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Chemicals management<br />

The current range of genetically modified crops<br />

has been developed in Northern countries for the<br />

agricultural systems operating there. The main<br />

thrust has been to produce crops that are herbicide-tolerant<br />

(allowing simplified weed control) or<br />

that contain insecticides to confer protection<br />

against a range of pests, or both of these traits. This<br />

fits with current practices <strong>and</strong> has produced<br />

encouraging results in many countries. The technology<br />

itself is being adopted very rapidly, with the<br />

global area growing from 1.7 million hectares in<br />

1996 to 67.7 million hectares in 2003 (Figure 3).<br />

The benefits from biotechnology could be enormous.<br />

It has the capacity to speed up breeding programmes,<br />

create crops that are resistant to pests<br />

<strong>and</strong> disease, improve the nutritional value of crops,<br />

<strong>and</strong> provide crops that can survive <strong>and</strong> thrive in<br />

hostile <strong>environment</strong>s. Delivering these benefits<br />

relies on the technology being presented to end<br />

users in an appropriate form, at an acceptable price<br />

<strong>and</strong> with the knowledge <strong>and</strong> skills required to utilize<br />

the technology. These are not dissimilar to<br />

requirements for conventional crop management.<br />

Therefore, many of the problems with implementing<br />

existing technologies may well apply to<br />

biotechnology. It may be that genetically modified<br />

crops are easier to distribute, as the seeds will contain<br />

the trait <strong>and</strong> there will be no need to apply<br />

additional components as there was in the first<br />

Green Revolution. However, this requires a reliable<br />

distribution network, which is often lacking in the<br />

countries that most need to improve production.<br />

If the potential benefits are examined, it can be<br />

seen that they are potentially wide-ranging. The<br />

following examples show how GM technology<br />

can be applied to specific agricultural problems.<br />

Pest resistance<br />

Specific resistance to a particular pest is obviously<br />

beneficial to farmers. They will either be able to<br />

grow the crop where they couldn’t before, or be<br />

able to reduce the amount of pesticide that they<br />

use to control it. Crops containing insect resistance<br />

genes from Bacillus thuringiensis confer protection<br />

to a range of lepidopterous pests. This has<br />

significantly reduced the quantity of insecticide<br />

used in cotton crops in the United States, where<br />

1million kilograms less insecticide was used in<br />

1999 compared with 1998. Reports indicate that<br />

the introduction of Bt cotton into China has<br />

reduced the number of sprays from 20 to seven<br />

per season in many parts of the country. However,<br />

there are reports that some farmers still spray<br />

up to 22 times even if the modified crop is being<br />

grown. Whether this technology can be trans-<br />

Mexico’s success in eliminating chlordane within a regional cooperation framework<br />

Mario Yarto, Director of Research on Chemical Substances <strong>and</strong> Ecotoxicological Risks, National Institute of Ecology-SEMARNAT,<br />

Periferico 5000, 4 th floor, Col. Insurgentes Cuicuilco, Mexico City 04530, Mexico (myarto@ine.gob.mx)<br />

A well-known group of chemicals are classified as persistent organic pollutants<br />

(POPs). 1 Their properties include high toxicity, persistence in the<br />

<strong>environment</strong>, long-range transport in the atmosphere, <strong>and</strong> accumulation in<br />

fatty tissue. Direct contact with POPs can result in acute effects; accidents<br />

with POPs used as pesticides, for example, have killed agricultural workers<br />

or made them seriously ill.<br />

Chlordane, a pesticide classified as a POP, was widely used in the past to<br />

control insect pests in crops <strong>and</strong> forests. It also had domestic <strong>and</strong> industrial<br />

applications, including termite control in wood <strong>and</strong> wood products. It<br />

has been designated a probable human carcinogen. High levels can damage<br />

the nervous system or liver. Chlordane is also known to affect the endocrine<br />

system <strong>and</strong> digestive system. It can cause behavioural disorders in children<br />

exposed before birth or while nursing.<br />

Exposure to chlordane may occur due to eating contaminated foods or<br />

exposure to contaminated soil. It has been shown to be toxic to non-target<br />

species, including birds, fish, bees <strong>and</strong> earthworms.<br />

Member countries of the Intergovernmental Forum on Chemical Safety<br />

(IFCS) agreed that there was sufficient evidence to warrant international<br />

action on POPs, including chlordane (IFCS/Forum-II/97). This was the<br />

basis for a decision of the UNEP Governing Council in January 1997 to the<br />

effect that a legally binding international instrument for the control of<br />

POPs should be developed.<br />

Development of a Regional Action Plan<br />

Chlordane was originally introduced into Mexico <strong>and</strong> many other countries<br />

for extensive use in agriculture. In recent years, however, use of this<br />

pesticide has been limited to termite control in certain wood products.<br />

Chlordane use was one of the first targets of the Sound Management of<br />

Chemicals (SMOC) initiative of the North American Commission for<br />

Environmental Cooperation (CEC). In 1997 a North American Regional<br />

Action Plan (NARAP) on chlordane was approved by the governments of<br />

Mexico, Canada <strong>and</strong> the United States, with the goal of phasing out registered<br />

uses by 1998.<br />

In developing a NARAP for chlordane, the Parties involved committed<br />

to ongoing cooperative activities <strong>and</strong> annual reporting on the progress<br />

made. The reports were subsequently made public <strong>and</strong> forwarded to the<br />

Council of the Commission for Environmental Cooperation. The Parties<br />

also continued their commitment to the principle of prior informed consent<br />

(PIC): if an importing country does not consent to import a chemical<br />

substance, the exporting country has the obligation to inform the exporting<br />

<strong>industry</strong> of that decision <strong>and</strong> take appropriate legislative <strong>and</strong> administrative<br />

measures to ensure that export does not occur.<br />

The NARAP for chlordane was intended to be the basis of a coordinated<br />

regional contribution to these international initiatives. A number of specific<br />

regulatory <strong>and</strong> administrative actions were included:<br />

1. The United States encouraged <strong>industry</strong> to voluntarily phase out chlordane<br />

production;<br />

2. Canada <strong>and</strong> the US worked closely with Mexico to provide available risk<br />

assessments concerning suitable alternatives to chlordane;<br />

3. Canada <strong>and</strong> the US continued to provide support for hazardous waste<br />

collection programmes that included chlordane. Information on these programmes<br />

was shared with Mexico, which administered its own hazardous<br />

waste collection programme;<br />

4. All three countries reported publicly available data on chlordane use,<br />

production, import <strong>and</strong> export;<br />

5. Canada, Mexico <strong>and</strong> the US produced annual reports on progress<br />

achieved under the NARAP.<br />

Implementation <strong>and</strong> benefits<br />

After production ended in the United States, the next step was to find out how<br />

much chlordane was being used in Mexico <strong>and</strong> where. Canadian <strong>and</strong> US agencies<br />

came to Mexico in order to demonstrate the best <strong>and</strong> cheapest ways to test<br />

for chlordane <strong>and</strong> monitor its use. They shared detailed information on the<br />

elimination of its use <strong>and</strong> on which regulations had been effective. The CEC<br />

also set up workshops to explain the dangers of chlordane <strong>and</strong> present alternatives.<br />

For example, heating furniture above certain temperatures kills termites<br />

just as effectively as spraying with a noxious chemical.<br />

Mexico imported 212.8 tonnes of chlordane between 1992 <strong>and</strong> 1996, all<br />

from the US.<br />

Use of chlordane in Mexico is currently illegal. This means that the use,<br />

commercialization, import <strong>and</strong> formulation of chlordane <strong>and</strong> of its active<br />

ingredient are prohibited by law. Its phase-out is now complete, as the only<br />

company holding a chlordane active ingredient registration stopped<br />

importing it in 1997 <strong>and</strong> had no stocks by 1999. Apparently, no pesticides<br />

containing chlordane were imported at that time.<br />

Another factor in the success of this programme is that it encouraged<br />

optimism about similar low-cost efforts in the future. Apart from a few<br />

grants to Mexico for some studies, the bulk of the work consisted of<br />

exchanging expertise <strong>and</strong> techniques, with information dissemination <strong>and</strong><br />

capacity-building actions.<br />

What also made this easier was the fact that Mexico had begun to control<br />

the use of chlordane. By 1997 this was limited to urban use to control termites,<br />

mainly in houses. However, completely ending chlordane’s use took<br />

several more years <strong>and</strong> required mutual help across the continent.<br />

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

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