Pesticides can harm people, animals and the environment. It is therefore important to pay adequate attention to selection and procurement procedures. This section provides further technical background regarding the selection and procurement of pesticides. 
Procurement of the wrong type or quantity of products may result in: - acute poisoning of users;
- chronic poisoning of people, leading to cancers, birth defects and chronic health problems;
- disruption or destruction of ecosystems;
- leftover pesticides becoming unusable/obsolete and turning into hazardous waste.
- Determining the WHO Hazard Class for specific pesticides
- Identifying controversial products
- POP and PIC lists
- Procurement
- Preventing products becoming hazardous waste
- Points for special attention
Determining the WHO Hazard Class for specific pesticides The World Health Organization (WHO) provides an internationally accepted standard for hazard classification in The WHO Recommended Classification of Pesticides by Hazard and Guidelines to Classification. This document is updated every two years.
The WHO classification distinguishes 4 different hazard classes (see below). The appearance of a given active ingredient in WHO Class IA, IB or II should trigger closer evaluation. However, the relevant factor is the classification of the formulated product and not the active ingredient (A product with a high concentration of a Class II active ingredient can be more hazardous than a product with a very low concentration of a Class I active ingredient).
The classification by hazard is based on the acute toxicity expressed in LD50 values. LD50 stands for Lethal Dose 50% and is a statistical estimate of the dose, in milligrams of the material per kilogram of body weight, which will kill 50 percent of a group of test organisms. The lower the LD50, the more toxic the product. Both oral and dermal LD50s are used, since many pesticides are easily absorbed through the skin. Toxicity through inhalation can also be a hazard, but the measurement and evaluation of this hazard is more complex.
Often the manufacturer declares the Hazard Class on the label or in other documentation regarding the product concerned. If the Hazard Class is not declared it can be estimated as follows: - Look up the LD50 for the active ingredient (a.i.) in the WHO Tables (see Tables 1-4) and determine whether it concerns oral or dermal toxicity. (The default is oral toxicity. If it concerns dermal toxicity instead of oral toxicity, the figure in the LD50 table will be preceded by the letter D.)
- Calculate the estimated actual LD 50 of the formulated product by using the formula:
LD50 of formulated product
| = | (LD50 of a.i.) x 100 % of a.i. in formulated product |
Use the table below to determine the Hazard Class on the basis of the calculated LD 50, the physical state of the formulated product (liquid or solid) and the most hazardous mode of action oral or dermal). The physical state of a product can generally be determined by the unit of quantity (L or Kg) or the formulation code (detailed below table).
| Hazard Class | LD50 for the rat (mg/kg body weight) | Oral | Dermal | Solids | Liquids | Solids | Liquids | | Ia Extremely hazardous | 5 or less | 20 or less | 10 or less | 40 or less | | Ib Highly hazardous | 5 - 50 | 20 - 200 | 10 – 100 | 40 - 400 | | II Moderately hazardous | 50 - 500 | 200 - 2000 | 100 – 1000 | 400 - 4000 | | III Slightly hazardous | Over 500 | Over 2000 | Over 1000 | Over 4000 |
Some common codes for formulations that are often part of the product name and provide indication of its intended mode of application and physical state: | D | Dust (powder) | Solid | | EC | Emulsifiable Concentrate | Liquid | | G | Granular | Solid | | P or PS | Pelleted | Solid | | S or SC | Solution | Liquid | | SP | Soluble Powder | Liquid after preparation | | ULV | Ultra Low Volume Concentrate | Liquid | | WP | Wettable Powder | Liquid after preparation |
 For further information, see also: Pesticide formulations and application techniques Reducing health and environmental risks Newer products with higher selectivity and lower toxicity Identifying controversial products
In addition to products with a high acute toxicity, products may be considered controversial or undesirable because of their chronic toxicity or impact on the ecosystem or the environment.
Indicators that there may be something wrong with a product include: - Inclusion on the list of Persistent Organic Pollutants (POPs list- see below)
- Inclusion on the list of products subject to the Prior Informed Consent procedure (PIC list -see below)
- Registration of the proposed use of the product has been rejected or cancelled for health or environmental reasons in the US and the EU
POP and PIC lists
Requests for Bank-financing of products that appear on the POPs and PIC list (see box below) should be given extra scrutiny. In most cases these product will be excluded from Bank-financing on the ground that these provide unnecessary risks to the environment or human health (OP 4.09 Paragraph 6a and 6c). A possible exception is the use of DDT for malaria control.
POP and PIC Conventions | POPs Persistent Organic Pollutants (POPs) are chemicals that persist in the environment, bio-accumulate through the food web, and pose a risk of causing adverse effects to human health and the environment. With evidence of long-range transport of these substances to regions where they have never been used or produced, and the consequent threats they pose to the environment of the whole globe, the international community is striving to reduce and eliminate releases of these chemicals through the Stockholm Convention on POPs. The initial list of substances subject to the POPs Convention contains 9 pesticides (see table below). For further information on POPs chemicals and the POPs Convention, see UNEP's POPs site).
PIC The Prior Informed Consent (PIC) procedure was developed to help ensure that governments have information they need about hazardous chemicals for assessing the risks and taking informed decisions on chemical imports. Since 1989 the PIC procedure has been part of the voluntary "International Code of Conduct on the Distribution and Use of Pesticides". In 1998, the PIC procedure was made mandatory through a Convention on the Prior Informed Consent Procedure for Certain Hazardous Chemicals in International Trade (sometimes referred to as the Rotterdam Convention). The procedure applies to banned and severely restricted products that meet defined criteria. In 2010, the official list of products subject to the PIC procedure included 29 pesticides. (See also UNEP's site on PIC). |
In 1985, the Pesticide Action Network established a "dirty dozen" list of pesticides that are highly hazardous and a common cause of farmer poisoning, or a threat to the environment because of their persistence. This Pesticide Action Network is a global network of NGOs that campaigned for the phasing out of these products. At that time, many aid agencies did not yet have a policy on pest management and the "dirty dozen list" became a tool for aid agencies, which adopted it as a black list of pesticides excluded from procurement. Since 1985 the list has been updated several times and now contains 20 products. In the late 80s and early 90s the Bank also used this list as a black list. The Bank now uses the criteria in OP 4.09 for the selection of pesticides. The products on the "Dirty Dozen List" are excluded from Bank financing because they do not meet the selection criteria of OP 4.09. The only exception is the use of DDT for Malaria control (see section on POPs Convention).
| Pesticide | "Dirty Dozen" (1985 + updates) | Appears on PIC list (2010) | Appears on POP list (2010) | | 2,4,5,-T | Xx | X |  | | Aldicarb | .Xx | . |  | | Aldrin | X | X | X | | Binapacryl | . | X | . | | Captafol | . | X | . | | Chlordane | X | X | X | | Chlordecone | | X | X | | Chlordimeform | X. | X |  | | Chlorobenzilate | . | X | . | | DDT | X | X | X | | Dieldrin | X | X | X | | Dinoseb and dinoseb salts | .X | X |  | | 1,2-dibromoethane (EDB) | .X | X |  | | Endrin | X | . | X | | Fluoracetamide | . | X | . | | HCH (mixed isomers) | X. | X |  | | Heptachlor | X | X | X | | Hexachlorobenzene | X | X | . | | Lindane | X. | X |  | | Mercury compounds | . | X | . | | Mirex | X | . | . | | Paraquat | X. | . |  | | Pentachlorophenol | X. | X |  | | Toxaphene | X | X | X | | Monocrotophos* | . | Certain formulations | . | | Methamidophos* | . | Certain formulations | . | | Phosphamidon* | . | Certain formulations | . | | Methyl-parathion* | X. | Certain formulations |  | | Parathion* | X. | X |  | | Alpha hexachlorocyclohexane | | X | X | | Beta hexachlorocyclohexane | | X | X | | Pentachlorobenzene | | X | X | * included on PIC list because of high acute toxicity
Procurement
The Bank requires that any pesticides it finances be manufactured, packaged, labeled, handled, stored, disposed of, and applied according to standards acceptable to the Bank. The FAO Technical Guidelines for the implementation of the International Code of Conduct for the Distribution and Use of Pesticides serve as the main reference. (See section on resources for links to these documents)
Many problems associated with pesticide use originate from lack of specification in tenders and procurement documents. Such documents should not only specify the products but also their packaging type, size and durability.Â
Several safeguards can be built in at the stage of procurement. The tender can require that the supplier of pesticides also supplies protective gear, Material Safety Data Sheets, and training in proper handling, use, and antidotes. The tender should also make explicit that the supplier is obliged to take back, at its own expense, products that upon arrival turn out not to conform with the specifications. In some cases, suppliers may agree to take back products that remain unused after a specified period of time.Â
Important details in the tender/procurement document | q | Have the following items been specified in the tender or procurement document? | . | q active ingredient | . | q formulation | . | q container type and size | . | q packaging type and durability | . | q labeling requirements (language, FAO labeling requirements) | . | q minimum remaining shelf-life from the date of entry into the country of destination | | . | .. | q | Does the procurement document specify the supplier's obligation to take back products that deviate from the specifications? | q | Are additional services required from the supplier and have these been specified ( e.g.: provision of Material Safety Data Sheets, training of users and store keepers, provision of protective gear, etc.)? | q | Has consideration been given to clauses or provisions for the return of left-over products to their suppliers or manufacturers? | q | Does the tender require the supplier to provide a "certificate of country of origin" for the product? |
Preventing products from becoming obsolete
The following checklist aims to help avoid mistakes that have contributed to the accumulation of obsolete pesticide stocks. It should be anticipated that the Bank eventually may be held responsible for obsolete pesticides that were procured with Bank loans and that could have been avoided by better assessment and specification of requirements.
Avoiding the accumulation of obsolete pesticides | q | Is the product registered for its envisaged use in the country concerned? | q | Is the product effective for the envisaged purpose? | q | Is the formulation suitable for the available application equipment? | q | Is the quantity consistent with the capacity to store, transport and apply the product? | q | Is the quantity based on an accurate assessment of needs? | q | Have existing stocks been taken into consideration when establishing requirements? | q | Are there any economic or other factors that may slow down the sale/distribution of the product concerned (e.g.: abolishment of subsidies; changes in supply/distribution systems)? | q | Are containers durable enough to withstand anticipated transport, handling and storage conditions? | q | Are containers of an appropriate size for the envisaged use? |
FAO Guidelines for the Prevention of Accumulation of Obsolete Pesticide Stocks recommend that for centrally organized pest control programs, such as vector control, and locust and other migratory pest control programs, quantities of pesticides supplied should not exceed a one year requirement. Nor should these exceed the capacity to store, transport or apply the product concerned. The storage capacity is determined by the availability of storage space in adequate pesticides stores. The application capacity is determined by the available application equipment, the availability of staff to use the equipment and the transport facilities to bring staff and products to the location where application is needed. Exceeding any of these capacities is likely to lead to obsolete pesticide stocks.
Points for special attention - Donor coordination: In some cases, inadequate donor coordination led to excessive supplies of pesticides under declared emergency situations. Such excessive stocks are likely to contribute to the build up of stockpiles of obsolete pesticides.
- Consider supply in small consignments spread over time to reduce the risk of build up of stocks. New consignments should only be released upon confirmation that earlier consignments are being depleted at the anticipated rate.
- Changes of products or formulations may require further training of users.
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