61. Using, Storing and Transporting Chemicals
Chapter Editors: Jeanne Mager Stellman and Debra Osinsky
Safe Handling and Usage of Chemicals
Case Study: Hazard Communication: The Chemical Safety Data Sheet or the Material Safety Data Sheet (MSDS)
Classification and Labelling Systems for Chemicals
Konstantin K. Sidorov and Igor V. Sanotsky
Case Study: Classification Systems
Safe Handling and Storage of Chemicals
A.E. Quinn
Compressed Gases: Handling, Storage and Transport
A. Türkdogan and K.R. Mathisen
Laboratory Hygiene
Frank Miller
Methods for Localized Control of Air Contaminants
Louis DiBernardinis
The GESTIS Chemical Information System: A Case Study
Karlheinz Meffert and Roger Stamm
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62. Minerals and Agricultural Chemicals
Chapter Editors: Debra Osinsky and Jeanne Mager Stellman
Table of Contents
Minerals
Agricultural Chemicals
Gary A. Page
The WHO Guidelines to Classification of Pesticides by Hazard (Slightly Hazardous)
The WHO Guidelines to Classification of Pesticides by Hazard (Unlikely to Present Acute Hazard)
The WHO Guidelines to Classification of Pesticides by Hazard (Present Acute Hazard continued)
The WHO Guidelines to Classification of Pesticides by Hazard (Obsolete or Discontinued)
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63. Metals: Chemical Properties and Toxicity
Chapter Editor: Gunnar Nordberg
Table of Contents
GENERAL PROFILE
ACKNOWLEDGEMENTS
Aluminium
Antimony
Arsenic
Barium
Bismuth
Cadmium
Chromium
Copper
Iron
Gallium
Germanium
Indium
Iridium
Lead
Magnesium
Manganese
Metal Carbonyls (especially Nickel Carbonyl)
Mercury
Molybdenum
Nickel
Niobium
Osmium
Palladium
Platinum
Rhenium
Rhodium
Ruthenium
Selenium
Silver
Tantalum
Tellurium
Thallium
Tin
Titanium
Tungsten
Vanadium
Zinc
Zirconium and Hafnium
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The ILO Code of Practice
Much of the information and excerpts in this chapter are taken from the Code of Practice “Safety in the Use of Chemicals at Work” of the International Labour Organization (ILO 1993). The ILO Code provides practical guidelines on the implementation of the provisions of the Chemicals Convention, 1990 (No. 170), and Recommendation, 1990 (No. 177). The object of the Code is to provide guidance to those who may be engaged in the framing of provisions relating to the use of chemicals at work, such as competent authorities, the management in companies where chemicals are supplied or used, and emergency services, which should also offer guidelines to suppliers’, employers’ and workers’ organizations. The Code provides minimum standards and is not intended to discourage competent authorities from adopting higher standards. For more detailed information on individual chemicals and chemical families, see the “Guide to chemicals” in Volume IV of this “Encyclopaedia”.
The objective (section 1.1.1) of the ILO Code of Practice Safety in the Use of Chemicals at Work is to protect workers from the hazards of chemicals, to prevent or reduce the incidence of chemically- induced illnesses and injuries resulting from the use of chemicals at work, and consequently to enhance the protection of the general public and the environment by providing guidelines for:
Section 2 of the ILO Code of Practice outlines the general obligations, responsibilities and duties of the competent authority, the employer and the worker. The section also details the general responsibilities of suppliers and the rights of workers, and it offers guidelines regarding special provisions for the employer’s disclosure of confidential information. The final recommendations address the need for cooperation among employers, workers and their representatives.
General Obligations, Responsibilities and Duties
It is the responsibility of the appropriate governmental agency to follow existing national measures and practices, in consultation with the most representative organizations of employers and workers concerned, in order to assure safety in the use of chemicals at work. National practices and laws should be viewed in the context of international regulations, standards and systems, and with the measures and practices recommended by the ILO Code of Practice and the ILO Convention No. 170 and Recommendation No. 177.
The major focus of such measures which provide for safety of workers are, in particular:
There are various means by which the competent authority may achieve this aim. It may enact national laws and regulations; adopt, approve or recognize existing standards, codes or guidelines; and, where such standards, codes or guidelines do not exist, an authority may encourage their adoption by another authority, which can then be recognized. The governmental agency may also require that employers justify the criteria by which they are working.
According to the Code of Practice (section 2.3.1), it is the responsibility of employers to set out, in writing, their policy and arrangements on safety in the use of chemicals, as part of their general policy and arrangements in the field of occupational safety and health, and the various responsibilities exercised under these arrangements, in accordance with the objectives and principles of the Occupational Safety and Health Convention, 1981 (No. 155), and Recommendation, 1981 (No. 164). This information should be brought to the attention of their workers in a language the latter readily understand.
Workers, in turn, should take care of their own health and safety, and that of other persons who may be affected by their acts or omissions at work, as far as possible and in accordance with their training and with instructions given by their employer (section 2.3.2).
The suppliers of chemicals, whether manufacturers, importers or distributors, should ensure that, in accordance with the guidelines in the relevant paragraphs of the Code and in pursuance of the requirements of Convention No. 170 and Recommendation No. 177:
Operational Control Measures
Certain general principles exist for the operation control of chemicals at work. These are dealt with in Section 6 of the ILO Code of Practice, which prescribes that after reviewing the chemicals being used at work and obtaining information about their hazards and making an assessment of the potential risks involved, employers should take steps to limit exposure of workers to hazardous chemicals (on the basis of the measures outlined in sections 6.4 to 6.9 of the Code), in order to protect workers against hazards from the use of chemicals at work. The measures taken should eliminate or minimize the risks, preferably by substitution of non-hazardous or less hazardous chemicals, or by the choice of better technology. When neither substitution nor engineering control are feasible, other measures, such as safe working systems and practices, personal protective equipment (PPE) and the provision of information and training will further minimize risks and may have to be relied upon for some activities entailing the use of chemicals.
When workers are potentially exposed to chemicals that are hazardous to health, they must be safeguarded against the risk of injury or disease from these chemicals. There should be no exposure which exceeds exposure limits or other exposure criteria for the evaluation and control of the working environment established by the competent authority, or by a body approved or recognized by the competent authority in accordance with national or international standards.
Control measures to provide protection for workers could be any combination of the following:
1. good design and installation practice:
2. plants processes or work systems which minimize generation of, or suppress or contain, hazardous dust, fumes, etc., and which limit the area of contamination in the event of spills and leaks:
3. work systems and practices:
4. personal protection (where the above measures do not suffice, suitable PPE should be provided until such time as the risk is eliminated or minimized to a level that would not pose a threat to health)
5. prohibition of eating, chewing, drinking and smoking in contaminated areas
6. provision of adequate facilities for washing, changing and storage of clothing, including arrangements for laundering contaminated clothing
7. use of signs and notices
8. adequate arrangements in the event of an emergency.
Chemicals known to have carcinogenic, mutagenic or teratogenic health effects should be kept under strict control.
Record Keeping
Record keeping is an essential element of the work practices which provide a safe use of chemicals. Records should be kept by employers on measurements of airborne hazardous chemicals. Such records should be clearly marked by date, work area and plant location. The following are some elements of section 12.4 of the ILO Code of Practice, which deals with record-keeping requirements.
Besides the numerical results of measurements, the monitoring data should include, for example:
Records should be kept for a specified period of time determined by the competent authority. Where this has not been prescribed, it is recommended that the employer keep the records, or a suitable summary, for:
Information and Training
Correct instruction and quality training are essential components of a successful hazard communication programme. The ILO Code of Practice Safety in the Use of Chemicals at Work provides general principles of training (sections 10.1 and 10.2). These include the following:
Review of training needs
The extent of the training and instruction received and required should be reviewed and updated simultaneously with the review of the working systems and practices referred to in section 8.2 (Review of work systems).
The review should include the examination of:
Hazard classification and labelling systems are included in legislation covering the safe production, transport, use and disposal of chemicals. These classifications are designed to provide a systematic and comprehensible transfer of health information. Only a small number of significant classification and labelling systems exist at the national, regional and international levels. Classification criteria and their definitions used in these systems vary in the number and degree of hazard scales, specific terminology and test methods, and the methodology for classifying mixtures of chemicals. The establishment of an international structure for harmonizing classification and labelling systems for chemicals would have a beneficial impact on chemical trade, on the exchange of information related to chemicals, on the cost of risk assessment and management of chemicals, and ultimately on the protection of workers, the general public and the environment.
The major basis for classification of chemicals is the assessment of exposure levels and environmental impact (water, air and soil). About half of the international systems contain criteria related to a chemical’s production volume or the effects of pollutant emissions. The most widespread criteria used in chemical classification are values of median lethal dose (LD50) and median lethal concentration (LC50). These values are evaluated in laboratory animals via three main pathways—oral, dermal and inhalation—with a one-time exposure. Values of LD50 and LC50 are evaluated in the same animal species and with the same exposure routes. The Republic of Korea considers LD50 with intravenous and intracutaneous administration as well. In Switzerland and Yugoslavia chemical management legislation requires quantitative criteria for LD50 with oral administration and adds a provision which specifies the possibility of different hazard classifications based on the route of exposure.
In addition, differences in the definitions of comparable hazard levels exist. While the European Community (EC) system utilizes a three-level acute toxicity scale (“very toxic”, “toxic” and “harmful”), the US Occupational Safety and Health Administration (OSHA) Hazard Communication Standard applies two acute toxicity levels (“highly toxic” and “toxic”). Most classifications apply either three categories (United Nations (UN), World Bank, International Maritime Organization (IMO), EC and others) or four (the former Council for Mutual Economic Assistance (CMEA), the Russian Federation, China, Mexico and Yugoslavia).
International Systems
The following discussion of existing chemical classification and labelling systems focuses primarily on major systems with long application experience. Hazard assessments of pesticides are not covered in general chemical classifications, but are included in the Food and Agricultural Organization/World Health Organization (FAO/WHO) classification as well as in various national legislation (e.g., Bangladesh, Bulgaria, China, the Republic of Korea, Poland, the Russian Federation, Sri Lanka, Venezuela and Zimbabwe).
Transport-oriented classifications
Transport classifications, which are broadly applied, serve as a basis for regulations governing labelling, packaging and transport of dangerous cargoes. Among these classifications are the UN Recommendations on the Transport of Dangerous Goods (UNRTDG), the International Maritime Dangerous Goods Code developed within the IMO, the classification established by the Group of Experts on the Scientific Aspects of Marine Pollution (GESAMP) for hazardous chemicals carried by ship, as well as national transport classifications. National classifications as a rule comply with UN, IMO and other classifications within international agreements on transportation of dangerous goods by air, rail, road and inland navigation, harmonized with the UN system.
The United Nations Recommendations on the Transport of Dangerous Goods and related transport modal authorities
The UNRTDG create a widely accepted global system which provides a framework for intermodal, international and regional transport regulations. These Recommendations are increasingly being adopted as the basis of national regulations for domestic transport. The UNRTDG is rather general on issues such as notification, identification and hazard communication. The scope has been restricted to the transport of hazardous substances in packaged form; the Recommendations do not apply to exposed hazardous chemicals or to transport in bulk. Originally the objective was to prevent dangerous goods from causing acute injury to workers or the general public, or damage to other goods or the means of transport employed (aircraft, vessel, railcar or road vehicle). The system has now been extended to include asbestos and substances hazardous to the environment.
The UNRTDG focus primarily on hazard communication based on labels which include a combination of graphic symbols, colours, warning words and classification codes. They also provide key data for emergency response teams. The UNRTDG are relevant for the protection of such transport workers as aircrew, mariners and the crews of trains and road vehicles. In many countries the Recommendations have been incorporated in legislation for the protection of dock workers. Parts of the system, such as the Recommendations on explosives, have been adapted to regional and national regulations for the workplace, generally including manufacturing and storage. Other UN organizations concerned with transport have adopted the UNRTDG. The transport classification systems of dangerous goods of Australia, Canada, India, Jordan, Kuwait, Malaysia and United Kingdom basically comply with the major principles of these Recommendations, for example.
The UN classification subdivides chemicals into nine classes of hazards:
The packaging of goods for the purpose of transport, an area specified by the UNRTDG, is not covered as comprehensively by other systems. In support of the Recommendations, organizations such as IMO and International Civil Aviation Organization (ICAO) carry out very significant programmes aimed at training dock workers and airport personnel in the recognition of label information and packaging standards.
The International Maritime Organization
The IMO, with a mandate from the 1960 Conference on Safety of Life at Sea (SOLAS 1960), has developed the International Maritime Dangerous Goods (IMDG) Code. This code supplements the mandatory requirements of chapter VII (Carriage of Dangerous Goods) of SOLAS 74 and those of Annex III of the Maritime Pollution Convention (MARPOL 73/78). The IMDG Code has been developed and kept up to date for more than 30 years in close cooperation with the UN Committee of Experts on Transport of Dangerous Goods (CETG) and has been implemented by 50 IMO members representing 85% of the world’s merchant tonnage.
Harmonization of the IMDG Code with the UNRTDG ensures compatibility with the national and international rules applicable to the transport of dangerous goods by other modes, in so far as these other modal rules are also based on the recommendations of the UNCETG—that is, ICAO Technical Instructions for the Safe Transport of Dangerous Goods by Air and the European Regulations concerning the international carriage of dangerous goods by road (ADR) and by rail (RID).
In 1991 the 17th IMO Assembly adopted a Resolution on the Coordination of Work in Matters Relating to Dangerous Goods and Hazardous Substances, urging, inter alia, UN bodies and governments to coordinate their work in order to ensure the compatibility of any legislation on chemicals, dangerous goods and hazardous substances with established international transport rules.
Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and their Disposal, 1989
The Convention’s Annexes define 47 categories of wastes, including domestic wastes. Although the hazard classification parallels that of the UNRTDG, a significant difference includes the addition of three categories reflecting more specifically the nature of toxic wastes: chronic toxicity, liberation of toxic gases from interaction of wastes with air or water, and capacity of wastes to yield secondary toxic material after disposal.
Pesticides
National classification systems related to the hazard assessment of pesticides tend to be quite comprehensive because of the wide use of these chemicals and the potential long-term damage to the environment. These systems may identify from two to five hazard classifications. The criteria are based on median lethal doses with different routes of exposure. While Venezuela and Poland recognize only one route of exposure, ingestion, the WHO and various other countries identify both ingestion and skin application.
The criteria for hazard assessment of pesticides in East European countries, Cyprus, Zimbabwe, China and others are based on median lethal doses via inhalation. Bulgaria’s criteria, however, include skin and eye irritation, sensitization, accumulation ability, persistence in environmental media, blastogenic and teratogenic effects, embryotoxicity, acute toxicity and medical treatment. Many classifications of pesticides also include separate criteria based on median lethal doses with different aggregative states. For example, criteria for liquid pesticides are usually more severe than those for solid ones.
WHO Recommended Classification of Pesticides by Hazard
This Classification was first issued in 1975 by the WHO and updated subsequently on a regular basis by the United Nations Environment Programme, the ILO and the WHO (UNEP/ILO/WHO) International Programme on Chemical Safety (IPCS) with input from the Food and Agriculture Organization (FAO). It consists of one hazard category or classification criterion, acute toxicity, divided in four classification levels based on LD50 (rat, oral and dermal values for liquid and solid forms) and ranging from extremely to slightly hazardous. Apart from general considerations, no specific labelling rules are provided. The 1996–97 update contains a guide to classification which includes a list of classified pesticides and comprehensive safety procedures. (See the chapter Minerals and agricultural chemicals.)
FAO International Code of Conduct on the Distribution and Use of Pesticides
The WHO Classification is supported by another document, the FAO International Code of Conduct on the Distribution and Use of Pesticides. Although it is only a recommendation, this classification is applied most widely in developing countries, where it is often included into pertinent national legislation. With regard to labelling, the FAO has published Guidelines on Good Labelling Practice for Pesticides as an addendum to these guidelines.
Regional Systems (EC, EFTA, CMEA)
The EC Council Directive 67/548/EEC has been in application for over two decades and has harmonized the pertinent legislation of 12 countries. It has evolved into a comprehensive system which includes an inventory of existing chemicals, a notification procedure for new chemicals prior to marketing, a set of hazard categories, classification criteria for each category, testing methods, and a hazard communication system including labelling with codified risk and safety phrases and hazard symbols. Chemical preparations (mixtures of chemicals) are regulated by Council Directive 88/379/EEC. The definition of the chemical safety data sheet data elements is practically identical to that defined in ILO Recommendation No. 177, as discussed earlier in this chapter. A set of classification criteria and a label for chemicals that are dangerous to the environment have been produced. The Directives regulate chemicals placed on the market, with the goal of protecting human health and the environment. Fourteen categories are divided into two groups related respectively to physico-chemical properties (explosive, oxidizing, extremely flammable, highly flammable, flammable) and toxicological properties (very toxic, toxic, harmful, corrosive, irritant, carcinogenic, mutagenic, toxic to reproduction, properties dangerous to health or the environment).
The Commission of European Communities (CEC) has an extension to the system specifically addressed to the workplace. In addition, these measures on chemicals should be considered within the overall framework of the protection of the health and safety of workers provided for under Directive 89/391/EEC and its individual Directives.
With the exception of Switzerland, the countries in EFTA follow the EC system to a large degree.
Former Council for Mutual Economic Assistance (CMEA)
This system was elaborated under the umbrella of the Standing Commission for Cooperation in Public Health of the CMEA, which included Poland, Hungary, Bulgaria, the former USSR, Mongolia, Cuba, Romania, Vietnam and Czechoslovakia. China still uses a system which is similar in concept. It consists of two classification categories, namely toxicity and hazard, using a four-level ranking scale. Another element of the CMEA system is its requirement for the preparation of a “toxicological passport of new chemical compounds subjected to introduction in the economy and domestic life”. Criteria for irritancy, allergic effects, sensitization, carcinogenicity, mutagenicity, teratogenicity, antifertility and ecological hazards are defined. However, the scientific basis and the testing methodology related to the classification criteria are significantly different from those used by the other systems.
Provisions for workplace labelling and hazard symbols are also different. The UNRTDG system is used for labelling goods for transport, but there does not seem to be any linkage between the two systems. There are no specific recommendations for chemical safety data sheets. The system is described in detail in the UNEP International Register of Potentially Toxic Chemicals (IRPTC) International Survey of Classification Systems. While the CMEA system contains most of the basic elements of the other classification systems, it differs significantly in the area of hazard assessment methodology, and uses exposure standards as one of the hazard classification criteria.
Examples of National Systems
Australia
Australia has enacted legislation for the notification and assessment of industrial chemicals, the Industrial Chemicals Notification and Assessment Act of 1989, with similar legislation enacted in 1992 for agricultural and veterinary chemicals. The Australian system is similar to that of the EC. The differences are mainly due to its utilization of the UNRTDG classification (i.e., the inclusion of the categories compressed gas, radioactive and miscellaneous).
Canada
The Workplace Hazardous Materials Information System (WHMIS) was implemented in 1988 by a combination of federal and provincial legislation designed to enforce the transfer of information about hazardous materials from producers, suppliers and importers to employers and in turn to workers. It applies to all industries and workplaces in Canada. WHMIS is a communication system aimed primarily at industrial chemicals and composed of three interrelated hazard communication elements: labels, chemical safety data sheets and worker education programmes. A valuable support to this system was the earlier creation and commercial distribution worldwide of a computerized database, now available on compact disc, containing over 70,000 chemical safety data sheets voluntarily submitted to the Canadian Centre for Occupational Health and Safety by manufacturers and suppliers.
Japan
In Japan, the control of chemicals is covered mainly by two laws. First, the Chemical Substances Control Law, as amended in 1987, is aimed at preventing environmental contamination by chemical substances that are low in biodegradability and harmful to human health. The law defines a premarket notification procedure and three “hazard” classes:
Control measures are defined, and a list of existing chemicals is provided.
The second regulation, the Industrial Safety and Health Law, is a parallel system with its own list of “Specified chemical substances” which require labelling. Chemicals are classified into four groups (lead, tetraalkyl lead, organic solvents, specified chemical substances). The classification criteria are (1) possible occurrence of serious health impairment, (2) possible frequent occurrence of health impairment and (3) actual health impairment. Other laws dealing with the control of hazardous chemicals include the Explosives Control Law; the High Pressure Gas Control Law; the Fire Prevention Law; the Food Sanitation Law; and the Drugs, Cosmetics and Medical Instruments Law.
United States
The Hazard Communication Standard (HCS), a mandatory standard promulgated by OSHA, is a workplace-oriented binding regulation which refers to other existing laws. Its goal is to ensure that all chemicals produced or imported are evaluated, and that information related to their hazards is transmitted to employers and to workers through a comprehensive hazard communication programme. The programme includes labelling and other forms of warning, chemical safety data sheets and training. Label and data sheet minimum contents are defined, but the use of hazard symbols is not mandatory.
Under the Toxic Substances Control Act (TSCA), administered by the Environmental Protection Agency (EPA), an inventory listing approximately 70,000 existing chemicals is maintained. The EPA is developing regulations to complement the OSHA HCS which would have similar hazard evaluation and worker communication requirements for the environmental hazards of chemicals on the inventory. Under TSCA, prior to manufacture or import of chemicals which are not on the inventory, the manufacturer must submit a premanufacture notice. The EPA may impose testing or other requirements based on the premanufacture notice review. As new chemicals are introduced into commerce, they are added to the inventory.
Labelling
Labels on containers of hazardous chemicals provide the first alert that a chemical is hazardous, and should provide basic information about safe handling procedures, protective measures, emergency first aid and the chemical’s hazards. The label should also include the identity of the hazardous chemical(s) and the name and address of the chemical manufacturer.
Labelling consists of phrases as well as graphic and colour symbols applied directly on the product, package, label or tag. The marking should be clear, easily comprehensible and able to withstand adverse climatic conditions. The labelling should be placed against a background that contrasts with the product’s accompanying data or package colour. The MSDS provides more detailed information on the nature of the chemical product’s hazards and the appropriate safety instructions.
While presently there are no globally harmonized labelling requirements, there are established international, national and regional regulations for labelling hazardous substances. Requirements for labelling are incorporated into the Law on Chemicals (Finland), the Act on Dangerous Products (Canada) and EC Directive N 67/548. Minimum label content requirements of the European Union, United States and Canadian systems are relatively similar.
Several international organizations have established labelling content requirements for handling chemicals at the workplace and in transport. The labels, hazard symbols, risk and safety phrases, and emergency codes of the International Organization for Standardization (ISO), the UNRTDG, the ILO and EU are discussed below.
The section on labelling in the ISO/IEC guide 51, Guidelines for Inclusion of Safety Aspects in Standards, includes commonly recognized pictograms (drawing, colour, sign). In addition, short and plain warning phrases alert the user to potential hazards and provide information on preventive safety and health measures.
The guidelines recommend the use of the following “signal” words to alert the user:
The UNRTDG establish five main pictograms for easy visible recognition of dangerous goods and significant hazard identification:
These symbols are supplemented by other representations such as:
The Chemicals Convention, 1990 (No. 170), and Recommendation, 1990 (No. 177), were adopted at the 77th Session of the International Labour Conference (ILC). They establish requirements for the labelling of chemicals to ensure the communication of basic hazard information. The Convention states that label information should be easily understandable and should convey the potential risks and appropriate precautionary measures to the user. Regarding the transport of dangerous goods, the Convention refers to the UNRTDG.
The Recommendation outlines labelling requirements in accordance with existing national and international systems, and establishes criteria for classification of chemicals including chemical and physical properties; toxicity; necrotic and irritating properties; and allergic, teratogenic, mutagenic and reproductive effects.
The EC Council Directive N 67/548 stipulates the form of label information: graphic hazard symbols and pictograms including risk and safety phrases. Hazards are coded by the Latin letter R accompanied with combinations of Arabic numerals from 1 to 59. For example, R10 corresponds with “flammable”, R23 with “toxic by inhalation”. The hazard code is given with a safety code consisting of the Latin letter S and combinations of numerals from 1 to 60. For example, S39 means “Wear eye/face protection”. The EC labelling requirements serve as a reference for chemical and pharmaceutical companies throughout the world.
Despite significant efforts in chemical hazard data acquisition, evaluation and organization by different international and regional organizations, there is still a lack of coordination of these efforts, particularly in the standardization of assessment protocols and methods and interpretation of data. The ILO, the Organization for Economic Cooperation and Development (OECD), the IPCS and other concerned bodies have initiated a number of international activities aimed toward establishing a global harmonization of chemical classification and labelling systems. The establishment of an international structure to monitor chemical hazard assessment activities would greatly benefit workers, the general public and the environment. An ideal harmonization process would reconcile the transport, marketing and workplace classification and labelling of hazardous substances, and address consumer, worker and environmental concerns.
Adapted from 3rd edition, Encyclopaedia of Occupational Health and Safety
Before a new hazardous substance is received for storage, information concerning its correct handling should be provided to all users. Planning and maintaining of storage areas are necessary to avoid material losses, accidents and disasters. Good housekeeping is essential, and special attention should be paid to incompatible substances, suitable location of products and climatic conditions.
Written instructions of storage practices should be provided, and the chemicals’ material safety data sheets (MSDSs) should be available in storage areas. Locations of the different classes of chemicals should be illustrated in a storage map and in a chemical register. The register should contain the maximum allowed quantity of all chemical products and the maximum allowed quantity of all chemical products per class. All substances should be received at a central location for distribution to the storerooms, stockrooms and laboratories. A central receiving area is also helpful in monitoring substances that may eventually enter the waste-disposal system. An inventory of substances contained in the storerooms and stockrooms will give an indication of the quantity and nature of substances targeted for future disposal.
Stored chemicals should be examined periodically, at least annually. Chemicals with expired shelf lives and deteriorated or leaking containers should be disposed of safely. A “first in, first out” system of keeping stock should be used.
The storage of dangerous substances should be supervised by a competent, trained person. All workers required to enter storage areas should be fully trained in appropriate safe work practices, and a periodic inspection of all storage areas should be carried out by a safety officer. A fire alarm should be situated in or near the outside of the storage premises. It is recommended that persons should not work alone in a storage area containing toxic substances. Chemical storage areas should be located away from process areas, occupied buildings and other storage areas. In addition, they should not be in proximity of fixed sources of ignition.
Labelling and Relabelling Requirements
The label is the key to organizing chemical products for storage. Tanks and containers should be identified with signs indicating the name of the chemical product. No containers or cylinders of compressed gases should be accepted without the following identifying labels:
The label may also offer precautions for correct storage, such as “Keep in a cool place” or “Keep container dry”. When certain dangerous products are delivered in tankers, barrels or bags and repackaged at the workplace, each new container should be relabelled so that the user will be able to identify the chemical and recognize the risks immediately.
Explosive Substances
Explosive substances include all chemicals, pyrotechnics and matches which are explosives per se and also those substances such as sensitive metallic salts which, by themselves or in certain mixtures or when subject to certain conditions of temperature, shock, friction or chemical action, may transform and undergo an explosive reaction. In the case of explosives, most countries have stringent regulations regarding safe storage requirements and precautions to be taken in order to prevent theft for use in criminal activities.
The storage places should be situated far away from other buildings and structures so as to minimize damage in case of an explosion. Manufacturers of explosives issue instructions as to the most suitable type of storage. The storerooms should be of solid construction and kept securely locked when not in use. No store should be near a building containing oil, grease, waste combustible material or flammable material, open fire or flame.
In some countries there is a legal requirement that magazines should be situated at least 60 m from any power plant, tunnel, mine shaft, dam, highway or building. Advantage should be taken of any protection offered by natural features such as hills, hollows, dense woods or forests. Artificial barriers of earth or stone walls are sometimes placed around such storage places.
The storage place should be well ventilated and free from dampness. Natural lighting or portable electric lamps should be used, or lighting provided from outside the storehouse. Floors should be constructed of wood or other non-sparking material. The area surrounding the storage place should be kept free of dry grass, rubbish or any other material likely to burn. Black powder and explosives should be stored in separate storehouses, and no detonators, tools or other materials should be kept in an explosive store. Non-ferrous tools should be used for opening cases of explosives.
Oxidizing Substances
Oxidizing substances provide sources of oxygen, and thus are capable of supporting combustion and intensifying the violence of any fire. Some of these oxygen suppliers give off oxygen at storage-room temperature, but others require the application of heat. If containers of oxidizing materials are damaged, the contents may mix with other combustible materials and start a fire. This risk can be avoided by storing oxidizing materials in a separate storage place. However, this practice may not always be available, as, for example, in dock warehouses for goods in transit.
It is dangerous to store powerful oxidizing substances near liquids that even have a low flash point or even slightly flammable materials. It is safer to keep all flammable materials away from a place where oxidizing substances are stored. The storage area should be cool, well ventilated and of fire-resisting construction.
Flammable Substances
A gas is deemed to be flammable if it burns in the presence of air or oxygen. Hydrogen, propane, butane, ethylene, acetylene, hydrogen sulphide and coal gas are among the most common flammable gases. Some gases such as hydrogen cyanide and cyanogen are both flammable and poisonous. Flammable materials should be stored in places which are cool enough to prevent accidental ignition if the vapours mix with the air.
Vapours of flammable solvents may be heavier than air and may move along the floor to a distant ignition source. Flammable vapours from spilled chemicals have been known to descend into stairwells and elevator shafts and ignite at a lower storey. It is therefore essential that smoking and open flames be prohibited where these solvents are handled or stored.
Portable, approved safety cans are the safest vessels for storing flammables. Quantities of flammable liquids greater than 1 litre should be stored in metal containers. Two-hundred-litre drums are commonly used to ship flammables, but are not intended as long-term storage containers. The stopper should be removed carefully and replaced by an approved pressure-relief vent to avoid increased internal pressure from heat, fire or exposure to sunlight. When transferring flammables from metal equipment, the worker should use an enclosed transfer system or have adequate exhaust ventilation.
The storage area should be situated away from any source of heat or fire hazard. Highly flammable substances should be kept apart from powerful oxidizing agents or from materials which are susceptible to spontaneous combustion. When highly volatile liquids are stored, any electric light fittings or apparatus should be of certified flameproof construction, and no open flames should be permitted in or near the storage place. Fire extinguishers and absorbent inert materials, such as dry sand and earth, should be available for emergency situations.
The walls, ceilings and floors of the storage room should consist of materials with at least a 2-hour fire resistance. The room should be fitted with self-closing fire doors. The storage-room installations should be electrically grounded and periodically inspected, or equipped with automatic smoke- or fire-detection devices. Control valves on storage vessels containing flammable liquids should be clearly labelled, and pipelines should be painted with distinctive safety colours to indicate the type of liquid and the direction of flow. Tanks containing flammable substances should be situated on ground sloping away from the main buildings and plant installations. If they are on level ground, protection against fire spread can be obtained by adequate spacing and the provision of dykes. The dyke capacity should preferably be 1.5 times that of the storage tank, as a flammable liquid may be likely to boil over. Provision should be made for venting facilities and flame arrestors on such storage tanks. Adequate fire extinguishers, either automatic or manual, should be available. No smoking should be allowed.
Toxic Substances
Toxic chemicals should be stored in cool, well ventilated areas out of contact with heat, acids, moisture and oxidizing substances. Volatile compounds should be stored in spark-free freezers (–20 °C) to avoid evaporation. Because containers may develop leaks, storerooms should be equipped with exhaust hoods or equivalent local ventilation devices. Open containers should be closed with tape or other sealant before being returned to the storeroom. Substances which can react chemically with each other should be kept in separate stores.
Corrosive Substances
Corrosive substances include strong acids, alkalis and other substances which will cause burns or irritation of the skin, mucous membranes or eyes, or which will damage most materials. Typical examples of these substances include hydrofluoric acid, hydrochloric acid, sulphuric acid, nitric acid, formic acid and perchloric acid. Such materials may cause damage to their containers and leak into the atmosphere of the storage area; some are volatile and others react violently with moisture, organic matter or other chemicals. Acid mists or fumes may corrode structural materials and equipment and have a toxic action on personnel. Such materials should be kept cool but well above their freezing point, since a substance such as acetic acid may freeze at a relatively high temperature, rupture its container and then escape when the temperature rises again above its freezing point.
Some corrosive substances also have other dangerous properties; for example, perchloric acid, in addition to being highly corrosive, is also a powerful oxidizing agent which can cause fire and explosions. Aqua regia has three dangerous properties: (1) it displays the corrosive properties of its two components, hydrochloric acid and nitric acid; (2) it is a very powerful oxidizing agent; and (3) application of only a small amount of heat will result in the formation of nitrosyl chloride, a highly toxic gas.
Storage areas for corrosive substances should be isolated from the rest of the plant or warehouses by impervious walls and floor, with provision for the safe disposal of spillage. The floors should be made of cinder blocks, concrete that has been treated to reduce its solubility, or other resistant material. The storage area should be well ventilated. No store should be used for the simultaneous storage of nitric acid mixtures and sulphuric acid mixtures. Sometimes it is necessary to store corrosive and poisonous liquids in special types of containers; for example, hydrofluoric acid should be kept in leaden, gutta percha or ceresin bottles. Since hydrofluoric acid interacts with glass, it should not be stored near glass or earthenware carboys containing other acids.
Carboys containing corrosive acids should be packed with kieselguhr (infusorial earth) or other effective inorganic insulating material. Any necessary first-aid equipment such as emergency showers and eyewash bottles should be provided in or immediately close to the storage place.
Water-reactive Chemicals
Some chemicals, such as sodium and potassium metals, react with water to produce heat and flammable or explosive gases. Certain polymerization catalysts, such as alkyl aluminium compounds, react and burn violently on contact with water. Storage facilities for water-reactive chemicals should not have water in the storage area. Non-water automatic sprinkler systems should be employed.
Legislation
Detailed legislation has been drawn up in many countries to regulate the manner in which various dangerous substances may be stored; this legislation includes the following specifications:
In many countries there is no central authority concerned with the supervision of the safety precautions for the storage of all dangerous substances, but a number of separate authorities exist. Examples include mine and factory inspectorates, dock authorities, transport authorities, police, fire services, national boards and local authorities, each of which deals with a limited range of dangerous substances under various legislative powers. It is usually necessary to obtain a licence or permit from one of these authorities for the storage of certain types of dangerous substances such as petroleum, explosives, cellulose and cellulose solutions. The licensure procedures require that storage facilities comply with specified safety standards.
Adapted from 3rd edition, Encyclopaedia of Occupational Health and Safety
Gases in their compressed state, and particularly compressed air, are almost indispensable to modern industry, and are also used widely for medical purposes, for the manufacture of mineral waters, for underwater diving and in connection with motor vehicles.
For purposes of the present article, compressed gases and air are defined as being those with a gauge pressure exceeding 1.47 bar or as liquids having a vapour pressure exceeding 2.94 bar. Thus, consideration is not given to such cases as natural gas distribution, which is dealt with elsewhere in this Encyclopaedia.
Table 1 shows the gases commonly encountered in compressed cylinders.
Table 1. Gases often found in compressed form
Acetylene* |
Ammonia* |
Butane* |
Carbon dioxide |
Carbon monoxide* |
Chlorine |
Chlorodifluormethane |
Chloroethane* |
Chloromethane* |
Chlorotetrafluoroethane |
Cyclopropane* |
Dichlorodifluoromethane |
Ethane* |
Ethylene* |
Helium |
Hydrogen* |
Hydrogen chloride |
Hydrogen cyanide* |
Methane* |
Methylamine* |
Neon |
Nitrogen |
Nitrogen dioxide |
Nitrous oxide |
Oxygen |
Phosgene |
Propane* |
Propylene* |
Sulphur dioxide |
*These gases are flammable.
All the above gases present either an irritant, asphyxiant or highly toxic respiratory hazard and may also be flammable and an explosive when compressed. Most countries provide for a standard colour-coding system whereby different coloured bands or labels are applied to the gas cylinders to indicate the type of hazard to be expected. Particularly toxic gases, such as hydrogen cyanide, are also given special markings.
All compressed gas containers are so constructed that they are safe for the purposes for which they are intended when first put into service. However, serious accidents may result from their misuse, abuse or mishandling, and the greatest care should be exercised in the handling, transport, storage and even in the disposal of such cylinders or containers.
Characteristics and Production
Depending on the characteristics of the gas, it may be introduced into the container or cylinder in liquid form or simply as a gas under high pressure. In order to liquefy a gas, it is necessary to cool it to below its critical temperature and to subject it to an appropriate pressure. The lower the temperature is reduced below the critical temperature, the less the pressure required.
Certain of the gases listed in table 1 have properties against which precautions must be taken. For example, acetylene can react dangerously with copper and should not be in contact with alloys containing more than 66% of this metal. It is usually delivered in steel containers at about 14.7 to 16.8 bar. Another gas that has a highly corrosive action on copper is ammonia, which must also be kept out of contact with this metal, use being made of steel cylinders and authorized alloys. In the case of chlorine, no reaction takes place with copper or steel except in the presence of water, and for this reason all storage vessels or other containers must be kept free from contact with moisture at all times. Fluorine gas, on the other hand, although reacting readily with most metals, will tend to form a protective coating, as, for example, in the case of copper, where a layer of copper fluoride over the metal protects it from further attack by the gas.
Among the gases listed, carbon dioxide is one of the most readily liquefied, this taking place at a temperature of 15 °C and a pressure of about 14.7 bar. It has many commercial applications and may be kept in steel cylinders.
The hydrocarbon gases, of which liquefied petroleum gas (LPG) is a mixture formed mainly of butane (about 62%) and propane (about 36%), are not corrosive and are generally delivered in steel cylinders or other containers at pressures of up to 14.7 to 19.6 bar. Methane is another highly flammable gas that is also generally delivered in steel cylinders at a pressure of 14.7 to 19.6 bar.
Hazards
Storage and transport
When a filling, storage and dispatch depot is being selected, consideration must be given to the safety of both the site and the environment. Pump rooms, filling machinery and so on must be located in fire-resistant buildings with roofs of light construction. Doors and other closures should open outwards from the building. The premises should be adequately ventilated, and a system of lighting with flameproof electrical switches should be installed. Measures should be taken to ensure free movement in the premises for filling, checking and dispatch purposes, and safety exits should be provided.
Compressed gases may be stored in the open only if they are adequately protected from the weather and direct sunlight. Storage areas should be located at a safe distance from occupied premises and neighbouring dwellings.
During the transport and distribution of containers, care must be taken to ensure that valves and connections are not damaged. Adequate precautions should be taken to prevent cylinders from falling off the vehicle and from being subjected to rough usage, excessive shocks or local stress, and to prevent excessive movement of liquids in large tanks. Every vehicle should be equipped with a fire extinguisher and an electrically conductive strip for earthing static electricity, and should be clearly marked “Flammable liquids”. Exhaust pipes should have a flame-control device, and engines should be halted during loading and unloading. The maximum speed of these vehicles should be rigorously limited.
Use
The main dangers in the use of compressed gases arise from their pressure and from their toxic and/or flammable properties. The principal precautions are to ensure that equipment is used only with those gases for which it was designed, and that no compressed gases are used for any purpose other than that for which their use has been authorized.
All hoses and other equipment should be of good quality and should be examined frequently. The use of non-return valves should be enforced wherever necessary. All hose connections should be in good condition and no joints should be made by forcing together threads that do not exactly correspond. In the case of acetylene and combustible gases, a red hose should be used; for oxygen the hose should be black. It is recommended that for all flammable gases, the connection-screw thread shall be left-handed, and for all other gases, it shall be right-handed. Hoses should never be interchanged.
Oxygen and some anaesthetic gases are often transported in large cylinders. The transfer of these compressed gases to small cylinders is a hazardous operation, which should be done under competent supervision, making use of the correct equipment in a correct installation.
Compressed air is widely used in many branches of industry, and care should be taken in the installation of pipelines and their protection from damage. Hoses and fittings should be maintained in good condition and subjected to regular examinations. The application of a compressed air hose or jet to an open cut or wound through which air can enter the tissues or the bloodstream is particularly dangerous; precautions should also be taken against all forms of irresponsible behaviour which could result in a compressed air jet coming in contact with any openings in the body (the result of which can be fatal). A further hazard exists when compressed air jets are used to clean machined components or workplaces: flying particles have been known to cause injury or blindness, and precautions against such dangers should be enforced.
Labelling and marking
4.1.1. The competent authority, or a body approved or recognized by the competent authority, should establish requirements for the marking and labelling of chemicals to enable persons handling or using chemicals to recognize and distinguish between them, both when receiving and when using them, so that they may be used safely (see paragraph 2.1.8 (criteria and requirements)). Existing criteria for marking and labelling established by other competent authorities may be followed where they are consistent with the provisions of this paragraph and are encouraged where this may assist uniformity of approach.
4.1.2. Suppliers of chemicals should ensure that chemicals are marked and hazardous chemicals are labelled, and that revised labels are prepared and provided to employers whenever new relevant safety and health information becomes available (see paragraphs 2.4.1 (suppliers’ responsibilities) and 2.4.2 (classification)).
4.1.3. Employers receiving chemicals that have not been labelled or marked should not use them until the relevant information is obtained from the supplier or from other reasonably available sources. Information should be obtained primarily from the supplier but may be obtained from other sources listed in paragraph 3.3.1 (sources of information), with a view to marking and labelling in accordance with the requirements of the national competent authority, prior to use. ...
4.3.2. The purpose of the label is to give essential information on:
The information should refer to both acute and chronic exposure hazards.
4.3.3. Labelling requirements, which should be in conformity with national requirements, should cover:
(a) the information to be given on the label, including as appropriate:
(b) the legibility, durability and size of the label;
(c) the uniformity of labels and symbols, including colours.
Source: ILO 1993, Chapter 4.
Labelling and marking should be in accordance with standard practice in the country or region in question. The use of one gas for another by mistake, or the filling of a container with a gas different from that which it previously contained, without the necessary cleaning and decontamination procedures, may cause serious accidents. Colour marking is the best method of avoiding such errors, painting specific areas of containers or piping systems in accordance with the colour code stipulated in national standards or recommended by the national safety organization.
Gas Cylinders
For convenience in handling, transportation and storage, gases are commonly compressed in metal gas cylinders at pressures that range from a few atmospheres overpressure to 200 bar or even more. Alloy steel is the material most commonly used for the cylinders, but aluminium is also widely used for many purposes—for example, for fire extinguishers.
The hazards met with in handling and using compressed gases are:
Cylinder manufacture. Steel cylinders may be seamless or welded. The seamless cylinders are made from high-quality alloy steels and carefully heat-treated in order to obtain the desired combination of strength and toughness for high-pressure service. They may be forged and hot-drawn from steel billets or hot-formed from seamless tubes. Welded cylinders are made from sheet material. The pressed top and bottom parts are welded to a cylindrical seamless or welded tube section and heat-treated to relieve material stresses. Welded cylinders are extensively used in low-pressure service for liquefiable gases and for dissolved gases such as acetylene.
Aluminium cylinders are extruded in large presses from special alloys that are heat-treated to give the desired strength.
Gas cylinders must be designed, produced and tested according to strict norms or standards. Every batch of cylinders should be checked for material quality and heat treatment, and a certain number of cylinders tested for mechanical strength. Inspection is often aided by sophisticated instruments, but in all cases the cylinders should be inspected and hydraulically tested to a given test pressure by an approved inspector. Identification data and the inspector’s mark should be permanently stamped on the cylinder neck or another suitable place.
Periodic inspection. Gas cylinders in use may be affected by rough treatment, corrosion from inside and outside, fire and so on. National or international codes therefore require that they shall not be filled unless they are inspected and tested at certain intervals, which mostly range between two and ten years, depending on the service. Internal and external visual inspection together with a hydraulic pressure test is the basis for the approval of the cylinder for a new period in a given service. The test date (month and year) is stamped on the cylinder.
Disposal. A large number of cylinders are scrapped every year for various reasons. It is equally important that these cylinders be disposed of in such a way that they will not find their way back into use through uncontrolled channels. The cylinders should therefore be made completely unserviceable by cutting, crushing or a similar safe procedure.
Valves. The valve and any safety attachment must be regarded as a part of the cylinder, which must be kept in good working condition. Neck and outlet threads should be intact, and the valve should close tight without the use of undue force. Shut-off valves are often equipped with a pressure-relief device. This may be in the form of a resetting safety valve, bursting disc, fuse plug (melt plug) or a combination of bursting disc and fuse plug. The practice varies from country to country, but cylinders for low-pressure liquefied gases are always equipped with safety valves connected to the gas phase.
Hazards
Different transport codes classify gases as compressed, liquefied or dissolved under pressure. For the purpose of this article, it is useful to use the type of hazard as a classification.
High pressure. If cylinders or equipment burst, damage and injuries may be caused by flying debris or by the gas pressure. The more a gas is compressed, the higher is the stored energy. This hazard is always present with compressed gases and will increase with temperature if the cylinders are heated. Hence:
Low temperature. Most liquefied gases will evaporate rapidly under atmospheric pressure, and may reach very low temperatures. A person whose skin is exposed to such liquid may sustain injuries in the form of “cold burns”. (Liquid CO2 will form snow particles when expanded.) Correct protective equipment (e.g., gloves, goggles) should therefore be used.
Oxidation. The hazard of oxidation is most evident with oxygen, which is one of the most important compressed gases. Oxygen will not burn on its own, but is necessary for combustion. Normal air contains 21% oxygen by volume.
All combustible materials will ignite more easily and burn more vigorously when the oxygen concentration is increased. This is noticeable with even a slight increase in oxygen concentration, and utmost care must be taken to avoid oxygen enrichment in the working atmosphere. In confined spaces small oxygen leaks may lead to dangerous enrichment.
The danger with oxygen increases with increasing pressure to the point where many metals will burn vigorously. Finely divided materials may burn in oxygen with explosive force. Clothing that is saturated with oxygen will burn very rapidly and be difficult to extinguish.
Oil and grease have always been regarded as dangerous in combination with oxygen. The reason is that they react readily with oxygen, their existence is common, the ignition temperature is low and the developed heat may start a fire in the underlying metal. In high-pressure oxygen equipment the necessary ignition temperature may easily be reached by the compression shock that may result from rapid valve opening (adiabatic compression).
Therefore:
Flammability. The flammable gases have flashpoints below room temperature and will form explosive mixtures with air (or oxygen) within certain limits known as the lower and upper explosion limits.
Escaping gas (also from safety valves) may ignite and burn with a shorter or longer flame depending on the pressure and amount of gas. The flames may again heat nearby equipment, which may burn, melt or explode. Hydrogen burns with an almost invisible flame.
Even small leaks may cause explosive mixtures in confined spaces. Some gases, such as liquefied petroleum gases, mostly propane and butane, are heavier than air and are difficult to vent away, as they will concentrate in the lower parts of buildings and “float” through channels from one room to another. Sooner or later, the gas may reach an ignition source and explode.
Ignition may be caused by hot sources, but also by electrical sparks, even very small ones.
Acetylene takes a special place among the combustible gases because of its properties and wide use. If heated, the gas may start to decompose with the development of heat even without the presence of air. If allowed to proceed, this may lead to cylinder explosion.
Acetylene cylinders are, for safety reasons, filled with a highly porous mass which also contains a solvent for the gas. Outside heating from a fire or welding torch, or in certain cases internal ignition by strong backfires from welding equipment, may start a decomposition within the cylinder. In such cases:
Acetylene cylinders in several countries are equipped with fuse (melting) plugs. These will release the gas pressure when they melt (usually at about 100 °C) and prevent cylinder explosion. At the same time there is a risk that the released gas may ignite and explode.
Common precautions to observe in respect of combustible gases are as follows:
Toxicity. Certain gases, if not the most common, may be toxic. At the same time, they may be irritating or corrosive to the skin or eyes.
Persons who handle these gases should be well trained and aware of the danger involved and the necessary precautions. The cylinders should be stored in a well ventilated area. No leaks should be tolerated. Suitable protective equipment (gas masks or breathing equipment) should be used.
Inert gases. Gases such as argon, carbon dioxide, helium and nitrogen are widely used as protective atmospheres to prevent unwanted reactions in welding, chemical plants, steel works and so on. These gases are not labelled as being hazardous, and serious accidents may happen because only oxygen can support life.
When any gas or gas mixture displaces the air so that the breathing atmosphere becomes deficient in oxygen, there is a danger of asphyxiation. Unconsciousness or death may result very rapidly when there is little or no oxygen, and there is no warning effect.
Confined spaces where the breathing atmosphere is deficient in oxygen must be ventilated before entering. When breathing equipment is used, the person entering must be supervised. Breathing equipment must be used even in rescuing operations. Normal gas masks give no protection against oxygen deficiency. The same precaution must be observed with large, permanent firefighting installations, which are often automatic, and those who may be present in such areas should be warned of the danger.
Cylinder filling. Cylinder filling involves the operation of high-pressure compressors or liquid pumps. The pumps may operate with cryogenic (very low-temperature) liquids. The filling stations may also incorporate large storage tanks of liquid gases in a pressurized and/or deeply refrigerated state.
The gas filler should check that the cylinders are in acceptable condition for filling, and should fill the correct gas in not more than the approved amount or pressure. The filling equipment should be designed and tested for the given pressure and type of gas, and protected by safety valves. Cleanliness and material requirements for oxygen service must be observed strictly. When filling flammable or toxic gases, special attention should be given to the safety of the operators. The primary requirement is good ventilation combined with correct equipment and technique.
Cylinders which are contaminated with other gases or liquids by the customers constitute a special hazard. Cylinders with no residual pressure may be purged or evacuated before filling. Special care should be taken to ensure that medical gas cylinders are free from any harmful matter.
Transport. Local transport tends to become more mechanized through the use of fork-lift trucks and so on. Cylinders should be transported only with the caps on and secured against falling from the vehicles. Cylinders must not be dropped from trucks directly onto the ground. For hoisting with cranes, suitable lifting cradles should be used. Magnetic lifting devices or caps with uncertain threads should not be used for lifting cylinders.
When cylinders are manifolded into larger packages, great care should be taken to avoid strain on the connections. Any hazard will be increased because of the greater amount of gas involved. It is good practice to divide larger units into sections and to place shut-off valves where they can be operated in any emergency.
The most frequently occurring accidents in cylinder handling and transport are injuries caused by the hard, heavy and difficult-to-handle cylinders. Safety shoes should be worn. Trolleys should be provided for longer transport of single cylinders.
In international transport codes, compressed gases are classified as dangerous goods. These codes give details about which gases may be transported, cylinder requirements, allowed pressure, marking and so on.
Identification of content. The most important requirement for safe handling of compressed gases is the correct identification of the gas content. Stamping, labelling, stencilling and colour marking are the means that are used for this purpose. Certain requirements for marking are covered in International Organization for Standardization (ISO) standards. The colour marking of medical gas cylinders follows the ISO standards in most countries. Standardized colours are also used in many countries for other gases, but this is not a sufficient identification. In the end only the written word can be regarded as a proof of the cylinder content.
Standardized valve outlets. The use of a standardized valve outlet for a certain gas or group of gases strongly reduces the chance of connecting cylinders and equipment made for different gases. Adapters should therefore not be used, as this sets aside the safety measures. Only normal tools and no excessive force should be used when making connections.
Safe Practice for Users
The safe use of compressed gases entails applying the safety principles outlined in this chapter and the ILO Code of Practice Safety in the Use of Chemicals at Work (ILO 1993). This is not possible unless the user has some basic knowledge of the gas and the equipment that he or she is handling. In addition the user should take the following precautions:
Occupational exposure to hazardous chemicals in laboratories 1990 OSHA Laboratory Standard 29 CFR 1910.1450
The following description of a laboratory chemical hygiene plan corresponds with Section (e:1-4), Chemical hygiene plan-General, of the 1990 OSHA Laboratory Standard. This plan should be made readily available to employees and employee representatives.The chemical hygiene plan shall include each of the following elements and shall indicate specific measures that the employer will take to ensure laboratory employee protection:
(a) establishment of a designated area;
(b) use of containment devices such as fume hoods or glove boxes;
(c) procedures for safe removal of contaminated waste; and
(d) decontamination procedures.
The employer shall review and evaluate the effectiveness of the chemical hygiene plan at least annually and update it as necessary.
Setting up a Safe and Healthy Laboratory
A laboratory can only be safe and hygienic if the work practices and procedures that are followed there are safe and hygienic. Such practices are fostered by first giving responsibility and authority for laboratory safety and chemical hygiene to a laboratory safety officer who, together with a safety committee of laboratory personnel, decides what tasks must be accomplished and assigns responsibility for carrying out each of them.
The safety committee’s specific tasks include conducting periodic laboratory inspections and summarizing the results in a report submitted to the laboratory safety officer. These inspections are properly done with a checklist. Another important aspect of safety management is periodic inspections of safety equipment to ensure that all equipment is in good working order and in designated locations. Before this can be done, an annual inventory of all the safety equipment must be made; this includes a brief description, including size or capacity and manufacturer. Of no less importance is a semiannual inventory of all laboratory chemicals, including proprietary products. These should be classified into groups of chemically similar substances and also classified according to their fire hazard. Another essential safety classification depends on the degree of hazard associated with a substance, since the treatment a substance receives is directly related to the harm it can cause and the ease with which the harm is unleashed. Each chemical is put into one of three hazard classes chosen on the basis of grouping according to the order of magnitude of risk involved; they are:
Ordinary hazard substances are those that are relatively easily controlled, are familiar to laboratory personnel and present no unusual risk. This class ranges from innocuous substances such as sodium bicarbonate and sucrose to concentrated sulphuric acid, ethylene glycol and pentane.
High-hazard substances present much greater hazards than ordinary hazards. They require special handling or, sometimes, monitoring, and present high fire or explosion hazards or severe health risks. In this group are chemicals that form unstable explosive compounds on standing (e.g., hydroperoxides formed by ethers) or substances that have high acute toxicities (e.g., sodium fluoride, which has an oral toxicity of 57 mg/kg in mice), or that have chronic toxicities such as carcinogens, mutagens or teratogens. Substances in this group often have the same kind of hazard as those in the group that follows. The difference is one of degree—those in group 3, the extremely hazardous materials, have either a greater intensity of hazard, or their order of magnitude is much greater, or the dire effects can be released far more easily.
Extremely hazardous materials, when not handled correctly, can very readily cause a serious accident resulting in severe injury, loss of life or extensive property damage. Extreme caution must be exercised in dealing with these substances. Examples of this class are nickel tetracarbonyl (a volatile, extremely poisonous liquid, the vapours of which have been lethal in concentrations as low as 1 ppm) and triethylaluminium (a liquid that spontaneously ignites on exposure to air and reacts explosively with water).
One of the most important of the safety committee’s tasks is to write a comprehensive document for the laboratory, a laboratory safety and chemical hygiene plan, that fully describes its safety policy and standard procedures for carrying out laboratory operations and fulfilling regulatory obligations; these include guidelines for working with substances that may fall into any of the three hazard categories, inspecting safety equipment, responding to a chemical spill, chemical waste policy, standards for laboratory air quality and any recordkeeping required by regulatory standards. The laboratory safety and chemical hygiene plan must be kept in the laboratory or must be otherwise easily accessible to its workers. Other sources of printed information include: chemical information sheets (also called material safety data sheets, MSDSs), a laboratory safety manual, toxicological information and fire hazard information. The inventory of laboratory chemicals and three associated derivative lists (classification of chemicals according to chemical class, fire safety class and the three degrees of hazard) must also be kept with these data.
A file system for records of safety-related activities is also required. It is not necessary that this file either be in the laboratory or be immediately accessible to laboratory workers. The records are mainly for the use of laboratory personnel who oversee laboratory safety and chemical hygiene and for the perusal of regulatory agency inspectors. It should thus be easily available and kept up to date. It is advisable that the file be kept outside the laboratory in order to reduce the possibility of its destruction in the event of a fire. The documents on file should include: records of laboratory inspections by the safety committee, records of inspections by any local regulatory agencies including fire departments and state and federal agencies, records dealing with hazardous waste disposal, records of taxes levied on various classes of hazardous waste, where applicable, a second copy of the inventory of laboratory chemicals, and copies of other pertinent documents dealing with the facility and its personnel (e.g., records of attendance of personnel at annual laboratory safety sessions).
Causes of Illness and Injury in the Laboratory
Measures for the prevention of personal injury, illness and anxiety are an integral part of the plans for the day-to-day operation of a well-run laboratory. The people who are affected by unsafe and unhygienic conditions in a laboratory include not only those who work in that laboratory but also neighbouring personnel and those who provide mechanical and custodial services. Since personal injuries in laboratories stem largely from inappropriate contact between chemicals and people, inappropriate mixing of chemicals or inappropriate supply of energy to chemicals, protecting health entails preventing such undesirable interactions. This, in turn, means suitably confining chemicals, combining them properly and closely regulating the energy supplied to them. The main kinds of personal injury in the laboratory are poisoning, chemical burns and injury resulting from fires or explosions. Fires and explosions are a source of thermal burns, lacerations, concussions and other severe bodily harm.
Chemical attack on the body. Chemical attack takes place when poisons are absorbed into the body and interfere with its normal function through disturbance of metabolism or other mechanisms. Chemical burns, or the gross destruction of tissue, usually occur by contact with either strong acids or strong alkalis. Toxic materials that have entered the body by absorption through the skin, eyes or mucous membranes, by ingestion or by inhalation, can cause systemic poisoning, usually by being spread via the circulatory system.
Poisoning is of two general types—acute and chronic. Acute poisoning is characterized by ill effects appearing during or directly after a single exposure to a toxic substance. Chronic poisoning becomes evident only after the passage of time, which may take weeks, months, years or even decades. Chronic poisoning is said to occur when each of these conditions is met: the victim must have been subjected to multiple exposures over long periods of time and to metabolically significant amounts of a chronic poison.
Chemical burns, usually encountered when liquid corrosives are spilled or splashed on the skin or in the eyes, also occur when those tissues come in contact with corrosive solids, ranging in size from powdery dusts to fairly large crystals, or with corrosive liquids dispersed in the air as mists, or with such corrosive gases as hydrogen chloride. The bronchial tubes, lungs, tongue, throat and epiglottis can also be attacked by corrosive chemicals in either the gaseous, liquid or solid states. Toxic chemicals also, of course, may be introduced into the body in any of these three physical states, or in the form of dusts or mists.
Injury through fires or explosions. Both fires or explosions may produce thermal burns. Some of the injuries caused by explosions, however, are particularly characteristic of them; they are injuries engendered either by the concussive force of the detonation itself or by such of its effects as glass fragments hurled through the air, causing loss of fingers or limbs in the first case, or skin lacerations or loss of vision, in the second.
Laboratory injuries from other sources. A third class of injuries may be caused neither by chemical attack nor by combustion. Rather they are produced by a miscellany of all other sources—mechanical, electrical, high-energy light sources (ultraviolet and lasers), thermal burns from hot surfaces, sudden explosive shattering of screw-capped glass chemical containers from the unexpected build-up of high internal gas pressures and lacerations from the sharp, jagged edges of newly broken glass tubing. Among the most serious sources of injury of a mechanical origin are tall, high-pressure gas cylinders tipping over and falling to the floor. Such episodes can injure legs and feet; in addition, should the cylinder stem break during the fall, the gas cylinder, propelled by the rapid, massive, uncontrolled escape of gas, becomes a deadly, undirected missile, a potential source of greater, more widespread harm.
Injury Prevention
Safety sessions and information dissemination. Injury prevention, dependent on performance of laboratory operations in a safe and prudent manner, is, in turn, dependent on laboratory workers being trained in correct laboratory methodology. Although they have received some of this training in their undergraduate and graduate education, it must be supplemented and reinforced by periodic laboratory safety sessions. Such sessions, which should emphasize understanding the physical and biological bases of safe laboratory practice, will enable laboratory workers to reject questionable procedures easily and to select technically sound methods as a matter of course. The sessions should also acquaint laboratory personnel with the kinds of data needed to design safe procedures and with sources of such information.
Workers must also be provided with ready access, from their work stations, to pertinent safety and technical information. Such materials should include laboratory safety manuals, chemical information sheets and toxicological and fire hazard information.
Prevention of poisoning and chemical burns. Poisoning and chemical burns have a common feature—the same four sites of entry or attack: (1) skin, (2) eyes, (3) mouth to stomach to intestines and (4) nose to bronchial tubes to lungs. Prevention consists in making these sites inaccessible to poisonous or corrosive substances. This is done by placing one or more physical barriers between the person to be protected and the hazardous substance or by ensuring that the ambient laboratory air is not contaminated. Procedures that use these methods include working behind a safety shield or using a fume hood, or utilizing both methods. The use of a glove box, of course, of itself affords a twofold protection. Minimization of injury, should contamination of tissue occur, is accomplished by removing the toxic or corrosive contaminant as quickly and completely as possible.
Prevention of acute poisoning and chemical burns in contrast with the prevention of chronic poisoning. Although the basic approach of isolation of the hazardous substance from the person to be protected is the same in preventing acute poisoning, chemical burns and chronic poisoning, its application must be somewhat different in preventing chronic poisoning. Whereas acute poisoning and chemical burns may be likened to massive assault in warfare, chronic poisoning has the aspect of a siege. Usually produced by much lower concentrations, exerting their influence through multiple exposures over long periods of time, its effects surface gradually and insidiously through sustained and subtle action. Corrective action involves either first detecting a chemical capable of causing chronic poisoning before any physical symptoms appear, or recognizing one or more aspects of a laboratory worker’s discomfort as possibly being physical symptoms connected with chronic poisoning. Should chronic poisoning be suspected, medical attention must be sought promptly. When a chronic poison is found at a concentration exceeding the allowable level, or even approaching it, steps must be taken either to eliminate that substance or, at the very least, to reduce its concentration to a safe level. Protection against chronic poisoning often requires that protective equipment be used for all or much of the workday; however, for reasons of comfort, the use of a glove box or a self-contained breathing apparatus (SCBA) is not always feasible.
Protection against poisoning or chemical burns. Protection against contamination of the skin by a particular splashed corrosive liquid or scattered poisonous airborne solid is best done by the use of safety gloves and a laboratory apron made of a suitable natural or synthetic rubber or polymer. The term suitable here is taken to mean a material which is neither dissolved, swelled nor in any other way attacked by the substance against which it must afford protection, nor should it be permeable to the substance. The use of a safety shield on the laboratory bench interposed between apparatus in which chemicals are being heated, reacted or distilled and the experimenter is a further safeguard against chemical burns and poisoning via skin contamination. Since the speed with which a corrosive or a poison is washed from the skin is a critical factor in preventing or minimizing the damage these substances can inflict, a safety shower, conveniently located in the laboratory, is an indispensable piece of safety equipment.
The eyes are best protected from splashed liquids by safety goggles or face shields. Airborne contaminants, in addition to gases and vapours, include solids and liquids when they are present in a finely subdivided state as dusts or mists. These are most effectively kept out of the eyes by conducting operations in a fume hood or glove box, although goggles afford some protection against them. To afford additional protection while the hood is being used, goggles may be worn. The presence of easily accessible eyewash fountains in the laboratory will often eliminate, and certainly will, at least, reduce eye damage through contamination by splashed corrosives or poisons.
The mouth to stomach to intestines route is usually connected with poisoning rather than with attack by corrosives. When toxic materials are ingested, it usually happens unwittingly through the chemical contamination of foods or cosmetics. Sources of such contamination are food stored in refrigerators with chemicals, food and beverages consumed in the laboratory, or lipstick kept or applied in the laboratory. Prevention of this kind of poisoning is done by avoiding practices known to cause it; this is feasible only when refrigerators to be used exclusively for food, and dining space outside of the laboratory, are made available.
The nose to bronchial tubes to lungs route, or respiratory route, of poisoning and chemical burns deals exclusively with airborne substances, whether gases, vapours, dusts or mists. These airborne materials may be kept from the respiratory systems of people within and outside of the laboratory by the concurrent practices of: (1) confining operations that either use or produce them to the fume hood (2) adjusting the laboratory air supply so that the air is changed 10 to 12 times per hour and (3) keeping the laboratory air pressure negative with respect to that of the corridors and rooms around it. Fume- or dust-producing operations that involve very bulky pieces of apparatus or containers the size of a 218-l drum, which are too large to be enclosed by an ordinary fume hood, should be done in a walk-in hood. In general, respirators or SCBA should not be used for any laboratory operations other than those of an emergency nature.
Chronic mercury poisoning, produced by the inhalation of mercury vapours, is occasionally found in laboratories. It is encountered when a pool of mercury that has accumulated in a hidden location—under floorboards, in drawers or a closet—has been emitting vapours over a long enough period of time to affect the health of laboratory personnel. Good laboratory housekeeping will avert this problem. Should a hidden source of mercury be suspected, the laboratory air must be checked for mercury either by the use of a special detector designed for the purpose or by sending an air sample for analysis.
Preventing fires and explosions and extinguishing fires. The principal cause of laboratory fires is the accidental ignition of flammable liquids. Flammable liquid is defined, in the fire safety sense, as being a liquid having a flashpoint of less than 36.7 °C. Ignition sources known to have caused this kind of laboratory fire include open flames, hot surfaces, electric sparks from switches and motors found in such equipment as stirrers, household-type refrigerators and electric fans, and sparks produced by static electricity. When ignition of a flammable liquid occurs, it takes place, not in the liquid itself, but above it, in the mixture of its vapours with air (when the concentration of vapour falls between certain upper and lower limits).
Preventing laboratory fires is accomplished by confining the vapours of flammables completely within the containers in which the liquids are kept or the apparatus in which they are used. If it is not possible to contain these vapours completely, their rate of escape should be made as low as possible and a continuous vigorous flow of air should be supplied to sweep them away, so as to keep their concentration at any given time well below the lower critical concentration limit. This is done both when reactions involving a flammable liquid are run in a fume hood and when drums of flammables are stored in safety solvent cabinets vented to an exhaust.
A particularly unsafe practice is the storage of such flammables as ethanol in a household-type refrigerator. These refrigerators will not keep vapours of stored flammable liquids from the sparks of its switches, motors and relays. No containers of flammables must ever be put in this type of refrigerator. This is especially true of open vessels and trays containing flammable liquids. However, even flammables in screw-capped bottles, kept in this type of refrigerator, have caused explosions, presumably by vapours leaking through a faulty seal or by the bottles breaking. Flammable liquids that require refrigeration must be kept only in explosion-proof refrigerators.
A significant source of fires that occur when large quantities of flammables are poured or siphoned from one drum to another is sparks produced through the accumulation of electric charge produced by a moving fluid. Spark generation of this sort can be prevented by electrically grounding both drums.
Most chemical and solvent fires that occur in the laboratory and are of manageable size, may be extinguished with either a carbon dioxide or dry-chemical type fire extinguisher. One or more 4.5 kg extinguishers of either kind should be supplied to a laboratory, according to its size. Certain special types of fires require other kinds of extinguishing agents. Many metal fires are put out with sand or graphite. Burning metal hydrides require graphite or powdered limestone.
When clothing is set afire in the laboratory, the flames must be put out quickly to minimize the injury caused by thermal burns. A wall-mounted wrap-around fire blanket extinguishes such fires effectively. It may be used for unassisted smothering of flames by the person whose clothing is on fire. Safety showers may also be used to extinguish these fires.
There are limits to the total volumes of flammable liquids that may be safely kept in a particular laboratory. Such limits, generally written into local fire codes, vary and depend on the materials of construction of the laboratory and on whether it is equipped with an automatic fire-extinguishing system. They usually range from about 55 to 135 litres.
Natural gas is often available from numbers of valves located throughout a typical laboratory. These are the most common sources of gas leaks, along with the rubber tubes and burners leading from them. Such leaks, when not detected soon after their onset, have led to severe explosions. Gas detectors, designed to indicate the level of gas concentration in the air, may be used to locate the source of such leakage quickly.
Prevention of injury from miscellaneous sources. Harm from tall, high-pressure gas cylinders falling, among the most familiar in this group of accidents, is avoided easily by strapping or chaining these cylinders securely to a wall or laboratory bench and putting cylinder caps on all unused and empty cylinders.
Most of the injuries from jagged edges of broken glass tubing are sustained through breakage while the tubing is being put into corks or rubber stoppers. They are avoided by lubricating the tube with glycerol and protecting the hands with leather work gloves.
Appendix A to 1910.1450—National Research Council recommendations concerning chemical hygiene in laboratories (non-mandatory)
The following guidelines concerning proper laboratory ventilation correspond with the information provided in Section C. The Laboratory Facility; 4. Ventilation - (a) General laboratory ventilation, Appendix A of the 1990 OSHA Laboratory Standard, 29 CFR 1910.1450.
Ventilation(a) General laboratory ventilation. This system should: Provide a source of air for breathing and for input to local ventilation devices; it should not be relied on for protection from toxic substances released into the laboratory; ensure that laboratory air is continually replaced, preventing increase of air concentrations of toxic substances during the working day; direct air flow into the laboratory from non-laboratory areas and out to the exterior of the building.
(b) Hoods. A laboratory hood with 2.5 linear feet (76 cm) of hood space per person should be provided for every 2 workers if they spend most of their time working with chemicals; each hood should have a continuous monitoring device to allow convenient confirmation of adequate hood performance before use. If this is not possible, work with substances of unknown toxicity should be avoided or other types of local ventilation devices should be provided.
(c) Other local ventilation devices. Ventilated storage cabinets, canopy hoods, snorkels, etc. should be provided as needed. Each canopy hood and snorkel should have a separate exhaust duct.
(d) Special ventilation areas. Exhaust air from glove boxes and isolation rooms should be passed through scrubbers or other treatment before release into the regular exhaust system. Cold rooms and warm rooms should have provisions for rapid escape and for escape in the event of electrical failure.
(e) Modifications. Any alteration of the ventilation system should be made only if thorough testing indicates that worker protection from airborne toxic substances will continue to be adequate.
(f) Performance. Rate: 4-12 room air changes/hour is normally adequate general ventilation if local exhaust systems such as hoods are used as the primary method of control.
(g) Quality. General air flow should not be turbulent and should be relatively uniform throughout the laboratory, with no high velocity or static areas; airflow into and within the hood should not be excessively turbulent; hood face velocity should be adequate (typically 60-100 lf/min) (152-254 cm/min).
(h) Evaluation. Quality and quantity of ventilation should be evaluated on installation, regularly monitored (at least every 3 months), and reevaluated whenever a change in local ventilation is made.
Incompatible Materials
Incompatible materials are a pair of substances that, on contact or mixing, produce either a harmful or potentially harmful effect. The two members of an incompatible pair may be either a pair of chemicals or a chemical and a material of construction such as wood or steel. The mixing or contact of two incompatible materials leads either to a chemical reaction or to a physical interaction that generates a large amount of energy. Specific harmful or potentially harmful effects of these combinations, which can ultimately lead to serious injury or damage to the health, include liberation of large amounts of heat, fires, explosions, production of a flammable gas or generation of a toxic gas. Since a fairly extensive variety of substances is usually found in laboratories, the occurrence of incompatibles in them is quite common and presents a threat to life and health if they are not handled correctly.
Incompatible materials are seldom mixed intentionally. Most often, their mixing is the result of a simultaneous accidental breaking of two adjacent containers. Sometimes it is the effect of leakage or dripping, or results from the mixing of gases or vapours from nearby bottles. Although in many cases in which a pair of incompatibles is mixed, the harmful effect is easily observed, in at least one instance, a not readily detectable chronic poison is formed. This occurs as the result of the reaction of formaldehyde gas from 37% formalin with hydrogen chloride that has escaped from concentrated hydrochloric acid to form the potent carcinogen bis(chloromethyl) ether. Other instances of not immediately detectable effects are the generation of odourless, flammable gases.
Keeping incompatibles from mixing through the simultaneous breaking of adjacent containers or through escape of vapours from nearby bottles is simple—the containers are moved far apart. The incompatible pair, however, must first be identified; not all such identifications are simple or obvious. To minimize the possibility of overlooking an incompatible pair, a compendium of incompatibles should be consulted and scanned occasionally to acquire an acquaintance with less familiar examples. Preventing a chemical from coming in contact with incompatible shelving material, through dripping or through a bottle breaking, is done by keeping the bottle in a glass tray of sufficient capacity to hold all of its contents.
Occupational health professionals have generally relied on the following hierarchy of control techniques to eliminate or minimize worker exposures: substitution, isolation, ventilation, work practices, personal protective clothing and equipment. Usually a combination of two or more of these techniques is applied. Although this article focuses primarily on the application of ventilation techniques, the other approaches are briefly discussed. They should not be ignored when attempting to control exposure to chemicals by ventilation.
The occupational health professional should always think of the concept of source-path-receiver. The primary focus should be on control at the source with control of the path the second focus. Control at the receiver should be considered the last choice. Whether it is during the start-up or design phases of a process or during the evaluation of an existing process, the procedure for control of exposure to air contaminants should start at the source and progress to the receiver. It is likely that all or most of these control strategies will need to be used.
Substitution
The principle of substitution is to eliminate or reduce the hazard by substituting non-toxic or less toxic materials or redesigning the process to eliminate escape of contaminants into the workplace. Ideally, substitute chemicals would be non-toxic or the process redesign would completely eliminate exposure. However, since this is not always possible the subsequent controls in the above hierarchy of controls are attempted.
Note that extreme care should be taken to assure that substitution does not result in a more hazardous condition. While this focus is on the toxicity hazard, the flammable and chemical reactivity of substitutes must also be considered when assessing this risk.
Isolation
The principle of isolation is to eliminate or reduce the hazard by separating the process emitting the contaminant from the worker. This is accomplished by completely enclosing the process or locating it a safe distance away from people. However, to accomplish this, the process may need to be operated and/or controlled remotely. Isolation is particularly useful for jobs requiring few workers and when control by other methods is difficult. Another approach is to perform hazardous operations on off shifts where fewer workers may be exposed. Sometimes the use of this technique does not eliminate exposure but reduces the number of people who are exposed.
Ventilation
Two types of exhaust ventilation are commonly employed to minimize airborne exposure levels of contaminants. The first is called general or dilution ventilation. The second is referred to as source control or local exhaust ventilation (LEV) and is discussed in more detail later in this article.
These two types of exhaust ventilation should not be confused with comfort ventilation, whose main purpose is to provide measured amounts of outdoor air for breathing and to maintain design temperature and humidity. Various types of ventilation are discussed elsewhere in this Encyclopaedia.
Work Practices
Work practices control encompasses the methods workers employ to perform operations and the extent to which they follow the correct procedures. Examples of this control procedure are given throughout this Encyclopaedia wherever general or specific processes are discussed. General concepts such as education and training, principles of management and social support systems include discussions of the importance of work practices in controlling exposures.
Personal Protective Equipment
Personal protective equipment (PPE) is considered the last line of defence for control of worker exposure. It encompasses the use of respiratory protection and protective clothing. It is frequently used in conjunction with other control practices, particularly to minimize the effects of unexpected releases or accidents. These issues are discussed in more detail in the chapter Personal protection.
Local Exhaust Ventilation
The most efficient and cost-effective form of contaminant control is LEV. This involves capture of the chemical contaminant at its source of generation. There are three types of LEV systems:
Enclosures are the preferable type of hood. Enclosures primarily are designed to contain the materials generated within the enclosure. The more complete the enclosure the more completely the contaminant will be contained. Complete enclosures are those that have no openings. Examples of complete enclosures include glove boxes, abrasive blasting cabinets and toxic gas storage cabinets (see figure 1, figure 2 and figure 3). Partial enclosures have one or more sides open but the source is still inside the enclosure. Examples of partial enclosures are a spray paint booth (see figure 4) and a laboratory hood. Often it might appear that the design of enclosures is more art than science. The basic principle is to design a hood with the smallest opening possible. The volume of air required is usually based on the area of all openings and maintaining an airflow velocity into the opening of 0.25 to 1.0 m/s. The control velocity chosen will depend on the operation’s characteristics, including the temperature and the degree to which the contaminant is propelled or generated. For complex enclosures, extreme care must be taken to assure that the exhaust flow is evenly distributed throughout the enclosure, particularly if the openings are distributed. Many enclosure designs are evaluated experimentally and if demonstrated to be effective are included as design plates in the American Conference of Governmental Industrial Hygienists’ industrial ventilation manual (ACGIH 1992).
Figure 1. Complete enclosure: Glovebox
Figure 2. Complete enclosure: Toxic gas storage cabinet
Figure 3. Complete enclosure: Abrasive blasting cabinet
Figure 4. Partial enclosure: Spray paint booth
Louis DiBernardinis
Often, total enclosure of the source is not possible, or is not necessary. In these cases, another form of local exhaust, an exterior or capture hood, can be used. An exterior hood prevents the release of toxic materials into the workplace by capturing or entraining them at or close to the source of generation, usually a work station or process operation. Considerably less air volume is usually required than for the partial enclosure. However, since the contaminant is generated outside the hood, it must be designed and used properly in order to be as effective as a partial enclosure. The most effective control is a complete enclosure.
To work effectively, the air inlet of an exterior hood must be of appropriate geometrical design and placed near the point of chemical release. The distance away will depend on the size and shape of the hood and the velocity of air needed at the generation source to capture the contaminant and bring it into the hood. Generally, the closer to the generation source, the better. Design face or slot velocities are typically in the range of 0.25 to 1.0 and 5.0 to 10.0 m/s, respectively. Many design guidelines exist for this class of exhaust hoods in Chapter 3 of the ACGIH manual (ACGIH 1992) or in Burgess, Ellenbecker and Treitman (1989). Two types of exterior hoods that find frequent application are “canopy” hoods and “slot” hoods.
Canopy hoods are used primarily for capture of gases, vapours and aerosols released in one direction with a velocity that can be used to aid capture. These are sometimes called “receiving” hoods. This type of hood is generally used when the process to be controlled is at elevated temperatures, to make use of the thermal updraft, or the emissions are directed upward by the process. Examples of operations that may be controlled in this manner include drying ovens, melting furnaces and autoclaves. Many equipment manufacturers recommend specific capture hood configurations that are suitable for their units. They should be consulted for advice. Design guidelines are also provided in the ACGIH manual, Chapter 3 (ACGIH 1992). For example, for an autoclave or oven where the distance between the hood and the hot source does not exceed approximately the diameter of the source or 1 m, whichever is smaller, the hood may be considered a low canopy hood. Under such conditions, the diameter or cross-section of the hot air column will be approximately the same as the source. The diameter or side dimensions of the hood therefore need only be 0.3 m larger than the source.
The total flow rate for a circular low canopy hood is
Qt=4.7 (Df)2.33 (Dt)0.42
where:
Qt = total hood air flow in cubic feet per minute, ft3/min
Df = diameter of hood, ft
Dt = difference between temperature of the hood source, and the ambient, °F.
Similar relationships exist for rectangular hoods and high canopy hoods. An example of a canopy hood can be seen in figure 5.
Figure 5. Canopy hood: Oven exhaust
Louis DiBernardinis
Slot hoods are used for control of operations that cannot be performed inside a containment hood or under a canopy hood. Typical operations include barrel filling, electroplating, welding and degreasing. Examples are shown in figure 6 and figure 7.
Figure 6. Exterior hood: Welding
Figure 7. Exterior hood: Barrel filling
Louis DiBernardinis
The required flow can be calculated from a series of equations determined empirically by the size and shape of the hood and the distance of the hood from the source. For example, for a flanged slot hood, the flow is determined by
Q = 0.0743LVX
where:
Q = total hood air flow, m3/min
L = the length of the slot, m
V = the velocity needed at the source to capture it, m/min
X = distance from the source to the slot, m.
The velocity needed at the source is sometimes called “capture velocity” and is usually between 0.25 and 2.5 m/s. Guidelines for selecting an appropriate capture velocity are provided in the ACGIH manual. For areas with excessive cross-drafts or for high-toxicity materials, the upper end of the range should be selected. For particulates, higher capture velocities will be necessary.
Some hoods may be some combination of enclosure, exterior and receiving hoods. For example, the spray paint booth shown in figure 4 is a partial enclosure that is also a receiving hood. It is designed to provide efficient capture of particles generated by making use of the particle momentum created by the rotating grinding wheel in the direction of the hood.
Care must be used in selecting and designing local exhaust systems. Considerations should include (1) ability to enclose the operation, (2) source characteristics (i.e., point source vs. widespread source) and how the contaminant is generated, (3) capacity of existing ventilation systems, (4) space requirements and (5) toxicity and flammability of contaminants.
Once the hood is installed, a routine monitoring and maintenance programme for the systems shall be implemented to assure its effectiveness in preventing exposure to workers (OSHA 1993). Monitoring of the standard laboratory chemical hood has become standardized since the 1970s. However, there is no such standardized procedure for other forms of local exhaust; therefore, the user must devise his or her own procedure. The most effective would be a continuous flow monitor. This could be as simple as a magnetic or water pressure gauge measuring static pressure at the hood (ANSI/AIHA 1993). The required hood static pressure (cm of water) will be known from the design calculations, and flow measurements can be made at the time of installation to verify them. Whether or not a continuous flow monitor is present, there should be some periodic evaluation of the hood performance. This can be done with smoke at the hood to visualize capture and by measuring total flow in the system and comparing that to the design flow. For enclosures it is usually advantageous to measure face velocity through the openings.
Personnel must also be instructed in the correct use of these types of hoods, particularly where the distance from the source and the hood can be easily changed by the user.
If local exhaust systems are designed, installed and used correctly they can be an effective and economical means of controlling toxic exposures.
GESTIS, the hazardous substance information system of the Berufsgenossenschaften (BG, statutory accident insurance carriers) in Germany, is presented here as a case study of an integrated information system for the prevention of risks from workplace chemical substances and products.
With the enactment and application of the regulation on hazardous substances in Germany in the mid-1980s, there was a huge increase in demand for data and information on hazardous substances. This demand had to be met directly by the BG within the framework of their industrial advisory and supervisory activities.
Specialists, including persons working with technical inspection services of the BG, workplace safety engineers, occupational physicians and those cooperating with expert panels, require specific health data. However, information regarding chemical hazards and the necessary safety measures is no less important for the layperson working with hazardous products. In the factory the effectiveness of work protection rules is what finally counts; it is therefore essential that relevant information be easily accessible to the factory owner, safety personnel, workers and, if appropriate, the work committees.
Against this background GESTIS was set up in 1987. Individual BG institutions had maintained databases mostly for more than 20 years. Within the framework of GESTIS, these databases were combined and supplemented with new components, including a “fact” database on substances and products, and information systems specific to particular branches of industry. GESTIS is organized on a central and peripheral basis, with comprehensive data for and about industry in Germany. It is arranged and classified according to branches of industry.
GESTIS consists of four core databases located centrally with the Berufsgenossenschaften Association and their Institute for Occupational Safety (BIA), plus peripheral, branch-specific information systems and documentation on occupational medicine surveillance and interfaces with external databases.
The target groups for hazardous substance information, such as safety engineers and occupational physicians, require different forms and specific data for their work. The form of information directed towards employees should be understandable and related to the specific handling of substances. Technical inspectors may require other information. Finally, the general public has a right to and an interest in workplace health information, including the identification and status of particular risks and the incidence of occupational disease.
GESTIS must be able to satisfy the information needs of various target groups by providing accurate information that focuses on practice.
Which data and information are needed?
Core information on substances and products
Hard facts must be the primary foundation. In essence these are facts about pure chemical substances, based on scientific knowledge and legal requirements. The scope of the subjects and information in safety data sheets, as, for example, defined by the European Union in EU Directive 91/155/EEC, correspond to the requirements of work protection in the factory and provide a suitable framework.
These data are found in the GESTIS central substance and product database (ZeSP), an online database compiled since 1987, with an emphasis on substances and in cooperation with the governmental labour inspection services (i.e., the hazardous substance databases of the states). The corresponding facts on products (mixtures) are established only on the basis of valid data on substances. In practice, a large problem exists because producers of safety data sheets often do not identify the relevant substances in preparations. The above-mentioned EU directive provides for improvements in the safety data sheets and requires more precise data on the listing of components (depending on the concentration levels).
The compilation of safety data sheets within GESTIS is indispensable for combining the producer data with substance data that are independent of the producers. This result occurs both through the branch-specific recording activities of the BG and through a project in cooperation with producers, who ensure that the safety data sheets are available, up-to-date and largely in data-processed form (see figure 1) in the ISI database (Information System Safety datasheets).
Figure 1.Collection and information centre for safety data sheets - basic structure
Because safety data sheets often do not adequately consider the special use of a product, specialists in branches of industry compile information on product groups (e.g., cooling lubricants for practical work protection in the factory) from producers’ information and substance data. Product groups are defined according to their use and their chemical risk potential. The information made available on product groups is independent of the data provided by producers on the composition of individual products because it is based on general formulae of composition. Thus, the user has access to a supplementary independent information source in addition to the safety data sheet.
A characteristic feature of ZeSP is the provision of information on the safe handling of hazardous substances in the workplace, including specific emergency and preventive measures. Furthermore, ZeSP contains comprehensive information on occupational medicine in a detailed, understandable and practice-related form (Engelhard et al. 1994).
In addition to the practice-oriented information outlined above, further data are needed in connection with national and international expert panels in order to undertake risk assessments for chemical substances (e.g., the EU Existing Chemicals Regulation).
For the evaluation of risk, data are required for the handling of hazardous substances, including (1) the use category of substances or products; (2) the amounts used in production and handling, and the number of persons working with or exposed to the hazardous substance or product; and (3) exposure data. These data can be obtained from hazardous substance registers at the factory level, which are obligatory under European hazardous substance law, for pooling at a higher level to form branch or general trade registers. These registers are becoming increasingly indispensable for providing the required background for political decision- makers.
Exposure data
Exposure data (i.e., measurement values of hazardous substance concentrations) are obtained through the BG within the framework of the BG measurement system for hazardous substances (BGMG 1993), to carry out compliance measurements in view of threshold values in the workplace. Their documentation is necessary for considering the level of technology when establishing threshold values and for risk analyses (e.g., in connection with the determination of risks in existing substances), for epidemiological studies and for evaluating occupational diseases.
The measurement values determined as part of workplace surveillance are therefore documented in the Documentation for Measurement Data on Hazardous Substances in the Workplace (DOK-MEGA). Since 1972 more than 800,000 measurement values have become available from over 30,000 firms. At present about 60,000 of these values are being added annually. Particular features of the BGMG include a quality assurance system, education and training components, standardized procedures for sampling and analysis, a harmonized measurement strategy on a legal basis and tools supported by data processing for information gathering, quality assurance and evaluation (figure 2).
Figure 2. BG measurement system for hazardous substances (BGMG) —cooperation between the BIA and the BG.
Exposure measurement values must be representative, repeatable and compatible. Exposure data from workplace surveillance in the BGMG are viewed strictly as “representative” of the individual factory situation, since the selection of measurement sites is carried out according to technical criteria in individual cases, not in accordance with statistical criteria. The question of representativeness arises, however, when measurement values for the same or a similar workplace, or even for entire branches of industry, have to be pooled statistically. Measurement data determined as part of surveillance activity generally give higher average values than data that have initially been collected to obtain a representative cross-section of a branch of industry.
For each measurement, differentiated recording and documentation of the relevant factory, process and sampling parameters are required so that the measured values can be combined in a way that is statistically reasonable, and evaluated and interpreted in a technically adequate manner.
In DOK-MEGA this goal is achieved on the following bases of data recording and documentation:
The BIA makes use of its experience with DOK-MEGA in a EU research project with representatives of other national exposure databases with the aim of improving the comparability of exposure and measurement results. In particular, an attempt is being made here to define core information as a basis for comparability and to develop a “protocol” for data documentation.
Health data
In addition to facts about chemical substances and products and about the results of exposure measurements, information is needed on the health effects of actual exposure to hazardous substances in the workplace. Adequate conclusions concerning occupational safety on and beyond the corporate level can be drawn only from an overall view of risk potential, actual risk and effects.
A further component of GESTIS is therefore the occupational disease documentation (BK-DOK), in which all cases of occupational disease reported since 1975 have been registered.
Essential to occupational disease documentation in the area of hazardous substances is the unambiguous, correct determination and recording of the relevant substances and products associated with each case. As a rule the determination is very time-consuming, but acquiring knowledge for prevention is impossible without the accurate identification of substances and products. Thus, for respiratory and skin diseases, which present a particular need for better understanding of possible causative agents, particular effort must be given to record substance and product use information as accurately as possible.
Literature data
The fourth component proposed for GESTIS was background information made available in the form of literature documents, so that the basic facts could be judged appropriately on the basis of current knowledge, and conclusions drawn. For this purpose an interface was developed with the literature database (ZIGUV-DOK), with a total of 50,000 references at present, of which 8,000 are on the subject of hazardous substances.
Linkage and Problem-oriented Preparation of Data
Information linkage
The components of GESTIS described above cannot stand in isolation if such a system is to be used efficiently. They require appropriate linkage possibilities, for example, between exposure data and cases of occupational disease. This linkage permits the creation of a truly integrated information system. The linkage occurs through core information that is available, coded in the standardized GESTIS coding system (see table 1).
Table 1. Standardized GESTIS code system
Object | Individual | Group |
Code | Code | |
Substance, product | ZVG central allocation number (BG) | SGS/PGS, substance/product group code (BG) |
Workplace | IBA sphere of activity of individual factory (BG) | AB sphere of activity (BIA) |
Exposed person | Activity (BIA, on the basis of the Federal Statistical Office’s systematic listing of occupations) |
Origins of codes appear in parentheses.
With the help of the GESTIS code both individual items of information can be linked to each other (e.g., measurement data from a particular workplace with a case of occupational disease that has occurred in the same or similar workplace) and statistically condensed, “typified” information (e.g., diseases related to particular work processes with average exposure data) can be obtained. With individual linkages of data (e.g., using the pension insurance number) the data protection laws must of course be strictly observed.
It is clear, therefore, that only a systematic coding system is capable of meeting these linkage requirements within the information system. Attention must, however, also be drawn to the possibility of linkage between various information systems and across national boundaries. These possibilities of linkage and comparison are crucially dependent on the use of internationally unified coding standards, if necessary in addition to national standards.
Preparation of problem-oriented and use-oriented information
The structure of GESTIS has at its centre the fact databases on substances and products, exposures, occupational diseases and literature, the data compiled both through specialists active at the centre and through the peripheral activities of the BG. For the application and use of the data, it is necessary to reach the users, centrally through publication in relevant journals (e.g., on the subject of the incidence of occupational disease), but also specifically through the advisory activities of the BG in their member firms.
For the most efficient possible use of information made available in GESTIS, the question arises regarding the problem-specific and target-group-specific preparation of facts as information. User-specific requirements are addressed in the fact databases on chemical substances and products—for example, in the depth of information or in the practice-oriented presentation of information. However, not all the specific requirements of possible users can be directly addressed in the fact databases. Target-group-specific and problem-specific preparation, if necessary supported by data processing, is required. Workplace-oriented information must be made available on the handling of hazardous substances. The most important data from the database must be extracted in a generally understandable and workplace-oriented form, for example, in the form of “workplace instructions”, which are prescribed in the occupational safety laws of many countries. Frequently too little attention is paid to this user-specific preparation of data as information for workers. Special information systems can prepare this information, but specialized information points which respond to individual queries also provide information and give the necessary support to firms. Within the framework of GESTIS this information- gathering and preparation proceeds, for instance, through branch-specific systems such as GISBAU (Hazardous Substances Information System of the Building Industry BG), GeSi (Hazardous Substances and Safety System), and through specialized information centres in the BG, in the BIA or in the association of the Berufsgenossenschaften.
GESTIS provides the relevant interfaces for data exchange and fosters cooperation by means of task-sharing:
Outlook
The emphasis of further development will be on prevention. In cooperation with the producers, plans encompass a comprehensive and up-to-date preparation of product data; the establishment of statistically determined workplace characteristic values derived from the exposure measurement data and from the substance-specific and product-specific documentation; and an evaluation in the occupational disease documentation.
A systematic approach to safety requires an efficient flow of information from the suppliers to the users of chemicals on potential hazards and correct safety precautions. In addressing the need for a written hazard communication programme, the ILO Code of Practice Safety in the Use of Chemicals at Work (ILO 1993) states, “The supplier should provide an employer with essential information about hazardous chemicals in the form of a chemical safety data sheet.” This chemical safety data sheet or material safety data sheet (MSDS) describes the hazards of a material and provides instructions on how the material can be safely handled, used and stored. MSDSs are produced by the manufacturer or importer of hazardous products. The manufacturer must provide distributors and other customers with MSDSs upon first purchase of a hazardous product and if the MSDS changes. Distributors of hazardous chemicals must automatically provide MSDSs to commercial customers. Under the ILO Code of Practice, workers and their representatives should have a right to an MSDS and to receive the written information in forms or languages they easily understand. Because some of the required information might be intended for specialists, further clarification may be needed from the employer. The MSDS is only one source of information on a material and, therefore, it is best used along with technical bulletins, labels, training and other communications.
The requirements for a written hazard communication programme are outlined in at least three major international directives: the US Occupational Safety and Health Administration (OSHA) Hazard Communication Standard, Canada’s Workplace Hazardous Materials Information System (WHMIS) and the European Community’s Commission Directive 91/155/EEC. In all three directives, the requirements for preparing a complete MSDS are established. Criteria for the data sheets include information about the identity of the chemical, its supplier, classification, hazards, safety precautions and the relevant emergency procedures. The following discussion details the type of required information included in the 1992 ILO Code of Practice Safety in the Use of Chemicals at Work. While the Code is not intended to replace national laws, regulations or accepted standards, its practical recommendations are intended for all those who have a responsibility for ensuring the safe use of workplace chemicals.
The following description of chemical safety data sheet content corresponds with section 5.3 of the Code:
Chemical safety data sheets for hazardous chemicals should give information about the identity of the chemical, its supplier, classification, hazards, safety precautions and the relevant emergency procedures.
The information to be included should be that established by the competent authority for the area in which the employer’s premises are located, or by a body approved or recognized by that competent authority. Details of the type of information that should be required are given below.
(a) Chemical product and company identification
The name should be the same as that used on the label of the hazardous chemical, which may be the conventional chemical name or a commonly used trade name. Additional names may be used if these help identification. The full name, address and telephone number of the supplier should be included. An emergency telephone number should also be given, for contact in the event of an emergency. This number may be that of the company itself or of a recognized advisory body, so long as either can be contacted at all times.
(b) Information on ingredients (composition)
The information should allow employers to identify clearly the risks associated with a particular chemical so that they may conduct a risk assessment, as outlined in section 6.2 (Procedures for assessment) of this code. Full details of the composition should normally be given but may not be necessary if the risks can be properly assessed. The following should be provided except where the name or concentration of an ingredient in a mixture is confidential information which can be omitted in accordance with section 2.6:
(c) Hazard identification
The most important hazards, including the most significant health, physical and environmental hazards, should be stated clearly and briefly, as an emergency overview. The information should be compatible with that shown on the label.
(d) First-aid measures
First-aid and self-help measures should be carefully explained. Situations where immediate medical attention is required should be described and the necessary measures indicated. Where appropriate, the need for special arrangements for specific and immediate treatment should be emphasized.
(e) Firefighting measures
The requirements for fighting a fire involving a chemical should be included; for example:
Information should also be given on the properties of the chemical in the event of fire and on special exposure hazards as a result of combustion products, as well as the precautions to be taken.
(f) Accidental release measures
Information should be provided on the action to be taken in the event of an accidental release of the chemical. The information should include:
(g) Handling and storage
Information should be given about conditions recommended by the supplier for safe storage and handling, including:
(h) Exposure controls and personal protection
Information should be given on the need for personal protective equipment during use of a chemical, and on the type of equipment that provides adequate and suitable protection. Where appropriate, a reminder should be given that the primary controls should be provided by the design and installation of any equipment used and by other engineering measures, and information provided on useful practices to minimize exposure of workers. Specific control parameters such as exposure limits or biological standards should be given, along with recommended monitoring procedures.
(i) Physical and chemical properties
A brief description should be given of the appearance of the chemical, whether it is a solid, liquid or gas, and its colour and odour. Certain characteristics and properties, if known, should be given, specifying the nature of the test to determine these in each case. The tests used should be in accordance with the national laws and criteria applying at the employer’s workplace and, in the absence of national laws or criteria, the test criteria of the exporting country should be used as guidance. The extent of the information provided should be appropriate to the use of the chemical. Examples of other useful data include:
(j) Stability and reactivity
The possibility of hazardous reactions under certain conditions should be stated. Conditions to avoid should be indicated, such as:
Where hazardous decomposition products are given off, these should be specified along with the necessary precautions.
(k) Toxicological information
This section should give information on the effects on the body and on potential routes of entry into the body. Reference should be made to acute effects, both immediate and delayed, and to chronic effects from both short- and long-term exposure. Reference should also be made to health hazards as a result of possible reaction with other chemicals, including any known interactions, for example, resulting from the use of medication, tobacco and alcohol.
(l) Ecological information
The most important characteristics likely to have an effect on the environment should be described. The detailed information required will depend on the national laws and practice applying at the employer’s workplace. Typical information that should be given, where appropriate, includes the potential routes for release of the chemical which are of concern, its persistence and degradability, bioaccumulative potential and aquatic toxicity, and other data relating to ecotoxicity (e.g., effects on water treatment works).
(m) Disposal considerations
Safe methods of disposal of the chemical and of contaminated packaging, which may contain residues of hazardous chemicals, should be given. Employers should be reminded that there may be national laws and practices on the subject.
(n) Transport information
Information should be given on special precautions that employers should be aware of or take while transporting the chemical on or off their premises. Relevant information given in the United Nations Recommendations on the Transport of Dangerous Goods and in other international agreements may also be included.
(o) Regulatory information
Information required for the marking and labelling of the chemical should be given here. Specific national regulations or practices applying to the user should be referred to. Employers should be reminded to refer to the requirements of national laws and practices.
(p) Other information
Other information which may be important to workers’ health and safety should be included. Examples are training advice, recommended uses and restrictions, references, and sources of key data for compiling the chemical safety data sheet, the technical contact point and date of issue of the sheet.
3.1. General
3.1.1. The competent authority, or a body approved or recognised by the competent authority, should establish systems and specific criteria for classifying a chemical as hazardous and should progressively extend these systems and their application. Existing criteria for classification established by other competent authorities or by international agreement may be followed, if they are consistent with the criteria and methods outllined in this code, and this is encouraged where it may assist uniformity of approach. The results of the work of the UNEP/ILO/WHO International Programme on Chemical Safety (IPCS) coordinating group for the harmonisation of classification of chemicals should be considered when appropriate. The responsibilities and role of competent authorities concerning classification systems are set out in paragraphs 2.1.8 (criteria and requirements), 2.1.9 (consolidated list) and 2.1.10 (assessment of new chemicals).
3.1.2. Suppliers should ensure that chemicals they supplied have been classified or that they have been identified and their properties assessed (see paragraphs 2.4.3 (assessment) and 2.4.4 (classification)).
3.1.3. Manufacturers or importers, unless exempted, should give to the competent authority information about chemical elements and compounds not yet included in the consolidated classification list compiled by the competent authority, prior to their use at work (see paragraph 2.1.10 (assessment of new chemicals)).
3.1.4. The limited quantities of a new chemical required for research and development purposes may be produced by, handled in, and transported between laboratories and pilot plant before all hazards of this chemical are known in accordance with national laws and regulations. All available information found in literature or known to the employer from his or her experience with similar chemicals and applications should be fully taken into account, and adequate protection measures should be applied, as if the chemical were hazardous. The workers involved must be informed about the actual hazard information as it becomes known.
3.2. Criteria for classification
3.2.1. The criteria for the classification of chemicals should be based upon their intrinsic health and physical hazards, including:
3.3. Method of classification
3.3.1. The classification of chemicals should be based on available sources of information, e.g.:
3.3.2. Certain classification systems in use may be limited to particular classes of chemicals only. An example is the WHO Recommended classification of pesticides by hazard and guidelines to classification, which classifies pesticides by degree of toxicity only and principally by acute risks to health. Employers and workers should understand the limitations of any such system. Such systems can be useful to complement a more generally applicable system.
3.3.3. Mixtures of chemicals should be classified based on the hazards exhibited by the mixtures themselves. Only if mixtures have not been tested as a whole should they be classified on the basis of intrinsic hazards of their component chemicals.
Source: ILO 1993, Chapter 3.
Adapted from 3rd edition, Encyclopaedia of Occupational Health and Safety. Revision includes information from A. Bruusgaard, L.L. Cash, Jr., G. Donatello, V. D’Onofrio, G. Fararone, M. Kleinfeld, M. Landwehr, A. Meiklejohn, J.A. Pendergrass, S.A. Roach, T.A. Roscina, N.I. Sadkovskaja and R. Stahl.
Minerals are used in ceramics, glass, jewellery, insulation, stone carving, abrasives, plastics and numerous other industries in which they present primarily an inhalation hazard. The amount and type of impurities within the minerals may also determine the potential hazard associated with inhalation of the dust. The major concern during mining and production is the presence of silica and asbestos. The silica content in different rock formations, such as sandstone, feldspars, granite and slate, may vary from 20% to nearly 100%. It is therefore imperative that worker exposure to dust concentrations be kept to a minimum by the implementation of strict dust-control measures.
Improved engineering controls, wet drilling, exhaust ventilation and remote handling are recommended to prevent the development of lung disease in mineral workers. Where effective engineering controls are not possible, workers should wear approved respiratory protection, including the proper selection of respirators. Where possible, industrial substitution of less hazardous agents can reduce occupational exposure. Finally, the education of workers and employers regarding the hazards and proper control measures is an essential component of any prevention programme.
Regular medical examinations of mineral-dust-exposed workers should include evaluations for respiratory symptoms, lung function abnormalities and neoplastic disease. Workers showing the first signs of lung changes should be assigned to other jobs entailing no dust hazards. In addition to individual reports of illness, data from groups of workers should be collected for prevention programmes. The chapter Respiratory system provides more detail on the health effects of several of the minerals described here.
Apatite (Calcium Phosphate)
Occurrence and uses. Apatite is a natural calcium phosphate, usually containing fluorine. It occurs in the earth’s crust as phosphate rock, and it is also the chief component of the bony structure of teeth. Deposits of apatite are located in Canada, Europe, the Russian Federation and the United States.
Apatite is used in laser crystals and as a source of phosphorus and phosphoric acid. It is also employed in the manufacture of fertilizers.
Health hazards. Skin contact, inhalation or ingestion may cause irritation of skin, eyes, nose, throat or gastric system. Fluorine may be present in the dust and may cause toxic effects.
Asbestos
Occurrence and uses. Asbestos is a term used to describe a group of naturally occurring fibrous minerals which are widely distributed throughout the world. The asbestos minerals fall into two groups—the serpentine group, which includes chrysotile, and the amphiboles, which include crocidolite, tremolite, amosite and anthophyllite. Chrysotile and the various amphibole asbestos minerals differ in crystalline structure, in chemical and surface characteristics, and in the physical characteristics of their fibres.
The industrial features which have made asbestos so useful in the past are the high tensile strength and flexibility of the fibres, and their resistance to heat and abrasion and to many chemicals. There are many manufactured products which contain asbestos, including construction products, friction materials, felts, packings and gaskets, floor tiles, paper, insulation and textiles.
Health hazards. Asbestosis, asbestos-related pleural disease, malignant mesothelioma and lung cancer are specific diseases associated with exposure to asbestos dust. The fibrotic changes which characterize the pneumoconiosis, asbestosis, are the consequence of an inflammatory process set up by fibres retained in the lung. Asbestos is discussed in the chapter Respiratory system.
Bauxite
Occurrence and uses. Bauxite is the principal source of aluminium. It consists of a mixture of minerals formed by the weathering of aluminium-bearing rocks. Bauxites are the richest form of these weathered ores, containing up to 55% alumina. Some lateritic ores (containing higher percentages of iron) contain up to 35% Al2O3. The commercial deposits of bauxite are mainly gibbsite (Al2O3 3H2O) and boehmite (Al2O3 H2O), and are found in Australia, Brazil, France, Ghana, Guinea, Guyana, Hungary, Jamaica and Surinam. Gibbsite is more readily soluble in sodium hydroxide solutions than boehmite, and is therefore preferred for alumina production.
Bauxite is extracted by open-cast mining. The richer ores are used as mined. The lower-grade ores may be upgraded by crushing and washing to remove clay and silica waste.
Health hazards. Severe pulmonary disability has been reported in workers employed on smelting bauxite that is combined with coke, iron and very small amounts of silica. The affliction is known as “Shaver’s disease”. Because silica contamination of aluminium-containing ores is common, the health hazards associated with the presence of free crystalline silica in bauxite ores must be considered an important causal factor.
Clays (Hydrated Aluminium Silicates)
Occurrence and uses. Clay is a malleable plastic material formed by the weathered disintegration residues of argillaceous silicate rock; it usually contains 15 to 20% water and is hygroscopic. It occurs as a sediment in many geological formations in all parts of the world and contains in varying amounts feldspars, mica and admixtures of quartz, calcspar and iron oxide.
The quality of clay depends on the amount of alumina in it—for example, a good porcelain clay contains about 40% alumina, and the silica content is as low as 3 to 6%. On average the quartz content of clay deposits is between 10 and 20%, but at worst, where there is less alumina than usual, the quartz content may be as high as 50%. Content may vary in a deposit, and separation of grades may take place in the pit. In its plastic state, clay can be moulded or pressed, but when fired it becomes hard and retains the shape into which it has been formed.
Clay is often extracted in open-cast pits but sometimes in underground mines. In open-cast pits the method of extraction depends on the quality of the material and the depth of the deposit; sometimes the conditions require the use of hand-operated pneumatic tools, but, wherever possible, mining is mechanized, using excavators, power shovels, clay cutters, deep digging machines and so on. The clay is taken to the surface by truck or cable transport. The clay brought to the surface may be subjected to preliminary processing before dispatch (drying, crushing, pugging, mixing and so on) or it may be sold whole (see the chapter Mining and quarrying). Sometimes, as in many brickyards, the clay pit may be adjacent to the factory where the finished articles are made.
Different types of clay form the basic material in the manufacture of pottery, bricks and tiles, and refractories. Clay may be used without any processing in dam construction; in situ, it sometimes serves as a cover for gas stored in lower stratum. Appropriate ventilation and engineering controls are required.
Health hazards. Clays usually contain large amounts of free silica, and chronic inhalation can cause silicosis. Skin contact with wet clay may cause skin drying and irritation. There is a silicosis risk to underground workers where there is mechanized mining of clay with a high quartz content and little natural moisture. Here the decisive factor is not merely the quartz content but also the natural dampness: if the moisture level is less than 12%, much fine dust must be expected in mechanical extraction.
Coal
Occurrence and uses. Coal is a natural, solid, combustible material formed from prehistoric plant life. It occurs in layers or veins in sedimentary rocks. Conditions suitable for the natural formation of coal occurred between 40 and 60 million years ago in the Tertiary Age (brown-coal formation) and over 250 million years ago in the Carboniferous Age (bituminous-coal formation), when swampland forests thrived in a hot climate and then gradually subsided during ensuing geological movements. The main deposits of brown coal are found in Australia, eastern Europe, Germany, the Russian Federation and the United States. Major reserves of bituminous coal are located in Australia, China, India, Japan, the Russian Federation and the United States.
Coal is an important source of chemical raw materials. Pyrolysis or destructive distillation yields coal tar and hydrocarbon gases, which can be upgraded by hydrogenation or methanation to synthetic crude oil and fuel gas. Catalytic hydrogenation yields hydrocarbon oils and gasoline. Gasification produces carbon monoxide and hydrogen (synthetic gas), from which ammonia and other products can be made. While in 1900, 94% of the world’s energy requirements were met by coal and only 5% by petroleum and natural gas, coal has been increasingly replaced by liquid and gaseous fuels throughout the world.
Health hazards. Hazards of mining and of coal dust are discussed in the chapters Mining and quarrying and Respiratory system.
Corundum (Aluminium Oxide)
Occurrence and uses. Corundum is one of the principal natural abrasives. Natural corundum and artificial corundum (alundum or artificial emery) are usually relatively pure. The artificial material is produced from bauxite by smelting in an electric furnace. Because of its hardness, corundum is used to shape metals, wood, glass and ceramics, by a process of grinding or polishing. Health hazards are discussed elsewhere in this Encyclopaedia.
Diatomaceous Earth (Diatomite, Kieselguhr, Infusorial Earth)
Occurrence and uses. Diatomaceous earth is a soft, bulky material composed of skeletons of small, prehistoric aquatic plants related to algae (diatoms). Certain deposits comprise up to 90% free amorphous silica. They have intricate geometric forms and are available as light-coloured blocks, bricks, powder and so on. Diatomaceous earth absorbs 1.5 to 4 times its weight of water and has a high oil absorption capacity. Deposits occur in Algeria, Europe, the Russian Federation and the western United States. Diatomaceous earth may be used in foundries, in paper coating, in ceramics and in the maintenance of filters, abrasives, lubricants and explosives. It is used as a filtering medium in the chemical industry. Diatomaceous earth also finds use as a drilling-mud thickener; an extender in paints, rubber and plastic products; and as an anti-caking agent in fertilizers.
Health hazards. Diatomaceous earth is highly respirable. For many industrial purposes diatomaceous earth is calcined at 800 to 1,000 ºC to produce a greyish-white powder called kieselguhr, which may contain 60% or more crystobalite. During mining and processing of diatomaceous earth, the risk of death from both respiratory diseases and lung cancer has been related to the inhalation of dust as well as to cumulative crystalline silica exposures, as discussed in the chapter Respiratory system.
Erionite
Occurrence and uses. Erionite is a crystalline, fibrous zeolite. Zeolites, a group of alumino-silicates found in the cavities of volcanic rocks, are used in the filtration of hard water and in the refining of oil. Erionite occurs in California, Nevada and Oregon in the United States, and in Ireland, Iceland, New Zealand and Japan.
Health hazards. Erionite is a known human carcinogen. Chronic inhalation may cause mesothelioma.
Feldspar
Occurrence and uses. Feldspar is a general name for a group of sodium, potassium, calcium and barium aluminium silicates. Commercially, feldspar usually refers to the potassium feldspars with the formula KAlSi3O8, usually with a little sodium. Feldspar occurs in the United States. It is used in pottery, enamel and ceramic ware, glass, soaps, abrasives, cements and concretes. Feldspar serves as a bond for abrasive wheels, and it finds use in insulating compositions, tarred roofing materials and fertilizers.
Health hazards. Chronic inhalation may cause silicosis due to the presence of substantial amounts of free silica. Feldspars may also contain irritating sodium oxide (soda spars), potassium oxide (potash spars), and calcium oxide (lime spars) in insoluble form. See the section “Silica” below.
Flint
Occurrence and uses. Flint is a crystalline form of native silica or quartz. It occurs in Europe and the United States. Flint is used as an abrasive, a paint extender and a filler for fertilizer. In addition, it finds use in insecticides, rubber, plastics, road asphalt, ceramics and chemical tower packing. Historically, flint has been an important mineral because it was used to make some of the first known tools and weapons.
Health hazards are related to the toxic properties of silica.
Fluorspar (Calcium Fluoride)
Occurrence and uses. Fluorspar is a mineral that contains 90 to 95% calcium fluoride and 3.5 to 8% silica. It is extracted by drilling and blasting. Fluorspar is a principal source of fluorine and its compounds. It is used as a flux in open hearth steel furnaces and in metal smelting. In addition, it finds use in the ceramics, paint and optical industries.
Health hazards. The hazards of fluorspar are due primarily to the harmful effects of the fluorine content and its silica content. Acute inhalation may cause gastric, intestinal, circulatory and nervous system problems. Chronic inhalation or ingestion may cause loss of weight and appetite, anaemia, and bone and teeth defects. Pulmonary lesions have been reported among persons inhaling dust containing 92 to 96% calcium fluoride and 3.5% silica. It appears that calcium fluoride intensifies the fibrogenic action of silica in the lungs. Cases of bronchitis and silicosis have been reported among fluorspar miners.
In the mining of fluorspar, dust control should be carefully enforced, including wet drilling, watering of loose rock, and exhaust and general ventilation. When heating fluorspar, there is also the hazard of hydrofluoric acid being formed, and the relevant safety measures should be applied.
Granite
Occurrence and uses. The coarse-grained igneous rock granite consists of quartz, feldspar and mica in shapeless interlocking grains. It finds use as crushed granite and as dimension granite. After it is crushed to the required size, granite may be used for concrete aggregate, road metal, railroad ballast, in filter beds, and for riprap (large chunks) in piers and breakwaters. The colors—pink, grey, salmon, red and white—are desirable for dimension granite. The hardness, uniform texture and other physical properties make dimension granite ideal for monuments, memorials, foundation blocks, steps and columns.
Large production of crushed granite comes mainly from California, with substantial amounts from the other US States of Georgia, North Carolina, South Carolina and Virginia. Major production areas of dimension granite in the United States include Georgia, Maine, Massachusetts, Minnesota, North Carolina, South Dakota, Vermont, and Wisconsin.
Health hazards. Granite is heavily contaminated with silica. Therefore, silicosis is a major health hazard in granite mining.
Graphite
Occurrence and uses. Graphite is found in almost every country of the world, but the majority of production of the natural ore is limited to Austria, Germany, Madagascar, Mexico, Norway, the Russian Federation and Sri Lanka. Most, if not all, natural graphite ores contain crystalline silica and silicates.
Lump graphite is found in veins which cross different types of igneous and metamorphic rock containing mineral impurities of feldspar, quartz, mica, pyroxine, zircon, rutile, apatite and iron sulphides. The impurities are often in isolated pockets in the veins of ore. Mining is commonly underground, with hand drills for selective mining of narrow veins.
Deposits of amorphous graphite are also underground, but usually in much thicker beds than the veins of lumps. Amorphous graphite is commonly associated with sandstone, slate, shale, limestone and adjunct minerals of quartz and iron sulphides. The ore is drilled, blasted and hand-loaded into wagons and brought to the surface for grinding and impurity separation.
Flake graphite is usually associated with metamorphosed sedimentary rock such as gneiss, schists and marbles. The deposits are often on or near the surface. Consequently, normal excavating equipment such as shovels, bulldozers and scarifiers are used in open-cast mining, and a minimum of drilling and blasting is necessary.
Artificial graphite is produced by the heating of coal or petroleum coke, and generally contains no free silica. Natural graphite is used in the manufacture of foundry linings, lubricants, paints, electrodes, dry batteries and crucibles for metallurgical purposes. The “lead” in pencils is also graphite.
Health hazards. Inhalation of carbon, as well as associated dusts, may occur during the mining and milling of natural graphite, and during the manufacture of artificial graphite. X-ray examinations of natural and artificial graphite workers have shown varying classifications of pneumoconioses. Microscopic histopathology has revealed pigment aggregates, focal emphysema, collagenous fibrosis, small fibrous nodules, cysts and cavities. The cavities have been found to contain an inky fluid in which graphite crystals were identified. Recent reports note that the materials implicated in exposures leading to severe cases with massive pulmonary fibrosis are likely to be mixed dusts.
Graphite pneumoconiosis is progressive even after the worker has been removed from the contaminated environment. Workers may remain asymptomatic during many years of exposure, and disability often comes suddenly. It is essential that periodic analyses are made of the raw ore and airborne dust for crystalline silica and silicates, with special attention to feldspar, talc and mica. Acceptable dust levels must be adjusted to accommodate the effect these disease-potentiating dusts may have on workers’ health.
In addition to being exposed to the physical hazards of mining, graphite workers may also face chemical hazards, such as hydrofluoric acid and sodium hydroxide used in graphite purification. Protection against the risks associated with these chemicals should be part of any health programme.
Gypsum (Hydrated Calcium Sulphate)
Occurrence and uses. Though it occurs throughout the world, gypsum is rarely found pure. Gypsum deposits may contain quartz, pyrites, carbonates and clayey and bituminous materials. It occurs in nature in five varieties: gypsum rock, gypsite (an impure, earthy form), alabaster (a massive, fine-grained translucent variety), satin spar (a fibrous silky form) and selenite (transparent crystals).
Gypsum rock may be crushed and ground for use in the dihydrate form, calcined at 190 to 200 ºC (thus removing part of the water of crystallization) to produce calcium sulphate hemihydrate or plaster of Paris, or completely dehydrated by calcining at over 600 ºC to produce anhydrous or dead-burned gypsum.
Ground dihydrate gypsum is used in the manufacture of Portland cement and artificial marble products; as a soil conditioner in agriculture; as a white pigment, filler or glaze in paints, enamels, pharmaceuticals, paper and so on; and as a filtration agent.
Health hazards. Workers employed in the processing of gypsum rock may be exposed to high atmospheric concentrations of gypsum dust, furnace gases and smoke. In gypsum calcining, workers are exposed to high environmental temperatures, and there is also the hazard of burns. Crushing, grinding, conveying and packaging equipment presents a danger of machinery accidents. The pneumoconiosis observed in gypsum miners has been attributed to silica contamination.
Dust formation in gypsum processing should be controlled by mechanization of dusty operations (crushing, loading, conveying and so on), addition of up to 2% by volume of water to gypsum prior to crushing, use of pneumatic conveyors with covers and dust traps, enclosure of dust sources and provision of exhaust systems for kiln openings and for conveyor transfer points. In the workshops containing the calcining kilns, it is advisable to face the walls and floors with smooth materials to facilitate cleaning. Hot piping, kiln walls and drier enclosures should be lagged to reduce the danger of burns and to limit heat radiation to the work environment.
Limestone
Occurrence and uses. Limestone is a sedimentary rock composed mainly of calcium carbonate in the form of mineral calcite. Limestones may be classified either according to the impurities they contain (dolomitic limestone, which contains substantial amounts of magnesium carbonate; argillaceous limestone, with a high clay content; siliceous limestone, which contains sand or quartz; and so on) or according to the formation in which they occur (e.g., marble, which is a crystalline limestone). Limestone deposits are widely distributed throughout the earth’s crust and are extracted by quarrying.
Since early times, limestone has been used as a building stone. It is also crushed for use as a flux in smelting, in refining, and for the manufacture of lime. Limestone is used as hardcore and ballast in road and railway construction, and it is mixed with clay for the manufacture of cement.
Health hazards. During extraction, the appropriate quarrying safety measures should be taken, and machinery-guarding principles should be observed on crushers. The main health hazard in limestone quarries is the possible presence, in the airborne limestone dust, of free silica, which normally accounts for 1 to 10% of limestone rock. In studies of limestone quarry and processing workers, x-ray examinations revealed pulmonary changes, and clinical examination showed pharyngitis, bronchitis and emphysema. Workers dressing stone for construction work should observe the safety measures appropriate to the stone industry.
Marble (Calcium Carbonate)
Occurrence and uses. Marble is geologically defined as a metamorphosed (re-crystallized) limestone composed primarily of crystalline grains of calcite, dolomite, or both, having a visible crystalline texture. Long usage of the term marble by the quarry and finishing industry has led to the development of the term commercial marble, which includes all crystalline rock capable of taking a polish and composed primarily of one or more of the following minerals: calcite, dolomite or serpentine.
Marble has been utilized throughout historic time as an important construction material because of its strength, durability, ease of workability, architectural adaptability and aesthetic satisfaction. The marble industry comprises two major branches—dimension marble and crushed and broken marble. The term dimension marble is applied to deposits of marble quarried for the purpose of obtaining blocks or slabs that meet specifications as to size and shape. The uses of dimension marble include building stone, monumental stone, ashlar, veneer panelling, wainscotting, tiling, statuary and so on. Crushed and broken marble ranges in size from large boulders to finely ground products, and products include aggregates, ballast, roofing granules, terrazzo chips, extenders, pigments, agricultural lime and so on.
Health hazards. Occupational diseases specifically connected with the mining, quarrying and processing of marble itself have not been described. In underground mining there may be exposure to toxic gases produced by blasting and some types of motor-driven equipment; adequate ventilation and respiratory protection are necessary. In abrasive blasting there will be exposure to silica if sand is used, but silicon carbide or aluminium oxide are equally effective, carry no silicosis risk, and should be substituted. The large quantities of dust generated in processing marble should be subject to dust control, either by the use of moist methods or by exhaust ventilation.
Mica
Occurrence and uses. Mica (from the Latin micare, to gleam or sparkle) is a mineral silicate which occurs as a primary constituent of igneous rocks, particularly granites. It is also a common component of such silicate materials as kaolin, which are produced by the weathering of these rocks. In the rock bodies, particularly in the pegmatite veins, mica occurs as lenticular masses of cleavable sheets (known as books) of up to 1 m in diameter, or as particles. There are many varieties, of which the most useful are muscovite (common, clear or white mica), phlogopite (amber mica), vermiculite, lepidolite and sericite. Muscovite is generally found in siliceous rocks; there are substantial deposits in India, South Africa and the United States. Sericite is the small plate variety of muscovite. It results from the weathering of schists and gneisses. Phlogopite, which occurs in calcareous rocks, is concentrated in Madagascar. Vermiculite has the outstanding characteristic of expanding considerably when quickly heated to around 300 ºC. There are large deposits in the United States. The main value of lepidolite lies in its high content of lithium and rubidium.
Mica is still used for slow-combustion stoves, lanterns or peep-holes of furnaces. The supreme quality of mica is that it is dielectric, which makes it a top-priority material in aircraft construction. Mica powder is used in the manufacture of electric cables, pneumatic tyres, welding electrodes, bituminized cardboard, paints and plastics, dry lubricants, dielectric dressings and flameproof insulators. It is often compacted with alkyd resins. Vermiculite is widely used as an insulating material in the building industry. Lepidolite is used in the glass and ceramic industries.
Health hazards. When working with mica, the generation of static electricity is possible. Straightforward engineering techniques can harmlessly discharge it. Mica miners are exposed to the inhalation of a wide variety of dusts, including quartz, feldspar and silicates. Chronic inhalation may cause silicosis. Exposure of workers to mica powder may cause irritation of the respiratory tract, and, after several years, nodular fibrotic pneumoconiosis can occur. It was long considered to be a form of silicosis, but it is now believed not to be, because pure mica dust contains no free silica. The radiological appearance is often close to that of asbestosis. Experimentally, mica has proved to possess a low cytotoxicity on macrophages and to induce only a poor fibrogenic response limited to the formation of thick reticulin fibres.
Chronic inhalation of vermiculite, which often contains asbestos, may cause asbestosis, lung cancer and mesothelioma. Ingestion of vermiculite is also suspected in stomach and intestinal cancer.
Pumice
Occurrence and uses. Pumice is a porous rock, grey or white, fragile and of low specific gravity, coming from recent volcanic magma; it is composed of quartz and silicates (mainly feldspar). It is found either pure or mixed with various substances, chief among them obsidian, which differs by its shiny black colour and its specific gravity, which is four times greater. It occurs principally in Ethiopia, Germany, Hungary, Italy (Sicily, Lipari), Madagascar, Spain and the United States. Some varieties, such as Lipari pumice, have a high content of total silica (71.2 to 73.7%) and a fair amount of free silica (1.2 to 5%).
In commerce and for practical uses, a distinction is made between pumice in blocks and in powder. When it is in block form the designation differs according to the size of block, colour, porosity and so on. The powder form is classified by numbers according to grain size. Industrial processing comprises a number of operations: sorting to separate the obsidian, crushing and pulverizing in machines with stone or metal grinding wheels, drying in open kilns, sifting and screening using hand-operated flat and open sieves and reciprocating or rotating screens, the waste matter generally being recovered.
Pumice is used as an abrasive (block or powder), as a lightweight building material, and in the manufacture of stoneware, explosives and so on.
Health hazards. The most dangerous operations involving exposure to pumice are kiln drying and sifting, because of the large amount of dust produced. Apart from the characteristic signs of silicosis observed in the lungs and sclerosis of the hilar lymphatic glands, the study of some fatal cases has revealed damage to various sections of the pulmonary arterial tree. Clinical examination has revealed respiratory disorders (emphysema and sometimes pleural damage), cardiovascular disorders (cor pulmonale) and renal disorders (albuminuria, haematuria, cylindruria), as well as signs of adrenal deficiency. Radiological evidence of aortitis is more common and serious than in the case of silicosis. A typical radiological appearance of lungs in liparitosis is the presence of linear thickening due to lamellar atelactasis.
Sandstone
Occurrence and uses. Sandstone is a siliciclastic sedimentary rock consisting primarily of sand, usually sand that is predominantly quartz. Sandstones often are poorly cemented and can be easily crumbled into sand. Yet, strong, durable sandstone, with tan and grey colours, is used as dimension sandstone for exterior facing and trim for buildings, in houses, as curbstones, in bridge abutments and in various retaining walls. Firm sandstones are crushed for use as concrete aggregate, railroad ballast and riprap. However, many commercial sandstones are weakly cemented and therefore are crumbled and used for moulding sand and glass sand. Glass sand is the main ingredient in glass. In the metalworking industry, sand with good cohesiveness and refractoriness is used for making special shaped moulds into which molten metal is poured.
Sandstone is found throughout the United States, in Illinois, Iowa, Minnesota, Missouri, New York, Ohio, Virginia and Wisconsin.
Health hazards. The primary risks are from the silica exposure, which is discussed in the chapter Respiratory system.
Silica
Occurrence and uses. Silica occurs naturally in crystalline (quartz, cristobalite and tridymite), cryptocrystalline (e.g., chalcedony) and amorphous (e.g., opal) forms, and the specific gravity and melting point depend on the crystalline form.
Crystalline silica is the most widely occurring of all minerals, and it is found in most rocks. The most commonly occurring form of silica is the sand found on beaches throughout the world. The sedimentary rock sandstone consists of grains of quartz cemented together with clays.
Silica is a constituent of common glass and most refractory bricks. It is also used extensively in the ceramic industry. Rocks containing silica are used as common building materials.
Free and combined silica. Free silica is silica which is not combined with any other element or compound. The term free is used to distinguish it from combined silica. Quartz is an example of free silica. The term combined silica originates from the chemical analysis of naturally occurring rocks, clays and soils. The inorganic constituents are found to consist almost always of oxides bound chemically, commonly including silicon dioxide. Silica so combined with one or more other oxides is known as combined silica. The silica in mica, for example, is present in the combined state.
In crystalline silica, the silicon and oxygen atoms are arranged in a definite, regular pattern throughout the crystal. The characteristic crystal faces of a crystalline form of silica are the outward expression of this regular arrangement of atoms. The crystalline forms of free silica are quartz, cristobalite and tridymite. Quartz is crystallized in the hexagonal system, cristobalite in the cubic or tetragonal system and tridymite in the ortho-rhombic system. Quartz is colourless and transparent in the pure form. The colours in naturally occurring quartz are due to contamination.
In amorphous silica the different molecules are in a dissimilar spatial relationship one to another, with the result that there is no definite regular pattern between molecules some distance apart. This absence of long-range order is characteristic of amorphous materials. Cryptocrystalline silica is intermediate between crystalline and amorphous silica in that it consists of minute crystals or crystallites of silica which are themselves arranged in no regular orientation one to another.
Opal is an amorphous variety of silica with a varying amount of combined water. A commercially important form of amorphous silica is diatomaceous earth, and calcinated diatomaceous earth (kieselguhr). Chalcedony is a cryptocrystalline form of silica which occurs filling cavities in lavas or associated with flint. It is also found in the annealing of ceramics when, under certain temperature conditions, the quartz in silicates may crystallize out in minute crystals in the body of the ware.
Health hazards. The inhalation of airborne dust of silica gives rise to silicosis, a serious and potentially fatal fibrotic disease of the lungs. The chronic, accelerated, and acute forms of silicosis reflect differing exposure intensities, latency periods and natural histories. Chronic silicosis may progress to progressive massive fibrosis, even after exposure to silica-containing dust has ceased. Hazards of silica are discussed in more detail in the chapter Respiratory system.
Slate
Occurrence and uses. Slate is very fine-grained, sedimentary argillaceous or schisto-argillaceous rock, easily split, of a leaden-grey, reddish or greenish colour. The principal deposits are in France (Ardennes), Belgium, the United Kingdom (Wales, Cornwall), the United States (Pennsylvania, Maryland) and Italy (Liguria). With a high calcium carbonate content, they contain silicates (mica, chlorite, hydrosilicates), iron oxides and free silica, amorphous or crystalline (quartz). The quartz content of hard slates is in the region of 15%, and that of soft slates, less than 10%. In North Wales quarries, respirable slate dust contains between 13 and 32% of respirable quartz.
Slate slabs are used for roofing; stair treads; door, window and porch casements; flooring; fireplaces; billiard tables; electricity switch panels; and school blackboards. Powdered slate has been used as a filler or pigment in rustproofing or insulating paints, in mastics, and in paints and bituminous products for road surfacing.
Health hazards. Disease in slate workers has attracted attention since the early nineteenth century, and cases of “miner’s phthisis” uncomplicated by tubercle bacilli were described at an early date. Pneumoconiosis has been found in a third of workers studied in the slate industry in North Wales, and in 54% of slate pencil makers in India. Slateworkers’ pneumoconiosis may have features of silicosis due to the high quartz content of some slates. Chronic bronchitis and emphysema are frequently observed, especially in extraction workers.
The replacement of the hand pick by low-velocity mechanical equipment considerably reduces dust generation in slate quarries, and the use of local exhaust ventilation systems makes it possible to maintain airborne dust concentrations within acceptable limits for 8-hour exposure. Ventilation of underground workings, drainage of groundwater into pits, lighting and work organization are improving the general hygiene of working conditions.
Circular sawing should be carried out under water jets, but planing does not usually give rise to dust provided the slivers of slate are not allowed to fall to the ground. Larger sheets are usually wet-polished; however, where dry-polishing is carried out, well-designed exhaust ventilation should be employed since slate dust is not easily collected even when using scrubbers. The dust readily clogs bag filters.
Workshops should be cleaned daily to prevent accumulation of dust deposits; in certain cases, it may be preferable to prevent deposited dust in gangways from becoming airborne again by covering dust with sawdust rather than by wetting it.
Talc
Occurrence and uses. Talc is a hydrous magnesium silicate whose basic formula is (Mg Fe+2)3Si4O10 (OH2), with theoretical weight percentages as follows: 63% SiO2, 32% MgO and 5% H2O. Talc is found in a variety of forms and is frequently contaminated with other minerals, including silica and asbestos. Talc production occurs in Australia, Austria, China, France and the United States.
The texture, stability and fibrous or flaky properties of the various talcs have made them useful for many purposes. The purest grades (i.e., those which most nearly approximate the theoretical composition) are fine in texture and colour, and are therefore widely used in cosmetics and toilet preparations. Other varieties, containing admixtures of different silicates, carbonates and oxides, and perhaps free silica, are relatively coarse in texture and are used in the manufacture of paint, ceramics, automobile tyres and paper.
Health hazards. Chronic inhalation may cause silicosis if silica is present, or asbestosis, lung cancer, and mesothelioma if asbestos or asbestos-like minerals are present. Investigations of workers exposed to talc without associated asbestos fibres revealed trends for higher mortality from silicosis, silicotuberculosis, emphysema and pneumonia. The major clinical symptoms and signs of talc pneumoconiosis include chronic productive cough, progressive shortness of breath, diminished breath sounds, limited chest expansion, diffuse rales and clubbing of the finger tips. Lung pathology has revealed various forms of pulmonary fibrosis.
Wollastonite (Calcium Silicate)
Occurrence and uses. Wollastonite (CaSiO3) is a natural calcium silicate found in metamorphic rock. It occurs in many different forms in New York and California in the United States, in Canada, Germany, Romania, Ireland, Italy, Japan, Madagascar, Mexico, Norway and Sweden.
Wollastonite is used in ceramics, welding-rod coatings, silica gels, mineral wool and paper coating. It is also used as a paint extender, a soil conditioner, and as a filler in plastics, rubber, cements and wallboard.
Health hazards. Wollastonite dust may cause skin, eye and respiratory irritation.
Agricultural chemicals are usually defined as pesticides, fertilizers and health products. The US Environmental Protection Agency (EPA) defines pesticides as any materials manufactured or formulated to kill a pest. This means that herbicides, fungicides, insecticides and miticides are pesticides. Fertilizers are nutrient chemicals that enhance the growth of the plant. The important elements in the fertilizers are nitrogen, phosphorus and potassium. Nitrogen is usually in the form of ammonia, ammonium nitrate, ammonium sulphate, ammonium phosphate or solutions of these materials. Other nitrogen-containing chemicals are used for some special nutrient needs. Ammonium phosphate is the normal source of phosphorous. Potash (potassium oxide) is the potassium nutrient. Animal health products are any chemicals that are used to promote the health or growth of an animal. This includes products that are used topically by drenching or pouring-on, orally as a tablet or gel, and injectibles.
Pesticides
The most significant development in the pesticide manufacturing industry has been the introduction of the environmentally friendly pesticides. The imidazolinone family of herbicides has been a benefit to soybean and other field crops, as the herbicides are much more effective pound for pound; are less toxic to humans, animals and fish; have less persistence in the soil; and are formulated using water instead of flammable solvents, as compared to the old generation nitroaromatics. Concurrent with these innovations is the development of imidazolinones-resistant seeds that can be protected from weed growth. Corn is in the forefront in this area and has been successfully grown, protected by the imidazolinones. This also makes carry-over from year to year of the herbicide an insignificant problem, as in many areas soybeans and corn are rotated.
A newer development is the production of the synthetic pyrethroids, which are broad-range pesticides. These products are effective pesticides and are less toxic to animals and humans than the old organophosphates and carbamates. They are activated by the insect’s biological system and therefore not a danger to vertebrates. They are also less persistent in the environment, as they are biodegradable.
There have also been developments in the use of the old generation pesticides and herbicides. Herbicide formulations have been developed that utilize water dispersion technology that eliminates the use of volatile solvents. This not only reduces the amount of volatile organic chemicals that go to the atmosphere, but also makes handling, storage, formulation and transportation much safer. In the area of pesticides, a superior method of handling the toxic pesticides has been developed that uses closed container transfer of the material from the package to the spreader, called “Lock-N-Load”. This reduces the chances of exposure to these toxic materials. Organophosphates are still being used successfully to help eradicate health problems such as malaria and river blindness. Some of the less toxic organophosphates are effective in the treatment of animals for insects, worms and mites by direct application to the skin using pour-on or aerosol formulations.
The pesticide industry is regulated by many countries, and labelling, application to plants and soil, training in pesticide use, and transportation are controlled. Many pesticides can only be spread by licensed applicators. Precautions during pesticide application are discussed elsewhere in this Encyclopaedia. Bulk transportation vehicles can only be operated by qualified drivers. The producers of pesticide have a legal obligation to provide safe handling and application methods. This is usually accomplished by providing comprehensive labelling, training and material safety data sheets (MSDSs) (see the chapter Using, storing and transporting chemicals).
Another problem is the disposal of empty containers. It is not advisable, and in many places it is illegal, to reuse pesticide containers. Many advances have been made to mitigate this problem. Plastic containers have been collected by the distributors and reprocessed into plastic pipe. Bulk, refillable containers have been used. With the advent of the wettable powders and water-based dispersions, triple rinsing the container into the solutions tank gives the applicator a method to decontaminate the container before landfilling or recycling. Hand lances with spray nozzles that can pierce the container are used to assure proper cleaning and the destruction of the container so that it can not be reused.
Pesticides are made to kill; therefore, care is necessary to handle them safely. Some of the problems have been lessened by the product advances. In most cases, copious quantities of water are the best first-aid treatment for superficial exposures to skin and eyes. For ingestion, it is best to have a specific antidote available. It is important that the nearest health facility know what is being used and have a supply of the appropriate antidote on hand. For instance, organophosphates and carbamates cause cholinesterase inhibition. Atropine, the specific antidote for the treatment of this reaction, should be available wherever these pesticides are used.
For further discussion of pesticides, see the eponymous article in this chapter.
Fertilizers
Ammonia is the base of most important fertilizers. The major fertilizers are ammonia itself, ammonium nitrate, urea, ammonium sulphate and ammonium phosphate. There appears to be an environmental problem associated with nitrogen use, as the ground water in many farming areas is contaminated with nitrates, which causes health problems when the water is consumed as drinking water. There are pressures for farmers to use less fertilizer and to rotate crops of nitrogen-using legumes such as soy beans and rye grass. Ammonium nitrate, an oxidizer, is explosive if heated. The dangers of ammonium nitrate as a blasting agent were demonstrated by the destruction of a US federal building in Oklahoma City, Oklahoma, in 1995. There is some movement to add inert ingredients to make fertilizer-grade ammonium nitrate detonation-resistant. An industrial explosion resulting in multiple fatalities which occurred in an ammonium nitrate solutions plant that was thought to be safe from detonation because the ammonium nitrate was handled as an 85% solution is anonther example. Investigation results indicated that an intricate condition of temperature and contamination caused the incident. These conditions would not exist in the retail or farming sector. Anhydrous ammonia is a moderately toxic gas at room temperature and must be kept under pressure or refrigeration during storage and use. It is a skin, eye and respiratory irritant, can cause burns, and is flammable. It is directly applied to the soil or used as an aqueous solution. There is significant anhydrous ammonia storage in many farming areas. A hazardous condition is created if the storage is not managed correctly. This should include monitoring for leaks and emergency leak procedures.
Animal Health Products
The development and marketing of bovine somatotropin (BST) has caused controversy. BST, a fermentation product, raises the productivity of milk cows by 10 to 20%. Many people are opposed to the product because it introduces a chemical into the production of milk. However, the BST milk is indistinguishable from ordinary milk since BST is produced naturally by the milk cow. A problem seems to be an increase in infections of the cow’s udder. Antibiotics for these infections are available, but the use of these antibiotics is also controversial. The important benefits of BST are the increased production of milk with a reduction in food consumption and a similar reduction in cow manure, a material that is a solid-waste problem in many areas. A similar product, porcine somatotropin (PST), is still in the testing stage. It produces bigger hogs quickly, utilizing less feed, and results in pork containing less fat.
Antibiotic use in the beef-raising industry is also causing controversy. There is fear that consumption of large amounts of beef will result in hormonal problems in humans. There has been little in the way of confirmed problems, but the concern persists. Animal health products have been developed that control worms in animals. The previous generation was a synthetic chemical product, but the new generation products are the result of biological fermentation technology. These products are effective in many types of animals at very low use levels, and include domestic pets in their protection arena. These products are very toxic to aquatic life, though, so much care must be taken to avoid contamination of creeks and streams. These materials do biodegrade, so there appear to be no long-term or residual aquatic problems.
Manufacture of Agricultural Chemicals
The manufacturing of agricultural chemicals entails many processes and raw materials. Some agricultural chemicals are batch chemical syntheses that involve exothermic reactions where temperature control and emergency relief sizing are an issue. Hazard evaluations are necessary to assure that all the hazards are discovered and addressed. Hazard and operability studies (HAZOP) are recommended for conducting reviews. Relief sizing must be conducted using Design Institute for Emergency Relief Systems (DIERS) technology and data from calorimetric equipment. Usually, because of the complexity of the molecules, the production of agricultural chemicals involves many steps. Sometimes there is considerable aqueous and organic liquid waste. Some of the organics may be recyclable, but most of the aqueous waste must be biologically treated or incinerated. Both methods are difficult because of the presence of organic and inorganic salts. The previous generation herbicides, because they involved nitrations, were produced using continuous reactors to minimize the quantities of the nitrated materials at reaction temperatures. Severe runaway reactions, resulting in property damage and injuries, have occurred when batch reactors of nitrated organics have been subjected to a temperature excursion or contamination.
Many modern pesticide products are dry powders. If the concentration, particle size, oxygen concentration and a source of ignition are present at the same time, a dust explosion can occur. The use of inerting, the exclusion of oxygen, and utilization of nitrogen or carbon dioxide minimizes the oxygen source and can make the processes safer. These dusts may also be an industrial hygiene issue. Ventilation, both general and local, is a solutions to these problems.
The major fertilizers are made continuously rather than by the batch process. Ammonia is made by reforming methane at high temperatures utilizing a specific catalyst. Carbon dioxide and hydrogen are also formed and must be separated from the ammonia. Ammonium nitrate is made from ammonia and nitric acid in a continuous reactor. The nitric acid is formed by the continuous oxidation of ammonia on a catalytic surface. Ammonium phosphate is a reaction of ammonia and phosphoric acid. Phosphoric acid is made by reacting sulphuric acid with phosphate -containing ores. Sulphuric acid is formed by burning sulphur to sulphur dioxide, and catalytically converting the sulphur dioxide continuously to sulphur trioxide, and then adding water to form the sulphuric acid. Urea is a continuous high-pressure reaction of carbon dioxide and ammonia, the carbon dioxide usually coming from the ammonia continuous reaction by-product.
Many of these raw materials are toxic and volatile. Release of the raw materials or finished products, through an equipment failure or operator error, can expose employees and others in the community. A detailed emergency response plan is a necessary tool to minimize the effects of a release. This plan should be developed by determining a credible worst-case event through hazard evaluations and then forecasting consequences using dispersion modelling. This plan should include a method to notify employees and the community, an evacuation plan, emergency services and a recovery plan.
Transportation of agricultural chemicals should be thoroughly investigated to choose the safest route—one that minimizes the exposures if an incident occurs. A transportation emergency response plan should be implemented to address transportation incidents. This plan should include a published emergency response telephone number, company personnel to respond to calls and, in some cases, an accident site emergency response team.
Fermentation is the method of producing some of the animal health products. Fermentation is usually not a hazardous process, as it involves growing a culture using a nutritional medium such as lard oil, glucose, or starch. Sometimes anhydrous ammonia is used for pH (acidity) control or as a nutrient, so the process can involve hazards. Solvents may be used to extract the active cells, but the quantities and the methodology are such that is can be done safely. Recycling these solvents is often part of the process.
Adapted from 3rd edition, Encyclopaedia of Occupational Health and Safety. Revision includes information from A. Baiinova, J.F. Copplestone, L.A. Dobrobolskij,
F. Kaloyanova-Simeonova, Y.I. Kundiev and A.M. Shenker.
The word pesticide generally denotes a chemical substance (which may be mixed with other substances) that is used for the destruction of an organism deemed to be detrimental to humans. The word clearly has a very wide meaning and includes a number of other terms, such as insecticides, fungicides, herbicides, rodenticides, bactericides, miticides, nematocides and molluscicides, which individually indicate the organisms or pests that the chemical or class of chemicals is designed to kill. As different types of chemical agents are used for these general classes, it is usually advisable to indicate the particular category of pesticide.
General Principles
Acute toxicity is measured by the LD50 value; this is a statistical estimate of the number of mg of the chemical per kg of body weight required to kill 50% of a large population of test animals. The dose may be administered by a number of routes, usually orally or dermally, and the rat is the standard test animal. Oral or dermal LD50 values are used according to which route has the lower value for a specific chemical. Other effects, either as a result of short-term exposure (such as neurotoxicity or mutagenicity) or of long-term exposure (such as carcinogenicity), have to be taken into account, but pesticides with such known properties are not registered for use. The WHO Recommended Classification of Pesticides by Hazard and Guidelines to Classification 1996-1997 issued by the World Health Organization (WHO) classifies technical products according to the acute risk to human health as follows:
The guidelines based on the WHO Classification list pesticides according to toxicity and physical state; these are presented in a separate article in this chapter.
Poisons enter the body through the mouth (ingestion), the lungs (inhalation), the intact skin (percutaneous absorption) or wounds in the skin (inoculation). The inhalation hazard is determined by the physical form and solubility of the chemical. The possibility and degree of percutaneous absorption varies with the chemical. Some chemicals also exert a direct action on the skin, causing dermatitis. Pesticides are applied in many different forms—as solids, by spraying in dilute or concentrated form, as dusts (fine or granulated), and as fogs and gases. The method of use has a bearing on the likelihood of absorption.
The chemical may be mixed with solids (often with food used as bait), water, kerosene, oils or organic solvents. Some of these diluents have some degree of toxicity of their own and may influence the rate of absorption of the pesticide chemical. Many formulations contain other chemicals which are not themselves pesticides but which enhance the effectiveness of the pesticide. Added surface-active agents are a case in point. When two or more pesticides are mixed in the same formulation, the action of one or both may be enhanced by the presence of the other. In many cases, the combined effects of mixtures have not been fully worked out, and it is a good rule that mixtures should always be treated as more toxic than any of the constituents on their own.
By their very nature and purpose, pesticides have adverse biological effects on at least some species, human beings included. The following discussion provides a broad overview of the mechanisms by which pesticides can act, and some of their toxic effects. Carcinogenicity, biological monitoring and safeguards in the use of pesticides are discussed in more detail elsewhere in this Encyclopaedia.
Organochlorine Pesticides
The organochlorine pesticides (OCPs) have caused intoxication following skin contact, ingestion or inhalation. Examples are endrin, aldrin and dieldrin. The rate of absorption and toxicity differ depending on the chemical structure and the solvents, surfactants and emulsifiers used in the formulation.
The elimination of OCPs from the body takes place slowly through the kidneys. Metabolism in the cells involves various mechanisms—oxidation, hydrolysis and others. OCPs have a strong tendency to penetrate cell membranes and to be stored in the body fat. Because of their attraction to fatty tissues (lipotropic properties) OCPs tend to be stored in the central nervous system (CNS), liver, kidneys and the myocardium. In these organs they cause damage to the function of important enzyme systems and disrupt the biochemical activity of the cells.
OCPs are highly lipophilic and tend to accumulate in fatty tissue as long as exposure persists. When exposure ceases, they are released slowly into the bloodstream, often over a period of many years, from whence they can be transported to other organs where genotoxic effects, including cancer, may be initiated. The great majority of US residents, for example, have detectable levels of organochlorine pesticides, including breakdown products of DDT, in their adipose (fatty) tissue, and the concentrations increase with age, reflecting lifetime accumulations.
A number of OCPs that have been used throughout the world as insecticides and herbicides are also proven or suspected carcinogens to humans. These are discussed in more detail in the Toxicology and Cancer chapters of this Encyclopaedia.
Acute intoxications
Aldrin, endrin, dieldrin and toxaphene are most frequently implicated in acute poisoning. Delay in the onset of symptoms in severely acute intoxications is about 30 minutes. With lower toxicity OCPs it is several hours but not more than twelve.
Intoxication is demonstrated by gastrointestinal symptoms: nausea, vomiting, diarrhoea and stomach pains. The basic syndrome is cerebral: headache, dizziness, ataxia and paraesthesia. Gradually tremors set in, starting from the eyelids and the face muscles, descending towards the whole body and the limbs; in severe cases this leads to fits of tonic-clonic convulsions, which gradually extend to the different muscle groups. Convulsions may be connected with elevated body temperature and unconsciousness and may result in death. In addition to the cerebral signs, acute intoxications may lead to bulbar paralysis of the respiratory and/or vasomotor centres, which causes acute respiratory deficiency or apnoea, and to severe collapse.
Many patients develop signs of toxic hepatitis and toxic nephropathy. After these symptoms have disappeared some patients develop signs of prolonged toxic polyneuritis, anaemia and haemorrhagic diathesis connected with the impaired thrombocytopoiesis. Typical of toxaphene is an allergic bronchopneumonia.
Acute intoxications with OCPs last up to 72 hours. When organ function has been seriously impaired, the illness may continue up to several weeks. Complications in cases of liver and kidney damage can be long-lasting.
Chronic poisoning
During the application of OCPs in agriculture as well as in their production, poisoning is most commonly chronic—that is, low doses of exposure over time. Acute intoxication (or high-level exposures at a particular instant) are less common and are usually the result of misuse or accidents, both in the home and in industry. Chronic intoxication is characterized by damage to the nervous, digestive and cardiovascular systems and the blood-formation process. All OCPs are CNS stimulants and are capable of producing convulsions, which frequently appear to be epileptic in character. Abnormal electroencephalographic (EEG) data have been recorded, such as irregular alpha rhythms and other abnormalities. In some cases bitemporal sharp-peaked waves with shifting localization, low voltage and diffuse theta activity have been observed. In other cases paroxysmal emissions have been registered, composed of slow sharp-peaked waves, sharp-peaked complexes and rhythmic peaks with low voltage.
Polyneuritis, encephalopolyneuritis and other nervous system effects have been described following occupational exposure to OCPs. Tremor of the limbs and alterations in the electromyograms (EMGs) have also been observed in workers. In workers handling OCPs such as BHC, polychloropinene, hexachlorobutadiene and dichloroethane, non-specific signs (e.g., diencephalic signs) have been observed and very often develop together with other signs of chronic intoxication. The most common signs of intoxication are headache, dizziness, numbness and tingling in the limbs, rapid changes in blood pressure and other signs of circulatory disturbances. Less frequently, colic pains below the right ribs and in the region of the umbilicus, and dyskinesia of the bile ducts, are observed. Behavioural changes, such as disturbances of sensory and equilibrium functions, are found. These symptoms are often reversible after cessation of the exposure.
OCPs cause liver and kidney damage. Microsomal enzyme induction has been observed, and increased ALF and aldolase activity have also been reported. Protein synthesis, lipoid synthesis, detoxification, excretion and liver functions are all affected. Reduction of creatinine clearance and phosphorus reabsorption are reported in workers exposed to pentachlorophenol, for example. Pentachlorophenol, along with the family of chlorophenols, are also considered possible human carcinogens (group 2B as classified by the International Agency for Research on Cancer (IARC)). Toxaphene is also considered to be a group 2B carcinogen.
Cardiovascular disturbances have been observed in exposed persons, most frequently demonstrated as dyspnoea, high heart rate, heaviness and pain in the heart region, increased heart volume and hollow heart tones.
Blood and capillary disturbances have also been reported following contact with OCPs. Thrombopenia, anaemia, pancytopenia, agranulocytosis, haemolysis and capillary disorders have all been reported. Medullar aplasia can be complete. The capillary damage (purpura) can develop following long- or short-term but intensive exposures. Eosinopenia, neutropenia with lymphocytosis, and hypochromic anaemia have been observed in workers subjected to prolonged exposures.
Skin irritation is reported to follow from skin contact with some OCPs, particularly chlorinated terpenes. Often chronic intoxications are clinically demonstrated by signs of allergic damage.
Organophosphate Pesticides
The organophosphorus pesticides are chemically related esters of phosphoric acid or certain of its derivatives. The organic phosphates are also identified by a common pharmacological property—the ability to inhibit the action of the cholinesterase enzymes.
Parathion is among the most dangerous of the organophosphates and is discussed in some detail here. In addition to parathion’s pharmacological effects, no insect is immune to its lethal action. Its physical and chemical properties have rendered it useful as an insecticide and acaricide for agricultural purposes. The description of parathion’s toxicity applies to other organophosphates, although their effects may be less rapid and extensive.
The toxic action of all organic phosphates is on the CNS through inhibition of the cholinesterase enzymes. Inhibiting these cholinesterases produces excessive and continuous stimulation of those muscle and gland structures which are activated by acetylcholine, to a point where life can no longer be sustained. Parathion is an indirect inhibitor because it must be converted in the environment or in vivo before it can effectively inhibit cholinesterase.
Organophosphates can generally enter the body by any route. Serious and even fatal poisoning may occur by ingesting a small amount of parathion while eating or smoking, for example. Organophosphates may be inhaled when dusts or volatile compounds are even briefly handled. Parathion is easily absorbed through the skin or the eye. The ability to penetrate the skin in fatal quantities without the warning of irritation makes parathion especially difficult to handle.
Signs and symptoms of organophosphate poisoning can be explained on the basis of cholinesterase inhibition. Early or mild poisoning may be hard to distinguish because of a number of other conditions; heat exhaustion, food poisoning, encephalitis, asthma and respiratory infections share some of the manifestations and confuse the diagnosis. Symptoms can be delayed for several hours after the last exposure but rarely longer than 12 hours. Symptoms most often appear in this order: headaches, fatigue, giddiness, nausea, sweating, blurred vision, tightness in the chest, abdominal cramps, vomiting and diarrhoea. In more advanced poisoning, difficult breathing, tremors, convulsions, collapse, coma, pulmonary oedema and respiratory failure follow. The more advanced the poisoning, the more obvious are the typical signs of cholinesterase inhibition, which are: pinpoint pupils; rapid, asthmatic type breathing; marked weakness; excessive sweating; excessive salivation; and pulmonary oedema.
In very severe parathion poisoning, in which the victim has been unconscious for some time, brain damage from anoxia may occur. Fatigue, ocular symptoms, electroencephalogram abnormalities, gastrointestinal complaints, excessive dreams and exposure intolerance to parathion have been reported to persist for days to months following acute poisoning. There is no evidence that permanent impairment occurs.
Chronic exposure to parathion may be cumulative in the sense that repeated exposures closely following each other can reduce cholinesterase faster than it can be regenerated, to the point where a very small exposure can precipitate acute poisoning. If the person is removed from exposure, clinical recovery is usually rapid and complete within a few days. The red blood cells and plasma should be tested for cholinesterase inhibition when phosphate ester poisoning is suspected. Red cell cholinesterase activity is most often reduced and close to zero in severe poisoning. Plasma cholinesterase is also severely reduced and is a more sensitive and more rapid indicator of exposure. There is no advantage in chemical determinations of parathion in the blood because metabolism of the pesticide is too rapid. However, p-nitrophenol, an end-product of the metabolism of parathion, can be determined in the urine. Chemical examination to identify the pesticide can be made on contaminated clothing or other material where contact is suspected.
Carbamates and Thiocarbamates
The biological activity of carbamates was discovered in 1923 when the structure of the alkaloid eserine (or physostigmine) contained in the seeds of Calabar beans was first described. In 1929 physostigmine analogues were synthesized, and soon such derivatives of dithiocarbamic acid as thiram and ziram were available. The study of carbamic compounds began in the same year, and now more than 1,000 carbamic acid derivatives are known. More than 50 of them are used as pesticides, herbicides, fungicides and nematocides. In 1947 the first carbamic acid derivatives having insecticide properties were synthesized. Some thiocarbamates have proved effective as vulcanization accelerators, and derivatives of dithiocarbamic acid have been obtained for the treatment of malignant tumours, hypoxia, neuropathies, radiation injuries and other diseases. Aryl esters of alkylcarbamic acid and alkyl esters of arylcarbamic acid are also used as pesticides.
Some carbamates can produce sensitization in exposed individuals, and a variety of foetotoxic, embryotoxic and mutagenic effects have also been observed for members of this family.
Chronic effects
The specific effects produced by acute poisoning have been described for each substance listed. A review of the specific effects gained from an analysis of published data makes it possible to distinguish similar features in the chronic action of the different carbamates. Some authors believe that the main toxic effect of carbamic acid esters is the involvement of the endocrine system. One of the peculiarities of carbamate poisoning is the possible allergic reaction of exposed subjects. The toxic effects of carbamates may not be immediate, which can present a potential hazard because of lack of warning. Results from animal experiments are indicative of embryotoxic, teratogenic, mutagenic and carcinogenic effects of some carbamates.
Baygon (isopropoxyphenyl-N-methylcarbamate) is produced by reaction of alkyl isocyanate with phenols, and is used as an insecticide. Baygon is a systemic poison. It causes inhibition of the serum cholinesterase activity up to 60% after oral administration of 0.75 to 1 mg/kg. This highly toxic substance exerts a weak effect on the skin.
Carbaryl is a systemic poison which produces moderately severe acute effects when ingested, inhaled or absorbed through the skin. It may cause local skin irritation. Being a cholinesterase inhibitor, it is much more active in insects than in mammals. Medical examinations of workers exposed to concentrations of 0.2 to 0.3 mg/m3 seldom reveal a fall in cholinesterase activity.
Betanal (3-(methoxycarbonyl)aminophenyl-N-(3-methylphenyl) carbamate; N-methylcarbanilate) belongs to the arylcarbamic acid alkyl esters and is used as a herbicide. Betanal is slightly toxic for the gastrointestinal and respiratory tracts. Its dermal toxicity and local irritation are insignificant.
Isoplan is a highly toxic member of the group, its action, like that of Sevin and others, being characterized by the inhibition of acetylcholinesterase activity. Isoplan is used as an insecticide. Pyrimor (5,6-dimethyl-2-dimethylamino-4-pyrimidinyl methylcarbamate) is a derivative of arylcarbamic acid alkyl esters. It is highly toxic for the gastrointestinal tract. Its general absorption and local irritative effect are not very pronounced.
Thiocarbamic Acid Esters
Ronite (sym-ethylcyclohexylethyl thiocarbamate; Eurex); Eptam (sym-ethyl-N,N-dipropyl thiocarbamate); and Tillam (sym-propyl-N-ethyl-N-butylthiocarbamate) are esters which are synthesized by reaction of alkylthiocarbamates with amines and of alkaline mercaptides with carbamoyl chlorides. They are effective herbicides of selective action.
The compounds of this group are slightly to moderately toxic, and the toxicity is reduced when they are absorbed through the skin. They can affect the oxidative processes as well as the nervous and endocrine systems.
Dithiocarbamates and bisdithiocarbamates include the following products, which have much in common as regards their use and their biological effects. Ziram is used as a vulcanization accelerator for synthetic rubbers and, in agriculture, as a fungicide and seed fumigant. This compound is very irritant to the conjunctiva and upper airway mucous membranes. It can cause extreme pain in the eyes, skin irritation and liver function disorders. It has embryotoxic and teratogenic effects. TTD is used as a seed fumigant, irritates the skin, causes dermatitis and affects the conjunctiva. It increases sensitivity to alcohol. Nabam is a plant fungicide and serves as an intermediate in the production of other pesticides. It is irritating to the skin and mucous membranes, and it is a narcotic in high concentrations. In the presence of alcohol it can cause violent vomiting. Ferbam is a fungicide of relatively low toxicity, but may cause renal function disorders. It irritates the conjunctiva, the mucous membranes of the nose and upper airways, and the skin.
Zineb is an insecticide and fungicide that can cause irritation of the eyes, nose and larynx, and is harmful if inhaled or swallowed. Maneb is a fungicide that can cause irritation of the eyes, nose and larynx, and is harmful if inhaled or swallowed. Vapam (sodium methyldithiocarbamate; carbation) is white crystalline powder of unpleasant smell similar to that of carbon disulphide. It is an effective soil fumigant which destroys weed seeds, fungi and insects. It irritates the skin and mucous membranes.
Rodenticides
Rodenticides are toxic chemicals used for the control of rats, mice and other pest species of rodents. An effective rodenticide must conform to stringent criteria, a fact that is borne out by the small number of compounds that are currently in satisfactory use.
Poisoned baits are the most generally effective and widely used means of formulating rodenticides, but some are used as “contact” poisons (i.e., dusts, foams and gels), where the toxicant adheres to the fur of the animal and is ingested during subsequent grooming, while a few are applied as fumigants to burrows or infested premises. Rodenticides may conveniently be divided into two categories, depending on their mode of action: acute (single dose) poisons and chronic (multiple dose) poisons.
Acute poisons, such as zinc phosphide, norbormide, fluoracetamide, alpha-chloralose, are highly toxic compounds, with LD50s that are usually less than 100 mg/kg, and can cause death after a single dose consumed during a period not longer than a few hours.
Most acute rodenticides have the disadvantages of producing symptoms of poisoning rather quickly, of being generally rather non-specific, and lacking satisfactory antidotes. They are used at relatively high concentrations (0.1 to 10%) in bait.
Chronic poisons, which may act, for example, as anticoagulants (e.g., calciferol), are compounds that, having a cumulative mode of action, may need to be eaten by the prey over a succession of days to cause death. Anticoagulants have the advantage of producing symptoms of poisoning very late, usually well after the target species has eaten a lethal dose. An effective antidote to anticoagulants is available for those accidentally exposed. Chronic poisons are used at relatively low concentrations (0.002 to 0.1%).
Application
Rodenticides intended for use in baits are available in one or more of the following forms: technical grade material, concentrate (“master-mix”) or ready-to-use bait. Acute poisons are usually acquired as the technical material and mixed with the bait-base shortly before use. Chronic poisons, because they are used at low concentrations, are normally sold as concentrates, where the active ingredient is incorporated into a finely powdered flour (or talc) base.
When the final bait is prepared, the concentrate is added to the bait-base at the relevant rate. If the bait-base is of a coarse consistency, it may be necessary to add a vegetable or mineral oil at a prescribed rate to act as a “sticker”, thus ensuring that the poison adheres to the bait-base. It is commonly compulsory for a warning dye to be added to concentrates or ready-to-use baits.
In control treatments against rats and mice, poisoned baits are laid at frequent intervals throughout the infested area. When acute rodenticides are used, better results are obtained when unpoisoned bait (“prebait”) is laid for a few days before the poison is given. In “acute” treatments, poisoned bait is presented for a few days only. When anticoagulants are used, prebaiting is unnecessary, but the poison should remain in position for 3 to 6 weeks to achieve complete control.
Contact formulations of rodenticides are especially useful in situations where baiting is difficult for any reason, or where the rodents are not being drawn satisfactorily off their normal diet. The poison is usually incorporated in a finely divided powder (e.g., talc), which is laid on runways or around bait points, or is blown into burrows, wall cavities and so on. The compound may also be formulated in gels or foams, which are inserted into burrows.
The use of contact rodenticides relies on the target animal ingesting the poison while grooming itself. Because the amount of dust (or foam, etc.) adhering to the fur may be small, the concentration of the active ingredient in the formulation is usually relatively high, making it safe to use only where the contamination of food and so on cannot occur. Other specialized formulations of rodenticides include water baits and wax-impregnated blocks. The former, which are aqueous solutions of soluble compounds, are especially useful in dry environments. The latter are made by impregnating the toxicant and bait-base in molten paraffin wax (of low melting point) and casting the mixture into blocks. Wax-impregnated baits are designed to withstand wet climates and insect attack.
Hazards of rodenticides
Although toxicity levels of rodenticides may vary between target and non-target species, all poisons must be presumed to be potentially lethal to humans. Acute poisons are potentially more dangerous than chronic ones because they are rapid in action, non-specific and generally lack effective antidotes. Anticoagulants, on the other hand, are slow and cumulative, allowing adequate time for the administration of a reliable antidote, such as vitamin K.
As stated above, the concentrations of active ingredients in contact formulations of a given poison are higher than those in bait preparations, thus making operator hazard considerably greater. Fumigants present a special danger when used to treat infested premises, holds of ships and so on, and should be used only by trained technicians. The gassing of rodent burrows, although less hazardous, must also be carried out with extreme caution.
Herbicides
Grassy and broad-leaved weeds compete with crop plants for light, space, water and nutrients. They are hosts to bacteria, fungi and viruses, and hamper mechanical harvesting operations. Losses in crop yields as a result of weed infestation can be very heavy, commonly reaching 20 to 40%. Weed-control measures such as hand weeding and hoeing are ineffective in intensive farming. Chemical weedkillers or herbicides have successfully replaced mechanical methods of weed control.
In addition to their use in agriculture in cereals, meadows, open fields, pastures, fruit growing, greenhouses and forestry, herbicides are applied on industrial sites, railway tracks and power lines to remove vegetation. They are used for destroying weeds in canals, drainage channels and natural or artificial pools.
Herbicides are sprayed or dusted on weeds or on the soil they infest. They remain on the leaves (contact herbicides) or penetrate into the plant and so disturb its physiology (systemic herbicides). They are classified as non-selective (total—used to kill all vegetation) and selective (used to suppress the growth of or kill weeds without damaging the crop). Both non-selective and selective can be contact or systemic.
Selectivity is true when the herbicide applied in the correct dose and, at the right time, is active against certain species of weed only. An example of true selective herbicides are the chlorophenoxy compounds, which affect broad-leaved but not grassy plants. Selectivity can also be achieved by placement (i.e., by using the herbicide in such a way that it comes into contact with the weeds only). For example, paraquat is applied to orchard crops, where it is easy to avoid the foliage. Three types of selectivity are distinguished:
1. physiological selectivity, which relies upon the plant’s ability to degrade the herbicide into non-phytotoxic components
2. physical selectivity, which exploits the particular habit of the cultivated plant (e.g., the upright in cereals) and/or a specially fashioned surface (e.g., wax-coating, resistant cuticule) protecting the plant against herbicide penetration
3. positional selectivity, in which the herbicide remains fixed in the upper soil layers adsorbed on colloidal soil particles and does not reach the root zone of the cultivated plant, or at least not in harmful quantities. Positional selectivity depends on the soil, precipitation and temperature as well as the water solubility and soil adsorption of the herbicide.
Some commonly used herbicides
Following are brief descriptions of acute and chronic effects associated with some commonly used herbicides.
Atrazine gives rise to decreased body weight, anaemia, disturbed protein and glucose metabolism in rats. It causes occupational contact dermatitis due to skin sensitization. It is considered a possible human carcinogen (IARC group 2B).
Barban, in repeated contact with 5% water emulsion, causes severe skin irritation in rabbits. It provokes skin sensitization in both experimental animals and agricultural workers, and causes anaemia, methaemoglobinaemia and changes in lipid and protein metabolism. Ataxia, tremor, cramps, bradycardia and ECG deviations are found in experimental animals.
Chlorpropharm can produce slight dermal irritation and penetration. In rats, exposure to atrazine causes anaemia, methaemoglobinaemia and reticulocytosis. Chronic application causes skin carcinoma in rats.
Cycloate causes polyneuropathia and liver damage in experimental animals. No clinical symptoms have been described after occupational exposure of workers for three consecutive days.
2,4-D poses moderate dermal toxicity and skin irritancy risks to exposed persons. It is highly irritating to the eyes. Acute exposures in workers provoke headache, dizziness, nausea, vomiting, raised temperature, low blood pressure, leucocytosis, and heart and liver injury. Chronic occupational exposure without protection may cause nausea, liver functional changes, contact toxic dermatitis, irritation of airways and eyes, as well as neurological changes. Some of the derivatives of 2,4-D are embryotoxic and teratogenic for experimental animals in high doses only.
2,4-D and the related phenoxy herbicide 2,4,5-T are rated as group 2B carcinogens (possible human carcinogens) by the IARC. Lymphatic cancers, particularly non-Hodgkin lymphoma (NHL), have been associated in Swedish agricultural workers with exposure to a commercial mixture of 2,4-D and 2,4,5-T (similar to the herbicide Agent Orange used by the US military in Viet Nam during the years 1965 to 1971). Possible carcinogenicity is often ascribed to contamination of 2,4,5-T with 2,3,7,8-tetrachloro-dibenzo-p-dioxin. However, a US National Cancer Institute research group reported a risk of 2.6 for adult NHL among Kansas residents exposed to 2,4-D alone, which is not thought to be dioxin-contaminated.
Dalapon-Na can cause depression, an unbalanced gait, decreased body weight, kidney and liver changes, thyroid and pituitary dysfunctions, and contact dermatitis in workers who are exposed. Diallate has dermal toxicity and causes irritation to the skin, eyes and mucous membranes. Diquat is an irritant to the skin, eyes and upper respiratory tract. It can cause a delay in the healing of cuts and wounds, gastrointestinal and respiratory disturbances, bilateral cataract and functional liver and kidney changes.
Dinoseb presents dangers because of its toxicity through dermal contact. It can cause moderate skin and pronounced eye irritation. The fatal dose for humans is about 1 to 3 g. After an acute exposure, Dinoseb causes central nervous system disturbances, vomiting, reddening (erythema) of the skin, sweating and high temperature. Chronic exposure without protection results in decreased weight, contact (toxic or allergic) dermatitis and gastrointestinal, liver and kidney disturbances. Dinoseb is not used in many countries because of its serious adverse effects.
Fluometuron is a moderate skin sensitizer in guinea-pigs and humans. It has been observed to cause decreased body weight, anaemia, and liver, spleen and thyroid gland disturbances. The biological action of diuron is similar.
Linuron causes mild irritation to the skin and eyes, and has low cumulative toxicity (threshold value after single inhalation 29 mg/m3). It causes CNS, liver, lung and kidney changes in experimental animals, as well as thyroid dysfunction.
MCPA is highly irritant to skin and mucous membranes, has low cumulative toxicity and is embryotoxic and teratogenic in high doses in rabbits and rats. Acute poisoning in humans (an estimated dose of 300 mg/kg) results in vomiting, diarrhoea, cyanosis, mucus burns, clonic spasms, and myocardium and liver injury. It provokes severe contact toxic dermatitis in workers. Chronic exposure without protection results in dizziness, nausea, vomiting, stomach aches, hypotonia, enlarged liver, myocardium dysfunction and contact dermatitis.
Molinate can reach a toxic concentration after single inhalation of 200 mg/m3 in rats. It causes liver, kidney and thyroid disturbances, and is gonadotoxic and teratogenic in rats. It is a moderate skin sensitizer in humans.
Monuron in high doses can result in liver, myocardium and kidney disturbances. It causes skin irritation and sensitization. Similar effects are shown by monolinuron, chloroxuron, chlortoluron and dodine.
Nitrofen is a strong skin and eye irritant. Chronic occupational exposure without protection results in CNS disturbances, anaemia, raised temperature, decreased body weight, fatigue and contact dermatitis. It is considered a possible human carcinogen (group 2B) by the IARC.
Paraquat has dermal toxicity and irritant effects on skin or mucous membranes. It causes nail damage and nose bleeding in occupational conditions without protection. Accidental oral poisoning with paraquat has resulted when it was left within reach of children or transferred from the original container into a bottle used for a beverage. Early manifestations of such intoxication are corrosive gastrointestinal effects, renal tubular damage and liver dysfunction. Death is due to circulatory collapse and progressive pulmonary damage (pulmonary oedema and haemorrhage, intra-alveolar and interstitial fibrosis with alveolitis and hyaline membranes), clinically revealed by dyspnoea, hypoxaemia, basal rales and roentgenographic evidence of infiltration and athelectasis. The renal failure is followed by lung damage, and accompanied in some cases by liver or myocardium disturbances. Mortality is higher with poisoning from liquid concentrate formulations (87.8%), and lower from granular forms (18.5%). The fatal dose is 6 g paraquat ion (equivalent to 30 ml Gramoxone or 4 packets of Weedol), and no survivors are reported at greater doses, irrespective of the time or vigour of treatment. Most survivors had ingested less than 1 g paraquat ion.
Potassium cyanate is associated with high inhalation and dermal toxicity in experimental animals and humans due to the metabolic conversion to cyanide, which is discussed elsewhere in this Encyclopaedia.
Prometryn exhibits moderate dermal toxicity and skin and eye irritation. It provokes decreased clotting and enzyme abnormalities in animals and has been found to be embryotoxic in rats. Exposed workers may complain of nausea and sore throat. Analogous effects are shown by propazine and desmetryne.
Propachlor’s toxicity is doubled at high environmental temperatures. Skin and mucous membrane irritation and mild skin allergy are associated with exposure. The toxic concentration after single inhalation is 18 mg/m3 in rats, and it is thought to exhibit moderate cumulative toxicity. Propachlor causes polyneuropathies; liver, myocardium and kidney disturbances; anaemia; and damage to testes in rats. During spraying from the air, the concentration in the spray cabin has been found to be about 0.2 to 0.6 mg/m3. Similar toxic properties are shown by propanil.
Propham exhibits moderate cumulative toxicity. It causes haemodynamic disturbances, and liver, lung and kidney changes are found in experimental animals.
Simazine causes slight irritation of the skin and mucous membranes. It is a moderate skin sensitizer in guinea-pigs. It also causes CNS, liver and kidney disturbances and has mutagenic effect in experimental animals. Workers may complain of weariness, dizziness, nausea and olfactory deviations after application without protective equipment.
2,4,5-T causes pronounced irritation and embryotoxic, teratogenic and carcinogenic effects in animals; there are also data on its gonadotoxic action in women. Because the extremely toxic chemical dioxin can be a contaminant of the trichlorophenoxy acids, use of 2,4,5-T is prohibited in many countries. Agricultural, forestry and industrial workers exposed to mixtures of 2,4-D and 2,4,5-T have been reported at increased risk for both soft-tissue sarcomas and non-Hodgkin lymphomas.
Trifluralin causes slight irritation of skin and mucous membranes. An increased incidence of liver carcinoma has been found in hybrid female mice, probably due to contamination with N-nitroso compounds. Trifluralin causes anaemia and liver, myocardium and kidney changes in experimental animals. Extensively exposed workers have developed contact dermatitis and photodermatitis.
Fungicides
Some fungi, such as rusts, mildews, moulds, smuts, storage rots and seedling blights, are able to infect and cause diseases in plants, animals and humans. Others can attack and destroy non-living materials such as wood and fibre products. Fungicides are used to prevent these diseases and are applied by spraying, dusting, seed dressing, seedling and soil sterilization, and fumigation of warehouses and greenhouses.
Fungi causing plant diseases can be arranged into four sub-groups, which differ by the microscopic characters of the mycelium, the spores and the organs on which the spores were developed:
1. phycomycetes—soil-borne organisms causing club rot of brassicae, wart diseases of potatoes and so on
2. ascomycetes—perithecia-forming powdery mildews and fungi causing apple scab, black currant leaf spot and rose black spot
3. basidiomycetes, including loose smut of wheat and barley, and several rusts species
4. fungi imperfecti, which includes the genera Aspergillus, Fusarium, Penicillium and so on, that are of great economic importance because they cause significant losses during plant growth, at harvest, and after harvest. (e.g., Fusarium species infect barley, oats and wheat; Penicillium species cause brown rot of pomaceous fruit).
Fungicides have been used for centuries. Copper and sulphur compounds were the first to be used, and Bordeaux mixture was applied in 1885 to vineyards. A great number of widely differing chemical compounds with fungicidal action are used in many countries.
Fungicides can be classified into two groups according to their mode of action: protective fungicides (applied at a time prior to the arrival of the fungal spores—e.g., sulphur and copper compounds) or eradicant fungicides (applied after the plant has become infected—e.g., mercury compounds and nitroderivatives of the phenols). The fungicides either act on the surface of the leaves and seeds or penetrate into the plant and exert their toxic action directly on the fungi (systemic fungicides). They can also alter the physiological and biochemical processes in the plant and thus produce artificial chemical immunization. Examples of this group are the antibiotics and the rodananilides.
Fungicides applied to seed act primarily against surface-borne spores. However, in some cases they are required to persist on the seed coat long enough to be effective against the dormant mycelium contained within the seed. When applied to the seed before sowing, the fungicide is called seed disinfectant or seed dressing, though the latter term may include treatment not intended to counter seed-borne fungi or soil pests. To protect wood, paper, leather and other materials, fungicides are used by impregnation or staining. Special drugs with fungicidal action are also used to control fungal diseases in humans and animals.
Specific field applications include:
Hazards of fungicides
The fungicides cover a great variety of chemical compounds differing widely in their toxicity. Highly toxic compounds are used as fumigants of foods and warehouses, for seed dressing and for soil disinfection, and cases of poisoning have been described with organomercurials, hexachlorobenzene and pentachlorobenzene, as well as with the slightly toxic dithiocarbamates. These and several other chemicals are discussed in more detail elsewhere in this article, chapter and Encyclopaedia. Some are briefly reviewed here.
Chinomethionate has a high cumulative toxicity and inhibits thiol groups and some enzymes containing them; it lowers phagocytic activity and has antispermatogenic effects. It is irritant to the skin and the respiratory system. It can damage the CNS, the liver and the gastrointestinal tract. Glutathione and cysteine provide protection against the acute effects of chinomethionate.
Chloranil is irritating to the skin and the upper respiratory tract; it can also cause depression of the CNS and dystrophic changes in the liver and kidney. The biological monitoring of exposed persons has shown an increased level of the urinary phenols, both free and bound.
Dazomet is used also as a nematocide and a slimicide. This compound and its decomposition products are sensitizers and mild irritants of the eye, nose, mouth and skin. Poisoning is characterized by a variety of symptoms, including anxiety, tachycardia and quick breathing, hypersalivation, clonic cramps, impaired movement coordination, sometimes hyperglycaemia and cholinesterase inhibition. The main pathomorphological findings are enlargement of the liver and degenerative changes of the kidney and other internal organs.
Dichlofluanid inhibits thiol groups. In experimental animals it caused histological changes in liver, proximal tubules of the kidney and adrenal cortex, with the reduction of the lymphatic tissue in the spleen. It is a moderate irritant of the skin and mucous membranes.
Diclone, in addition to sharing the irritant and blood depressant properties common to quinones, is an experimental animal carcinogen.
Dinobuton, like dinitro-o-cresol (DNOC), disturbs cell metabolism by inhibiting oxidative phosphorylation, with the loss of energy-rich compounds such as adenosintriphosphoric acid (ATP). It can cause severe liver dystrophy and necrosis of the convoluted tubules of the kidneys. The clinical manifestations of the intoxication are high temperature, methaemoglobinaemia and haemolysis, nervous disturbances and irritation of the skin and mucous membranes.
Dinocap can increase the blood level of alkaline phosphatase and is a moderate irritant of the skin and mucous membranes. It produces distrophic changes in the liver and kidney, and hypertrophy of the myocardium. In acute poisoning, disturbances in thermoregulation, clonic cramps and breathing difficulties have been observed.
Hexachlorobenzene (HCB) is stored in the body fat. It interferes with porphyrin metabolism, increasing the urinary excretion of coproporphyrins and uroporphyrins; it increases also the levels of transaminases and dehydrogenases in the blood. It can produce liver injury (hepatomegaly and cirrhosis), photosensitization of the skin, a porphyria similar to porphyria cutanea tarda, arthritis and hirsutism (monkey disease). It is a skin irritant. Chronic poisoning needs long-term treatment, mainly symptomatic, and it is not always reversible on cessation of exposure. It is classified as a possible human carcinogen (group 2B) by the IARC.
Milneb can cause gastrointestinal disturbances, weakness, decrease of the body temperature and leukopoenia.
Nirit has haemotoxic properties and causes anaemia and leucocytosis with toxic granulation of the leucocytes, in addition to degenerative changes in the liver, spleen and kidneys.
Quinones, in general, cause blood disturbances (methaemoglobinaemia, anaemia), affect the liver, disturb vitamin metabolism, particularly that of ascorbic acid, and are irritant to the respiratory ways and the eye. Chloranil and dichlone are the quinone derivatives most widely used as fungicides.
Thiabendazole has caused thymus involution, colloid depletion in the thyroid and increase in liver and kidney size. It is also used as an anthelmintic in cattle.
Safety and Health Measures
Labelling and storage
The requirements regarding the labelling of pesticides laid down in national and international legislation should be strictly applied to both imported and locally produced chemicals. The label should give the following essential information: both the approved name and the trade name of the chemical; the name of the manufacturer, packager or supplier; the directions for use; the precautions to be taken during use, including details of protective equipment to be worn; the symptoms of poisoning; and the first-aid treatment for suspected poisoning.
The greater the degree of toxicity or hazard of the chemical, the more precise should be the wording on the label. It is sound practice for the different classes to be clearly distinguished by background colours on the label and, in the case of compounds of high or extreme hazard, for the appropriate danger symbol to be incorporated. It often occurs that an adequately labelled quantity of pesticide in bulk is locally repacked into smaller containers. Each such small package should bear a similar label, and repacking in containers which have held, or are easily identifiable with, containers used for food should be absolutely forbidden. If small packages are to be transported, the same rules apply as for the carriage of larger packages. (See the chapter Using, storing and transporting chemicals.)
Pesticides of moderate or higher hazard should be so stored that only authorized persons can have access to them. It is particularly important that children should be excluded from any contact with pesticide concentrates or residues. Spillages often occur in storage and repacking rooms, and they must be cleaned up with care. Rooms used only for storage should be soundly constructed and fitted with secure locks. Floors should be kept clear and the pesticides clearly identified. If repacking is carried out in storage rooms, adequate ventilation and light should be available; floors should be impervious and sound; washing facilities should be available; and eating, drinking and smoking should be prohibited in the area.
A few compounds react with other chemicals or with air, and this has to be taken into account when planning storage facilities. Examples are cyanide salts (which react with acid to produce hydrogen cyanide gas) and dichlorvos (which vaporizes in contact with air). (Dichlorvos is classified as a group 2B possible human carcinogen by the IARC.).
Mixing and application
Mixing and application may comprise the most hazardous phase of the use of pesticides, since the worker is exposed to the concentrate. In any particular situation, only selected persons should be responsible for mixing; they should be thoroughly conversant with the hazards and provided with the proper facilities for dealing with accidental contamination. Even when the mixed formulation is of such a toxicity that it can be used with a minimum of personal protective equipment (PPE), more elaborate equipment may need to be provided for and used by the mixer.
For pesticides of moderate or higher hazard, some type of PPE is almost always necessary. The choice of particular items of equipment will depend on the hazard of the pesticide and the physical form in which it is being handled. Any consideration of PPE must also include not only provision but also adequate cleaning, maintenance and replacement.
Where climatic conditions preclude the use of some types of PPE, three other principles of protection can be applied—protection by distance, protection by time and protection by change of working method. Protection by distance involves modification of the equipment used for application, so that the person is as far away as possible from the pesticide itself, bearing in mind the likely routes of absorption of a specific compound.
Protection by time involves limitation of hours of work. The suitability of this method depends on whether the pesticide is readily excreted or whether it is cumulative. Accumulation of some compounds occurs in the body when the rate of excretion is slower than the rate of absorption. With some other compounds, a cumulative effect may occur when the person is exposed to repeated small doses which, taken individually, may not give rise to symptoms.
Protection by change of working method involves a reconsideration of the whole operation. Pesticides differ from other industrial processes in that they can be applied from the ground or the air. Changes of method on the ground depend largely on the choice of equipment and the physical nature of the pesticide to be applied.
Pesticides that are applied from the air can be in the form of liquids, dusts or granules. Liquids may be sprayed from very low altitudes, frequently as fine droplets of concentrated formulations, known as ultra-low volume (ULV) applications. Drift is a problem particularly with liquids and dusts. Aerial application is an economical way of treating large tracts of land but entails special hazards to pilots and to workers on the ground. Pilots can be affected by leakage from hoppers, by pesticides carried into the cockpit on clothes and boots, and by flying back through the swathe just released or through the drift from the swathe. Even minor degrees of absorption of some pesticides or their local effects (such as may be caused, for instance, by an organophosphorus compound in the eye) can affect a pilot to the extent that he or she cannot maintain the high degree of vigilance necessary for low flying. Pilots should not be allowed to engage in pesticide operations unless they have been specially trained in the items listed above, in addition to any special aviation and agricultural operational requirements.
On the ground, loaders and flaggers may be affected. The same principles apply to loaders as to others dealing with pesticides in bulk. Flaggers mark the swathe to be flown and can be severely contaminated if the pilot misjudges the moment of release. Balloons or flags can be placed in position before or ahead of the operation, and workers should never be used as flaggers within the flight pattern.
Other restrictions
The hazards associated with pesticides do not end with their application; with the more toxic compounds it has been shown that there is a danger to workers entering a sprayed crop too soon after application. It is therefore important that all workers and members of the general public should be informed concerning the areas where a toxic pesticide has been applied and the earliest date on which it is safe to enter and work in these areas. Where a food crop has been sprayed, it is also important that the crop not be harvested until a sufficient period has elapsed for degradation of the pesticide to take place, in order to avoid excessive residues on food.
Disposal of pesticides and containers. Spillage of pesticides at any stage of their storage or handling should be treated with great care. Liquid formulations may be reduced to solid phase by evaporation. Dry sweeping of solids is always hazardous; in the factory environment, these should be removed by vacuum cleaning or by dissolving them in water or other solvent. In the field they may be washed away with water into a suitable soak-hole. Contaminated topsoil should be removed and buried if any domestic animals or fowls are in the area. Soak-holes should be used for disposing of washing waters from cleaning application equipment, clothing or hands. These should be at least 30 cm deep and sited well away from wells or watercourses.
Empty pesticide containers should be collected with care, or disposed of safely. Plastic liners, and paper or card containers should be crushed and buried well below the topsoil or burned, preferably in an incinerator. Metal containers of some pesticides can be decontaminated according to the instructions of the pesticide manufacturers. Such drums should be clearly marked “Not to be used for food or for water for drinking or domestic use”. Other metal containers should be punctured, crushed or buried.
Hygiene and first aid
Where a pesticide is of moderate or higher hazard and can be readily absorbed through the skin, special precautions are necessary. In some situations where workers may become accidentally contaminated with large quantities of concentrate, such as in factory situations and mixing, it is necessary to provide a shower bath in addition to the usual washing facilities. Special arrangements for cleaning clothing and overalls may be necessary; in any case, these should not be left for the worker to wash at home.
Since pesticides are often applied outside the factory environment, depending on the chemical used, special care may have to be taken to provide washing facilities at the workplace, even though this may be in remote fields. Workers must never bathe themselves in canals and rivers, the water from which may be subsequently used for other purposes; the washing water provided should be disposed of with care as outlined above. Smoking, eating and drinking before washing should be absolutely prohibited when any pesticide of moderate or higher toxicity is being handled or used.
Where an antidote exists which can be readily used as a first-aid measure for a specific pesticide (e.g., atropine for organophosphorus poisoning), it should be readily available to workers, who should be instructed in the method of its use. When any pesticide is being used on a substantial scale, medical personnel in the area should be informed by the persons responsible for distribution. The nature of the chemical used should be well defined so that medical facilities can be equipped and will know the specific antidotes, where these are applicable and how to recognize cases of poisoning. Facilities should also be available in order to make proper differential diagnosis, even if these are of the simplest type, such as test papers for determining cholinesterase levels. Strict routine medical supervision of workers heavily exposed to concentrates, as in the manufacture and packing of pesticides, is essential and should include laboratory tests and routine surveillance and record keeping.
Training
While all workers using pesticide formulations of moderate or higher hazard should be thoroughly trained in their use, such training is particularly important if the pesticide is extremely toxic. Training programmes must cover: toxicity of compounds used and routes of absorption; handling of concentrates and formulations; methods of use; cleaning of equipment; precautions to be taken and PPE to be worn; maintenance of PPE; avoidance of contamination of other crops, foods and water supplies; early symptoms of poisoning; and first-aid measures to be taken. All training should be strictly relevant to the pesticide actually being used, and, in the case of extremely hazardous compounds, it is wise to license operators following an examination to show that they have, in fact, a good understanding of the hazards and the procedures to be followed.
Public health measures
When pesticides are used, every effort must be made to avoid contamination of water supplies, whether these are officially recognized supplies or not. This not only concerns the actual application (when there may be immediate contamination) but must also include consideration of remote contamination by run-off through rainfall on recently treated areas. While pesticides in natural watercourses may be diluted to such a degree that the contaminated water may not be hazardous in itself, the effect on fish, on water vegetables used as food and grown in the watercourses, and on wild life as a whole must not be overlooked. Such hazards may be economic rather than directly related to health, but are no less important.
Adapted from WHO 1996.
Individual products are classified in a series of tables according to the products’ oral and dermal toxicity and physical states. Technical products classified as Class IA (extremely hazardous, Class IB (highly hazardous), Class II (moderately hazardous) and Class III (slightly hazardous) are listed in table 1, table 2, table 3 and table 4, respectively. Technical products unlikely to present any acute hazard in normal use are listed in table 5. The classification given in tables 1 to 5 is of technical compounds and only forms the starting point for the final classification of an actual formulation: the final classification of any product depends on its formulation. Classification of mixtures of pesticides is not included; many of these mixtures are marketed with varying concentrations of active constituents. (For information on how to find the hazard class of formulations and mixtures, see WHO 1996.) Technical products believed to be absolete or discontinued (see table 6) are not inclued in the Classification. Table 7 lists gaseous fumigants not included in the WHO Recommanded Classification of Pesticides by Hazard.C
On this page are the following tables. Please return to the Minerals and Agricultural Chemicals chapter page for the remaining tables.
Table 1. List of technical products classified in Class IA: "Extremely hazardous"
Table 2. List of technical products classified in Class IB: "Highly hazardous"
Table 3. List of technical products classified in Class II: "Moderately hazardous"
Table 1. List of technical products classified in Class IA: "Extremely hazardous"
Name |
Status |
Main use |
Chemical type |
Physical state |
Route |
LD50 (mg/kg) |
Remarks |
Acrolein |
C |
H |
L |
O |
29 |
EHC 127; HSG 67 |
|
Alachlor |
ISO |
H |
S |
O |
930 |
Adjusted classification; carcinogenic in rats and mice; DS 84 |
|
Aldicarb |
ISO |
I-S |
C |
S |
O |
0.93 |
DS 53; EHC 121; HSG 64 |
Arsenous oxide |
C |
R |
S |
O |
180 |
Adjusted classification; minimum lethal dose for humans of 2 mg/kg; evidence of carcinogenicity for humans is sufficient; EHC 18; HSG 70 |
|
Brodifacoum |
ISO |
R |
S |
O |
0.3 |
DS 57; EHC 175; HSG 93 |
|
Bromadialone |
ISO |
R |
S |
O |
1.12 |
DS 88; EHC 175; HSG 94 |
|
Bromethalin |
ISO |
R |
S |
O |
2 |
||
Calcium cyanide |
C |
FM |
S |
O |
39 |
Adjusted classification; calcium cyanide is in Class IA as it reacts with moisture to produce hydrogen cyanide gas; the gas is not classified under the WHO system (see table 7) |
|
Captafol |
ISO |
F |
S |
O |
5,000 |
Adjusted classification; carcinogenic in rats and mice; HSG 49 |
|
Chlorfenvinphos |
ISO |
I |
OP |
L |
O |
10 |
|
Chlormephos |
ISO |
I |
OP |
L |
O |
7 |
|
Chlorophacinone |
ISO |
R |
S |
O |
3.1 |
DS 62; EHC 175 |
|
Chlorthiophos |
ISO |
I |
OP |
L |
O |
9.1 |
|
Coumaphos |
ISO |
AC, MT |
OP |
L |
O |
7.1 |
|
CVP |
N(J) |
See chlorfenvinphos |
|||||
Cycloheximide |
ISO |
F |
S |
O |
2 |
||
DBCP |
N(J) |
See dibromochloropropane |
|||||
Demephion-O and -S |
ISO |
I |
OP |
L |
O |
15 |
|
Demeton-O and -S |
ISO |
I |
OP |
L |
O |
2.5 |
DS 60 |
Dibromochloropropane |
C |
F-S |
L |
O |
170 |
Adjusted classification; has been found to cause sterility in humans and is mutagenic and carcinogenic in animals |
|
Difenacoum |
ISO |
R |
S |
O |
1.8 |
EHC 175; HSG 95 |
|
Difethialone |
ISO |
R |
S |
O |
0.56 |
EHC 175 |
|
Difolatan |
N(J) |
See captafol |
|||||
Dimefox |
ISO |
I |
OP |
L |
O |
1 |
Volatile |
Diphacinone |
ISO |
R |
S |
O |
2.3 |
EHC 175 |
|
Disulfoton |
ISO |
I |
OP |
L |
O |
2.6 |
DS 68 |
EPN |
N(A,J) |
I |
OP |
S |
O |
14 |
Has been reported as causing delayed neurotoxicity in hens |
Ethoprop |
N(A) |
See ethoprophos |
|||||
Ethoprophos |
ISO |
I-S |
OP |
L |
D |
26 |
DS 70 |
Ethylthiometon |
N(J) |
See disulfoton |
|||||
Fenamiphos |
ISO |
N |
OP |
L |
O |
15 |
DS 92 |
Fensulfothion |
ISO |
I |
OP |
L |
O |
3.5 |
DS 44 |
Flocoumafen |
N(B) |
R |
S |
O |
0.25 |
EHC 175 |
|
Fonofos |
ISO |
I-S |
OP |
L |
O |
c8 |
|
Hexachlorobenzene |
ISO |
FST |
S |
D |
10,000 |
Adjusted classification; has caused a serious outbreak of porphyria in humans; DS 26 |
|
Leptophos |
ISO |
I |
OP |
S |
O |
50 |
Adjusted classification; has been shown to cause delayed neurotoxicity; DS 38 |
M74 |
N(J) |
See disulfoton |
|||||
MBCP |
N(J) |
See leptophos |
|||||
Mephosfolan |
ISO |
I |
OP |
L |
O |
9 |
|
Mercuric chloride |
ISO |
F-S |
S |
O |
1 |
||
Merkaptophos |
N(U) |
When mixed with merkaptophosteolovy, see demeton -O and -S |
|||||
Metaphos |
N(U) |
See parathion-methyl |
|||||
Mevinphos |
ISO |
I |
OP |
L |
D |
4 |
DS 14 |
Nitrofen |
ISO |
H |
S |
O |
c3,000 |
Adjusted classification; carcinogenic in rats and mice; teratogenic in several species tested; DS 84 |
|
Parathion |
ISO |
I |
OP |
L |
O |
13 |
DS 6; HSG 74 |
Parathion-methyl |
ISO |
I |
OP |
L |
O |
14 |
DS 7; EHC 145; HSG 75 |
Phenylmercury acetate |
ISO |
FST |
S |
O |
24 |
Adjusted classification; highly toxic to mammals and very small doses have produced renal lesions; teratogenic in the rat |
|
Phorate |
ISO |
I |
OP |
L |
O |
2 |
DS 75 |
Phosfolan |
ISO |
I |
OP |
L |
O |
9 |
|
Phosphamidon |
ISO |
I |
OP |
L |
O |
7 |
DS 74 |
Prothoate |
ISO |
AC,I |
OP |
L |
O |
8 |
|
Red squill |
See scilliroside |
||||||
Schradan |
ISO |
I |
OP |
L |
O |
9 |
|
Scilliroside |
C |
R |
S |
O |
c0.5 |
Induces vomiting in mammals |
|
Sodium fluoroacetate |
C |
R |
S |
O |
0.2 |
DS 16 |
|
Sulfotep |
ISO |
I |
OP |
L |
O |
5 |
|
TEPP |
ISO |
AC |
OP |
L |
O |
1.1 |
|
Terbufos |
ISO |
I-S |
OP |
L |
O |
c2 |
|
Thiofos |
N(U) |
See parathion |
|||||
Thionazin |
ISO |
N |
OP |
L |
O |
11 |
|
Timet |
N(U) |
See phorate |
Table 2. List of technical products classified in Class IB: "Highly hazardous"
Name |
Status |
Main use |
Chemical type |
Physical state |
Route |
LD50 (mg/kg) |
Remarks |
Aldoxycarb |
ISO |
I,N |
C |
S |
O |
27 |
|
Aldrin |
ISO |
I |
OC |
S |
D |
98 |
DS41; EHC 91; HSG 21 |
Allyl alcohol |
C |
H |
L |
O |
64 |
Highly irritant to skin and eyes |
|
Aminocarb |
ISO |
I |
C |
S |
O |
50 |
|
Antu |
ISO |
R |
S |
O |
8 |
Induces vomiting in dogs. Some impurities are carcinogenic |
|
Azinphos-ethyl |
ISO |
I |
OP |
S |
O |
12 |
DS 72 |
Azinphos-methyl |
ISO |
I |
OP |
S |
O |
16 |
DS 59 |
Benfuracarb |
N(B) |
I |
C |
L |
O |
138 |
|
Bis(tributyltin) oxide |
C |
F,M |
L |
O |
194 |
Irritant to skin. DS 65; EHC 15 |
|
Blasticidin-S |
N(J) |
F |
S |
O |
16 |
||
Bromophos-ethyl |
ISO |
I |
OP |
L |
O |
71 |
|
Butocarboxim |
ISO |
I |
C |
L |
O |
158 |
|
Butoxycarboxim |
ISO |
I |
C |
L |
D |
288 |
|
Cadusafos |
ISO |
N,I |
OP |
L |
O |
37 |
|
Calcium arsenate |
C |
I |
S |
O |
20 |
||
Carbofuran |
ISO |
I |
C |
S |
O |
8 |
DS 56 |
Carbophenothion |
ISO |
I |
OP |
L |
O |
32 |
|
3-chloro-1,2-propanediol |
C |
R |
L |
O |
112 |
In non-lethal dosage is a sterilant for male rats |
|
Coumachlor |
ISO |
R |
S |
D |
33 |
||
Coumatetralyl |
ISO |
R |
S |
O |
16 |
||
Crotoxyphos |
ISO |
I |
OP |
L |
O |
74 |
|
zeta-Cypermethrin |
ISO |
I |
PY |
L |
O |
c86 |
|
DDVF |
N(U) |
See dichlorvos |
|||||
DDVP |
N(J) |
See dichlorvos |
|||||
Delnav |
N(U) |
See dioxathion |
|||||
Demeton-S-methyl |
ISO |
I |
OP |
L |
O |
40 |
DS 61 |
Demeton-S-methylsulphon |
ISO |
I |
OP |
S |
O |
37 |
|
Dichlorvos |
ISO |
I |
OP |
L |
O |
56 |
Volatile, DS 2; EHC 79; HSG 18 |
Dicrotophos |
ISO |
I |
OP |
L |
O |
22 |
|
Dieldrin |
ISO |
I |
OC |
S |
O |
37 |
DS 17: EHC 91 |
Dimetilan |
N(A,B) |
I |
C |
S |
O |
47 |
|
Dinoseb |
ISO |
H |
CNP |
L |
O |
58 |
|
Dinoseb acetate |
ISO |
H |
CNP |
L |
O |
60 |
|
Dinoterb |
ISO |
H |
CNP |
S |
O |
25 |
|
Dioxathion |
ISO |
I |
OP |
L |
O |
23 |
|
DMTP |
N(J) |
See methidathion |
|||||
DNBP |
N(J) |
See dinoseb |
|||||
DNBPA |
N(J) |
See dinoseb acetate |
|||||
DNOC |
ISO |
I-S,H |
CNP |
S |
O |
25 |
|
EDDP |
N(J) |
See edifenfos |
|||||
Edifenphos |
ISO |
F |
OP |
L |
O |
150 |
|
Endrin |
ISO |
I |
OC |
S |
O |
7 |
DS 1; EHC 130; HSG 60 |
ESP |
N(J) |
I |
OP |
L |
O |
105 |
|
Famphur |
N(A) |
I |
OP |
S |
O |
48 |
|
Flucythrinate |
ISO |
I |
PY |
L |
O |
c67 |
Irritant to skin and eyes |
Fluoroacetamide |
C |
R |
S |
O |
13 |
||
Formetanate |
ISO |
AC |
C |
S |
O |
21 |
|
Fosmethilan |
ISO |
I |
OP |
S |
O |
49 |
Irritant to skin and eyes. |
Furathiocarb |
N(B) |
I-S |
C |
L |
O |
42 |
|
Heptenophos |
ISO |
I |
OP |
L |
O |
96 |
|
Isazofos |
ISO |
I-S |
OP |
L |
O |
60 |
|
Isofenphos |
ISO |
I |
OP |
oil |
O |
28 |
|
Isothioate |
ISO |
I |
OP |
L |
O |
150 |
|
Isoxathion |
ISO |
I |
OP |
L |
O |
112 |
|
Lead arsenate |
C |
L |
S |
O |
c10 |
||
Mecarbam |
ISO |
I |
C |
oil |
O |
36 |
|
Mercuric oxide |
ISO |
O |
S |
O |
18 |
||
Methamidophos |
ISO |
I |
OP |
L |
O |
30 |
HSG 79 |
Methidathion |
ISO |
I |
OP |
L |
O |
25 |
|
Methomyl |
ISO |
I |
C |
S |
O |
17 |
DS 55, EHC 178; HSG 97 |
Methyl-merkapto-phosteolovy |
N(U) |
See demeton-S-methyl |
|||||
Metilmerkapto-phosoksid |
N(U) |
See oxydemeton-methyl |
|||||
Metriltriazotion |
N(U) |
See azinphos-methyl |
|||||
Monocrotophos |
ISO |
I |
OP |
S |
O |
14 |
HSG 80 |
MPP |
N(J) |
See fenthion |
|||||
Nicotine |
ISO |
L |
D |
50 |
|||
Omethoate |
ISO |
I |
OP |
L |
O |
50 |
|
Oxamyl |
ISO |
I |
C |
S |
O |
6 |
DS 54 |
Oxydemeton-methyl |
ISO |
I |
OP |
L |
O |
65 |
|
Oxydeprofos |
N(B) |
See ESP |
|||||
Paris green |
C |
L |
S |
O |
22 |
Copper-arsenic complex |
|
Pentachlorophenol |
ISO |
I,F,H |
CNP |
S |
D |
80 |
Irritant to skin; EHC 71; HSG 19 |
Phenylmercury nitrate |
C |
FST |
OM |
S |
Oral LD50 not available, rat i.v. LD50 is 27 mg/kg |
||
Pirimiphos-ethyl |
ISO |
I |
OP |
L |
O |
140 |
|
Propaphos |
N(J) |
I |
OP |
L |
O |
70 |
|
Propetamphos |
ISO |
I |
OP |
L |
O |
106 |
|
Sodium arsenite |
C |
R |
S |
O |
10 |
||
Sodium cyanide |
C |
R |
S |
O |
6 |
||
Strychnine |
C |
R |
S |
O |
16 |
||
TBTO |
See bis-(tributyltin) oxide |
||||||
Tefluthrin |
N(B) |
I-S |
PY |
S |
O |
c22 |
|
Thallium sulfate |
C |
R |
S |
O |
11 |
DS 10 |
|
Thiofanox |
ISO |
I-S |
C |
S |
O |
8 |
|
Thiometon |
ISO |
I |
OP |
oil |
O |
120 |
DS 67 |
Thioxamyl |
See oxyamyl |
||||||
Triamiphos |
ISO |
F |
S |
O |
20 |
||
Triazophos |
ISO |
I |
OP |
L |
O |
82 |
|
Triazotion |
N(U) |
See azinphos-ethyl |
|||||
Vamidothion |
ISO |
I |
OP |
L |
O |
103 |
|
Warfarin |
ISO |
R |
S |
O |
10 |
DS 35, EHC 175; HSG 96 |
|
Zinc phosphide |
C |
R |
S |
O |
45 |
DS 24, EHC 73 |
Table 3. List of technical products classified in Class II: "Moderately hazardous"
Name |
Status |
Main Use |
Chemical type |
Physical state |
Route |
LD50 (mg/kg) |
Remarks |
Alanycarb |
ISO |
I |
C |
S |
O |
330 |
|
Allidochlor |
ISO |
H |
L |
O |
700 |
Irritant to skin and eyes |
|
Anilofos |
ISO |
H |
S |
O |
472 |
||
Azaconazole |
N(B) |
F |
S |
O |
308 |
||
Azocyclotin |
ISO |
AC |
OT |
S |
O |
80 |
|
Bendiocarb |
ISO |
I |
C |
S |
O |
55 |
DS 52 |
Bensulide |
ISO |
H |
L |
O |
270 |
||
Benzofos |
N(U) |
See phosalone |
|||||
BHC |
ISO |
See HCH |
|||||
gamma-BHC |
See gamma-HCH |
||||||
Bifenthrin |
N(B) |
I |
PY |
S |
O |
c55 |
|
Bilanafos |
ISO |
H |
S |
O |
268 |
||
Binapacryl |
ISO |
AC |
S |
O |
421 |
||
Bioallethrin |
C |
I |
PY |
L |
O |
c700 |
Bioallethrin, esbiothrin, esbiol and esdepalléthrine are members of the allethrin series; their toxicity varies considerably within this series according to concentrations of isomers. |
Bisthiosemi |
N(J) |
R |
S |
O |
c150 |
Induces vomiting in non-rodents |
|
BPMC |
See fenobucarb |
||||||
Bromoxynil |
ISO |
H |
S |
O |
190 |
||
Bronopol |
N(B) |
B |
S |
O |
254 |
||
Bufencarb |
ISO |
I |
C |
S |
O |
87 |
|
Butamifos |
ISO |
H |
L |
O |
630 |
||
Butenachlor |
ISO |
H |
L |
O |
1,630 |
||
Butylamine |
ISO |
F |
L |
O |
380 |
Irritant to skin |
|
Camphechlor |
ISO |
I |
OC |
S |
O |
80 |
DS 20; EHC 45 |
Carbaryl |
ISO |
I |
C |
S |
O |
c300 |
DS 3; EHC 153; HSG 78 |
Carbosulfan |
ISO |
I |
L |
O |
250 |
||
Cartap |
ISO |
I |
S |
O |
325 |
||
Chloralose |
C |
R |
S |
O |
400 |
||
Chlordane |
ISO |
I |
OC |
L |
O |
460 |
DS 36; EHC 34; HSG 13 |
Chlordimeform |
ISO |
AC |
OC |
S |
O |
340 |
|
Chlorphenamidine |
N(J) |
See chlordimeform |
|||||
Chlorphonium |
ISO |
PGR |
S |
O |
178 |
Irritant to skin and eyes |
|
Chlorpyrifos |
ISO |
I |
OP |
S |
O |
135 |
DS 18 |
Clomazone |
ISO |
H |
L |
O |
1,369 |
||
Copper sulfate |
C |
F |
S |
O |
300 |
||
Cuprous oxide |
C |
F |
S |
O |
470 |
||
Cyanazine |
ISO |
H |
T |
S |
O |
288 |
|
Cyanofenphos |
ISO |
I |
OP |
S |
O |
89 |
Has been reported as causing delayed neurotoxicity in hens; no longer manufactured |
Cyanophos |
ISO |
I |
OP |
L |
O |
610 |
|
CYAP |
N(J) |
See cyanophos |
|||||
Cyfluthrin |
ISO |
I |
PY |
S |
O |
c250 |
|
beta-Cyfluthrin |
ISO |
I |
PY |
S |
O |
450 |
|
Cyhalothrin |
ISO |
Ix |
PY |
oil |
O |
c144 |
EHC 99 |
lambda-Cyhalothrin |
N(B) |
I |
PY |
S |
O |
c56 |
EHC 142; HSG 38 |
CYP |
N(J) |
See cyanofenphos |
|||||
Cypermethrin |
ISO |
I |
PY |
S |
O |
c250 |
DS 58; EHC 82; HSG 22 |
alpha-Cypermethrin |
ISO |
I |
PY |
S |
O |
c79 |
EHC 142 |
beta-Cypermethrin |
ISO |
I |
PY |
S |
O |
166 |
|
Cyphenothrin ((1R)-isomers) |
ISO |
I |
PY |
L |
O |
318 |
|
Cyprofuram |
ISO |
F |
S |
O |
174 |
||
2,4-D |
ISO |
H |
PA |
S |
O |
375 |
DS 37; EHC 29; EHC 84 |
DAPA |
N(J) |
See fenaminosulf |
|||||
DDT |
ISO |
I |
OC |
S |
O |
113 |
DS 21; EHC 9; EHC 83 |
Deltamethrin |
ISO |
I |
PY |
S |
O |
c135 |
DS 50; EHC 97; HSG 30 |
Dialifor |
N(A,J) |
See dialifos |
|||||
Dialifos |
ISO |
I |
OP |
S |
D |
145 |
|
Di-allate |
ISO |
H |
TC |
L |
O |
395 |
|
Diazinon |
ISO |
I |
OP |
L |
O |
300 |
DS 45 |
Dibrom |
N (Denmark) |
See naled |
|||||
Dichlofenthion |
ISO |
I-S |
OP |
L |
O |
270 |
|
Difenzoquat |
ISO |
H |
S |
O |
470 |
||
Dimethoate |
ISO |
I |
OP |
S |
O |
c150 |
DS 42; EHC 90; HSG 20 |
Dinobuton |
ISO |
AC,F |
S |
O |
140 |
||
Dioxabenzophos |
N(B) |
I |
OP |
S |
O |
125 |
|
Dioxacarb |
ISO |
I |
C |
S |
O |
90 |
|
Diquat |
ISO |
H |
P |
S |
O |
231 |
Irritant to skin, and eyes, and damages nails; DS 40; EHC 39; HSG 52 |
Drazoxolon |
(ISO) |
FST |
S |
O |
126 |
||
ECP |
N(J) |
See dichlofenthion |
|||||
Endosulfan |
ISO |
I |
OC |
S |
O |
80 |
DS 15; EHC 40; HSG 17 |
Endothal-sodium |
(ISO) |
H |
S |
O |
51 |
||
EPBP |
N(J) |
I-S |
OP |
oil |
O |
275 |
|
EPTC |
ISO |
H |
TC |
L |
O |
1,652 |
|
Esbiol |
See bioallethrin |
||||||
Esbiothrin |
See bioallethrin |
||||||
Esdepalléthrine |
See bioallethrin |
||||||
Esfenvalerate |
ISO |
I |
PY |
S |
O |
87 |
|
Ethiofencarb |
ISO |
I |
C |
L |
O |
411 |
|
Ethion |
ISO |
I |
OP |
L |
O |
208 |
|
Etrimfos |
ISO |
I |
OP |
L |
O |
1,800 |
|
Fenaminosulf |
ISO |
F-S |
S |
O |
60 |
||
Fenazaquin |
ISO |
AC |
S |
O |
134 |
||
Fenchlorphos |
ISO |
I |
OP |
L |
O |
1,740 |
DS 69 |
Fenitrothion |
ISO |
I |
OP |
L |
O |
503 |
DS 30; EHC 133; HSG 65 |
Fenobucarb |
N(B) |
I |
C |
S |
O |
620 |
|
Fenpropathrin |
ISO |
I |
PY |
S |
O |
c66 |
|
Fenthion |
ISO |
I,L |
OP |
L |
D |
586 |
DS 23 |
Fentin acetate |
(ISO) |
F |
OT |
S |
O |
125 |
DS 22 |
Fentin hydroxide |
(ISO) |
F |
OT |
S |
O |
108 |
DS 22 |
Fenvalerate |
ISO |
I |
PY |
L |
O |
c450 |
EHC 95, DS 90; HSG 34 |
Fipronil |
N(B) |
I |
Pyrazole |
S |
O |
92 |
|
Fluvalinate |
N(B) |
I |
oil |
O |
282 |
Irritant to skin |
|
Fluxofenim |
ISO |
H |
oil |
O |
670 |
||
Formothion |
ISO |
I |
OP |
L |
O |
365 |
|
Fosfamid |
N(U) |
See dimethoate |
|||||
Furconazole-cis |
ISO |
F |
S |
O |
450 |
||
Guazatine |
N(B) |
FST |
S |
O |
230 |
LD50 value refers to triacetate |
|
Haloxyfop |
N(A,B) |
H |
S |
O |
393 |
||
HCH |
ISO |
I |
OC |
S |
O |
100 |
The LD50 varies according to the mixture of isomers. The value shown has been chosen, and the technical product placed in Class II, as a result of the cumulative properties of the beta isomer |
Gamma-HCH |
ISO |
I |
OC |
S |
O |
88 |
DS 12; EHC 124; HSG 54 |
Heptachlor |
ISO |
I |
OC |
S |
O |
100 |
DS 19; EHC 38; HSG 14 |
Imazalil |
ISO |
F |
S |
0 |
320 |
||
Imidacloprid |
N(B) |
I |
Nitro- guanidine |
S |
O |
450 |
|
Iminoctadine |
ISO |
F |
S |
O |
300 |
Eye irritant |
|
Ioxynil |
ISO |
H |
S |
O |
110 |
||
Ioxynil octanoate |
(ISO) |
H |
S |
O |
390 |
||
Isoprocarb |
ISO |
I |
C |
S |
O |
403 |
|
Karbation |
N(U) |
See metam-sodium |
|||||
Lindane |
ISO |
See gamma-HCH |
|||||
MEP |
N(J) |
See fenitrothion |
|||||
Mercaptodimethur |
See methiocarb |
||||||
Mercurous chloride |
C |
F |
S |
O |
210 |
||
Metaldehide |
ISO |
M |
S |
O |
227 |
||
Metam-sodium |
(ISO) |
F-S |
S |
O |
285 |
||
Methacrifos |
ISO |
I |
OP |
L |
O |
678 |
|
Methasulfocarb |
ISO |
F |
S |
O |
112 |
||
Methiocarb |
ISO |
I |
C |
S |
O |
100 |
|
Methyl isothiocyanate |
ISO |
F-S |
S |
O |
72 |
Skin and eye irritant |
|
Metolcarb |
ISO |
I |
C |
S |
O |
268 |
|
MICP |
N(J) |
See isoprocarb |
|||||
Molinate |
ISO |
H |
TC |
L |
O |
720 |
|
MPMC |
See xylylcarb |
||||||
Nabam |
ISO |
F |
TC |
S |
O |
395 |
Goitrogenic in rats |
NAC |
N(J) |
See carbaryl |
|||||
Naled |
ISO |
I |
OP |
L |
O |
430 |
DS 39 |
Norbormide |
ISO |
R |
S |
O |
52 |
||
2,4-PA |
N(J) |
See 2,4-D |
|||||
PAP |
N(J) |
See phenthoate |
|||||
Paraquat |
ISO |
H |
P |
S |
O |
150 |
Has serious delayed effects if absorbed; is relatively low hazard in actual use but is dangerous if accidentally taken orally; DS 4; EHC 39; HSG 51 |
Pebulate |
ISO |
H |
TC |
L |
O |
1,120 |
|
Permethrin |
ISO |
I |
PY |
L |
O |
c500 |
DS 51; EHC 94; HSG 33 |
PHC |
N(J) |
See propoxur |
|||||
Phenthoate |
ISO |
I |
OP |
L |
O |
c400 |
DS 48 |
Phosalone |
ISO |
I |
OP |
L |
O |
120 |
|
Phosmet |
ISO |
I,AC |
OP |
S |
O |
230 |
|
Phoxim |
ISO |
I |
OP |
L |
D |
1,975 |
DS 31 |
Phthalofos |
N(U) |
See phosmet |
|||||
Pindone |
ISO |
R |
S |
O |
50 |
||
Piperophos |
ISO |
H |
oil |
O |
324 |
||
Pirimicarb |
ISO |
AP |
C |
S |
O |
147 |
|
Polychlorcamphene |
N(U) |
See camphechlor |
|||||
Prallethrin |
ISO |
I |
PY |
oil |
O |
460 |
|
Profenofos |
ISO |
I |
OP |
L |
O |
358 |
|
Promacyl |
N(Aust) |
Ix |
C |
L |
O |
1,220 |
|
Promecarb |
ISO |
I |
C |
S |
O |
74 |
|
Propiconazole |
ISO |
F |
L |
O |
1,520 |
||
Propoxur |
ISO |
I |
C |
S |
O |
95 |
DS 25 |
Prosulfocarb |
ISO |
H |
L |
O |
1,820 |
||
Prothiofos |
ISO |
I |
OP |
L |
O |
925 |
|
Prothiophos |
See prothiofos |
||||||
Pyraclofos |
N(B) |
I |
OP |
L |
O |
237 |
|
Pyrazophos |
ISO |
F |
S |
O |
435 |
||
Pyrethrins |
C |
I |
L |
O |
500-1,000 |
Mixture of compounds present in Pyrethrum, Cineraefolium and other flowers; DS 11 |
|
Pyroquilon |
ISO |
F |
S |
O |
320 |
||
Quinalphos |
ISO |
I |
OP |
S |
O |
62 |
|
Quizalofop-p-tefuryl |
ISO |
H |
L |
O |
1,012 |
||
Reglon |
N(U) |
See diquat |
|||||
Ronnel |
N(A) |
See fenchlorphos |
|||||
Rotenone |
C |
I |
S |
O |
132-1,500 |
Compounds from roots of Derris and Lonchocarpus spp.; HSG 73 |
|
Salithion |
See dioxabenzofos |
||||||
SAP |
N(J) |
See bensulide |
|||||
Sec-butylamine |
See butylamine |
||||||
Sevin |
N(U) |
See carbaryl |
|||||
Sodium fluoride |
ISO |
I |
S |
O |
180 |
||
Sodium hexafluorosilicate |
ISO |
L-S |
S |
O |
125 |
||
Sulfallate |
ISO |
H |
oil |
0 |
850 |
Irritant to skin and eyes |
|
Sulprofos |
ISO |
I |
OP |
oil |
O |
130 |
|
2,4,5-T |
ISO |
H |
S |
O |
500 |
May contain a contaminant TCDD which affects toxicity: it should not exceed 0.01 mg/kg technical material; DS 13 |
|
TCA |
ISO |
The data shown refer to sodium trichloroacetic acid. In many countries, the term TCA refers to the free acid (now accepted by ISO); this is a solid with an oral LD50 of 400 mg/kg and if used as a pesticide is placed in Class II. It is highly corrosive to skin. |
|||||
Terbumeton |
ISO |
H |
T |
S |
O |
483 |
|
Tetraconazole |
ISO |
F |
oil |
O |
1,031 |
||
Thiazafluron |
ISO |
H |
S |
O |
278 |
||
Thiazfluron |
N(B) |
See thiazafluron |
|||||
Thicyofen |
ISO |
F |
S |
O |
368 |
||
Thiobencarb |
ISO |
H |
TC |
L |
O |
1,300 |
|
Thiocyclam |
ISO |
I |
S |
O |
310 |
||
Thiodan |
N(U) |
See endosulfan |
|||||
Thiodicarb |
ISO |
I |
S |
O |
66 |
||
Tolyl-methyl-carbamate |
See metolcarb |
||||||
Toxaphene |
N(A) |
See camphechlor |
|||||
Tralomethrin |
N(B) |
I |
PY |
S |
O |
c85 |
|
Trichloroacetic acid |
|||||||
Tricyclazole |
ISO |
F |
S |
O |
305 |
||
Tridemorph |
ISO |
F |
oil |
O |
650 |
||
Vernolate |
ISO |
H |
TC |
L |
O |
1,780 |
|
Xylylcarb |
N(B) |
I |
C |
S |
O |
380 |
Source: WHO 1996.
Table 4. List of technical products classified in Class III: "Slightly hazardous"
Name |
Status |
Main use |
Chemical type |
Physical state |
Route |
LD50 (mg/kg) |
Remarks |
Acephate |
ISO |
I |
OP |
S |
O |
945 |
|
Acetochlor |
ISO |
H |
L |
O |
2,950 |
||
Acifluorfen |
ISO |
H |
S |
O |
1,370 |
Strong irritant to eyes |
|
Allethrin |
ISO |
I |
PY |
oil |
O |
c685 |
EHC 87; HSG 24 |
Ametryn |
ISO |
H |
T |
S |
O |
1,110 |
|
Amitraz |
ISO |
AC |
S |
O |
800 |
||
Azamethiphos |
ISO |
I |
OP |
S |
O |
1,010 |
|
Azidithion |
N(F) |
See menazon |
|||||
Barban |
ISO |
H |
S |
O |
1,300 |
||
Bensultap |
ISO |
I |
S |
O |
1,100 |
||
Bentazone |
ISO |
H |
S |
O |
1,100 |
||
Benzoylprop-ethyl |
(ISO) |
H |
S |
O |
1,555 |
||
Benzthiazuron |
ISO |
H |
S |
O |
1,280 |
||
Bromofenoxim |
ISO |
H |
S |
O |
1,217 |
||
Bromophos |
ISO |
I |
OP |
S |
O |
c1,600 |
DS 76 |
Buthidazole |
ISO |
H |
S |
O |
1,480 |
||
Cacodylic acid |
See dimethylarsinic acid |
||||||
Carbofos |
N(U) |
See malathion |
|||||
Chlorfenac |
ISO |
H |
OC |
S |
O |
575 |
|
Chlorfenethol |
ISO |
AC |
OC |
S |
O |
930 |
|
Chlorfenson |
ISO |
AC |
OC |
S |
O |
c2,000 |
Irritant to skin |
Chlorinat |
N(U) |
See barban |
|||||
Chlormequat (chloride) |
ISO |
PGR |
S |
O |
670 |
||
Chloroacetic acid |
C |
H |
S |
O |
650 |
Irritant to skin and eyes; data refer to sodium salt |
|
Chlorobenzilate |
ISO |
AC |
OC |
S |
O |
700 |
|
Chlorocholine chloride |
C |
See chlormequat |
|||||
Chlorthiamid |
ISO |
H |
S |
O |
757 |
||
Cismethrin |
ISO |
Resmethrin is a mixture of isomers, the trans isomer (70-80%) being also known as bioresmethrin and the cis isomer (20-30%) as cismethrin. Bioresmethrin (see table 62.5) alone is of much lower toxicity (oral LD50 9,000 mg/kg) (DS 34) |
|||||
Citrex |
N(U) |
See dodine |
|||||
Clofop |
ISO |
H |
L |
O |
1,208 |
||
Copper hydroxide |
C |
F |
S |
O |
1,000 |
||
Copper oxychloride |
C |
F |
S |
O |
1,440 |
||
4-CPA |
ISO |
PGR |
S |
O |
850 |
||
Crufomate |
ISO |
I |
OP |
S |
O |
770 |
|
Cycloate |
ISO |
H |
TC |
L |
O |
+2,000 |
|
Cyhexatin |
ISO |
AC |
OT |
S |
O |
540 |
|
Cymoxanil |
ISO |
F |
S |
O |
1,196 |
||
Cyproconazole |
N(B) |
F |
S |
O |
1,020 |
||
Dazomet |
ISO |
F-S |
S |
O |
640 |
Irritant to skin and eyes |
|
2,4-DB |
N(B) |
H |
S |
O |
700 |
||
DCBN |
N(J) |
See chlorthiamid |
|||||
Deet |
See diethyltoluamide |
||||||
Dehydroacetic acid |
C |
F |
S |
O |
1,000 |
||
2,4-DES |
N(B,U) |
See disul |
|||||
Desmetryn |
ISO |
H |
T |
S |
O |
1,390 |
|
Diallyl dichloroacetamide |
See dichlormid |
||||||
Dicamba |
ISO |
H |
S |
O |
1,707 |
||
Dichlone |
ISO |
FST |
S |
O |
1,300 |
||
Dichlormid |
N(A) |
H |
L |
O |
2,080 |
||
Dichlorobenzene |
C |
FM |
S |
O |
500-5,000 |
Mixture of isomers |
|
Dichlorophen |
ISO |
F |
OC |
S |
O |
1,250 |
|
Dichlorprop |
ISO |
H |
S |
O |
800 |
||
Diclofop |
ISO |
H |
S |
O |
565 |
||
Dicofol |
ISO |
AC |
S |
O |
c690 |
DS 81 |
|
Dienochlor |
ISO |
AC |
S |
O |
3,160 |
Acutely toxic by inhalation; skin sensitizer |
|
Diethyltoluamide |
ISO |
RP (insect) |
L |
O |
c2,000 |
DS 80 |
|
Difenoconazole |
ISO |
F |
T |
S |
O |
1,453 |
|
Dimepiperate |
ISO |
H |
TC |
S |
O |
946 |
|
Dimethachlor |
ISO |
H |
S |
O |
1,600 |
||
Dimethametryn |
ISO |
H |
T |
L |
O |
3,000 |
|
Dimethipin |
ISO |
H |
S |
O |
1,180 |
||
Dimethylarsinic acid |
C |
H |
S |
O |
1,350 |
||
Diniconazole |
ISO |
F |
S |
O |
639 |
||
Dinocap |
ISO |
AC,F |
CNP |
S |
O |
980 |
|
Diphenamid |
ISO |
H |
S |
O |
970 |
||
Disul |
ISO |
H |
S |
O |
730 |
||
Dithianon |
ISO |
F |
S |
O |
640 |
||
2,4-DP |
N(U) |
See dichlorprop |
|||||
Dodine |
ISO |
F |
S |
O |
1,000 |
||
Doguadine |
N(F) |
See dodine |
|||||
DSMA |
See methylarsonic acid |
||||||
Empenthrin ((1R) isomers) |
ISO |
I |
PY |
oil |
O |
+2,280 |
|
Ephirsulphonate |
N(U) |
See chlorfenson |
|||||
Esprocarb |
ISO |
H |
TC |
L |
O |
+2,000 |
Skin and eye irritant |
Etacelasil |
ISO |
PGR |
L |
O |
2,065 |
||
Etaconazole |
ISO |
F |
S |
O |
1,340 |
||
Ethohexadiol |
N(A) |
RP (insect) |
L |
O |
2,400 |
||
Etridiazole |
ISO |
F |
L |
O |
2,000 |
||
Fenoprop |
ISO |
H |
S |
O |
650 |
||
Fenson |
ISO |
AC |
S |
O |
1,550 |
||
Fenothiocarb |
ISO |
L |
C |
S |
O |
1,150 |
|
Fenpropidin |
ISO |
F |
S |
O |
1,440 |
||
Fenthiaprop |
N(B) |
H |
S |
O |
915 |
||
Ferimzone |
ISO |
F |
S |
O |
725 |
||
Flamprop |
ISO |
H |
S |
O |
1,210 |
||
Fluchloralin |
ISO |
H |
S |
O |
1,550 |
||
Fluoroglycofen |
N(B) |
H |
S |
O |
1,500 |
||
Flurprimidol |
ISO |
PGR |
S |
O |
709 |
||
Flusilazole |
N(B) |
F |
S |
O |
1,110 |
||
Flutriafol |
ISO |
F,FST |
T |
S |
O |
1,140 |
|
Fomesafen |
ISO |
H |
OC |
S |
O |
1,250 |
|
Fuberidazole |
ISO |
F |
S |
O |
1,100 |
||
Furalaxyl |
ISO |
F |
S |
O |
940 |
||
Glufosinate |
ISO |
H |
S |
O |
1,625 |
||
Heptopargil |
ISO |
PGR |
L |
O |
2,100 |
||
Hexazinone |
ISO |
H |
S |
O |
1,690 |
||
Hydramethylnon |
N(A,B) |
I |
S |
O |
1,200 |
||
IBP |
See iprobenphos |
||||||
Iprobenphos |
N(B) |
F |
S |
O |
600 |
||
Isoprothiolane |
ISO |
F |
S |
O |
1,190 |
||
Isoproturon |
ISO |
H |
S |
O |
1,800 |
||
Isouron |
ISO |
H |
S |
O |
630 |
||
Isoxapyrifop |
ISO |
H |
S |
O |
500 |
||
Kelthane |
N(J) |
See dicofol |
|||||
Malathion |
ISO |
I |
OP |
L |
O |
c2,100 |
LD50 value can vary according to impurities. This value has been adopted for classification purposes and is that of a technical product conforming to WHO specifications; DS 29 |
Maldison |
N(Aus,NZ) |
See malathion |
|||||
MCPA |
ISO |
H |
S |
O |
700 |
||
MCPA-thioethyl |
ISO |
H |
S |
O |
790 |
||
MCPB |
ISO |
H |
S |
O |
680 |
||
Mecoprop |
ISO |
H |
S |
O |
930 |
||
Mecoprop-P |
ISO |
H |
S |
O |
1,050 |
||
Mefluidide |
ISO |
H |
S |
O |
1,920 |
||
Menazon |
ISO |
AP |
OP |
S |
O |
1,950 |
|
Mepiquat |
ISO |
PGR |
S |
O |
1,490 |
||
Metalaxyl |
ISO |
F |
S |
O |
670 |
||
Metaxon |
N(U) |
See MCPA |
|||||
Metconazole |
ISO |
F |
S |
O |
660 |
||
Methazole |
N(A,B) |
H |
S |
O |
4,543 |
Slightly irritant to eyes |
|
2-Methoxyethlymercury silicate |
C |
FST |
OM |
S |
O |
1,140 |
|
Methylarsonic acid |
ISO |
H |
S |
O |
1,800 |
||
Metolachlor |
ISO |
H |
L |
O |
2,780 |
||
MSMA |
See methylarsonic acid |
||||||
Myclobutanil |
N(B) |
F |
S |
O |
1,600 |
||
2-Napthyloxy acetic acid |
ISO |
PGR |
S |
O |
600 |
||
Nitrapyrin |
ISO |
B-S |
S |
O |
1,072 |
||
Nuarimol |
ISO |
F |
S |
O |
1,250 |
||
Octhilinone |
ISO |
F |
S |
O |
1,470 |
||
N-octyl bicycloheptene dicarboximide |
C |
SY |
L |
O |
2,800 |
||
Oxadixyl |
N(B) |
F |
S |
O |
1,860 |
||
Paclobutrazol |
ISO |
PGR |
S |
O |
1,300 |
||
Pallethrine |
N(F) |
See allethrin |
|||||
Para-dichlorobenzene |
See dichlorobenzene |
||||||
Pendimethalin |
ISO |
H |
S |
O |
1,050 |
||
Perfluidone |
ISO |
H |
S |
O |
920 |
||
Pimaricin |
N(B) |
F |
S |
O |
2,730 |
Antibiotic, identical with tennecetin and natamycin |
|
Piproctanyl |
ISO |
PGR |
S |
O |
820 |
||
Pirimiphos-methyl |
ISO |
I |
OP |
L |
O |
2,018 |
DS 49 |
Prochloraz |
ISO |
F |
S |
O |
1,600 |
||
Propachlor |
ISO |
H |
S |
O |
1,500 |
DS 78 |
|
Propanil |
ISO |
H |
S |
O |
c1,400 |
||
Propargite |
ISO |
AC |
L |
O |
2,200 |
||
Pyrazoxyfen |
ISO |
H |
S |
O |
1,644 |
||
Pyridaben |
ISO |
AC |
S |
O |
820 |
||
Pyridaphenthion |
N(J) |
I |
OP |
S |
O |
769 |
|
Pyridate |
ISO |
H |
S |
O |
c2,000 |
||
Pyrifenox |
ISO |
F |
L |
O |
2,900 |
||
Quinoclamine |
ISO |
H |
S |
O |
1,360 |
||
Quizalofop |
N(B) |
H |
S |
O |
1,670 |
||
Resmethrin |
ISO |
I |
PY |
S |
O |
2,000 |
See cismethrin; EHC 92, DS 83, HSG 25 |
Ryania |
C |
I |
S |
O |
c750 |
LD50 varies: vegetable product |
|
Sesamex |
N(A) |
SY |
L |
O |
2,000 |
||
Sethoxydim |
ISO |
H |
L |
O |
3,200 |
||
Silvex |
N(A) |
See fenoprop |
|||||
Simetryn |
ISO |
H |
T |
S |
O |
1,830 |
|
Sodium chlorate |
ISO |
H |
S |
O |
1,200 |
||
Sulfluramid |
ISO |
I |
S |
O |
543 |
||
Sulfoxide |
N(A) |
SY |
L |
O |
2,000 |
||
2,3,6-TBA |
ISO |
H |
S |
O |
1,500 |
||
Tebuthiuron |
ISO |
H |
S |
O |
644 |
||
Thiram |
ISO |
F |
S |
O |
560 |
DS 71 |
|
TMTD |
N(U) |
See thiram |
|||||
2,4,5-TP |
N(F,J,U) |
See fenoprop |
|||||
Tralkoxydim |
ISO |
H |
S |
O |
934 |
||
Triadimefon |
ISO |
F |
S |
O |
602 |
||
Triadimenol |
ISO |
FST |
S |
O |
900 |
||
Tri-allate |
ISO |
H |
TC |
L |
O |
2,165 |
HSG 89 |
Trichlorfon |
ISO |
H |
OP |
S |
O |
560 |
DS 27; EHC 132; HSG 66 |
Triclopyr |
ISO |
H |
S |
O |
710 |
||
Tridiphane |
N(B) |
H |
S |
O |
1,740 |
||
Trifenmorph |
ISO |
M |
S |
O |
1,400 |
DS 64 |
|
Triflumizole |
N(B) |
F |
S |
O |
695 |
||
Undecan-2-one |
C |
RP (dogs,cats) |
oil |
O |
2,500 |
||
Uniconazole |
ISO |
PGR |
S |
O |
1,790 |
||
XMC |
N(J) |
I |
C |
S |
O |
542 |
|
Ziram |
ISO |
F |
S |
O |
1,400 |
Irritant to skin; DS 73 |
Source: WHO 1996.
" DISCLAIMER: The ILO does not take responsibility for content presented on this web portal that is presented in any language other than English, which is the language used for the initial production and peer-review of original content. Certain statistics have not been updated since the production of the 4th edition of the Encyclopaedia (1998)."