, respectively. We observed an increase in the Tg values of the shell layer with higher EP content in the core layer. The use of EP-based copolymers raised the Tg values of the shell layer, significantly affecting the film formation behavior and their mechanical properties through interlayer crosslinking. Tensile modulus values for the films ranged from 200 to 500 MPa, marking the highest modulus reported for cast films of EA nanostructured films. Our findings reveal a straightforward and versatile method for producing high-modulus EA nanostructured films with customizable mechanical properties, making the model ideal for enhancing wood coating performance.
Article
Full-text available
Over time, paint chemistry has changed, posing health hazards to house painters. Surveys and interviews scheduled on work profiles determined the exposure to solvents in commercial painting. This research paper aims to identify the respiratory and lungs issues among painters due to their occupation. With this aim, this also explore the worker’s experiences with various types of paints regarding health implications. The current study is related to research on the health issues of paint workers. Subjects for the study were chosen by the use of cluster sampling from several places in three districts of Uttar Pradesh, India. An interview schedule was developed to collect relevant and maximum information. The study used a sample size of 150 that was not pre-determined. All the respondents were from the labour class and worked with paints. A schedule of the interview was developed to gather information about the painters’ demographic profile and current respiratory health status. Statistical approaches such as Standard Deviation, ANOVA and Pearson’s correlation were used for analysis. The study revealed that painters are exposed to paints and face various health issues. Majority of the respondents (50.7%) belongs to lower economic status, followed by upper lower (33.3%), and only 4% of them belong to the upper class. We found a significant difference between the respondent’s age and respiratory health. This data indicates that respondents who faced high respiratory issues belong to the age group of 61–75 years, and minimum problems were observed in the age group of 19–32 years. This data shows highly significant differences between age groups, and the problem occurs with the respiratory system in painters. The result indicates that wearing the mask was significantly associated with respiratory problems like cough (p = .004), chest tightness (p = .009), and whistling sound from the chest (p = .000). A perfect positive significant correlation between working year, days, and duration with different lung problems were identified. A perfect positive association (0.443**) was also identified between years of work and cough difficulties, indicating that workers who have worked for prolonged periods were more susceptible to cough. Cough problems were highly associated with painters who worked more days per week. Cough issues were perfectly and significantly associated (0.232**) with painters who use masks while working. The chest sound or whistling gets more intense as the cough problem worsens. Moreover, there was a positive and significant association between discomfort during breathing and working years (.340**), working days in a week (.195*), and working duration (.594**). This study highlighted the risk and problems among painters due to pain, including breathing problems, prolonged cough, chest discomfort, and almost all lung problems.
Article
Plant oils are one of popular starting raw materials of alkyd resin manufacturing and castor oil is well known plasticizer in coating industry. Coconut oil-based alkyd resins and blend of coconut and castor oil-based alkyd resins were synthesized as Bio-based plasticizers to evaluate their properties as plasticizers for nitrocellulose (nc) paint. During synthesis of those resins, variation of acid value, viscosity, oil length and generated water amount was evaluated. Series of nitrocellulose surface coatings (ncscs) were prepared using one alkyd resin at a time according to a dilution series and followed the same procedure for other alkyd resins and commercially available plasticizers (caps). All ncscs were tested for specific gravity, apparent viscosity, reduced viscosity, dry film thickness, dry film gloss, impact resistance, mandrel bending, Erichsen cupping, drying time, pencil hardness. According to the results it was proven that alkyd resins incorporated ncscs are better in viscosity, low drying time, film hardness. Ncscs with commercially available plasticizer (cap) is better in flexibility, impact resistance, dry film thickness, gloss
Thesis
Full-text available
Increasing student skills in the field work, and linking theory with application, become the motivation to students to join to factories and companies for achieving this target. One of chemical process industries is the paints industry. Paints is a main part of coatings, paints composed of five components which are; resin (binder), solvent, filler, pigments, and additives. From the point of view of chemical engineering; paints manufacturing, requires number of unit operation which are mixing, milling, and filtration. These of operations done using several industrial units which are; mixers, mills, and screen filters. Paints manufacturing done by adding binders, solvents, and thickeners to provide a gel phase which its existence is a mark for starting of adding fillers and pigment, through and after manufacturing processes a samples send to laboratory to done some tests, by which the manufacturer be sure from his products quality, the main tests are density, viscosity, and hiding power test, there several tests can be done also such as wash-ability and impact test .
Article
Full-text available
Although nanoparticles (NPs) have made incredible progress in the field of nanotechnology and biomedical research and their applications are demanded throughout industrial world particularly over the past decades, little is known about the fate of nanoparticles in ecosystem. Concerning the biosafety of nanotechnology, nanotoxicity is going to be the second most priority of nanotechnology that needs to be properly addressed. This review covers the chemical as well as the biological concerns about nanoparticles particularly titanium dioxide (TiO2) NPs and emphasizes the toxicological profile of TiO2 at the molecular level in both in vitro and in vivo systems. In addition, the challenges and future prospects of nanotoxicology are discussed thatmay provide better understanding and new insights into ongoing and future research in this field.
Article
Full-text available
Many ultrafine particles comprised classically of low–toxicity, low–solubility materials such as carbon black and titaniu dioxide have been found to have greater toxicity than larger, respirable particles made of the same material. The basis o the increased toxicity of the ultrafine form is not well understood and a programme of research has been carried out in Edinburg on the toxicology of ultrafines aimed at understanding the mechanism. We used fine and ultrafine carbon black, TiO2 and latex and showed that there was an approximately 10–fold increase in inflammation with the same mass of ultrafine compare with fine particles. Using latex particles in three sizes — 64, 202 and 535 nm — revealed that the smallest particles (6 nm) were profoundly inflammogenic but that the 202 and 535 nm particles had much less activity, suggesting that the cut–of for ultrafine toxicity lies somewhere between 64 and 202 nm. Increased oxidative activity of the ultrafine particle surfac was shown using the fluorescent molecule dichlorofluorescein confirming that oxidative stress is a likely process by whic the ultrafines have their effects. However, studies with transition–metal chelators and soluble extracts showed that the oxidativ stress of ultrafine carbon black is not necessarily due to transition metals. Changes in intracellular Ca2+ levels in macrophage–like cells after ultrafine particle exposure suggested one way by which ultrafines might have thei pro–inflammogenic effects.
Article
Full-text available
Background Nanomaterials can be contaminated with endotoxin (lipopolysaccharides, LPS) during production or handling. In this study, we searched for a convenient in vitro method to evaluate endotoxin contamination in nanoparticle samples. We assessed the reliability of the commonly used limulus amebocyte lysate (LAL) assay and an alternative method based on toll-like receptor (TLR) 4 reporter cells when applied with particles (TiO2, Ag, CaCO3 and SiO2), or after extraction of the endotoxin as described in the ISO norm 29701. Results Our results indicate that the gel clot LAL assay is easily disturbed in the presence of nanoparticles; and that the endotoxin extraction protocol is not suitable at high particle concentrations. The chromogenic-based LAL endotoxin detection systems (chromogenic LAL assay and Endosafe-PTS), and the TLR4 reporter cells were not significantly perturbed. Conclusion We demonstrated that nanoparticles can interfere with endotoxin detection systems indicating that a convenient test method must be chosen before assessing endotoxin contamination in nanoparticle samples.
Article
Full-text available
Although humans have been exposed to airborne nanosized particles (NSPs; < 100 nm) throughout their evolutionary stages, such exposure has increased dramatically over the last century due to anthropogenic sources. The rapidly developing field of nanotechnology is likely to become yet another source through inhalation, ingestion, skin uptake, and injection of engineered nanomaterials. Information about safety and potential hazards is urgently needed. Results of older biokinetic studies with NSPs and newer epidemiologic and toxicologic studies with airborne ultrafine particles can be viewed as the basis for the expanding field of nanotoxicology, which can be defined as safety evaluation of engineered nanostructures and nanodevices. Collectively, some emerging concepts of nanotoxicology can be identified from the results of these studies. When inhaled, specific sizes of NSPs are efficiently deposited by diffusional mechanisms in all regions of the respiratory tract. The small size facilitates uptake into cells and transcytosis across epithelial and endothelial cells into the blood and lymph circulation to reach potentially sensitive target sites such as bone marrow, lymph nodes, spleen, and heart. Access to the central nervous system and ganglia via translocation along axons and dendrites of neurons has also been observed. NSPs penetrating the skin distribute via uptake into lymphatic channels. Endocytosis and biokinetics are largely dependent on NSP surface chemistry (coating) and in vivo surface modifications. The greater surface area per mass compared with larger-sized particles of the same chemistry renders NSPs more active biologically. This activity includes a potential for inflammatory and pro-oxidant, but also antioxidant, activity, which can explain early findings showing mixed results in terms of toxicity of NSPs to environmentally relevant species. Evidence of mitochondrial distribution and oxidative stress response after NSP endocytosis points to a need for basic research on their interactions with subcellular structures. Additional considerations for assessing safety of engineered NSPs include careful selections of appropriate and relevant doses/concentrations, the likelihood of increased effects in a compromised organism, and also the benefits of possible desirable effects. An interdisciplinary team approach (e.g., toxicology, materials science, medicine, molecular biology, and bioinformatics, to name a few) is mandatory for nanotoxicology research to arrive at an appropriate risk assessment.
Article
Nanoparticles (NPs) have been reported to penetrate into human skin through lesional skin or follicular structures. Therefore, their ability to interact with dendritic cell (DC) was investigated using DCs generated from monocytes (mono-DCs). Hybrid titanium dioxide/para-amino benzoic acid (TiO(2)/PABA) NPs did not induce any cell toxicity. NPs were internalised into DCs through macropinocytosis and not by a receptor-mediated mechanism. Confocal microscopy showed that NPs were not detected in the nucleus. These data are confirmed by electronic microscopy which demonstrated that hybrid NPs were rapidly in contact with cellular membrane and localised into cytoplasmic vesicles without colocalisation with clathrin-coated vesicles. Hybrid NPs did not induce CD86 or HLA-DR overexpression or cytokine secretion (IL-8 and TNF-α) indicating no DC activation. Internalisation of hybrid NPs did not modify DC response towards sensitisers such as nickel and thimerosal or LPS used as positive controls. Moreover, hybrid NPs did not induce any oxidative stress implicated in DC activation process. After mono-DC irradiation by ultraviolet A (UVA), hybrid NP-treated cells did not produce UVA-induced reactive oxygen species (ROS) and exhibited a better cell viability compared with UVA-irradiated control cells, suggesting a protecting effect of hybrid TiO(2)/PABA NPs against UVA-induced ROS.
Article
Increasing application of nanotechnology highlights the need to clarify and understand nanotoxicity. Mammalian and in vitro studies have raised concerns about the toxicity of titanium dioxide nanoparticles (TiO2-NPs), but there are limited data on ecotoxicity to aquatic organisms. In this work, the sub-acute toxicity of TiO2-NPs to carp (Cyprinus carpio) was assessed. Superoxide dismutase (SOD), catalase (CAT) and peroxidase (POD) activities and lipid peroxidation (LPO) levels in liver, gill and brain tissues of carps varied with concentration of TiO2-NPs suspensions and exposure time (up to 8 d). As a result, 100 and 200 mg/L TiO2-NPs caused statistically significant decrease in SOD, CAT and POD activities and significant increase in LPO levels in tissues (P < 0.05), suggesting that the fish exposed to these two concentrations of TiO2-NPs suffered from the oxidative stress. The extent of depletion of antioxidant enzymes activities and the elevation of LPO in the liver was the greatest, indicating that the liver might be the most susceptible organ to TiO2-NPs exposure. In addition, carps had gill pathologies including edema and thickening of gill lamellae as well as gill filaments, and liver pathologies including necrotic and apoptosis hepatocytes after exposed to 100 and 200 mg/L TiO2-NPs for 20 d. These results indicated a potential risk from TiO2-NPs released into the aqueous environment.
Article
Epidemiologic studies have revealed that pollution by ambient particulates is associated with respiratory and cardiovascular diseases, particularly in older people. Toxicologic sensitivity of nanoparticles in different ages was investigated for the first time to demonstrate and explain an age-related difference in response to manufactured nanoparticles. Young, adult, and old rats physiologically inhaled air containing aerosol of manufactured SiO2 nanoparticles (24.1 mg/m3; 40 min/day) for four weeks. Changes in serum biomarkers, hemorheologic, pulmonary inflammation, heart injury, and pathology in rats of different ages and their corresponding controls were compared. Inhalation of SiO2 nanoparticles under identical conditions caused pulmonary and cardiovascular alterations in old rats, yet less change in young and adult rats, including pulmonary inflammation, myocardial ischemic damage, atrio-ventricular blockage, and increase in fibrinogen concentration and blood viscosity. Old individuals were more sensitive to nanoparticle exposure than the young and adult rats. The risk of causing pulmonary damages was: old > young > adult The risk of cardiovascular disorder was observed only in old age. Our results suggest that different ages may require different biomarkers for identifying pulmonary toxicity during inhalation of nanoparticles.
Article
Essential cytoskeletal functions of macrophages are migration, phagocytosis of foreign materials, and intracellular transport and digestion The influence of fine and ultrafine test particles (UFP), such as TiO(2), elemental carbon, commercial carbon black, diesel exhaust particulate matter, and urban dust (UrbD), on cytoskeleton-related functions of macrophages, such as phagocytosis, phagosome transport mechanisms, and mechanical cytoskeletal integrity, were studied by flow cytometry and by cytomagnetometry. Additionally, necrosis and apoptosis caused by the test particles was detected. The diameter of the test particles ranged from 12 to 220 nm and the Brunauer-Emmet-Teller specific surface area ranged from 6 to 600 m(2)/g. Primary alveolar macrophages from beagle dogs (BD-AM), obtained by bronchoalveolar lavage, were used as well as macrophages originating from the cell line J774A.1. For cytomagnetometry studies, spherical 1.8-microm ferromagnetic particles served as probes for cytoskeletal functions and were incubated together with the macrophages 24 h prior to UFP exposure. Macrophages were exposed in vitro with 10-320 microg UFP/ml/10(6) cells up to 24 h. In all experiments, J774A.1 macrophages were more sensitive than BD-AM to UFP exposure. Cytoskeletal dysfunctions evaluated by cytomagnetometry were an impaired phagosome transport and an increased cytoskeletal stiffness and occurred at concentrations of 100 microg UFP/ml/10(6) cells and above, in both BD-AM and J774A.1. Only fine TiO(2) did not show any effect. Urban dust (standard reference material 1649a) and diesel exhaust particles (DEP, standard reference material 1650) caused comparable cytoskeletal dysfunctions to elemental carbon with high specific surface area. Cytoskeletal dysfunctions induced by DEP or UrbD could be reduced after washing the particles by dichloromethane. UFP caused an impaired phagocytosis of 1-microm diameter fluorescent latex beads, inhibited cell proliferation, and decreased cell viability. All recorded cytotoxic parameters showed only weak correlations with the specific surface area or the total number of UFP, which can result from the different types of particles and different surface compositions. UFP cause cytoskeletal toxicity in vitro in macrophages, which can cause cellular dysfunctions, such as impaired proliferation, impaired phagocytic activity, and retarded intracellular transport processes as well as increased cell stiffness and can result in impaired defense ability in the lung.