Safe Handling of Cresols, Xylenols & Cresylic Acids

Introduction

Cresols, xylenols and cresylic acids are hazardous substances and dangerous both to people and the environment if handled improperly. Cresols, xylenols and cresylic acid products produced by Sasol Chemicals (USA) LLC are highly versatile materials and are used as intermediates in the manufacture of a wide variety of industrial products such as resins, flame retardants, antioxidants, and coatings. In these and other applications, cresylic acids can be stored, transferred, processed and disposed of safely when proper procedures and safeguards are used. 

“Cresol” refers to any of the three isomers of methylphenol (C7H8O) or combinations thereof. “Cresols” commonly refer to a mixture which is predominantly methylphenol but may also contain lesser amounts of other alkylphenols. “Xylenol” is a common name for any of the six isomers of dimethylphenol (C8H10O) or their various combinations. Material which is predominantly dimethylphenol but which also contains ethylphenols and other alkylphenols may be referred to as “Xylenols”. “Cresylic acid” is a generic term referring to various combinations of cresols, xylenols, phenol or other alkylphenols (ethylphenols, propylphenols, trimethylphenols, etc.). 

Purpose & Scope

The purpose of this document is to provide information gathered through Sasol’s long experience in the safe handling of cresylic acids. It focuses on basic and practical information about working safely with these substances. Additional references are provided and it is strongly recommended that these and others be consulted prior to working with cresylic acids. Please do not hesitate to contact your regional Sasol office if we can be of assistance in the safe storage, handling, processing and disposal of our products.

Hazards

Health Hazards

The primary dangers posed in handling cresylic acids are those resulting from physical exposure. Cresylic acids are highly corrosive and contact with exposed skin or mucous membranes causes severe burns. These burns progress from an initial whitening of the exposed skin to blackishbrown necroses within 24 hours after exposure. Cresylic acids also exhibit anesthetic properties. Therefore, victims frequently misjudge the extent of their exposure when the initial burning sensation rapidly subsides. This can result in prolonged contact, causing toxic effects in addition to the corrosive damage. 

Cresylic acids are readily absorbed through the skin and mucous membranes in liquid or vapor form and act as systemic toxins for which there is no established treatment. Relatively small areas of exposure (e.g. an arm or a hand) can allow sufficient absorption to cause severe poisoning. Progressive symptoms of such poisoning include headache, dizziness, ringing in the ears, nausea, vomiting, muscular twitching, mental confusion, loss of consciousness and, possibly, death from lethal paralysis of the central nervous system. Chronic exposure can lead to loss of appetite, vomiting, nervous disorders, headaches, dizziness, fainting and dermatitis. 

The Occupational Health & Safety Administration (OSHA) has established 5ppm or 22 mg/m3 permissible exposure limits (PEL’s) for cresols on an 8-hour time-weighted average basis. OSHA guidelines also indicate that adequate personal protective equipment (PPE) should be employed to avoid skin contact with cresols. Cresylic acids are not listed as carcinogens by OSHA, the International Agency for Research on Cancer (IARC) or the National Toxicology Program (NTP).

Environmental Hazards

Cresylic acids show high acute toxicity towards both fish and aquatic invertebrates and must be prevented from entering surface or ground waters. Depending upon the specific composition, the material may be classified as a marine pollutant. Please refer to the current label and safety datasheet.

Controls for Working with Cresols

Safe storage, handling, processing and disposal of cresylic acids begin long before they ever arrive on-site. Measures necessary to ensure the health and well-being of employees, customers, the community and the  environment include the development of effective administrative and engineering controls designed to specifically address the hazards associated with cresylic acids. Personal protective equipment (PPE) is integral to safe handling and should be viewed as the last line of defense against an accidental failure of the administrative and/or engineering controls. 

Administrative Controls

Administrative controls are the foundation of any program designed for safely handling cresylic acids. Every company is unique in how they run their business and establish administrative controls. Those specifically developed for working with cresylic acids should address comprehensive process planning, thorough communication of hazards to employees and extensive training of employees on the proper implementation of all safety measures.

Personal Protective Equipment (PPE)

All personnel who work with or near cresylic acids must use adequate personal protective equipment (PPE). The extent of the potential exposure and consideration of established permissible exposure limits (PEL’s) should dictate the level of protection necessary. Personnel working with or near lab-scale quantities should always wear safety glasses with side-shields or

chemical mono-goggles, chemical-resistant or impermeable gloves, long-sleeved shirts and trousers as a minimum.

Circumstances such as elevated temperature and pressure or vacuum conditions should dictate if more substantial protection is necessary, including face shields, chemically impermeable outerwear, and breathing protection. Personnel transferring larger quantities of cresylic acids, or working in areas where a line-break could result in similar exposure, should always wear full protective equipment.

Emergency Procedures

Physical Exposure – External

The primary dangers involved in working with cresylic acids are the corrosive and toxic effects resulting from a physical exposure. Studies suggest that the severity of the exposure depends more on the magnitude of the exposed skin area than the concentration of cresylic acid. Therefore, the critical factor in dealing with an external physical exposure to cresylic acids is to minimize the extent and duration of the contact. To this end, the immediate response must be thorough flushing of the exposed areas with copious amounts of running water to remove all the cresylic acid in contact with the skin or eyes. Any contaminated clothing should be removed as quickly and carefully as possible during this process to avoid any additional skin contact.

Any exposed areas will have readily absorbed the cresylic acids and may be evidenced by a characteristic whitening of the skin. After thorough flushing with water, a solution consisting of 2 parts polyethylene glycol 400 to 1 part ethanol (PEG/EtOH) should be liberally applied to any affected skin (avoid contact with eyes), allowed to remain 15 to 30 seconds and then flushed away with fresh running water. Continue the cycling of PEG/EtOH and water for at least 15 minutes and then finish with thorough washing with soap and water. This decontamination procedure reduces the severity of the exposure, but does not completely eliminate damage to the skin or toxic effects. Medical attention should be sought as soon as possible.

Spill Containment & Clean-Up

Spill containment and cleanup of cresylic acids should only be performed by properly trained personnel employing an appropriate level of protective equipment as dictated by the extent of the spill. Small to medium spills on land should be surrounded by and absorbed onto inert clay absorbent and transferred to a disposal container. Larger land-spills should be diverted away from waterways, contained with booms, dikes or trenches, and collected in a vacuum truck. Any residual cresylic acids remaining after vacuuming should be cleaned up using the clay absorbent. All soils affected by the spill should be removed and placed in approved disposal containers.

Water spills are of particular concern due to the acute toxicity of cresylic acids to marine life. Clean up efforts should focus on containing the spill and quickly removing the cresylic acids that settle in deeper areas of the waterway. This can be aided greatly if the flow of water can be slowed or stopped. Further efforts should focus on removing as much of the dissolved cresylic acids as possible from the water using activated charcoal.

The composition and extent of any spill should be evaluated against local guidelines (ex. SARA Title III and RCRA in the U.S.) and reported to the proper agencies, if necessary. Any non disposable clean-up equipment should be thoroughly decontaminated with soap and water after use.

Source : SASOL / USA

Safe Handling of Cresols, Xylenols & Cresylic Acids

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Some significant points to note about Cresylic Acid

Below is a photo taken 10 years ago in the Irish Army Air Corps NDT shop,  part of the Avionics / ERF building complex. Ardrox 666 can be seen spilled on the ground where it was free to leach through a shore onto the grass verge outside. 

  • 25% of fresh Ardrox 666 used by the Air Corps was Cresylic Acid. This percentage was higher in waste Ardrox 666 as Dichloromethane evaporated.
  • That greenish / yellow stain dripping from the extractor fan is also Ardrox 666 from the air.

DELAY – DENY – DIE

What are Isocyanates?

What are Isocyanates?

An isocyanate is any chemical that contains at least one isocyanate group in its structure. An isocyanate group is a group of atoms containing one nitrogen atom attached by a double covalent bond to one carbon atom, which in turn is attached by a second double bond to an oxygen atom (indicated in structure as -N=C=O). (Do not confuse this with the cyanate functional group which is arranged as –O–C≡N). A chemical containing two such isocyanate groups is called a diisocyanate. Common examples are toluene diisocyanate (TDI), hexamethylene diisocyanate (HDI) and methylene diphenylmethane diisocyanate (MDI).

Isocyanates (a description which includes diisocyanates) are the raw materials that make up all polyurethane products. Isocyanates react with compounds containing alcohols to produce polyurethane polymers – which are used in polyurethane foams, thermoplastic elastomers and “2 pack” type polyurethane paints to improve the performance, durability and finish of painted surfaces. Jobs that may involve exposure to isocyanates include painting with polyurethane products, foam-blowing and the manufacture of polyurethane products like insulation materials, surface coatings, furniture, foam mattresses, under-carpet padding, packaging materials, laminated fabrics, polyurethane rubber, adhesives and also exposure can occur during the thermal degradation of polyurethane products.

Health Effects

Exposure to hazardous materials may be acute or chronic. Acute exposures refer to single high concentration exposures over shorter periods, while chronic exposures are repeated or continuous exposures over longer periods. Exposures to any toxic material may have either acute, immediate effects and/or chronic, long term health effects.

Inhalation:

Isocyanates are known to have a strong effect on the respiratory tract in some people. It is reported that there is a susceptible group in the population (estimated to be 5-20% of workers who are exposed occupationally) who can become sensitised to Isocyanates. Sensitization is the body’s hyper-reactive (allergy-like) response to a substance which has been touched or inhaled by a susceptible individual. Sensitization may develop as a result of a large single overexposure, for example, from a spill or accident, or from repeated overexposure at lower levels.

Once sensitised, these people, when later exposed to even very low concentrations of isocyanates even at levels below the exposure standard, can react by developing asthma-like symptoms, such as chest tightness, cough, wheezing and shortness of breath. Such attacks may occur up to several hours after cessation of exposure (for example, during the night after exposure) but, if a person is particularly sensitive, the attack can occur earlier or immediately. This sensitisation is essentially irreversible and can prevent any further work for the individual in their job using Isocyanates or any position associated with use of Isocyanates – even at very low levels below the regulated exposure level and that may not affect others. Many spray painters working in smash repair shops have had to leave the industry because they are sensitised to isocyanates.

An individual’s response to isocyanate exposure can be immediate or may be delayed for several years. Asthmatic people are more prone to sensitisation and other adverse reactions. Persons with a history of asthma, allergies, hay fever, recurrent acute bronchitis or any occupational chest disease or impaired lung function is advised against risking exposure to isocyanates. In rare cases, death has occurred from a severe asthma attack after significant isocyanate exposure.

Skin

Isocyanates are also skin irritants (causing inflammation and dermatitis) and there is some evidence that skin exposure can also cause respiratory sensitisation.

Eyes

Isocyanates are an irritant to the eyes. Splashes can cause severe chemical conjunctivitis.

Other Health Effects

Other health effects which have been reported include liver and kidney dysfunction. Some Isocyanate materials are considered to be potential human carcinogens (IARC).

Spraying Isocyanate Paints

Spray painters need to understand the health risks involved in spraying polyurethane paints – these are the two-pack mixes of polyurethane paints and possibly also in the one-pack moisture-cured mixes. These products are widely used in the automotive and other industries because of their excellent gloss, hardness, adhesion and chemical resistance.

The major hazard with spraying polyurethane paints is breathing the mist or aerosol droplets of the paint spray and absorbing the isocyanate and other components into your lungs.

The odour threshold for isocyanates, i.e. the level at which an individual can smell an isocyanate, is typically higher than the allowed exposure limits. In other words, if a painter smells the sweet, fruity, pungent odour of an isocyanate, they are probably already overexposed. That is why the recommended respiratory protection for employees spraying isocyanates is a supplied air respirator and not an air purifying respirator (i.e. filter cartridge style). The issue with use of air purifying respirators is that they will reach a point at which the filter becomes saturated and will no longer capture the isocyanate or other solvents. When that filter breakthrough happens, an Isocyanates overexposure can occur, potentially causing an irreversible sensitization. Use of a supplied air system removes this filter change factor – it does not rely on the painter changing his gas/vapour filters at appropriate intervals.

Note: if isocyanate-containing paint is applied by brush, roller or dipping, in a well ventilated area, there is generally no more hazard than with ordinary paints. These application methods usually do not produce the higher concentrations of isocyanate vapour associated with spraying.

After curing, polyurethane paints contain no free isocyanates and are not hazardous under normal use. However, welding or burning of polyurethane coated surfaces can release a range of contaminants. Gases or vapours evolved can include HDI, TDI, MDI as well as many other compounds (metal fumes, organic gases or vapours, particulates), depending on the original polyisocyanate resin used. When welding or cutting metal coated with a polyurethane coating, a worker may be exposed to a range of these decomposition products which will vary depending on type of process being used to weld or cut, the nature of the base metal and type of coating. Respiratory protection that is suitable for welding applications will also provide suitable respiratory protection in these cases

Source 3M Australia / New Zealand

http://multimedia.3m.com/mws/media/777847O/isocyanates-3m-techupdate.pdf

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Some significant points to note from this 3M document.

  1. Exposure can occur when cured isocyanates are heated.
  2. An individual’s response to isocyanate exposure can be immediate or may be DELAYED FOR SEVERAL YEARS.
  3. Skin exposure can also cause respiratory sensitisation.
  4. The odour threshold for isocyanates, i.e. the level at which an individual can smell an isocyanate, is typically higher than the allowed exposure limits.
  5. The Air Corps did eventually provide a “supplied air” respirator to spray paint & welding personnel. Unfortunately they sourced the “supplied air” from an old machine compressor located in ERF where the air had previously tested as 3.5 times over the allowed limit for Dichloromethane i.e. allowed limit was 50ppm and sourced air was from a location measured at 175ppm…out of the frying pan and into the fire.

Air Corps Isocyanate Usage

Isocyanates were used by the Spray Paint Shop (Dope Shop) at Baldonnel. For most of the existence of this shop personnel were NOT supplied with ANY PPE. The walls between the Spray Paint Shop and Engineering Wing Hangar & Workshops were not sealed and so isocyanates and other chemicals entered these workplaces whilst spraying was in progress exposing all personnel.

Furthermore if a component could not be removed from an aircraft for spray painting it was spray painted in-situ in Engineering Wing Hangar whilst unprotected line & tech personnel worked in adjoining offices & workshops or on other aircraft in the hangar.

A “waterfall” system with an extractor fan was also present. Personnel spray painted aircraft components toward the waterfall which captured most of the over-spray droplets. Fumes from this waterfall were then extracted by a fan, up a duct and released at approximately 3m height where the prevailing winds then carried the extracted fumes in the doors & windows of Avionics Squadron & Engine Repair Flight exposing further unprotected personnel.

Sensitisation is irreversible and once sensitised it is next to impossible to avoid isocyanates in the modern environment. It is also likely that health effects are suffered beyond the respiratory system & skin for example the gastric & nervous systems. 

DELAY – DENY – DIE

Individual chemical constituents of Aviation Gasoline (AVGAS) & Jet Fuel (AVTUR)

We have just added links to Safety Data Sheets which show the constituent chemicals for AVGAS (100LL) as well as AVTUR (Jet A-1) on our Chemical Product Names & Safety Data Sheets page.

AVGAS - 100LL

Chemical NameCAS-NoClassification
Gasoline86290-81-5 Muta. 1B
Carc. 1B
Asp. Tox. 1
Tetraethyl lead 78-00-2 Acute Tox. 1
Repr. 1A
STOT RE 2
Toluene108-88-3Skin Irrit. 2
Repr. 2
STOT Single Exp. 3
STOT Rep. Exp. 2
Asp. Tox. 1
Xylene, mixed isomers1330-20-7
Acute Tox. 4 - Dermal
Acute Tox. 4 - Inhalation
Skin Irrit. 2
Ethylbenzene100-41-4Acute Tox. 4 - Inhalation
STOT Rep. Exp. 2
Asp. Tox. 1
Cyclohexane110-82-7
Skin Irrit. 2
STOT Single Exp. 3
Asp. Tox. 1
n-Hexane110-54-3Skin Irrit. 2
Repr. 2
STOT Single Exp. 3
STOT Rep. Exp. 2
Asp. Tox. 1
Trimethylbenzene, all
isomers
Trimethylbenzene, all
isomers
Skin Irrit. 2
Eye Irrit. 2B
STOT Single Exp. 3
STOT Rep. Exp. 1
Asp. Tox. 1
Naphthalene91-20-3
Acute Tox. 4 - Oral
Carc. 2
Cumene (Isopropylbenzene)98-82-8STOT Single Exp. 3
Asp. Tox. 1

 

AVTUR - Jet A1

Chemical NameCAS-NoClassification
Kerosine (petroleum) 8008-20-6 Asp. Tox.1
Skin Irrit.2
STOT RE3
Kerosine (petroleum),
hydrodesulfurized
64742-81-0
Asp. Tox.1
Skin Irrit.2
STOT RE3
Kerosene (Fischer
Tropsch), Full range,
C8-C16 branched and
linear
848301-66-6 Asp. Tox.1
Ethylbenzene100-41-4Acute Tox. 4 - Inhalation
STOT Rep. Exp. 2
Asp. Tox. 1
Xylene, mixed isomers1330-20-7

Acute Tox. 4 - Dermal
Acute Tox. 4 - Inhalation
Skin Irrit. 2
Cumene (Isopropylbenzene)98-82-8STOT Single Exp. 3
Asp. Tox. 1
*****
On the 26th of January 2016 the current head of Health & Safety in the Irish Army Air Corps stated in an email to the Medical Corps that “The Formation Safety & Unit Safety Personnel have reviewed refuelling work practices and believe that the risk of exposure is low.”

Defence admit another 12 sites “contaminated by toxic chemicals”

The Australian Defence Force has admitted its problem with toxic chemicals leaking from its bases is much bigger than first thought.

Another 12 ADF sites have been added to the original six investigated, causing more worry for the personnel who work there as well as the locals living nearby.

Defence Force widow Kristen Russell remembers the moment her partner Greg Lukes was diagnosed with kidney cancer at just 33 years old. Two years later, the father of two young children was dead.

“He was one of those people that went to the gym everyday, ate all the right things, never smoked, never drank. It was a shock that somebody like him could get that type of cancer,” Mrs Russell told 7 News.

Petty Officer Lukes served at HMAS Albatross in Nowra, working on Sea King helicopters. The ADF believes exposure to a number of chemicals related to the choppers was the likely cause of his deadly disease.

There is now further concern about chemicals known as preflourinated compounds used in firefighting foams at that base, among many others.

Petty Officer Luke’s widow has called on the ADF to “release the truth. If it’s happened, it’s happened. Let’s get it out there and move forward,” she said.

The ADF has already launched detailed investigations into six sites including HMAS Albatross.

On Tuesday it released a report revealing chemicals were found in the soil or ground water at another 12 bases. The sites include three in NSW, two in Queensland, two in Victoria, one in Western Australia and three in the NT. Lawyers are already preparing for class actions.

Read read article & watch related video by following link below.

Report on the Molecular Investigations into the Jet Fuel and solvent exposure in the DeSeal/ReSeal programme conducted at the Mater Research Institute (UQ), Brisbane.

Executive Summary

Overview

The main objective of this project was to investigate the toxicity of JP-8 fuel and the solvents used in the Deseal/Reseal programme using a systems biology approach. In the exposure environment (fuel tanks, aircraft hangers etc), workers were typically exposed either by inhalation of vapours or by absorption through the skin. There were occasionally reports of direct ingestion through the mouth. Health studies of exposed workers and other research reports show premature death for some individuals, an increased risk of unusual malignancies in internal organs such as small bowel, erectile dysfunction, and behavioural disturbances. These findings may manifest years after exposure suggesting changes to the cells and tissues not directly exposed to the fuel and solvents. Changes to the systems biology was investigated by proteomic and genomic studies.

Laboratory cell studies of DeSeal/ReSeal compounds

Development of Cell exposure model

Previous methods for studying cellular responses to JP8 and solvents involved direct addition of these compounds to cells in laboratory growth plates using other solvents such as Ethanol. These methods were considered to be inadequate because they did not recognise the role of circulating blood plasma in distributing these compounds to internal organs. The JFES project team developed a method of studying cells by exposing them to blood plasma, which they believe is a better model of the inhalation and skin exposure routes for distributing solvents to internal organs. This method has been published in a peer reviewed journal. (See Appendix 1)

Distribution of JP8 and DeSeal/ReSeal solvents

The studies of plasma exposed to JP8 and solvents showed that the compounds are not distributed by plasma in the same proportions as found in the fuel and solvent mixtures. This means that higher levels of some compounds are actually presented to cells and organs than those proportions in the fuel solvent mixtures. The study showed that the majority of the compounds are distributed by binding to plasma lipids rather than simply dissolved in the plasma water. This raises the possibility that individuals with higher bloods lipids may distribute more of the compounds to internal organs.

The effects of the JP8 and solvents on cells

The study then tested the effects of the JP8 and solvents on cells. The JP8
and solvents were tested as a mixture and individually. The key findings
were:-

  • Plasma exposed to JP8 alone is directly toxic to cells
  • Plasma exposed to a mixture of JP8 combined with solvents has greater
    toxicity to cells with 40% cells showing changes before 4 hours, and 90%
    cells affected at 12 hours.

The following individual components were found to have the highest cellular toxicity:-

  • Kerosene
  • Benzene and butylbenzene
  • All Alkanes including iso-octane, decane, dodecane, tetradecane and
    hexadecane
  • Diegme
  • N, N Dimethyl acetimide
  • Naptha
  • Thiophenol

The solvents used in the Deseal/Reseal programme demonstrated either low cell toxicity or manifest toxicity to a lesser extent than the JP8 fuel components.

Effects on gene expression

Gene expression in cells was altered following exposure. Changes greater then 5 fold were considered significant. The genes altered are shown in table (3). The function of these genes involved mostly cell survival/death, metabolism, cell cycle, DNA maintenance (housekeeping), and cell regulation. These genes have been implicated in pathological processes including cancer, neurodegeneration, and immune suppression.

Effects on proteins

Cellular proteins were altered after exposure. The changes to cellular proteins reflected the changes in gene expression involving cell survival/death, metabolism, cell division, and roles in cellular gene transcription/translation.

Cell Death

Cell death occurred by two mechanisms. A number of cells appeared more vulnerable with death occurring by disruption of cellular membranes and by lysis (bursting) of the cells. The more common mechanism of cell death was by apoptosis, which is a programmed response of cells to injury. Not all injured cells undergo complete apoptosis indicating persistence of injured cells. This may suggest a survival of injured cells with malignant potential. The cell culture methods could not determine the long term effects.

Study of exposed workers

The study of exposed workers showed differences from the matched control group in health indices, and in some genomic studies. The changes were not as significant as those seen in the acute cell exposure model in the laboratory.

Rating of exposure

Because of the unavailability of accurate exposure data (degree and duration), a problem also encountered in other studies, the workers were classified into 3 groups.

  1. Definite high exposure who worked inside the fuel tanks
  2. Significant contact such as by dosing of skin or accidental ingestion
  3. Minimal contact in the general area such as collection of rags or
    cleaning of the area.
Health Assessment Scores

The Health assessment scores showed exposed workers to have a lower health rating than controls. There did not appear to be a decrease in the health scores (dose response) related to the degree of exposure. Workers with mild exposure had the same decrease in their health scores as those with high exposure. This suggests that other factors beyond the Deseal/ Reseal contact have decreased the health scores.

Genetic studies of blood cells from exposed workers

All studies were undertaken on plasma and white blood cells as these were
the only tissues for which it was possible to obtain samples. The genetic studies of blood cells examined two types of changes in gene expression, the presence of chromosomal changes, and for appearance of mutations in
the mitochondrial DNA. There were no chromosomal changes detected at a
level of 50Kb using a high resolution SNP ARRAY.

There were no changes in the mitochondrial DNA mutation load between exposed workers and age matched controls (Mitochondrial DNA changes can accumulate with age).

There were no changes in the amount or type of protein coding mRNA expression, which is an index of cell activity. In disease states , these are usually tissue specific and may not appear in blood cells unless they are directly involved in the disease process.

There were small but significant and consistent changes in the expression of regulatory microRNAs that control activity of other genes. The regulatory functions of the altered genes have been linked to neurological changes and neurodegenerative disorders. It must be emphasised that interpretation of the function of regulatory genes is an evolving science with much uncertainty at present. The regulatory genes, which compose 98% of our genome, have a major role in human development, adaptation and response to disease. The function is only known for ~40% of these at present. Disease causing associations, with some early exceptions, are still unmapped.

Protein studies of plasma and blood cells

No significant changes were seen in the levels and types of protein expressed in the plasma and blood cells of exposed workers. A few small changes were seen consistently, but these did not reach a level that the researchers considered significant.

Discussion and Conclusions

Confounders and sensitivity
Dose response not detected

A dose response would have been expected but was not observed in the workers with different exposure histories. The unexpected similarity in the health scores and genomic studies within the exposed groups (low, medium, high) raises several hypotheses:-

Confounders

There are other factors independent of Deseal/Reseal exposure which could produce the changes seen. Confounders could include:-

  • An ascertainment bias whereby only those workers affected by any exposure volunteered to participate in the study.
  • An ascertainment bias whereby only those workers NOT affected by the exposure (i.e. Survivors) volunteered to participate in the study.
  • The workers were stratified by their exposure to Deseal/Reseal materials. The effects seen may NOT be due to the Deseal/Reseal materials but to some other experience of the workers. The cellular studies suggest that exposure to fuel alone could be responsible.
  • It was not possible to examine other possible shared confounding events in the work careers or in the lifestyle of the personnel. (e.g. other occupational exposure not related to Deseal/Reseal such as medications, substance abuse, nutrition)
  • This study was conducted on individuals between 10 and 30 years after their exposure. If significant changes occurred at the time of exposure, normal cellular repair and selection mechanisms may have lessened the biological signal that could be observed in this study. The small but consistent changes observed suggest this possibility. Either the effect at the time was minimal but has persisted, or the effect was larger but has diminished over-time.
  • The cellular studies show that the compounds are mostly distributed by plasma lipids. The exposure to organs within the body would likely depend on the concentration of plasma lipids at the time of fuel exposure. Plasma lipids vary genetically between individuals, with lifestyle and alcohol intake, with composition of their diet, as well as the time after meals when the exposure occurred. The lack of a dose effect could be explained if workers in the lower exposure group had higher plasma lipids at the time of exposure. Individuals in the high exposure group worked within the fuel tanks and were selected because they were leaner and smaller, possibly protected to some extent by lower plasma lipids.

Significance of findings

The cellular findings, supported by other recently published genomic studies, indicate a definite toxicity from JP8 to exposed cells. The components of JP8 tested are commonly found in most (aviation) fuels. The results indicate that there is a need for concern about exposure to fuels in general. The study was not designed to determine the degree of occupational exposure necessary to produce cellular changes. However, the results show that cells grown in a nutrient containing as little as 5% exposed plasma are affected. In the body, blood cells have 100% exposure to plasma while other organs will have less exposure depending on the net blood flow and cellular membrane barriers. Organs such as brain, liver and bowel have very high blood flow. Cellular membranes generally have greater permeability to substances dissolved in lipids.

The study was also not designed to determine the most toxic routes of exposure (inhalation, ingestion, skin contact), but did demonstrate that fuel components can be distributed to organs through blood plasma, i.e. organs such as brain or liver, not directly exposed in the contact, may undergo secondary exposure. The implication is that all body systems must be considered in assessing/monitoring the health of exposed workers.

While the changes seen many years after exposure were small, they were consistent. The changes are most apparent in gene regulation and had some association to the health problems (e.g., malignancy) identified in other studies.

There were no chromosomal changes or mutations linked to the exposure. The genes changes seen can be described as Epigenetic, which is a mechanism of cellular adaptation to some environmental influence. Epigenetic changes are less clearly linked (at the present knowledge) to disease. Epigenetic changes occur through a variety of cellular mechanisms and these were not investigated in this study. Some epigenetic changes can be transferred down through successive generations but currently have not been shown to cause birth defects or mutation in off-spring.

Recommendations

The cell results show a definite cellular toxicity from JP8 fuel. The components of the fuel exhibiting toxicity are common to most fuels. Consideration should be given to further studies of workers exposed to fuel of any type.

Newer genomic and bioinformatic technologies have been developed during the time of this study and have been employed in other studies of occupational fuel exposure. These technologies can be applied to other exposure risks (including PTSD) in defence (veteran) health risk assessment. An expert committee should be constituted to advise on research and clinical application of these technologies.

Plasma free DNA sequencing can now be used to assess (from blood samples), the cellular death associated with tumours, transplant rejection, miscarriage and infections. Targeted RNA expression studies can reveal immediate changes in gene activity following fuel exposure. A study of workers with recent or past fuel exposure is recommended.

The best time to study cellular changes would be immediately after direct exposure. A protocol should be established for assessment of an exposed individual to include sample collection immediately after the exposure for quantification of plasma lipids, plasma fuel components, free DNA sequencing, and targeted RNA expression.

Exposed veterans should be reassured that while small and consistent changes were observed in this study, there were no changes detected known to have immediate or severe health consequences. The changes support the findings from other studies that there is a possible increased risk of developing health problems. As the changes observed are in gene regulation, it is also possible that healthy lifestyle changes may ameliorate the risk.

31st JULY 2014

Download the full report on the Royal Australian Air Force website below.

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Difference between Jet A1 & JP8

Jet fuel, aviation turbine fuel (ATF), or avtur, is a type of aviation fuel designed for use in aircraft powered by gas-turbine engines. It is colorless to straw-colored in appearance. The most commonly used fuels for commercial aviation are Jet A and Jet A-1, which are produced to a standardized international specification. The only other jet fuel commonly used in civilian turbine-engine powered aviation is Jet B, which is used for its enhanced cold-weather performance.

Jet fuel is a mixture of a large number of different hydrocarbons. The range of their sizes (molecular weights or carbon numbers) is defined by the requirements for the product, such as the freezing or smoke point. Kerosene-type jet fuel (including Jet A and Jet A-1) has a carbon number distribution between about 8 and 16 (carbon atoms per molecule); wide-cut or naphtha-type jet fuel (including Jet B), between about 5 and 15.[1]

Additives

The DEF STAN 91-91 (UK) and ASTM D1655 (international) specifications allow for certain additives to be added to jet fuel, including:[13][14]

  • Antioxidants to prevent gumming, usually based on alkylated phenols, e.g., AO-30, AO-31, or AO-37;
  • Antistatic agents, to dissipate static electricity and prevent sparking; Stadis 450, with dinonylnaphthylsulfonic acid (DINNSA) as a component, is an example
  • Corrosion inhibitors, e.g., DCI-4A used for civilian and military fuels, and DCI-6A used for military fuels;
  • Fuel system icing inhibitor (FSII) agents, e.g., Di-EGME; FSII is often mixed at the point-of-sale so that users with heated fuel lines do not have to pay the extra expense.
  • Biocides are to remediate microbial (i.e., bacterial and fungal) growth present in aircraft fuel systems. Currently, two biocides are approved for use by most aircraft and turbine engine original equipment manufacturers (OEMs); Kathon FP1.5 Microbiocide and Biobor JF.[15]
  • Metal deactivator can be added to remediate the deleterious effects of trace metals on the thermal stability of the fuel. The one allowable additive is N,N’-disalicylidene 1,2-propanediamine.

As the aviation industry’s jet kerosene demands have increased to more than 5% of all refined products derived from crude, it has been necessary for the refiner to optimize the yield of jet kerosene, a high value product, by varying process techniques. New processes have allowed flexibility in the choice of crudes, the use of coal tar sands as a source of molecules and the manufacture of synthetic blend stocks. Due to the number and severity of the processes used, it is often necessary and sometimes mandatory to use additives. These additives may, for example, prevent the formation of harmful chemical species or improve a property of a fuel to prevent further engine wear.

JP-8, or JP8 (for “Jet Propellant 8”) is a jet fuel, specified and used widely by the US military. It is specified by MIL-DTL-83133 and British Defence Standard 91-87, and similar to commercial aviation’s Jet A-1, but with the addition of corrosion inhibitor and anti-icing additives.

A kerosene-based fuel, JP-8 is projected to remain in use at least until 2025. It was first introduced at NATO bases in 1978. Its NATO code is F-34.

‘Coincidences’ hinder Air Corps whistleblowers’ case

A number of whistleblowers allege that a health and safety failure on the part of the Air Corps has caused their chronic illnesses. Joe Leogue looks at their case and how, just as with Garda Maurice McCabe, ‘coincidence after coincidence after coincidence’ has emerged to undermine their position.

“THERE are those who may say that this litany of grave errors can’t just simply be coincidence after coincidence after coincidence that is being suggested,” the senior counsel said.

The line was a standout contribution in a tribunal that made headlines in every news outlet this summer.

Senior counsel Pat Marrinan was talking about Garda Whistleblower Maurice McCabe — and how every one of a number of apparent ‘coincidences’ in his case worked to his detriment.

However, the line also resonated with whistleblowers involved in a different dispute.

A dispute that has found some at odds with the State. An ongoing scandal that has seen allegations of a cover-up, the alleged intimidation of those speaking out against the Defence Forces, and one that can be boiled down to one question: Are a number of men who served the State now seriously ill because of the Defence Forces’ failure to protect them from the effects of harmful chemicals?

Those speaking out do not believe the various occurrences — revealed in a series of articles in this newspaper since January — can be
coincidental.

The ongoing issue relating to chemical exposure in the Air Corps concerns two separate, yet related problems for the Defence Forces — the first of which was raised in 2013.

Back then, the first of a number of lawsuits against the State was filed in the High Court in which it was alleged that there were historic failures to protect technicians from the effects of the chemicals they used.

The second problem was revealed in November 2015, when the first of four whistleblowers within the Air Corps made protected disclosures to the then-defence minister Simon Coveney.

These men warned that the Air Corps was not doing enough to protect currently serving technicians from the harmful effects of the chemicals with which they clean and service the aircraft.

Their warnings would be vindicated following an independent investigation last year.

And yet the red flags should have been raised as far back as 2013, when the first of the lawsuits came — allegations that would be echoed years later by the protected disclosures.

Read more on the Irish Examiner below…

Air Corps official denies documents destroyed

An Air Corps official has rejected claims that inspection reports at the centre of legal cases against the State were deliberately destroyed, describing the allegations as malicious, writes Joe Leogue.

Air Corps tail wags ministerial dog.

The rebuke of the claims is contained in a series of emails between the Defence Forces and the Department of Defence, which has been seen by the Irish Examiner.

The State faces legal action from several former Air Corps technicians who claim the Defence Forces failed to adequately protect them from the harmful effects of the toxic chemicals they used on a daily basis.

Four whistleblowers have made protected disclosures on health and safety issues within the Air Corps — with two alleging that inspection reports show the Defence Forces were aware of safety shortcomings in the 1990s were deliberately destroyed as part of a cover-up.

However, Comdt Mark Donnelly, the Air Corps formation safety adviser, rejected these claims, and said the missing reports were “misplaced with the passage of time”.

“AC Formation and former Formation safety personnel have already commented on their concerns regarding these allegations,” Comdt Donnelly wrote in an email on March 8.

“These allegations of deliberate destruction of such documents are completely unfounded. It is my opinion that these comments are intended to be inflammatory, vexatious and malicious.”

Read more in the Irish Examiner

Developments in laboratory diagnostics for Isocyanate Asthma

Purpose of review

Isocyanates, reactive chemicals used to generate polyurethane, are a leading cause of occupational asthma worldwide. Workplace exposure is the best-recognized risk factor for disease development, but is challenging to monitor. Clinical diagnosis and differentiation of isocyanates as the cause of asthma can be difficult. The gold-standard test, specific inhalation challenge, is technically and economically demanding, and is thus only available in a few specialized centers in the world. With the increasing use of isocyanates, efficient laboratory tests for isocyanate asthma and exposure are urgently needed.

Recent findings

The review focuses on literature published in 2005 and 2006. Over 150 articles, identified by searching PubMed using keywords ‘diphenylmethane’, ‘toluene’ or ‘hexamethylene diisocyanate’, were screened for relevance to isocyanate asthma diagnostics. New advances in understanding isocyanate asthma pathogenesis are described, which help improve conventional radioallergosorbent and enzyme-linked immunosorbent assay approaches for measuring isocyanate-specific IgE and IgG. Newer immunoassays, based on cellular responses and discovery science readouts are also in development.

Summary

Contemporary laboratory tests that measure isocyanate-specific human IgE and IgG are of utility in diagnosing a subset of workers with isocyanate asthma, and may serve as a biomarker of exposure in a larger proportion of occupationally exposed workers.

***

Introduction

Diisocyanates (toluene diisocyanate, TDI; hexamethylene diisocyanate, HDI; and diphenylmethane diisocyanate, MDI) or functionally similar polymeric isocyanates are the obligate cross-linking agent for the commercial production of polyurethane, a polymer upon which modern society has become dependent. Millions of tons of isocyanate are produced and consumed annually throughout the world in a wide variety of end-use work environments [1,2–5,6•,7•]. Workplace exposure remains the best-recognized risk factor for isocyanate asthma, but is complicated to quantitate, involving mixtures of isomers and ‘prepolymers’ diluted in solvents, in aerosol and vapor phases. In certain occupational settings, exposure can cause isocyanate asthma and long-lasting bronchial hyperreactivity [1,8,9,10•,11•]. Early recognition of isocyanate asthma and prompt removal from isocyanate exposure improves the long-term prognosis for sensitive individuals [9]. There thus exists the need for practical screening/diagnostic tests for isocyanate asthma as well as tests that can monitor personal exposure.

The clinical presentation of isocyanate asthma is strikingly similar to common environmental asthma, prompting the hypothesis that the disease has an immunological basis, although subtle differences have been noted [9,10•,12•]. Animal models support this hypothesis, and are beginning to dissect the potential role of individual genes with transgenic strains [13••,14••,15,16••,17,18]. Allergists and immunologists have overcome substantial challenges working with reactive isocyanates to develop serology assays for isocyanate-specific antibodies [19–21]. Such assays have provided evidence to support allergic asthma to isocyanate in a small percentage of workers, but cannot detect isocyanate-specific IgE in the majority of sensitive individuals. These results have left great uncertainty in the field. Does isocyanate asthma involve mechanisms of pathogenesis (e.g. non-IgE) distinct from those in common atopic asthma or are specific IgE antibodies present, but our detection assay for them is flawed? Are we using the wrong antigenic form of isocyanate in our serology tests, or testing workers at the wrong time (after removal from exposure)? Does isocyanate asthma, as presently defined, possibly represent a spectrum of diseases, which only in some cases is associated with an antibody response [3,9,10•]?

The present review summarizes the rationale and use of clinical laboratory tests for immune responses that reflect isocyanate exposure and asthma, with emphasis on data generated within the past year. The potential utility of ‘isocyanate-specific’ serum IgE and IgG as biomarkers and the isocyanate antigen recognized by these immunoglobulins are described [22••,23]. Clinical usage and limits of contemporary assays for isocyanate asthma and exposure are discussed along with promising future assays [20,24,25••].

Read more on the US National Center for Biotechnology Information

https://www.ncbi.nlm.nih.gov/pmc/articles/PMC3131002/

***

The Irish Army Air Corps has dismissed a number of previously fit personnel as suffering from asthma. It has never carried out a health study of personnel exposed long term and without protection to Isocyanates and has never carried out adequate risk specific health surveillance. Neither has the Air Corps ever carried out risk specific health surveillance for personnel who suffered long term exposure to jet fuel & jet exhaust gasses. 

Bizarrely serving and former Air Corps personnel have been “reassured” by Air Corps medical personnel that their asthma does not have a workplace related cause despite no evidence of any testing for them to form a conclusion either way.

Considering what is now known about the extremely poor chemical health & safety environment in the Irish Air Corps any doctor, dismissing without appropriate testing, any possibility of a workplace casual link is surely opening himself or herself up to accusations of professional misconduct.

The tiniest trickle of blood – Another human cost of the Irish Air Corps Toxic Chemical Health & Safety scandal

The tiniest trickle of blood

My father was an aircraft technician in the Air Corps at Casement Aerodrome in Baldonnel for 21 years. During his time there he worked on a variety of aircraft and worked with an assortment of chemicals and sprays often without, as he said himself, even glove protection.

Over that time he developed severe psoriasis on his body, but in particular his hands and legs. This resulted in intense itch and pain and a daily routine of medication and treatment of the various lesions on his legs and also a stay in St. Bricin’s Hospital. It was not until a combination of appointments with a renowned Traditional Medical Herbalist, coupled with his retirement from the Air Corps that improvements began. This psoriasis, while appearing at a much slighter level during his life, never appeared to the same extent after leaving Baldonnel.

My mother passed away in 2009, and since then Dad lived with my wife and I, and subsequently, our two daughters. He adored his family and his granddaughters. He also really enjoyed an active and healthy life, learning to swim, regularly walking, going dancing, and eating very healthily. He liked his few social pints but gave up smoking before his first granddaughter was born eight years ago. He also had regular full check-ups with his GP.

In December 2013, while Dad was feeling very well, in great form, he spotted the tiniest trickle of blood in his urine. After attending his GP and a urologist, it was confirmed that he had renal cancer, which had completely taken over one of his kidneys and indeed had also spread to his lungs. Treatment was possible but immediate: he would need to have his kidney removed and a tablet form of chemotherapy would need to be taken for the rest of his life. Thankfully medical advances had developed this treatment, otherwise he would not have survived.

Almost two years passed and Dad had little or no side-effects to his treatment other than his dark hair turning grey overnight. He maintained his life as it was, keeping up his hobbies and his active lifestyle, as well as continuing his breaks to Lanzarote. Unfortunately in November 2015, things began to change and his body rejected the tablet. He became very ill with a litany of mystery illnesses that befuddled doctors but, miraculously, he managed to survive and came home. However, he spent his New Year’s Day in A&E, complaining of intense pain in his back. On examination and scanning, it was found that he had a broken vertebrae due to cancer spreading to his back. Again, thankfully it was in the position that it was, as it was treatable and would not end up with him in a wheelchair. Inserting rods either side of his spine meant that he would walk again.

The last months of his life were a mix of regular check-ups, consultant appointments, progress and setbacks. It was a roller-coaster of emotions where his unyielding positivity was tested repeatedly but never left him. 

It would have been interesting to see if his background in Baldonnel could have informed his treatment, or if indeed anything could have been done to prevent his disease. However such thoughts are merely conjecture and would distract from the magnificent memories we hold of a man who touched so many hearts and leaves behind a legacy fitting for such a character.

Irish Air Corps Chemical List Update – Mastinox 6856k

We have just added some links to information on the constituent chemicals for Mastinox 6856k from PubChem the Open Chemistry Database. Please have a look at green links on our chemical info page here. We will add more on a regular basis.

Mastinox 6856k is a corrosion inhibitor and contains the following

  • Strontium Chromate
  • Barium Chromate
  • Xylene
  • Toluene
  • Ethylbenzene
  • N-Octane
  • Naptha
  • Heptane
  • Methylcyclohexane