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Cleaning and
Sanitizing - Water
Chemistry and Quality
1. Cleaning
2. Sanitizing
3. Sanitizers
4. References
Water comprises approximately 95-99% of cleaning and sanitizing
solutions. Water functions to:
- carry the
detergent or the sanitizer to the surface;
- carry soils or
contamination from the surface.
The impurities in water can drastically alter the effectiveness of a
detergent or a sanitizer. Water hardness is the most important chemical property
with a direct effect on cleaning and sanitizing efficiency. (Other impurities
can effect the food contact surface or may effect the soil deposit properties or
film formation.) Water pH ranges generally from pH 5 to 8.5. This range is of no
serious consequence to most detergents and sanitizers. However, highly alkaline
or highly acidic water may require additional buffering agents. Water can also
contain significant numbers of microorganisms. Water used for cleaning and
sanitizing must be potable and pathogen-free. Treatments and sanitization of
water may be required prior to use in cleaning regimes. Water impurities that
effect cleaning functions are presented in Table 1 and
Table 2.
Cleaning
Properties of Soils
Soil is generally defined as unwanted matter on contact surfaces. Soil is
visible or invisible. The primary source of soil is from the product being
handled. However, minerals from water residue and residues from cleaning
compounds contribute to films left on surfaces. Microbiological bio-films also
contribute to the soil buildup on surfaces. Since soils vary widely in
composition, no one detergent is capable of removing all types. Many complex
films contain: combinations of food components, surface oil or dust, insoluble
cleaner components, and insoluble hard-water salts. These films vary in their
solubility properties depending upon such factors as heat effect, age, dryness,
time, etc. It is essential that personnel involved have an understanding of the
nature of the soil to be removed before selecting a detergent or cleaning
regime. The rule of thumb is that acid cleaners dissolve alkaline soils
(minerals) and alkaline cleaners dissolve acid soils and food wastes. Improper
use of detergents can actually "set" soils, making them more difficult to remove
(e.g., acid cleaners can precipitate protein). Many films and bio-films require
more sophisticated cleaners which are amended with oxidizing agents (such as
chlorinated detergents) for removal. Soils may be classified as:
- soluble in
water (sugars, some starches, most salts);
- soluble in
acid (limestone and most mineral deposits);
- soluble in
alkali (protein, fat emulsions);
- soluble in
water, alkali, or acid.
The physical condition of the soil deposits also affects its solubility.
Freshly precipitated soil in a cool or cold solution is usually more easily
dissolved than an old, dried, or baked-on deposit, or a complex film. Food soils
are complex in that they contain mixtures of several components. A general soil
classification and removal characteristics is presented in Table 3.
Fat-based Soils
Fat usually is present as an emulsion and can generally be rinsed away with hot
water above the melting point. More difficult fat and oil residues can be
removed with alkaline detergents that have good emulsifying or saponifying
ingredients.
Protein-based Soils
Proteins are by far the most difficult soils to remove. In fact, casein (a major
milk protein) is used for its adhesive properties in many glues and paints. Food
proteins range from more simple proteins, which are easy to remove, to more
complex proteins, which are very difficult to remove. Heat-denatured proteins
can be extremely difficult. Generally, a highly alkaline detergent with
peptizing or dissolving properties is required to remove protein soils. Wetting
agents can also be used to increase the wettability and suspendability of
proteins. Protein films require alkaline cleaners that have hypochlorite in
addition to wetting agents.
Carbohydrate-based Soils
Simple sugars are readily soluble in warm water and are quite easily removed.
Starch residues, individually, are also easily removed with mild detergents.
Starches associated with proteins or fat-scan usually be easily removed by
highly alkaline detergents.
Mineral Salt-based Soils
Mineral salts can be either relatively easy to remove, or be highly troublesome
deposits or films. Calcium and magnesium are involved in some of the most
difficult mineral films. Under conditions involving heat and alkaline pH,
calcium and magnesium can combine with bicarbonates to form highly insoluble
complexes. Other difficult deposits contain iron or manganese. Salt films can
also cause corrosion of some surfaces. Difficult salt films require an acid
cleaner (especially organic acids which form complexes with these salts) for
removal. Sequestering agents such as phosphates or chelating agents are often
used in detergents for salt film removal.
Microbiological Films
Under certain conditions, microorganisms (bacteria, yeasts, and molds) can form
invisible films (bio-films) on surfaces. Bio-films can be difficult to remove
and usually require cleaners as well as sanitizers with strong oxidizing
properties.
Lubricating Greases and Oils
These deposits (insoluble in water, alkali, or acid) can often be melted with
hot water or steam, but often leave a residue. Surfactants can be used to
emulsify the residue to make it suspendable in water and flushable.
Other Insoluble Soils
Inert soils such as sand, clay, or surfactant-based detergents can remove fine
metal. Charred or carbonized material may require organic solvents.
Quantity of Soil
It is important to rinse contact surfaces prior to cleaning to remove most of
the soluble soil. Heavy deposits require more detergent to remove. Improper
cleaning can actually contribute to build-up of soil.
The Surface Characteristics
The cleanability of the surface is a primary consideration in evaluating
cleaning effectiveness. Included in surface characteristics are:
Surface Composition. Stainless steel is the preferred surface for food
equipment and is specified in many industry and regulatory design and
construction standards. For example: 3-A Sanitary Standards (equipment standards
used for milk and milk products applications) specify 300 series stainless steel
or equivalent. Other grades of stainless steel may be appropriate for specific
applications (i.e. 400 series) such as handling of high fat products, meats,
etc. For highly acidic, high salt, or other highly corrosive products, more
corrosion resistant materials (i.e. titanium) is often recommended.
Other "soft" metals (aluminum, brass, copper, or mild steel), or
nonmetallic surfaces (plastics, or rubber) are also used on food contact
surfaces. Surfaces of soft metals and nonmetallic materials are generally less
corrosion- resistant and care should be exercised in their cleaning. Acids as
well as highly alkaline cleaners that can render the surface non-cleanable
readily attack aluminum. Plastics are subject to stress cracking and clouding
from prolonged exposure to corrosive materials or cleaning agents. Hard wood
(maple or equivalent) or sealed wood surfaces should only be used in limited
applications such as cutting boards or cutting tables provided the surface is
maintained in good repair. Avoid using porous wood surfaces.
Surface Finish. Equipment design and construction standards also
specify finish and smoothness requirements. 3-A standards specify a finish at
least as smooth as a No. 4 ground finish for most application. With high-fat
products, a less smooth surface is used to allow product release from the
surface.
Surface Condition. Misuse or mishandling can result in pitted,
cracked, corroded, or roughened surfaces. Such surfaces are more difficult to
clean or sanitize, and may no longer be cleanable. Thus, care should be
exercised in using corrosive chemicals or corrosive food products.
Environmental Considerations
Detergents can be significant contributors to the waste discharge (effluent). Of
primary concern is pH. Many publicly owned treatment works limit effluent pH to
the range of 5 to 8.5. So, it is recommended that in applications where highly
alkaline cleaners are used, that the effluent be mixed with rinse water (or some
other method be used) to reduce the pH. Recycling of caustic soda cleaners is
also becoming a common practice in larger operations. Other concerns are
phosphates, which are not tolerated in some regions, and the overall soil load
in the waste stream which contributes to the chemical oxygen demand (COD) and
biological oxygen demand (BOD).
Chemistry of Detergents
Detergents and cleaning compounds are usually composed of mixtures of
ingredients that interact with soils in several ways:
- Physically
active ingredients alter physical characteristics such as solubility or
colloidal stability.
- Chemically
active ingredients modify soil components to make them more soluble and,
thus, easier to remove.
- In some
detergents, specific enzymes are added to catalytically react with, and
degrade, specific food soil components.
Physically Active Ingredients
The primary physically active ingredients are the surface-active compounds
termed surfactants. These organic molecules have general structural
characteristic where a portion of the structure is hydrophilic (water- loving)
and a portion is hydrophobic (not reactive with water). Such molecules function
in detergents by promoting the physical cleaning actions through:
emulsification, penetration, spreading, foaming, and wetting. The classes of
surfactants are:
Ionic surfactants, which are
negatively charged in water solution, are termed anionic surfactants.
Conversely, positively charged ionic surfactants are termed cationic
surfactants. If the charge of the water-soluble portion is depended upon the pH
of the solution it is termed an amphoteric surfactant. These surfactants behave
as cationic surfactants under acid conditions, and as anionic surfactants under
alkaline conditions. Ionic surfactants are generally characterized by their high
foaming ability.
Nonionic surfactants, which do not
dissociate when dissolved in water, have the broadest range of properties
depending upon the ratio of hydrophilic/ hydrophobic balance. This balance is
also affected by temperature. For example, the foaming properties of nonionic
detergents are affected by temperature of solution. As temperature increases,
the hydrophobic character and solubility decreases. At the cloud point (minimum
solubility), these surfactants generally act as defoamers, while below the cloud
point they are varied in their foaming properties.
It is a common practice to blend surfactant ingredients to optimize their
properties. However, because of precipitation problems, cationic and anionic
surfactants cannot be blended
Chemically Active Ingredients
Alkaline Builders
Highly Alkaline Detergents (or heavy-duty detergents) use caustic soda (sodium
hydroxide) or caustic potash (potassium hydroxide). An important property of
these highly alkaline detergents is that they saponify fats: forming soap. These
cleaners are used in many CIP systems or bottle-washing applications. Moderately
Alkaline Detergents include sodium, potassium, or ammonium salts of phosphates,
silicates, or carbonates. Tri-sodium phosphate (TSP) is one of the oldest and
most effective. Silicates are most often used as a corrosion inhibitor. Because
of interaction with calcium and magnesium and film formation, carbonate-based
detergents are of only limited use in food processing cleaning regimes.
Acid Builders
Acid Detergents include organic and inorganic acids. The most common inorganic
acids used include: phosphoric, nitric, sulfamic, sodium acid sulfate, and
hydrochloric. Organic acids, such as hydroxyacetic, citric, and gluconic, are
also in use. Acid detergents are often used in a two-step sequential cleaning
regime with alkaline detergents. Acid detergents are also used for the
prevention or removal of stone films (mineral stone, beer stone, or milk
stone).
Water Conditioners
Water conditioners are used to prevent the build-up of various mineral deposits
(water hardness, etc.). These chemicals are usually sequestering agents or
chelating agents. Sequestering agents form soluble complexes with calcium and
magnesium. Examples are sodium tripolyphosphate, tetra-potassium pyrophosphate,
organo-phosphates, and polyelectrolyte. Chelating agents include sodium
gluconate and ethylenediaminetetracetic acid (EDTA).
Oxidizing Agents
Oxidizing agents used in detergent application are hypochlorite (also a
sanitizer) and -- to a lesser extent -- perborate. Chlorinated detergents are
most often used to clean protein residues.
Enzyme Ingredients
Enzyme-based detergents, which are amended with enzymes such as amylases and
other carbohydrate- degrading enzymes, proteases, and lipases, are finding
acceptance in specialized food industry applications. The primary advantages of
enzyme detergents are that they are more environmentally friendly and often
require less energy input (less hot water in cleaning). Uses of most enzyme
cleaners are usually limited to unheated surfaces ( e.g., cold-milk surfaces).
However, new generation enzyme cleaners are expected to have broader
application. Fillers add bulk or mass, or dilute dangerous detergent
formulations that are difficult to handle. Strong alkalis are often diluted with
fillers for ease and safety of handling. Water is used in liquid formulations as
filler. Sodium chloride or sodium sulfate are often fillers in powdered
detergent formulations.
Miscellaneous Ingredients
Additional ingredients added to detergents may include: corrosion inhibitors,
glycol ethers, and butylcellosolve (improve oil, grease, and carbon removal).
Sanitizing
Thermal Sanitizing
As with any heat treatment, the effectiveness of thermal sanitizing is dependant
upon a number of factors including: initial contamination load, humidity, pH,
temperature, and time.
Steam
The use of steam as a sanitizing process has limited application. It is
generally expensive compared to alternatives, and it is difficult to regulate
and monitor contact temperature and time. Further, the byproducts of steam
condensation can complicate cleaning operations.
Hot Water
Hot-water sanitizing -- through immersion (small parts, knives, etc.), spray
(dishwashers), or circulating systems -- is commonly used. The temperature of
the water determines the time required. Typical regulatory requirements (Food
Code 1995) for use of hot water in dishwashing and utensil sanitizing
applications specify: immersion for at least 30 sec. at 77°C (170°F) for manual
operations; a final rinse temperature of 74°C (165°F) in single tank, single
temperature machines and 82°C (180°F) for other machines. Many regulations
require a utensil surface temperature of 71°C (160°F) as measured by an
irreversibly registering temperature indicator in ware washing machines.
Recommendations and requirements for hot water sanitizing in food processing may
vary. The Grade A Pasteurized Milk Ordinance specifies a minimum of 77°C (170°F)
for 5 min. Other recommendations for processing operations are: 85°C (185°F) for
15 min., or 80°C (176°F) for 20 min. The primary advantages of hot-water
sanitization are: relatively inexpensive, easy to apply and readily available,
generally effective over a broad range of microorganisms, relatively
non-corrosive, and penetrates into cracks and crevices. Hot-water sanitization
is a slow process which requires come-up and cool-down time; can have high
energy costs; and has certain safety concerns for employees. The process also
has the disadvantages of forming or contributing to film formations, and
shortening the life of certain equipment or parts thereof (gaskets, etc.).
Chemical Sanitizing
The ideal chemical sanitizer should:
- be approved for food contact surface application
- have a wide range or scope of activity
- destroy microorganisms rapidly
- be stable under all types of conditions
- be tolerant of a broad range of environmental conditions
- be readily solubilized and possess some detergency
- be low in toxicity and corrosiveness
- be inexpensive
No available sanitizer meets all of the above
criteria. Therefore, it is important to evaluate the properties, advantages, and
disadvantages of available sanitizer for each specific application.
Regulatory Considerations
The regulatory concerns involved with chemical sanitizers are: antimicrobial
activity or efficacy, safety of residues on food contact surfaces, and
environmental safety. It is important to follow regulations that apply for each
chemical usage situation. The registration of chemical sanitizers and
antimicrobial agents for use on food and food product contact surfaces, and on
non-product contact surfaces, is through local regulatory agencies. Thus, any
antimicrobial agent and its maximum usage level for direct use on food or on
food product contact surfaces must be approved by the FDA or CFIA.
Factors Affecting Sanitizer Effectiveness
Physical Factors
Surface Characteristics. Prior to the
sanitization process, all surfaces must be clean and thoroughly rinsed to remove
any detergent residue. An unclean surface cannot be sanitized. Since the
effectiveness of sanitization requires direct contact with the microorganisms,
the surface should be free of cracks, pits, or crevices that can harbor
microorganisms. Surfaces that contain biofilms cannot be effectively sanitized.
Exposure Time. Generally, the
longer time a sanitizer chemical is in contact with the equipment surface, the
more effective the sanitization effect; intimate contact is as important as
prolonged contact.
Temperature. Temperature is
also positively related to microbial kill by a chemical sanitizer. Avoid high
temperatures (above 55°C [131°F]) because of the corrosive nature of most
chemical sanitizers. Concentration. Generally, the activity of a
sanitizer increases with increased concentration. However, a leveling off occurs
at high concentrations. A common misconception regarding chemicals is that "if a
little is good, more is better." Using sanitizer concentrations above
recommendations does not sanitize better and, in fact, can be corrosive to
equipment and in the long run lead to less cleanable. Follow manufacturer's
label instructions.
Soil. The presence of organic matter dramatically
reduces the activity of sanitizers and may, in fact, totally inactivate them.
The adage is "you cannot sanitize an unclean surface."
Chemical Factors
pH. Sanitizers are dramatically affected by the
pH of the solution. Many chlorine sanitizers, for example, are almost
ineffective at pH values above 7.5. Water properties. Certain sanitizers are
markedly affected by impurities in the water.
Inactivators. Organic and/or
inorganic inactivators may react chemically with sanitizers giving rise to
non-germicidal products. Some of these inactivators are present in detergent
residue. Thus, it is important that surfaces be rinsed prior to sanitization.
Biological Factors
The microbiological load can
affect sanitizer activity. Also, the type of microorganism present is important.
Spores are more resistant than vegetative cells. Certain sanitizers are more
active against gram positive than gram negative microorganisms, and vice versa.
Sanitizers also vary in their effectiveness against yeasts, molds, fungi, and
viruses.
Specific Types of Chemical Sanitizers
The chemicals described here are those approved for use as no-rinse,
food-contact surface sanitizers. In food-handling operations, these are used as
rinses, sprayed onto surfaces, or circulated through equipment in CIP
operations. In certain applications the chemicals are foamed on a surface or
fogged into the air to reduce airborne contamination.
Chlorine-based Sanitizers
Chlorine Compounds
Chlorine, in its various forms, is the most commonly used sanitizer in food
processing and handling applications. Commonly used chlorine compounds include:
liquid chlorine, hypochlorites, inorganic chloramines, and organic chloramines.
Chlorine-based sanitizers form hypochlorous acid (HOCl, the most active form) in
solution. Available chlorine (the amount of HOCl present) is a function of pH.
At pH 5, nearly all is in the form of HOCl. At pH 7.0, approximately 75% is
HOCl. The maximum allowable level for no-rinse applications is 200ppm available
chlorine, but recommended usage levels vary. For hypochlorites, an exposure time
of 1 min at a minimum concentration of 50ppm and a temperature of 24°C (75°F) is
recommended. For each 10°C (18°F) drop in temperature, a doubling of exposure
time is recommended. For chloramines, 200 ppm for 1 min is recommended.
Chlorine compounds are broad-spectrum germicides that act on microbial
membranes, inhibit cellular enzymes involved in glucose metabolism, have a
lethal effect on DNA, and oxidize cellular protein. Chlorine has activity at low
temperature, is relatively cheap, and leaves minimal residue or film on
surfaces.
The activity of chlorine is dramatically affected by such factors as pH,
temperature, and organic load. However, chlorine is less affected by water
hardness when compared to other sanitizers (especially the quaternary ammonium
compounds).
The major disadvantage to chlorine compound is corrosiveness to many metal
surfaces (especially at higher temperatures). Health and safety concerns can
occur due to skin irritation and mucous membrane damage in confined areas. At
low pH (below 4.0), deadly Cl2 (mustard gas) can form. In recent
years, concerns have also been raised about the use of chlorine as a drinking
water disinfectant and as an antimicrobial with direct food contact (meat,
poultry and shellfish). This concern is based upon the involvement of chlorine
in the formation of potentially carcinogenic trihalomethanes (THMs) under
appropriate conditions. While chlorine's benefits as a sanitizer far outweigh
these risks, it is under scrutiny.
Chlorine dioxide
Chlorine dioxide (ClO2) is currently being considered as a
replacement for chlorine, since it appears to be more environmentally friendly.
Stabilized ClO2 has FDA approval for most applications in sanitizing
equipment or for use as a foam for environmental and non-food contact surfaces.
Approval has also been granted for use in flume waters in fruits and vegetable
operations and in poultry process waters. ClO2 has 2.5 times the
oxidizing power of chlorine and, thus, less chemical is required. Typical use
concentrations range from 1 to 10ppm.
CLO2s primary disadvantages are worker safety and toxicity. Its
highly concentrated gases can be explosive and the exposure risk to workers is
higher than that for chlorine. Its rapid decomposition in the presence of light,
or at temperatures greater than 50°C (122°F) makes on-site generation a
recommended practice.
Iodine
Use of iodine as an antimicrobial agent dates back to the 1800s. This sanitizer
exists in many forms and usually exists with a surfactant as a carrier. These
mixtures are termed iodophore. The most active agent is the dissociated free
iodine (also less stable). This form is most prevalent at low pH. The amount of
dissociation from the surfactant is dependent upon the type of surfactant.
Iodine solubility is very limited in water. Generally recommended usage for
iodophores is 12.5 to 25ppm for 1 min.
It is generally thought that the bactericidal activity of iodine is through
direct halogenation of proteins. More recent theories have centered upon cell
wall damage and destruction of microbial enzyme activity.
Iodophores, like chlorine compounds, have a very broad spectrum: being active
against bacteria, viruses, yeasts, molds, fungi, and protozoans. Iodine is
highly temperature-dependent and vaporizes at 120°F. Thus, it is limited to
lower temperature applications. The degree to which iodophores are affected by
environmental factors is highly dependant upon properties of the surfactant used
in the formulation. Organic matter and water hardness generally have less affect
on iodophores than chlorine. However, loss of activity is pronounced at high
pH.
Iodine has a long history of use in wound treatment. However, ingestion of
iodine gas does pose a toxicity risk in closed environments. The primary
disadvantage is that iodine can cause staining on some surfaces (especially
plastics).
Quaternary Ammonium Compounds (QACs)
The properties of these compounds depend upon the covalently bound alkyl groups
(R groups), which can be highly diverse. Since QACs are positively charged
actions, their mode of action is related to their attraction to negatively
charged materials such as bacterial proteins. It is generally accepted that the
mode of action is at the membrane function. The carbon length of R-group side
chain is, generally, directly related with sanitizer activity in QACs. However,
because of the lower solubility in QACs composed of large carbon chains, these
sanitizers may have lower activity than short chain structures.
QACs are active and stable over a broad temperature range. Because they are
surfactants, they possess some detergency. Thus, they are less affected by light
soil than are other sanitizers. However, heavy soil dramatically decreases
activity. QACs generally have higher activity at alkaline pH. While lack of
tolerance to hard water is often listed as a major disadvantage of QACs when
compared to chlorine, some QACs are fairly tolerant of hard water. Activity can
be improved by the use of EDTA as a chelator. QACs are effective against
bacteria, yeasts, mold, and viruses.
An advantage of QACs in some applications is that they leave a residual
antimicrobial film. However, this would be a disadvantage in operations such as
cultured dairy products, cheese, beer, etc. where microbial starter cultures are
used.
QACs are generally more active against gram positive than gram negative
bacteria. They are not highly effective against bacteriophages. Their
incompatibility with certain detergents makes thorough rinsing following
cleaning operations imperative. Further, many QAC formulations can cause
foaming problems in CIP applications.
Under recommended usage and precautions, QACs pose little toxicity or safety
risks. Thus, they are in common use as environmental fogs and as room
deodorizers. However, care should be exercised in handling concentrated
solutions or use as environmental fogging agents.
Acid-Anionic Sanitizers
Like QACs, acid-anionic sanitizers are surface-active sanitizers. These
formulations include an inorganic acid plus a surfactant, and are often used for
the dual function of acid rinse and sanitization.
Whereas QACs are positively charged, these sanitizers are negatively charged.
Their activity is moderately affected by water hardness. Their low use pH,
detergency, stability, low odor potential, and non-corrosiveness make them
highly desirable in some applications.
Disadvantages include: relatively high cost, a closely defined pH range of
activity (pH 2 to 3), low activity on molds and yeasts, excessive foaming in CIP
systems, and incompatibility with cationic surfactant detergents.
Fatty Acid Sanitizers
Fatty acid or carboxylic acid sanitizers were developed in the 1980s. Typical
formulations include fatty acids plus other acids (phosphoric acids, organic
acids). These agents also have the dual function of acid rinse and sanitization.
The major advantage over acid anionics is lower foaming potential. These
sanitizers have a broad range of activity, are highly stable in dilute form, are
stable to organic matter, and are stable to high temperature applications.
These sanitizers have low activity above pH 3.5 - 4.0, are not very effective
against yeasts and molds, and some formulations lose activity at temperatures
below 10°C (50°F). They also can be corrosive to soft metals and can degrade
certain plastics, or rubber.
Peroxides
Peroxides or peroxy compounds contain at least one pair of covalently bonded
oxygen atoms (-O-O-) and are divided into two groups: the inorganic group,
containing hydrogen peroxide (HP) and related compounds; and the organic group,
containing peroxyacetic acid (PAA) and related compounds.
Hydrogen peroxide (HP), while widely used in the medical field, has found only
limited application in the food industry. FDA approval has been granted for HP
use for sterilizing equipment and packages in aseptic operations.
The primary mode of action for HP is through creating an oxidizing environment
and generation of singlet or super oxide oxygen (SO). HP is fairly broad
spectrum with slightly higher activity against gram-negative than gram-positive
organisms.
High concentrations of HP (5% and above) can be an eye and skin irritant. Thus,
high concentrations should be handled with care.
Peroxyacetic Acid (PAA)
has been known for its germicidal properties for a
long time. However, it has only found wide application in recent years and is
being promoted as a potential chlorine replacement. PAA is relatively stable at
use strengths of 100 to 200ppm. Other desirable properties include: absence of
foam and phosphates, low corrosiveness, tolerance to hard water, and favorable
biodegradability. PAA solutions have been shown to be useful in removing
bio-films.
While precise mode of action mechanisms have not been determined, it is
generally theorized that the PAA reaction with microorganisms is similar to that
of HP. PAA, however, is highly active against both gram-positive and
gram-negative microorganisms. The germicidal activity of PAA is dramatically
affected by pH. Any pH increase above 7-8 drastically reduces the activity.
PAA has a pungent odor and the concentrated product (40%) is a highly toxic,
potent irritant, and powerful oxidizer. Thus, care must be used in its use.
A general comparison of the chemical and physical properties of commonly used
sanitizers is presented in Table 4 .
References
1. Bakka, R.L. 1995. Making the Right Choice - Cleaners. Ecolab, Inc./Food &
Beverage Div., St. Paul, MN.
2. Boufford, T. 1996. Making the Right Choice - Sanitizers. Ecolab, Inc./Food &
Beverage Div., St. Paul, MN.
3.Barnard, S. Extension. Handout. Penn. State Univ.
4. Cords, B.R. and G.R. Dychdala. 1993. Sanitizers: Halogens, Surface-Active
Agents, and Peroxides. Pp. 36-52. In: P M. Davidson and A. L. Branen, (eds.).
Antimicrobials in Foods . Marcel Dekker, Inc., New York, NY
5. Food Code 1995. U.S. Public Health Service, Food and Drug Admin., Washington,
DC.
6. Grade A Pasteurized Milk Ordinance, 1995. Revision. U.S. Public Health
Service, FDA, Washington, DC.
7. Marriott, N.G. 1994. Cleaning compounds for Effective Sanitation. Pp. 85-113.
Sanitatizers for Effective Sanitation. Pp. 114-166. Principles of Food
Sanitation. Chapman & Hall, New York, NY.
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Table 1. Water impurities and associated
problems.
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Impurity
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Problem Caused
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Common Impurities
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Oxygen
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Corrosion
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Carbon Dioxide
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Corrosion
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Bicarbonates (Sodium, Calcium or
Magnesium)
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Scale
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Chlorides or Sulfates (Sodium, Calcium or
Magnesium)
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Scale & Corrosion
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Silica
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Scale
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Suspended Solids
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Corrosion and Deposition
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Unusually high pH (above 8.5)
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Mediate Corrosion and Deposition; Alter
detergent efficiency
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Unusually low pH (below 5)
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Mediate Corrosion and Deposition; Alter
detergent efficiency
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Table 2. Water impurities and associated
problems.
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Impurity
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Problem Caused
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Less Common Impurities
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Iron
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Filming and Staining
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Manganese
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Corrosion
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Copper
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Filming and Staining
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Table 3. Characteristics of Food Soils
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Surface Deposit
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Solubility
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Ease of Removal
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Heat-Induced
Reactions
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Sugar
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Water soluble
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Easy
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Carmelization
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Fat
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Alkali soluble
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Difficult
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Polymerization
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Protein
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Alkali soluble
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Very Difficult
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Denaturation
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Starch
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Water soluble, Alkali soluble
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Easy to Moderately Easy
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Interactions with other constituents
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Monovalent Salts
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Water soluble; Acid soluble
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Easy to Difficult
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Generally not significant
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Polyvalent Salts
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Acid soluble
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Difficult
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Interaction with other constituents
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Table 4. Comparison of the Chemical and Physical Properties in Commonly Used
Sanitizers*
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Chlorine
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Iodophors
|
Quarternary-
ammonium
compounds
|
Acid anionic
|
Fatty Acid
|
Peroxyacetic acid
|
|
Corrosive
|
Corrosive
|
Slightly corrosive
|
Non-corrosive
|
Slightly corrosive
|
Slightly corrosive
|
Slightly corrosive
|
|
Irritating to skin
|
Irritating
|
Not irritating
|
Not irritating
|
Slightly irritating
|
Slightly irritating
|
Not irritating
|
|
Effective at neutral pH
|
Yes
|
Depends on type
|
In most cases
|
No
|
No
|
Yes
|
|
Effective at acid pH
|
Yes, but unstable
|
Yes
|
In some cases
|
Yes, below 3.0-3.5
|
Yes, below 3.5-4.0
|
Yes
|
|
Effective at alkaline pH
|
Yes, but less than at neutral pH
|
No
|
In most cases
|
No
|
No
|
Less effective
|
|
Affected by organic material
|
Yes
|
Moderately
|
Moderately
|
Moderately
|
Partially
|
Partially
|
|
Affected by water hardness
|
No
|
Slightly
|
Yes
|
Slightly
|
Slightly
|
Slightly
|
|
Residual antimicrobial activity
|
None
|
Moderate
|
Yes
|
Yes
|
Yes
|
None
|
|
Cost
|
Low
|
High
|
Moderate
|
Moderate
|
Moderate
|
Moderate
|
|
Incompatibilities
|
Acid solutions, phenols, amines
|
Highly alkaline detergents
|
Anionic wetting agents, soaps, and acids
|
Cationic surfactants and alkaline
detergents
|
Cationic surfactants and alkaline
detergents
|
Reducing agents, metal ions, strong
alkalis
|
|
Stability of use solution
|
Dissipates rapidly
|
Dissipates slowly
|
Stable
|
Stable
|
Stable
|
Dissipates slowly
|
|
Maximum level permitted by FDA without rinse
|
200ppm
|
25ppm
|
200ppm
|
Varied
|
Varied
|
100-200ppm
|
|
Water
temperature sensitivity
|
None
|
High
|
Moderate
|
Moderate
|
Moderate
|
None
|
|
Foam level
|
None
|
Low
|
Moderate
|
Low/Moderate
|
Low
|
None
|
|
Phosphate
|
None
|
High
|
None
|
High
|
Moderate
|
None
|
|
Soil load tolerance
|
None
|
Low
|
High
|
Low
|
Low
|
Low
|
|
*Comparisons made at approved 'no-rinse use'
levels. Adapted from B.R. Cords and G.R. Dychdala, 1993
|
|