This document describes a study that examined the factors influencing the effectiveness of hydrogen peroxide vapor for surface decontamination. The study tested different combinations of hydrogen peroxide concentration (400, 600, 800 ppm) and humidity levels on test surfaces inoculated with Geobacillus stearothermophilus spores. The results showed that higher hydrogen peroxide concentrations and higher humidity levels resulted in faster spore inactivation. Subvisible condensation enhanced inactivation, but visible condensation provided no further benefit. The deposition of water and hydrogen peroxide on surfaces, not gas phase concentration, was found to be the determining factor for microbial inactivation.
This file defines for researchers and editors the most important notes about scientific writing and prose according to the APA style. It elaborates the proper usage of some linguistic devices, shows how to be precise, clear, smooth and logical in writing.
¿Podemos tratar la artrosis y aliviar el dolor articular?CongresoAEEM
Symposium patrocinado por Bioibérica: artrosis en la mujer menopáusica: diagnóstico, tratamiento y pronóstico genético.
Dr. Pascual García Alfaro - ¿Podemos tratar la artrosis y aliviar el dolor articular?
This file defines for researchers and editors the most important notes about scientific writing and prose according to the APA style. It elaborates the proper usage of some linguistic devices, shows how to be precise, clear, smooth and logical in writing.
¿Podemos tratar la artrosis y aliviar el dolor articular?CongresoAEEM
Symposium patrocinado por Bioibérica: artrosis en la mujer menopáusica: diagnóstico, tratamiento y pronóstico genético.
Dr. Pascual García Alfaro - ¿Podemos tratar la artrosis y aliviar el dolor articular?
GWC Valve International brochure for valves that we manufacture nationally and internationally.
GWC products are designed, engineered and manufactured to exceed your stringent process requirements.
GWC's Global Operations are licensed and certified to API-6D, API-6A, API-600, PED and ISO 9000.
The International Journal of Mechanical Engineering Research and Technology is an international online journal in English published Quarterly offers a fast publication schedule whilst maintaining rigorous peer review the use of recommended electronic formats for article delivery expedites the process All submitted research articles are subjected to immediate rapid screening by the editors consultation with the Editorial Board or others working in the field as appropriate to ensure they are likely to be the level of interest and importance appropriate for the journal.
GWC Valve International brochure for valves that we manufacture nationally and internationally.
GWC products are designed, engineered and manufactured to exceed your stringent process requirements.
GWC's Global Operations are licensed and certified to API-6D, API-6A, API-600, PED and ISO 9000.
The International Journal of Mechanical Engineering Research and Technology is an international online journal in English published Quarterly offers a fast publication schedule whilst maintaining rigorous peer review the use of recommended electronic formats for article delivery expedites the process All submitted research articles are subjected to immediate rapid screening by the editors consultation with the Editorial Board or others working in the field as appropriate to ensure they are likely to be the level of interest and importance appropriate for the journal.
A new generation of cable grade poly(vinyl chloride) containing heavy metal f...Ali I. Al-Mosawi
Many additives are used to improve the performance of cables in terms of increasing their flame retardancy, thermal stability, thermal conductivity, and other characteristics. Unfortunately, most of these additives contain heavy metals. Therefore, the main objective of this study is to introduce a material representing a new generation of environmentally friendly heavy metal-free stabilizers for cable grade poly(vinyl chloride) that can compete with traditional materials in terms of performance and distinctive properties. This unique additive is Oxydtron, a synthetic silicate or simply nanocement. The tests performed are rheological properties represented by a capillary rheometry analysis, limiting oxygen index, and volume resistivity. The most significant improvement in Bagley correction measurements was 14.61%; 18.13%; and 27.20% more than poly(vinyl chloride) basic formulation when using 5wt.% Oxydtron at 160°C, 170°C, and 180°C, respectively. Also, the mean increases in relaxation time were 3.200 times, 8.825 times, and 12.458 times more than poly(vinyl chloride) basic formulation with 1wt.%, 3wt.%, and 5wt.% of Oxydtron, respectively. Furthermore, the Oxydtron lowered the value of the accompanying thermal gradient of the L.O.I test, reducing the heat-affected zone. The best result was with the extrusion processing method due to the uniformity of the processing conditions. However, the thermal gradient analysis showed residual heat stress in the test samples after cutting the burning layer and re-testing the samples again; this causes them to burn faster. This situation requires caution for designs that are exposed to high temperatures without burning. The optimum improvement in volume resistivity value was 14.71% and 38.24% more than poly(vinyl chloride) basic formulation after adding 5wt.% and 7wt.% of Oxydtron, respectively.
Optimization of ZLD in Distillery Industry by Reverse Osmosis Process for Pre...ijceronline
In this study, the effects of Operating Pressure, Potential Hydrogen, Oxidation Reduction Potential and Anti Scaling Agent on multi responses like Permeate, COD, Total Solids, Conductivity and Hardness in the Reverse Osmosis Process were experimentally investigated on RO 8100 ST8 PT44 400Wl machine. The settings of RO parameters were determined by using Taguchi’s experimental design method. Orthogonal arrays of Taguchi, the signal-to-noise (S/N) ratio, the analysis of variance (ANOVA) are employed to find the optimal levels and to analyze the effect of the RO parameters. Results show that potential of hydrogen, operating pressure, oxidation reduction potential and anti scaling agent are the four Parameters that influence the Permit more effectively and COD, Total Solids, Conductivity and Hardness respectively. Finally, the ranges for best RO conditions are proposed for ZLD process.
Investigation on the Effect of TiO2 and H2O2 for the Treatment of Inorganic C...inventy
Sodium hypochlorite (NaClO) is regularly used as a disinfectant or a bleaching agent because of its high efficiency against many bacteria and viruses present in seawater along with its cheaper cost. Now a days, with the increase in the environmental concerns concerning the use of chlorination for the disinfection or bleaching of treated water related to the formation of potentially harmful chloro-organic by products through reactions with natural organic matter (NOM), it is preferred to implement a process with environmentally friendly chemicals for water treatment processes. About This report aim to study the possibility of reducing the inorganic carbon present in seawater by oxidization reaction of seawater with TiO2 and H2O2. Investigated and a comparison between thin film method and suspension method with a reactor system in conjunction with a light concentrating system has been done.
The investigation of photo-oxidation of gas phase cyclohexane was an experimental study used to determine how the concentration of cyclohexane in a bulk flow influent to a photcatalytic reactor affects the rate of degradation. In addition, a secondary set of tests will be conducted to aide in obtaining data for determining the effect of particle size on degradation
Effect of Temperature and Humidity on Indoor Radon Concentrationijtsrd
Because radon gas is colorless and odorless, it is impossible for humans five senses to know whether one is exposed to it and as it is an inert gas that is nine times heavier than air it is prone to accumulation after being brought into the room through cracks in old buildings, connections and drains, thus creating indoor radon exposure problem. Although indoor radon concentration is related to indoor temperature and humidity, no research has been conducted to actually control indoor temperature and humidity, and to find out how changes in indoor temperature and relative humidity have affected indoor radon concentration. In this paper, we experimented with varying temperature and relative humidity respectively to certain conditions in the laboratory where the thermo hygrostat is installed, and using the results of the measured experiment, the relation between indoor temperature, and relative humidity and indoor radon concentration was explored. Jai-Won Chung | Tae-In Hyon | Gyu-Sik Kim ""Effect of Temperature and Humidity on Indoor Radon Concentration"" Published in International Journal of Trend in Scientific Research and Development (ijtsrd), ISSN: 2456-6470, Volume-4 | Issue-2 , February 2020,
URL: https://www.ijtsrd.com/papers/ijtsrd30128.pdf
Paper Url : https://www.ijtsrd.com/engineering/electrical-engineering/30128/effect-of-temperature-and-humidity-on-indoor-radon-concentration/jai-won-chung
The Effect of Formic Acid, Hydrogen Peroxyde and Other Conditions on Epoxidiz...ijtsrd
Epoxidized vegetable oil have drawn much attention in recent yearrs, especially in the polymer industry as they are economical, available, environmentally friendly, non noxious and renewable. Cashew nut shell liquid CNSL , an agricultural by product abundantly available in tropical countries such as Vietnam, India, is one of the major and economical resources of naturally occurring phenols. Cardanol a byproduct of CNSL could be epoxidized by reacting carbon carbon double bonds of long unsaturated chain with peracids via the Prileshajev epoxidation process or the conventional process. This paper deals with the epoxidized reaction of cardanol take place in formic acid and hydrogen peroxyde. The results shown that the conversion efficiency of the epoxidized reaction reacheres 80 at 600C, stirring rates 1800 rpm, 2 p toluenesulfonic acid catalyst and rate of double bonds DB HCOOH AF H2O2 = 1.0 0.5 1.5. The product of epoxidized cardanol is also characterized by FT IR, 1H NMR and13C NMR. Bach Trong Phuc | Nguyen Thanh Liem "The Effect of Formic Acid, Hydrogen Peroxyde and Other Conditions on Epoxidized Reaction of Cardanol Extracted from Cashew Nut Shell Liquid of Vietnam" Published in International Journal of Trend in Scientific Research and Development (ijtsrd), ISSN: 2456-6470, Volume-6 | Issue-3 , April 2022, URL: https://www.ijtsrd.com/papers/ijtsrd49624.pdf Paper URL: https://www.ijtsrd.com/chemistry/polymer-chemistry/49624/the-effect-of-formic-acid-hydrogen-peroxyde-and-other-conditions-on-epoxidized-reaction-of-cardanol-extracted-from-cashew-nut-shell-liquid-of-vietnam/bach-trong-phuc
Optimizing the Reverse Osmosis Process Parameters by Maximizing Recovery by T...QUESTJOURNAL
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COD reduction of aromatic polluted waste water by Advanced Oxidation Process ...Wade Bitaraf
In most petrochemical complexes and oil refineries the wastewater contains the aromatic compounds among which Benzene, Toluene, Ethyl Benzene and Xylene (BTEX) have harmful effects on environment and human health. The present work mainly deals with the UV-based advanced oxidation processes (AOPs), UV/H2O2 were tested in batch reactor systems to evaluate the removal efficiencies and optimal conditions for the photodegradation of BTEX in order to wastewater treatment. The efficiency of this method was analyzed by evaluating the Chemical Oxygen Demand (COD) as a pollution criterion through the COD reactor. The influence of the basic operational parameters such as initial concentration of H2O2, pH, Temperature, irradiation time and UV amount on the photo degradation of BTEX were also studied. The oxidation rate of BTEX and respectively the reduction rate of COD were low when the oxidation was carried out in the absence of H2O2 or UV light. The addition of proper amount of hydrogen peroxide improved the degradation, while the excess hydrogen peroxide could quench the formation of hydroxyl radicals (•OH). The optimal conditions of suspended slurry with 1.11(g/l) initial concentration of H2O2 and pH value of 3.1 were obtained under three UV lights illumination (6 W). Under the optimal conditions, COD reduction during the initial period of 180 min in UV/H2O2 systems reached about 90%.
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Things to remember while upgrading the brakes of your carjennifermiller8137
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Things to remember while upgrading the brakes of your car
Bosch H2O2 decon paper
1. J Pharm Innov (2008) 3:123–133
DOI 10.1007/s12247-008-9027-1
RESEARCH ARTICLE
The Influence of Humidity, Hydrogen Peroxide
Concentration, and Condensation on the Inactivation
of Geobacillus stearothermophilus Spores with Hydrogen
Peroxide Vapor
Beatriz Unger-Bimczok & Volker Kottke &
Christian Hertel & Johannes Rauschnabel
Published online: 8 May 2008
# International Society for Pharmaceutical Engineering 2008
Abstract The study presented here examined the factors Keywords Condensation . Decontamination . D value .
influencing the effectiveness of surface decontamination Geobacillus stearothermophilus . Hydrogen peroxide .
with hydrogen peroxide vapor. The impact of relative Inactivation . Isolator . Relative humidity . Vapor
humidity and hydrogen peroxide gas concentrations was
investigated and compared to a dew point analysis of these
various sterilant atmospheres. For this purpose, a series of Introduction
different H2O2 decontamination cycles were developed and
tested for antimicrobial effectiveness using biological Hydrogen peroxide is a strong oxidizing agent, and
indicators inoculated with greater than 106 spores of aqueous H2O2 solutions have been used for sterilization
Geobacillus stearothermophilus. The results indicate that and disinfection purposes for more than a century. Since it
an increasing concentration of hydrogen peroxide in the gas was discovered that the antimicrobial effectiveness of the
phase and higher humidity levels result in a faster sterilant is significantly increased in the gaseous phase [1],
inactivation of the test organisms. The higher the H2O2 hydrogen peroxide vapor is commonly used for surface
gas phase concentration was, the more independent the decontamination. Due to its environmentally friendly and
inactivation effect from the humidity level. At lower H2O2 nontoxic decomposition products, hydrogen peroxide is being
concentrations, the same kill was achieved with higher increasingly substituted for vapor phase sterilants like
humidity. Subvisible condensation was found to be neces- ethylene oxide and formaldehyde, which are toxic, carcino-
sary for short inactivation times, but condensation in the genic, and potentially explosive [2]. Vapor phase hydrogen
visible range did not further enhance the sporicidal activity. peroxide was shown to have effective broad-spectrum
The molecular deposition of water and hydrogen peroxide antimicrobial properties and to inactivate bacteria, fungi,
on the target surface represents the determining factor for viruses, and highly resistant spores [2–5].
microbial inactivation, whereas the hydrogen peroxide In the pharmaceutical industry, hydrogen peroxide vapor has
concentration in the gas phase is of secondary importance. been used in the decontamination of barrier systems for more
than 10 years [4, 6]. Today, the use of isolator technology is
increasing, and hydrogen peroxide vapor is gaining additional
importance as a decontamination agent [7–10]. Several
B. Unger-Bimczok : J. Rauschnabel (*)
Robert Bosch GmbH,
parameters are known to affect the decontamination success
Blaufelder Str. 45, of rooms and chambers with hydrogen peroxide vapor.
74564 Crailsheim, Germany Besides the construction materials that are to be decontami-
e-mail: johannes.rauschnabel@de.bosch.com nated [11, 12], the environmental conditions play an important
V. Kottke : C. Hertel
role. However, the cycle parameters that affect microbial
University of Hohenheim, inactivation by hydrogen peroxide vapor are still under
70599 Stuttgart, Germany investigation and remain controversial.
2. 124 J Pharm Innov (2008) 3:123–133
The literature reveals disagreement on the optimum Biological indicators (BIs) were exposed to the various
conditions concerning relative humidity, hydrogen peroxide sterilant atmospheres, and subsequently, both D values and
concentration, and temperature. There is also debate inactivation kinetics were determined.
concerning whether condensation is needed for the mech-
anism of microbial inactivation or if a dry cycle is
preferential. Several publications propose a direct correla- Materials and Methods
tion between the concentration of the gaseous sterilant in
the chamber air and the antimicrobial efficacy [5, 13, 14]. Study Design
In contrast, some authors report high inactivation rates with
comparatively low hydrogen peroxide concentrations [12], The following investigations were carried out during the study:
while others question a correlation between measured H2O2
& End-point D value studies with BIs sealed in Tyvek
concentration and the absolute antimicrobial efficacy [15].
(for four humidity levels [HLs] and three hydrogen
Associated with the issue of hydrogen peroxide concentra-
peroxide levels). Investigation into the influence on
tion is the question regarding appropriate levels of relative
D value of the following parameters:
humidity. Watling et al. [16] investigated flash vaporization
& Water and hydrogen peroxide concentrations
of 35% aqueous hydrogen peroxide solution in a closed-loop
& Hydrogen peroxide consumption
system. The authors demonstrated that the concentration of
& Condensation
gaseous hydrogen peroxide at the point when condensation
& End-point D value studies with BIs sealed in Tyvek
first occurs is higher when the initial relative humidity inside
and unsealed (for four HLs and one hydrogen
the chamber is low. Therefore, it is a common procedure to
peroxide level)
dehumidify the sealed enclosure prior to the introduction of
& Inactiviation kinetics using the most probable number
the hydrogen peroxide vapor to reach high sterilant concen-
(MPN) method (for four HLs and two hydrogen
trations in the gas phase and to prevent condensation [5, 14].
peroxide levels)
With this method, the microbial inactivation is regarded as a
dry process. Condensation is considered uncontrollable and
unwanted because of potential problems caused by material Decontamination System
corrosion, prolonged aeration time, and inhomogeneous
decontamination [5, 14]. Isolator and Vapor Generator
In a different approach, it is claimed that condensation
cannot be avoided during standard decontamination pro- The experiments were conducted in a five-glove, rigid-wall
cesses [17] and that the occurrence of condensation is the isolator with an internal volume of 7.5 m3. The machine was
critical factor affecting antimicrobial efficacy [17]. In this located within a clean room environment with the compart-
context, Imai et al. [15] suggested that relative humidity is a ment air temperature controlled at 22±2°C. The barrier
less critical factor for vapor phase hydrogen peroxide system was connected to a Bosch SafeVAP vapor generator
decontamination and proposed eliminating the dehumidifi- operated in open-loop mode. The gas generator was
cation phase. According to surveys conducted by Watling modified from standard operation to enable simultaneous
[18], invisible microcondensation is responsible for the flash vaporization of water and hydrogen peroxide by two
rapid microbial inactivation. parallel vaporizers. This provided the means to develop
As described, published data regarding the influence of customized cycles and to produce test atmospheres with any
operating conditions on the effectiveness of hydrogen combination of humidity and hydrogen peroxide concentra-
peroxide vapor decontaminations are not conclusive. Until tion in the isolator during the decontamination cycle. The
now, no standard system or method has been established for sporicidal agent used was 35% hydrogen peroxide by weight
the evaluation of the sporicidal effect of hydrogen peroxide. (Interox SG-35, Solvay Chemicals GmbH, Rheinberg), and
This paper provides an analysis of the parameters affecting the water vaporized for the regulation of the humidity was
sporicidal activity of hydrogen peroxide vapor for an open- high-performance liquid chromatography Gradient Grade
loop system. The objective of this study is to deepen the Water, Carl Roth, Karlsruhe.
understanding of the inactivation mechanism and to
optimize decontamination cycles. The article describes the Decontamination Cycle
evaluation of sterilant atmospheres with different levels of
hydrogen peroxide and water vapors, varied independently, The decontamination cycle included four successive cycle
and the resulting condensation levels. The various sterilant steps. The four stages of the decontamination cycle that are
atmospheres were systematically examined for the capabil- to specify the single-decontamination phases are illustrated
ity of inactivating certain microbial test populations. in Fig. 1. During the preparation phase (I), the relative
3. J Pharm Innov (2008) 3:123–133 125
Hydrogen trend of the water concentration during the bio-decontam-
peroxide
concentration
ination phase with a H2O2 concentration of 600 ppm.
I II II IV. I.Preparation phase
II.Conditioning phase
III.Bio-decontamination Measuring Instruments
phase
IV.Aeration phase
Inside the isolator chamber, a near-infrared spectrometer
probe (H2O2 Vapor Monitor, Guided Wave, Rancho Corvo,
Process time
CA, USA) was installed to record water and hydrogen
Fig. 1 Schematic example of the hydrogen peroxide concentration
during a decontamination cycle
peroxide concentrations during the decontamination cycles.
The Vapor Monitor provided a direct in situ measurement
of hydrogen peroxide and water concentrations in the gas
humidity of the isolator atmosphere was reduced to 20%, phase [19]. For qualitative verification of the measurement,
and the ductwork and evaporators were heated for the an additional electrochemical H2O2 sensor (Analytical
subsequent introduction of the hydrogen peroxide. In the Technology, Collegeville, PA, USA) was used to monitor
conditioning phase (II), hydrogen peroxide (and in this the H2O2 concentration. A capacitive dew sensor (BTF
configuration, water) is introduced at a high rate to reach 11356A, CIS Institut für Mikrosensorik gGmbH, Erfurt) was
the desired concentration levels within the isolator. During installed in the test chamber for the detection and quantifi-
the bio-decontamination phase (III), hydrogen peroxide is cation of condensation during the decontamination cycles.
introduced at a reduced rate such that only the consumed The dew point detector consisted of a silicon-integrated,
hydrogen peroxide is replaced, and a constant hydrogen stray field capacitor connected to a capacitance–frequency
peroxide concentration is maintained within the isolator. converter. Due to its dielectric constant, condensed vapor
The terminal phase of the decontamination cycle is the causes a rise in capacitance and therefore an increase in the
aeration (IV), during which the hydrogen peroxide is frequency output signal in proportion to the level of
removed from the system by dilution with fresh air. condensation.
For this study, customized decontamination cycles were
developed to produce 12 distinct sterilant atmospheres Biological Test Procedure
during the bio-decontamination phase. Table 1 shows the
12 sterilant atmospheres developed: Three distinct hydro- Test organisms were exposed to the different test atmosphere
gen peroxide concentrations (400, 600, and 800 ppm H2O2) combinations in the isolator to evaluate the inactivation
were developed, each at four distinct HLs. HL 1 (for 400, efficiency of the various decontamination conditions. BIs
600, and 800 ppm H2O2) was created by the introduction of were exposed to the decontamination cycle solely during the
the hydrogen peroxide solution only and provided a water bio-decontamination phase and removed from the test
concentration range of about 3,500 to 8,500 ppm. For HLs atmosphere at predetermined time intervals. The commercial-
2 through 4, vaporized water was introduced to the system ly available BIs were composed of grade 304 stainless steel
in increasing amounts. This resulted in water concentration carriers, each inoculated with 2.4×106 spores of Geobacillus
ranges of 8,500 to 13,000 (HL 2), 11,500 to 17,000 (HL 3), stearothermophilus American Type Culture Collection no.
and 14,500 to 21,000 ppm (HL 4). Figure 2 is an example 12980. The BIs, sealed in 1073B medical-grade TyvekTM,
of the composite hydrogen peroxide and water concentra- were manufactured by Apex Laboratories, Sanford, NC,
tion curves during the decontamination cycles with hydro- USA. The certified BI population was tested and verified
gen peroxide concentrations of 400, 600, and 800 ppm at according to the acceptance criteria specified in US
HL 2. The varying water content in the isolator atmosphere Pharmacopoeia (USP) [20]. All BIs used throughout the
for HLs 1 to 4 is demonstrated in Fig. 3, which shows the study were from a single production lot.
Table 1 Decontamination cycles with different combinations of hydrogen peroxide concentration and humidity levels during bio-
decontamination phase
HL: range of H2O concentration H2O2 concentration
400 ppm 600 ppm 800 ppm
HL 1 (3,500 to 8,500 ppm H2O) 400 ppm H2O2, HL1 600 ppm H2O2, HL1 800 ppm H2O2, HL1
HL 2 (8,500 to 13,000 ppm H2O) 400 ppm H2O2, HL2 600 ppm H2O2, HL2 800 ppm H2O2, HL2
HL 3 (11,500 to 17,000 ppm H2O) 400 ppm H2O2, HL3 600 ppm H2O2, HL3 800 ppm H2O2, HL3
HL 4 (14,500 to 21,000 ppm H2O) 400 ppm H2O2, HL4 600 ppm H2O2, HL4 800 ppm H2O2, HL4
4. 126 J Pharm Innov (2008) 3:123–133
Fig. 2 Water and hydrogen per- Preparation Conditioning Bio-decontamination Aeration
oxide concentrations during de-
1000 14000
contamination cycles with 400,
600, and 800 ppm H2O2 con-
12000
centrations at humidity level 2
Water concentration [ppm]
800
(measured with the NIR probe)
concentration [ppm]
10000
Hydrogen peroxide
600
8000
6000
400
4000
200
2000
0 0
00:15 00:30 00:44
Hydrogen peroxide concentration 400 ppm (for humidity level 2)
Bio-decontamination Hydrogen peroxide concentration 600 ppm (for humidity level 2)
cycle [hh:mm]
Hydrogen peroxide concentration 800 ppm (for humidity level 2)
Water concentration humidity level 2 (for 400 ppm H2O2)
Water concentration humidity level 2 (for 600 ppm H2O2)
Water concentration humidity level 2 (for 800 ppm H2O2)
D Value expiration of the incubation period, D values were
calculated according to the fraction-negative approach of
The D value is the time (in minutes) of exposure at given the Holcomb–Spearman–Karber method with at least two
sporicidal conditions, which causes a one log or 90% exposure times in the lethal area [22, 23]. The initial spore
reduction in the population of a specific test microorganism population, certified by the manufacturer of the BIs, was
[21]. At the beginning of the bio-decontamination phase, used for the calculation of the D values. For each test
BIs were exposed to the sporicidal conditions in the atmosphere, the cycle was repeated several times. One D
isolator. For the determination of D values, five BIs were value determination was performed per cycle run (five BIs
removed from the isolator at each exposure time. The per takeout interval) to obtain at least three values for every
samples were aseptically transferred into test tubes with test atmosphere. In some experiments, D values were
3 ml of sterile soybean casein digest broth (Caso-Bouillon, determined for unsealed BIs. In these cases, the bare
Merck KGaA, Darmstadt) and incubated at 55°C for 7 days. indicators were exposed without the Tyvek envelope; all
The test tubes were evaluated for growth daily, and after the other steps were identical.
25000
20000
Water concentration [ppm]
15000
10000
5000
0
00:00 00:02 00:05 00:08 00:11 00:14 00:17 00:20
Water concentration humidity level 4
Bio-decontamination phase [hh:mm]
Water concentration humidity level 3
Water concentration humidity level 2
Water concentration humidity level 1
Fig. 3 Water concentration during the bio-decontamination phase for humidity levels 1–4 and 600 ppm H2O2 (measured with the NIR probe)
5. J Pharm Innov (2008) 3:123–133 127
Most Probable Number that for the cycles with HL 2 (for 400, 600, and 800 ppm
H2O2), the water concentration was reproducible. The same
The MPN procedure is a standard method for the estimation repeatability was also found for the other cycles. Cycle
of densities of viable microorganisms in liquid samples. It repeatability was crucial because the duration of the study
does not rely on a direct count of single cells or colonies required 2 months, with each cycle performed several times
but on the statistical probability of diluting to extinction for the determination of repeated D values. As shown in
[24–26]. In this study, the MPN method was used to Fig. 2, the hydrogen peroxide concentration in the isolator
establish inactivation kinetics of the test populations atmosphere during the bio-decontamination phase was
exposed to the test atmospheres. At each exposure interval, constant as a function of time for all cycles. Due to reduced
one BI was removed from the chamber and eluted with injection rates in the bio-decontamination phase and
10 ml of sterile medium (Caso-Bouillon, Merck KGaA). To increasing chamber temperature during the cycle, from
remove the spores from the carrier and singularize them in 22°C at the beginning of the cycle to around 27°C at the
the suspension, samples were treated in an ultrasonic bath end of the bio-decontamination phase, the water concentra-
for 30 min (VWR Ultrasonic Cleaner USC200T, VWR tion decreased slightly over time. In Fig. 3, the trend of the
International GmbH, Darmstadt). A three-tube MPN pro- water concentration during the bio-decontamination phase
cedure with aseptic serial tenfold dilutions was used to was plotted against time for the four distinct HLs. Water
enumerate the density of viable microorganisms subsequent concentration follows a similar trend for HLs 1 to 4,
to vapor treatment. The samples were incubated for 7 days reaching a steady-state condition under each condition.
at 55°C, and the tubes were observed daily for the presence Although the exposure conditions for the BIs were not
or absence of growth. The resulting data were interpreted completely fixed in terms of water concentration, the D
by the means of MPN tables [27]. The determination of the values for the different HLs can be compared because of the
inactivation kinetics was repeated three times for every similar trend of the water concentration in HLs 1 to 4.
cycle parameter set.
Water and Hydrogen Peroxide Concentration
Results and Discussion In this study, the D values provide a means of comparing
the inactivation efficiency of the different sterilant atmos-
D Value Studies with BIs Sealed in Tyvek pheres. Table 2 summarizes all D values determined for the
various combinations of hydrogen peroxide and water. For
Decontamination Cycle the comparison of the different HLs, the water concentra-
tion of every decontamination cycle was averaged for the
The sterilizing atmospheres created for the D value studies first 15 min of the bio-decontamination phase and listed
were found to be very repeatable. Figure 2 demonstrates together with the respective D values. In Figs. 4, 5, and 6,
Table 2 D values and average water concentration for decontamination cycles with 400, 600, and 800 ppm hydrogen peroxide during bio-
decontamination phase
HL1 c (water) HL2 HL3 c (water) HL4 c (water)
D value (ppm) D value c (water) D value (ppm) D value (ppm)
(min) (min) (ppm) (min) (min)
400 ppm H2O2 14.83 3,612 4.27 10,177 1.38 13,588 0.68 18,151
14.33 3,919 4.27 10,081 1.13 13,880 0.78 17,469
14.70 3,919 3.14 10,109 1.43 13,880 0.93 17,469
– – – – – – 0.88 18,383
– – – – – – 0.78 18,383
600 ppm H2O2 2.87 6,414 0.87 10,413 0.75 13,924 0.75 18,272
2.56 5,518 0.83 11,497 0.53 12,898 0.35 18,126
2.14 7,349 0.88 11,497 0.58 12,898 0.45 18,126
– – 1.13 9,992 – – 0.58 20,052
800 ppm H2O2 0.56 6,741 0.48 11,250 0.25 14,046 0.38 17,184
0.53 7,213 0.65 9,550 0.28 14,525 0.48 17,378
0.53 8,633 0.65 9,550 0.28 14,525 0.43 17,378
– – 0.45 9,386 – – 0.43 17,378
6. 128 J Pharm Innov (2008) 3:123–133
20.0 5.0
4.0
15.0
D-value [min]
D-value [min]
3.0
10.0
2.0
5.0
1.0
0.0 0.0
0 5000 10000 15000 20000 25000 0 5000 10000 15000 20000 25000
Water concentration [ppm] Water concentration [ppm]
Average D-value 400 ppm H2O2, HL1 Average D-value 400 ppm H2O2, HL2 Average D-value 800 ppm H2O2, HL1 Average D-value 800 ppm H2O2, HL2
Average D-value 400 ppm H2O2, HL3 Average D-value 400 ppm H2O2, HL4 Average D-value 800 ppm H2O2, HL3 Average D-value 800 ppm H2O2, HL4
Fig. 4 Effect of increasing relative humidity on sporicidal activity at Fig. 6 Effect of increasing relative humidity on sporicidal activity at
400 ppm of hydrogen peroxide (water concentration averaged for first 800 ppm of hydrogen peroxide (water concentration averaged for first
15 min of bio-decontamination phase) 15 min of bio-decontamination phase)
the determined D values are plotted against the water 0.5 min. For HL 2, the experiments show the same
concentration for the 400, 600, and 800 ppm peroxide qualitative outcome but with diminished D value intervals
cycles. The data points represent a mean of the D values between the different hydrogen peroxide concentration
and the average water concentration determined for every levels (3.9 [400 ppm], 0.9 [600 ppm], and 0.6 min
set of water and hydrogen peroxide concentration. The y- [800 ppm H2O2]).
axis error bars show the standard deviation of the calculated The linear dependency of H2O2 vapor concentration and
D values. microbial kill has been the subject of controversial
The reported data is valid for the tested decontamination discussion in the literature. While some authors have the
equipment in combination with the according environmen- opinion that antimicrobial efficacy increases with peroxide
tal conditions and the biological test system used. The concentration [13], others doubt a correlation between the
results presented in Table 2 and Figs. 4, 5, and 6 show measured H2O2 concentration and the absolute antimicro-
clearly that, for an identical HL, an increasing concentration bial efficacy [15] and have provided inactivation studies
of hydrogen peroxide vapor results in a faster inactivation conducted at low hydrogen peroxide concentrations [12].
of the test organisms. A correlation between the hydrogen Figures 4, 5, and 6 demonstrate that the hydrogen
peroxide vapor concentration and the death rate of the peroxide concentration is an important factor in the
microorganisms is especially apparent for HL 1: The inactivation efficacy but that the D values converge with
average D value for 400 ppm hydrogen peroxide is increasing HLs. With a low hydrogen peroxide gas
14.6 min, for 600 ppm 2.5 min, and for 800 ppm only concentration (400 ppm), a higher humidity is necessary
to achieve the same kill rates than with a high gas
concentration (800 ppm). All test cycles show increasing
5.0 sporicidal activity with increasing water concentration in
the chamber. This could be explained by the intensified
4.0
condensation events occurring due to the saturation of the
isolator atmosphere with water and hydrogen peroxide [14,
D-value [min]
3.0
16]. The process of condensate deposition on a surface is
2.0 based on a series of successive steps starting with the
adsorption of gas molecules, followed by the formation and
1.0
growth of a thin film, and finally the development of droplets.
0.0 The process of the formation and the microscopic deposition
0 5000 10000 15000 20000 25000 of aqueous hydrogen peroxide solution on the chamber
Water concentration [ppm] surfaces can be referred to as “microcondensation.”
Average D-value 600 ppm H2O2, HL1 Average D-value 600 ppm H2O2, HL2
As seen in Table 2, the cycles consisting of HL 1 with
Average D-value 600 ppm H2O2, HL3 Average D-value 600 ppm H2O2, HL4
800 ppm hydrogen peroxide concentration showed an
average water concentration of 7,500 ppm. The water
Fig. 5 Effect of increasing relative humidity on sporicidal activity at
600 ppm of hydrogen peroxide (water concentration averaged for first content of the cycles consisting of HL 1 with 400 and
15 min of bio-decontamination phase) 600 ppm hydrogen peroxide exhibited water concentrations
7. J Pharm Innov (2008) 3:123–133 129
of 3,800 and 6,400 ppm water, respectively. The data The most economical decontamination cycles were those
suggest that for high hydrogen peroxide concentrations with a high peroxide concentration combined with a low
(equal to or exceeding 800 ppm), the additional humidity humidity (800 ppm H2O2, HLs 1 and 2), cycles with a
becomes less important with respect to the kill. This is medium peroxide concentration and a medium humidity
demonstrated in Fig. 6, where the amount of water (600 ppm H2O2, HL 2), or cycles with a low hydrogen
transferred into the system by evaporation of the 35% peroxide concentration and a high humidity (400 ppm
liquid hydrogen peroxide at HL 1 enables a highly efficient H2O2, HL 3). Both H2O2 vapor concentration and humidity
kill with a resulting average D value of 0.5 min. Higher determine the kill efficacy.
amounts of water in the system with around 10,100, The results for the other decontamination cycles shown
14,400, and 17,300 ppm water (HLs 2, 3, and 4) do not in Fig. 7 indicated either (a) insufficient inactivation of the
result in further significant reductions in the D value. test organisms (D values greater than 2 min for H2O2
Consequently, for the highest tested hydrogen peroxide vaporization less than 150 g) or (b) that unreasonably high
concentration (800 ppm H2O2), the inactivation effect is amounts of peroxide (H2O2 vaporization greater than
independent of the HL. 300 g) were expended without a decrease of the D value.
In the test system, a vaporization of greater than or equal to
Hydrogen Peroxide Consumption 200 g peroxide during the conditioning phase resulted in a
D value below 1 min for every cycle. An increase in the
For a cost-effective decontamination cycle, it is necessary mass of hydrogen peroxide vaporized did not result in any
to minimize the use of hydrogen peroxide. This produces a further decrease in the inactivation rate.
savings of the consumable sterilant, hydrogen peroxide, and The decontamination cycles in Fig. 7 that were econom-
a savings in the time and energy used for the aeration of the ical in their use of H2O2 all had high vaporization rates with
isolator following the bio-decontamination phase. Figure 7 hydrogen peroxide consumption ranging between 25 and
shows the amount of hydrogen peroxide consumed during 28 g/min. This indicates that less peroxide is needed to
the conditioning phase for every combination of H2O2 achieve a good kill when the H2O2 concentration in the
concentration and humidity tested. The H2O2 consumption isolator atmosphere is rapidly increased during the condi-
is plotted versus the average D value determined for the tioning phase. By the use of an efficient flash vaporizer,
particular decontamination cycle. high gas concentrations and an efficient decontamination
It can be seen from Fig. 7 that the decontamination process can be achieved. Additionally, a minimized H2O2
cycles with a consumption between 150 and 250 g injection volume also has the positive secondary effect that
hydrogen peroxide during the conditioning phase have a the load of peroxide on the barrier system (e.g., filters) is
noticeably economic ratio between the amount of hydrogen reduced, resulting in the preservation of the construction
peroxide vaporized and the achieved kill rate, compared to materials and a shortening of the cycle time.
the other cycles.
Condensation
14.0
12.0
According to the prevailing laws of physics, a certain
10.0
amount of condensation cannot be avoided when injecting
D-value [min]
hydrogen peroxide vapor and water vapor into a system at
8.0
conditions typically present in a pharmaceutical isolator
6.0
(20% relative humidity, 25°C to 30°C) [16, 17].
4.0
However, there is disagreement about the mechanism of
2.0
microbial inactivation by the hydrogen peroxide vapor.
0.0
Some investigators hold the opinion that decontamination is
0 100 200 300 400 500 600 700
a dry vapor process and condensation should be avoided
Hydrogen peroxide injected during conditioning phase [g]
[14], while others state that only condensation induces the
400 ppm H2O2, HL1 400 ppm H2O2, HL2 sporicidal activity of the hydrogen peroxide vapor [15, 17].
600 ppm H2O2, HL1 600 ppm H2O2, HL2
To learn more about the basic relationship between
800 ppm H2O2, HL1 800 ppm H2O2, HL2
condensation and microbial inactivation, the condensa-
400 ppm H2O2, HL3 400 ppm H2O2, HL4
600 ppm H2O2, HL3 600 ppm H2O2, HL4
tion level was recorded for every cycle in this study.
800 ppm H2O2, HL3 800 ppm H2O2, HL4 Figure 8 illustrates the correlation between the micro-
Fig. 7 Amount of hydrogen peroxide injected into the decontamina-
condensation level and D value, while Fig. 9 exhibits the
tion chamber during conditioning phase plotted against the average D relationship between the hydrogen peroxide concentration
value and humidity. The asterisks in each plot represent
8. 130 J Pharm Innov (2008) 3:123–133
7.0
Microcondensation [µg/mm 2 ]
6.0
5.0
4.0
3.0
2.0
1.0
0.0
00:00 00:01 00:02 00:04 00:05 00:07
Bio-decontamination phase [hh:mm]
400 ppm H2O2, HL 1 400 ppm H2O2, HL 2
600 ppm H2O2, HL 1 600 ppm H2O2, HL 2
800 ppm H2O2, HL 1
400 ppm H2O2, HL 3 400 ppm H2O2, HL 4
600 ppm H2O2, HL 3 600 ppm H2O2, HL 4
Fig. 8 Average microcondensation measured during bio-decontami- 800 ppm H2O2, HL 3 800 ppm H2O2, HL 4
nation phase plotted against average hydrogen peroxide concentration Fig. 10 Microcondensation measurement during bio-decontamination
during the first 15 min of bio-decontamination and humidity level phase for cycles with different combinations of water and hydrogen
(linear interpolation) peroxide concentrations in the isolator atmosphere
individual data points in the three-dimensional coordinate bio-decontamination phase for all test cycles. As expected, the
system. A linear interpolation is displayed by the colored lowest condensation level was found for the cycle with
traces. It was found that microcondensation occurred at all 400 ppm H2O2 and HL 1 and the highest for 800 ppm H2O2
tested humidity and hydrogen peroxide levels. The and HL 4. Within each set of cycles with the same hydrogen
condensation sensor detected condensation amounts con- peroxide concentration, condensation increases with rising
siderably beneath the range where fogging becomes HL. Similarly, for the same HL, the condensation grows with
visible. Condensation was reproducibly found to become increasing hydrogen peroxide concentration.
visible at about 2.9 g/mm2 for the given ambient In Fig. 12, the condensation during the bio-decontamina-
conditions. tion was averaged for every set of cycles and plotted against
Condensation during the bio-decontamination phase of the average D value, providing another way to evaluate the
the test cycles, as detected by the dew sensor, is shown in impact of condensation on the microbial inactivation. The
Fig. 10. The amount of condensate deposited on the diagram indicates that a low amount of microcondensation
surfaces during the various cycles remained stable during results in a noticeable decrease in the microbial inactivation
the bio-decontamination phase when the BIs were exposed rate. This is demonstrated, most obviously, by the cycle with
for the determination of D values. The bar chart in Fig. 11 400 ppm H2O2 and HL 1. The extremely low humidity
shows that the microcondensation levels averaged over the (1 µg/mm2 average microcondensation) during this cycle
results in a very low inactivation of the test organisms. An
increase in the microcondensation level from 1 to 2 g/mm2
Microcondensation [µg/mm 2]
6.0
5.0
4.0
3.0
2.0
1.0
0.0
Humidity Humidity Humidity Humidity
level 1 level 2 level 3 level 4
400 ppm H2O2 600 ppm H2O2 800 ppm H2O2
Fig. 9 Average D value plotted against average hydrogen peroxide Fig. 11 Comparison of average condensation during bio-decontami-
concentration and microcondensation during the first 15 min of bio- nation for cycles with 400, 600, and 800 ppm H2O2 and humidity
decontamination phase (linear interpolation) levels 1 to 4 measured with the NIR probe
9. J Pharm Innov (2008) 3:123–133 131
6.0
are illustrated in Fig. 13 together with D values for
indicators sealed in TyvekTM derived from the same set of
Microcondensation [µg/mm2 ]
5.0
decontamination cycles.
4.0
As expected, the spores on the unsealed carriers were
3.0 inactivated faster than those sealed in TyvekTM, and a
higher HL resulted in a faster kill for all indicators.
2.0
TyvekTM hinders the diffusion of the vapor to the BIs. For
1.0 higher HLs, the D value difference between unsealed and
sealed indicators decreased from 0.8 (HL 1) to 0.2 min (HL
0.0
4). The influence of the TyvekTM barrier on the D value
0.0 2.0 4.0 6.0 8.0 10.0 12.0 14.0
appears to diminish with increased humidity and more
D-value [min]
significant condensation. Increasing humidity appears to
400 ppm H2O2, HL1 400 ppm H2O2, HL2 promote the penetration of the TyvekTM barrier.
600 ppm H2O2, HL1 600 ppm H2O2, HL2
800 ppm H2O2, HL1 800 ppm H2O2, HL2
Spore Survivor Curves (MPN Method)
400 ppm H2O2, HL3 400 ppm H2O2, HL4
600 ppm H2O2, HL3 600 ppm H2O2, HL4
Decontamination cycles at 400 and 600 ppm H2O2 were
800 ppm H2O2, HL3 800 ppm H2O2, HL4
studied further to evaluate inactivation kinetics. The cycles
Fig. 12 Average microcondensation during first 15 min of bio- with 800 ppm hydrogen peroxide were omitted from this
decontamination phase plotted against average D value
part of the study because a preliminary experiment showed
rapid kill and no significant differences between the
inactivation curves of the four HLs.
reduces the D value dramatically from 14.6 (400 ppm H2O2, The number of spores surviving after predefined expo-
HL 1) to 3.9 min (400 ppm H2O2, HL 2). sure intervals was quantified by MPN procedures. For each
Figure 12 also demonstrates that, at similar H2O2 levels, condition, three consecutive decontamination runs were
higher water concentration and increased microcondensa- performed. The mean value of surviving spores from the
tion promote enhanced microbial inactivation. Beyond three enumerations was plotted in Fig. 14 versus the
microcondensation levels of 2.9 g/mm2, however, further respective exposure time, and the y-axis error bars represent
condensation does not improve inactivation. Another the standard deviation. In case no growth occurred in all
important finding that supports the results of Watling [18] test tubes of a dilution series, the resulting number of
is that visible condensation is apparently not necessary to surviving spores in the original sample according to the
achieve good sporicidal conditions. Subvisible microcon- applied MPN table [27] was three viable microorganisms.
densation is effectual for short inactivation times. This lower limit of detection for the MPN method is drawn
It is known that hydrogen peroxide, particularly in the as a horizontal line in the charts of Fig. 14. Data points for
liquid phase, can cause corrosion of construction materials. which no growth occurred in the experiment were plotted
In addition, the aeration phase can be prolonged and on the limit of detection line in the diagram.
problems with irregular decontamination can arise when
dripping condensation occurs in the system [14]. Strong
condensation with the formation of visible droplets during 3.0
decontamination is therefore undesirable and should be 2.5
prevented. The experiments conducted in this study showed
D-value [min]
2.0
that microcondensation is part of the sporicidal cycle with
vaporous hydrogen peroxide and that some condensation is 1.5
required for an efficient kill. Therefore, it is reasonable to 1.0
develop decontamination cycles with the required amount 0.5
of condensation needed to achieve quick microbial inacti-
0.0
vation but not sufficient to allow excessive condensation
Humidity Humidity Humidity Humidity
that can result in material and aeration problems. level 1 level 2 level 3 level 4
Humidity level
D Value Studies with BIs Sealed in TyvekTM and Unsealed
BIs wrapped in Tyvek unwrapped BIs
D values were determined for unsealed BIs exposed to HLs Fig. 13 D values for biological indicators with and without a
1 to 4 for the 600-ppm hydrogen peroxide level. The results TyvekTM envelope at 600 ppm H2O2
10. 132 J Pharm Innov (2008) 3:123–133
1.00E+08 1.00E+08
Log surviving spores
Log surviving spores
1.00E+07 1.00E+07
1.00E+06 1.00E+06
1.00E+05 1.00E+05
1.00E+04 1.00E+04
1.00E+03 1.00E+03
1.00E+02
1.00E+02
1.00E+01
1.00E+01
1.00E+00 1.00E+00
0 5 10 15 20 0 5 10 15 20
Exposure time [min] Exposure time [min]
600 ppm H2O2, HL1 400 ppm H2O2, HL1 600 ppm H2O2, HL2 400 ppm H2O2, HL2
MPN limit of detection MPN limit of detection
1.00E+08 1.00E+08
Log surviving spores
Log surviving spores
1.00E+07 1.00E+07
1.00E+06 1.00E+06
1.00E+05 1.00E+05
1.00E+04 1.00E+04
1.00E+03 1.00E+03
1.00E+02 1.00E+02
1.00E+01 1.00E+01
1.00E+00 1.00E+00
0 5 10 15 20 0 5 10 15 20
Exposure time [min] Exposure time [min]
600 ppm H2O2, HL3 400 ppm H2O2, HL3 600 ppm H2O2, HL4 400 ppm H2O2, HL4
MPN limit of detection MPN limit of detection
Fig. 14 Inactivation kinetics for humidity levels 1 to 4 for 400 and 600 ppm hydrogen peroxide (limit of detection=3.00E+00 spores)
The initial spore population on the inoculated discs condition, the slopes of all inactivation curves are very
presented in Fig. 14 was found to be slightly higher with the similar, indicating that decontamination follows similar
MPN method than the 2.4×106 cfu per carrier, which was kinetics at various humidity levels. In contrast, the inactiva-
certified by the manufacturer of the BIs and verified tion rates for 400 ppm H2O2 varies with HL. The plot
according to USP [20]. The maximum value detected by the indicates that the 600-ppm H2O2 atmospheres provide nearly
MPN procedure was 1.9×107, and the average value was decontamination rates, whereas the 400-ppm conditions show
8.3×106 cfu per carrier. This indicates that the MPN a lag phase and distinctive tailing, especially for HLs 1 and 2.
procedure tends to overestimate the number of microorgan- This correlates with the data in Figs. 10 and 12, which show a
isms. The finding corresponds to several articles that report a clearly lower microcondensation level for these two atmos-
built-in positive bias of the MPN method [28, 29]. Neverthe- pheres than for the other test atmospheres. The water and
less, the overall results of the spore survivor curves provide hydrogen peroxide vapor would appear to be inadequate to
valuable information concerning the inactivation pattern for assure sufficient sterilant deposition on the surfaces. This
the various sporicidal atmospheres, and the conclusions finding indicates that the deposition of water and hydrogen
derived from the end-point D value data are confirmed. peroxide on the surface is primarily responsible for the
Figure 14 shows that the kill proceeds faster for microbial inactivation, whereas the hydrogen peroxide vapor
atmospheres with a higher peroxide concentration (600 ppm concentration is of secondary significance. During cycle
compared to 400 ppm H2O2) and that an increased HL results development, it is common practice to extrapolate the cycle
in a faster inactivation of the spores. The differences between time needed to achieve a complete kill from the determined D
the HLs are more distinct for the 400-ppm H2O2 cycles as values. From the calculated time needed for a one log
compared to the 600-ppm cycles. The inactivation rates of reduction, the time needed for a 6 log reduction is
the cycles with 600 ppm H2O2, HL 1 and 400 ppm H2O2, extrapolated. The results of the MPN survey, shown in
HL 4 demonstrate that a lower hydrogen peroxide concen- Fig. 14, imply that, for a nonlinear inactivation curve, such an
tration can be compensated by a higher humidity. extrapolation might not be acceptable. It should, therefore,
Additional information is gained from the slope of the first be demonstrated that the test organisms show a linear
inactivation curves shown in Fig. 14. For the 600-ppm H2O2 inactivation behavior under the given conditions.
11. J Pharm Innov (2008) 3:123–133 133
Conclusions 10. US Pharmacopoeia. General information. Biological indicators for
sterilization (Chapter 1035). In: US Pharmacopoeia (USP) 27,
United States Pharmacopoeial; 2003, p. 2413–2416.
From the results presented in this investigation, it can be 11. Unger B, et al. Suitability of different construction materials for
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