12 Chemical and Biological Health Hazards and Risk Controls Flashcards
What are the physical forms of chemicals?
- Solid – a solid block of material (e.g. a lead ingot).
- Dust – very small solid particles normally created by grinding, polishing, milling, blasting, etc. and capable of becoming airborne (e.g. flour dust, rock dust).
- Fume – very small metallic particles that have condensed from the gaseous state during work with molten metal (e.g. welding) to create an airborne cloud.
- Gas – a basic state of matter; expands to fill the space available (e.g. carbon dioxide (CO2)). • Mist – very small liquid droplets suspended in air, normally created by spraying (e.g. paint spraying).
- Vapour – the gaseous form of a substance that exists as a solid or liquid at normal temperature and pressure (e.g. vapour given off by acetone solvent).
- Liquid – a basic state of matter; free flowing fluid (e.g. water at 20°C).
How can we categorized biological agents?
- Fungi – moulds, yeast and mushrooms. Most are harmless to humans but some can cause disease, such as fungal infections (e.g. athlete’s foot) and farmer’s lung (an allergic irritation caused by inhaling mould spores).
- Bacteria – single-celled organisms that are found in vast numbers in and on the human body. Some are harmless, some are beneficial (certain gut bacteria) and some cause disease (e.g. legionnaires’ disease, leptospirosis).
- Viruses – very small infectious organisms that reproduce by hijacking living cells to manufacture more viruses. Many viruses cause disease (e.g. hepatitis).
- Prions - abnormal, transmissible agents able to induce abnormal folding of normal cellular prion proteins in the brain, leading to brain damage (e.g. Creutzfeldt-Jakob Disease (CJD or “mad cow” disease” and variant CJD)).
Types of danger caused by chemicals.
- Physico-chemical effects – such as highly flammable, explosive or oxidising.
- Health effects – such as toxic or carcinogenic.
- Environmental effects – such as harmful to aquatic life.
Classification of chemicals hazardous to health:
- Toxic – small doses cause death or serious ill-health when inhaled, swallowed or absorbed via the skin (e.g. potassium cyanide (KCN)).
- Harmful – cause death or serious ill-health when inhaled, swallowed or absorbed via the skin in large doses.
- Corrosive – destroy living tissue on contact (e.g. concentrated sodium hydroxide (NaOH)). • Irritant – cause inflammation of the skin or mucous membranes (e.g. eyes and lungs) through immediate, prolonged or repeated contact (e.g. ozone (O3)).
- Carcinogenic – may cause cancer (abnormal growth of cells in the body) when inhaled, swallowed or absorbed via the skin (e.g. asbestos). (Note that there are two categories of substance that are infrequently found in workplaces but can be of great concern when they are present:
- Mutagens – may cause genetic mutations that can be inherited.
- Toxic to reproduction – may cause sterility or affect an unborn child.)
What are sensitizing agents?
Some chemicals are sensitising agents. This means that they are capable of producing an allergic reaction that will gradually worsen on repeat exposures. There are two groups of sensitising chemicals:
- Skin sensitisers – can cause allergic dermatitis on contact with the skin (e.g. epoxy resin).
- Respiratory sensitisers – can cause asthma on inhalation into the lungs (e.g. flour dust and isocyanates).
Type of dermatitis
- Primary contact dermatitis - following immediate, repeated or prolonged contact with a primary skin irritant. This dermatitis is restricted to the skin that was in contact with the irritant substance only.
- Allergic or secondary contact dermatitis – following immediate, repeated or prolonged contact with a skin sensitising agent. This form of dermatitis often appears on different parts of the body other than the point of contact with the substance and can flare up in response to very small exposures once the person has become sensitised.
Distinguish between acute and chronic-ill health.
- Acute effects – as a result of exposure to high levels of the substance, sometimes over very short periods of time, and usually quite quickly after exposure begins (seconds, minutes or hours), e.g. exposure to high concentrations of chlorine gas causes immediate irritation to the respiratory system.
- Chronic effects – as a result of exposure to lower levels of the substance, over long periods of time, and usually weeks, months or years after exposure began, e.g. asbestosis occurs 10-20 years after multiple exposures to asbestos.
What are the main route of entry of hazardous substances into the body?
Inhalation – the substance is breathed in through the nose and mouth and down into the lungs. Dust can be inhaled through the nose and mouth in this way, but not all dust will travel down into the lungs. These two types of dust are called: –– Inhalable dust – particles of all sizes that can be inhaled into the nose and mouth. –– Respirable dust – particles less than 7 microns (7/1000 mm) in diameter that can travel deep into the lungs on inhaled breath.
Ingestion – the substance is taken in through the mouth and swallowed down into the stomach and then moves on through the digestive system. Ingestion usually occurs by cross contamination
Absorption through the skin – the substance passes through the skin and into the tissues beneath and then into the blood stream. Only some substances (e.g. organic solvents)
Injection through the skin – the substance passes through the skin barrier either by physical injection (e.g. a needle-stick injury) or through damaged skin (cuts and grazes).
What are the defence mechanisms of the body?
- Cellular defence (internal defence), which allows cells to fight bacteria and other toxins mostly from blood, respiratory and ingestion entry routes.
- Superficial defence (external defence), which protects against toxins that enter through the skin and contaminants in the nose and throat (via collection by the hairs and mucus).
Respiratory defences
The respiratory system is made up of the nose and nasal cavity, windpipe (trachea) and lungs. The air passes down the bronchi and bronchioles to the alveoli. These are small air sacs where oxygen enters the bloodstream. The respiratory system is protected by the following defences:
- The sneeze reflex.
- Filtration in the nasal cavity (which has a thick mucus lining that particles stick to). This is very effective at removing large particles; only particles less than 10 microns in diameter pass through. Not prevent smaller asbestos fibres or fine powders such as cement and finer silica dusts.
- Ciliary escalator – the bronchioles, bronchi and trachea are lined with small hairs (cilia). Mucus lining these passages is gradually moved by these cilia up out of the lungs. Any particles trapped in this mucus are cleaned out of the lungs by this mechanism. This filtration mechanism is effective at removing all particles larger than 7 microns in diameter.
- Macrophages/phagocytes – scavenging white blood cells of irregular outline. They produce enzymes that attack and destroy particles that enter body tissues. • Inflammatory response – any particles that cannot be removed by macrophages are likely to trigger an inflammation response. This causes the walls of the alveoli to thicken and become fibrous. This can be temporary or may result in permanent scarring (as with silicosis from silica and asbestosis from asbestos fibres).
Skin Defences
The skin forms a waterproof barrier between the body and the outside world. It is made of two layers, the outer epidermis and the inner, thicker, dermis. Defence mechanisms include:
- A thick layer of dead cells at the surface of the epidermis which are constantly being replenished as they wear off.
- Sebum – an oily fluid secreted onto the surface of the skin that has biocidal properties.
Factors to consider when carrying out an assessment of health risks include the: (10)
- Hazardous nature of the substance present – is it toxic, corrosive, carcinogenic, etc.?
- Potential ill-health effects – will the substance cause minor ill-health or very serious disease and will these result from short-term or long-term exposure?
- Physical forms that the substance takes in the workplace – is it a solid, liquid, vapour, dust, fume, etc.?
- Routes of entry the substance can take in order to cause harm – is it harmful by inhalation, ingestion, skin absorption, etc.?
- Quantity of the hazardous substance present in the workplace – including the total quantities stored and the quantities in use or created at any one time.
- Concentration of the substance – if stored or used neat or diluted, and the concentration in the air if airborne.
- Number of people potentially exposed and any vulnerable groups or individuals – such as pregnant women or the infirm.
- Frequency of exposure – will people be exposed once a week, once a day or continuously?
- Duration of exposure – will exposure be very brief, last for several hours or last all day?
- Control measures that are already in place – such as ventilation systems and PPE.
What information should be included in a label? (5)
- The name of the substance/preparation.
- Some idea of the components which make the product hazardous (though this often depends on the overall classification of the product and any provisions for confidentiality or “trade secret” in the country).
- An indication of the danger, which may be by specific warning phrases or symbols or a combination of both.
- Basic precautions to take (things to avoid or PPE to wear, etc.).
- Name, address and telephone number of the supplier.
Safety data sheets contain the following information:
- Identification of the substance or preparation and supplier – including name, address and emergency contact telephone numbers.
- Composition and information on ingredients – chemical names.
- Hazard identification – a summary of the most important features, including adverse health effects and symptoms.
- First aid measures – separated for the various risks, and specific, practical and easily understood.
- Fire-fighting measures – emphasising any special requirements.
- Accidental release measures – covering safety, environmental protection and clean-up.
- Handling and storage – recommendations for best practice, including any special storage conditions or incompatible materials.
- Exposure controls and personal protection – any specific recommendations, such as particular ventilation systems and PPE.
- Physical and chemical properties – physical, stability and solubility properties.
- Stability and reactivity – conditions and materials to avoid.
- Toxicological information – acute and chronic effects, routes of exposure and symptoms.
- Ecological information – environmental effects, which could include effects on aquatic organisms (sea and river life), etc.
- Disposal considerations – advice on specific dangers and legislation.
- Transport information – special precautions.
- Regulatory information – overall classification of the product and any specific legislation that may be applicable.
- Other information – any additional relevant information (e.g. explanation of abbreviations used).
What are the limitations that MSDS has in providing information to assess health risks?
- They contain general statements of the hazards. They do not allow for the localised conditions in which the substances are to be used, which will affect the risk.
- The information can be highly technical and therefore meaningless to non-specialists. • Individual susceptibility to substances varies; a person can be very prone to the health effects of a certain chemical.
- They provide information about the specific substance or preparation in isolation and do not take into account the effects of mixed exposures.
- The information represents current scientific thinking and there may be hazards present that are not currently understood.
When should be appropriate to stablish the role of hazardous substance monitoring?
- When failure or deterioration of the control measures could result in serious health effects.
- When measurement is required so as to be sure that anexposure limit is not exceeded.
- The effectiveness of control measures.
- If adequate control of exposure is no longer being maintained, following process or production changes, for example
Types of Continuous monitoring
- Stain Tube detectors
- Passive Samplers
- Smoke tubes / Sticks Dust
- Monitoring Equipment
- Dust Lamp (Tyndall Lamp)
What are the disadvantages of continuous Monitoring devices.
- Are expensive and require considerable training in their use.
- May not record peaks and troughs, merely an average.
- May not identify a specific type of contaminant (depending upon the design of the equipment and sensors used).
- Can be tampered with by workers to impact the results.
- If used as a static sampler, their results cannot be extrapolated to give results for personal exposure.
Stain Tube Detectors
These are easy to use and useful for analysing gas and vapour contamination in air at one moment in time. The principle of operation is simple – a known volume of air is drawn through a chemical reagent contained in a glass tube. The contaminant in the air reacts with the reagent and a coloured stain is produced. The degree of staining gives a direct reading of concentration. The instrument comprises a glass tube containing the chemical reagent fitted to a hand-operated bellows or piston-type pump. Many types of tube are available for detecting different gases and vapours. Stain tubes are quick and cheap to use, require little training and provide an instant result with no additional analysis requirements. However, their use is limited, as they:
- Are only suitable for gases and vapours, not dusts.
- Can be inaccurate.
- Can only be used for grab-sampling and not for taking time-weighted measurements.
- Are fragile.
- Have a limited shelf-life.
- May be used incorrectly.
Passive Samplers
These use absorbent chemicals to sample contaminants without using a pump to draw air through the collector. At the end of the sampling period, the sampler is sent for laboratory analysis This a more complex and expensive (and slower) process, requiring training in its use. However, the results can be very accurate and can be used to calculate time-weighted measurement results.
Smoke Tubes / Sticks
These are simple devices that generate smoke in a controlled chemical reaction. They are similar in appearance to stain tubes and can be used in conjunction with a rubber bulb. Breaking the smoke tube open activates the chemical reaction, then the bulb is used to puff the smoke as required. Smoke tubes are useful for visualising the movement of air currents in a workplace and in particular can be used to assess the effectiveness of ventilation and extraction systems (and to provide general information about air movements).
Dust Monitoring Equipment
Dust exposure in the workplace can be quantified using a sampling train made up of an air pump, tube and sampling head. This equipment can be worn by a worker, so gives an indication of personal exposure
Dust Lamp (Tyndall Lamp)
Airborne dust in the workplace which is not visible to the naked eye can be visualised using a dust lamp. A strong beam of light is shone through the area where a cloud of finely divided dust is suspected. The eye of the observer is shielded from the light beam and the dust cloud is made visible. This method is used to determine how exhaust ventilation systems are working.
Limitations of hazardous Substance Monitoring
- Accuracy of results – monitoring equipment is often limited in its accuracy and variations between will occur depending on the time it is used.
- Variations in personal exposure – even when careful monitoring has been carried out there may still be variation in employees’ personal exposure from the monitoring results due to personal habits and one-off events.
- Absence of a standard – monitoring for its own sake is of no use if there is no occupational exposure limit (OEL) to compare monitoring results to. Not all hazardous substances have an OEL set.
- Other exposure routes – monitoring focuses exclusively on airborne contaminant.
Long-Term and Short-Term limits for OELS
Occupational exposure limits are time-weighted average exposures; in other words, they are calculated by measuring a person’s average exposure over a specific reference period of time. They only apply to airborne concentrations of a substance. The two reference periods of time commonly used are:
- 15 minutes (short-term exposure limit, also known as a STEL). Short-term exposure limits combat the ill-health effects of being exposed to very high levels of the substance for quite short periods of time.
- 8 hours (long-term exposure limit, also known as a LTEL ). Long-term exposure limits combat the illhealth effects of being exposed to relatively low concentrations of the substance for many or all hours of every working day through an entire working lifetime.
Define Time-weighted average.
A time-weighted average is equal to the sum of the part of each time period which is multiplied by the exposure level of the contaminant in that time period. It is then divided by the hours in the working day
Limitations of exposure limits
- OELs are designed only to control the absorption into the body of harmful substances following inhalation. They are not concerned with absorption following ingestion or through contact with the skin or eyes.
- They take no account of individual personal susceptibility. Many of the limits have also been established in countries in Europe and the USA and are based on male physiology, so variations due to ethnicity and gender may be significant.
- They do not take account of the synergistic (or combined) effects of mixtures of substances, e.g. the use of multiple substances.
- They may become invalid if the normal environmental conditions are changed, e.g. changes in temperature, humidity or pressure may increase the harmful potential of a substance.
- The organisation may believe that limits are being adhered to but the employees may be working with controls which are no longer effective.
- The monitoring equipment may become contaminated, resulting in inaccurate results.
- Some limits are only “guidelines”.
- Some limits do not consider all the possible health effects of a substance, e.g. impact on the skin, such as dermatitis, would not be considered with an airborne limit.
Principles of good practice with regards to controlling exposure to hazardous substances
- Minimisation of emission, release and spread of hazardous substances through design and operation of processes and task activities.
- Accounting for relevant routes of entry into the body when developing control measures for hazardous substances. This will give clear indication of the type of control required, whether personal or collective control is needed, and the level of control necessary (based on toxicity).
- Exposure control which is proportional to health risk.
- Effectiveness and reliability of control options that minimise the escape and spread of hazardous substances.
- Use of personal protective equipment (PPE) in combination with other control measures if adequate control cannot otherwise be achieved. Specifically, respiratory
- Regular checks and review of the control measures that are in place to ensure that they remain effective.
- Provision of information and training.
- Ensuring that any control measures implemented do not increase the overall risks to health and safety.