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Chemicals management<br />

ferred easily to developing countries is not yet certain.<br />

Resistance to pests in the US may not confer<br />

resistance to indigenous pests in developing countries.<br />

The other dimension is that pests have been<br />

shown to develop resistance to Bt crops if their use<br />

is not managed properly.<br />

Improvements in yield <strong>and</strong> stress<br />

tolerance<br />

Much of the benefit of the first Green Revolution<br />

came about through the development of highyielding<br />

dwarf varieties. The genes responsible for<br />

dwarfing have now been isolated <strong>and</strong> can be<br />

incorporated into other crops to achieve the same<br />

increased yields. In many regions of the world<br />

there are constraints on where crops can be grown<br />

since these regions have highly alkaline, acidic or<br />

saline soils. Genes conferring resistance have been<br />

isolated from plants such as mangroves <strong>and</strong> are<br />

being inserted into crop varieties to enable them<br />

to be grown in saline soils. This has the potential<br />

to reclaim large areas of l<strong>and</strong> that have been made<br />

saline by poor irrigation practices.<br />

Improvements in nutrition<br />

GM technology not only has the ability to produce<br />

plants that address many production problems. It<br />

also has the potential to improve nutritional quality.<br />

One widely known example is the so-called<br />

“Golden Rice”, which has been engineered to produce<br />

higher levels of beta-carotene as a precursor<br />

to vitamin A, which could help treat deficiencies<br />

in children living in the tropics.<br />

There can be little doubt that GM technology<br />

has the potential to meet the world’s food<br />

dem<strong>and</strong>s, but a number of questions still remain<br />

partially or totally unanswered. Many people are<br />

concerned about the potential for the spread of<br />

modified genes into the <strong>environment</strong>, either creating<br />

“super weeds” or polluting the genetic material<br />

of wild plants. Herbicide-tolerant plants can<br />

generally be controlled with conventional herbicides<br />

other than the one to which they are resistant.<br />

Whether the modified material will make its way<br />

into the native flora is less certain. The limited<br />

number of species that have been modified, <strong>and</strong><br />

their relatively limited distribution, have not really<br />

produced sufficient information to make a decision.<br />

There is a need to monitor the situation very<br />

carefully, especially where plants are being used in<br />

their centre of origin <strong>and</strong> gene flow may be easier.<br />

Human safety is also of concern since genetic modifications<br />

could lead to allergies or worse. However,<br />

over half a million hectares of GM crops have<br />

The main elements of the integrated pest management (IPM) strategy<br />

developed as part of the regional cooperation plan were:<br />

1. biological control (use of species of bacteria such as Bacillus thuringiensis;<br />

use of fungi, including Metarhizium anisopliae <strong>and</strong> Beauveria bassiana);<br />

2. physical barriers such as s<strong>and</strong> traps for underground termite control;<br />

3. baits such as food or substances used to attract, entice or lure termites to a<br />

desired location. The baiting technique involves the use of a “bait station”<br />

on which the termites aggregate <strong>and</strong> continue to feed once they have found<br />

the bait station.<br />

The safer chemical alternatives identified were chlorpirifos (Dursban),<br />

deltamethrin, permethrin (Dragnet), cypermethrin, <strong>and</strong> fipronil (Termidor).<br />

In developing <strong>and</strong> implementing this programme there were a few challenges<br />

along the way, including:<br />

1. lack of a detailed inventory of quantities used at the start of the Regional<br />

Action Plan;<br />

2. difficulty in finding the resources to gather monitoring <strong>and</strong> follow-up data;<br />

3. lack of enforcement instruments to measure success.<br />

Mexico also took several steps with wider implications on its own initiative,<br />

showing that the government was becoming more <strong>environment</strong>ally<br />

conscious. One of the first steps was to ban the import of chemicals that<br />

were prohibited in the producing country. Mexico thereby recognized the<br />

need to stop companies from turning to export markets when their products<br />

were deemed dangerous at home.<br />

Studies were also carried out for the first time on chlordane use in Mexico<br />

<strong>and</strong> its effects on birds, fish <strong>and</strong> worms. Contamination in these animals,<br />

although they are lower down on the food chain, quickly makes its way to<br />

humans.<br />

The NARAP included a three-phase regulatory programme specific to<br />

Mexico, which has resulted in the effective implementation of actions within<br />

the regional plan. This programme has also had positive benefits through<br />

reducing exposure to chlordane. Among the actions taken have been:<br />

1. development of an integrated control strategy including a pesticide lifecycle<br />

analysis, identification of alternatives to chlordane <strong>and</strong> government<br />

support for research;<br />

2. encouragement of stakeholders to participate in the development of control<br />

strategies <strong>and</strong> the identification of safer alternatives;<br />

3. a ban on imports of pesticides whose use is prohibited by the exporting<br />

country;<br />

4. limits on sales to authorized, trained personnel <strong>and</strong> restrictions regarding<br />

their use;<br />

5. making information on the NARAP’s scope <strong>and</strong> purpose available to the<br />

public;<br />

6. prohibition of the sale of technical <strong>and</strong> active ingredients for making<br />

chlordane;<br />

7. <strong>environment</strong>al monitoring <strong>and</strong> risk assessment to establish a baseline.<br />

Conclusions<br />

The North American Regional Action Plan on Chlordane can be considered<br />

a successful tri-national cooperation exercise, designed to curtail release<br />

to the <strong>environment</strong> of a toxic, persistent <strong>and</strong> bioaccumulative substance at<br />

the regional level. As a result of these NARAP activities, chlordane is no<br />

longer registered for use or manufactured in Canada, Mexico or the United<br />

States. Mexico’s institutional capacities for monitoring <strong>and</strong> analyzing chemicals<br />

in the <strong>environment</strong> have been strengthened in terms of information<br />

systems for toxic substances <strong>and</strong> actions to reduce the risks of toxic substances.<br />

The design <strong>and</strong> implementation of a chlordane sampling <strong>and</strong> analysis<br />

plan for Mexico is included under the Regional Action Plan on<br />

Monitoring <strong>and</strong> Assessment, currently under development.<br />

This experience has demonstrated the great benefits of regional cooperation<br />

when priority is given to the management <strong>and</strong> control of substances of<br />

mutual concern that are persistent <strong>and</strong> toxic. The authorities are now confident<br />

enough to say publicly that Mexico has eliminated chlordane use<br />

completely. To ensure that chlordane levels continue to decrease over time,<br />

follow-up recommendations have been made to report on chlordane levels<br />

<strong>and</strong> activities by means of continued monitoring <strong>and</strong> surveillance of illegal<br />

trade.<br />

Current field studies at selected sites in Mexico are being coordinated by<br />

the National Institute of Ecology. These studies are geared towards measuring<br />

a number of POPs (including chlordane) as part of the follow-up recommendations.<br />

Furthermore, <strong>and</strong> in compliance with international initiatives such as the<br />

Basel <strong>and</strong> Stockholm Conventions, Mexico has had the opportunity to take<br />

advantage of this regional cooperation <strong>and</strong> share the experience <strong>and</strong> expertise<br />

gained.<br />

References<br />

Commission for Environmental Cooperation (CEC) (1997) North American<br />

Regional Action Plan on Chlordane. Montreal, Canada.<br />

Moody, J. (2003) North America eliminates use of Chlordane, in:<br />

Trio Newsletter. Commission for Environmental Cooperation, Montreal,<br />

Canada.<br />

United Nations Environment Programme (UNEP) (2002) Ridding the<br />

World of POPS: A guide to the Stockholm Convention on Persistent Organic<br />

Pollutants. Geneva, Switzerl<strong>and</strong> (http://portalserver.unepchemicals.ch/Publications/SCGuideRidWPOPs.pdf)<br />

Yarto, M., A. Gavilan <strong>and</strong> J. Barrera (2003) El Convenio de Estocolmo<br />

sobre Contaminantes Orgánicos Persistentes y sus implicaciones para México,<br />

in: Gaceta Ecológica, Vol. 63. Mexico.<br />

1. See www.chem.unep.ch/pops.<br />

UNEP Industry <strong>and</strong> Environment April – September 2004 ◆ 31

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