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An Economic Analysis of GRDC Investment in Minor Use Chemicals

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crops. For the majority <strong>of</strong> the <strong>in</strong>dicated violations for which there is no MRL any<br />

detection above 0.01 mg/kg would register as a violation (Kev<strong>in</strong> Bodnaruk,<br />

pers.comm., 2010).<br />

Rae (2002) summarised a special report on residues <strong>in</strong> gra<strong>in</strong>s from 1995-1999 which<br />

showed that organophosphorus <strong>in</strong>secticides (as a group they are mostly<br />

biodegradable and do not concentrate <strong>in</strong> the food cha<strong>in</strong>) were the most commonly<br />

detected residues (<strong>in</strong> 4-24% <strong>of</strong> samples <strong>of</strong> various gra<strong>in</strong>s) but that MRLs were<br />

exceeded <strong>in</strong> only about 0.1% <strong>of</strong> samples. The Australian gra<strong>in</strong>s <strong>in</strong>dustry has an<br />

<strong>in</strong>creas<strong>in</strong>gly effective post harvest chemical usage strategy for control <strong>of</strong> residues<br />

and an enviable record <strong>in</strong> relation to food safety. In relation to food safety, Rae<br />

(2002) reported that the Australian Total Diet Survey consistently demonstrated very<br />

low levels <strong>of</strong> pesticides <strong>in</strong> Australian diets.<br />

Reduc<strong>in</strong>g trade risks – The performance <strong>in</strong> relation to MRL is achieved by highly<br />

effective procedures for registration. The process with the fungicide chlorothalonil<br />

widely used for ascochyta control <strong>in</strong> pulse crops is illustrative. Chlorothalonil has<br />

been used <strong>in</strong> many countries s<strong>in</strong>ce the 1960s <strong>in</strong> a variety <strong>of</strong> applications. MUP was<br />

<strong>in</strong>volved with Pulse Australia <strong>in</strong> secur<strong>in</strong>g various temporary permits for ascochyta<br />

disease control <strong>in</strong> chickpeas, faba beans & lentils issued over the period from 1999<br />

before the use appeared on the registered label <strong>in</strong> 2009. In 2006 APVMA had<br />

responded to concerns on potential for residues <strong>in</strong> meat exports; the current export<br />

value is <strong>of</strong> the order <strong>of</strong> $6 billion. <strong>An</strong> <strong>in</strong>itial evaluation <strong>of</strong> the application was<br />

completed <strong>in</strong> May 2006 <strong>in</strong>dicat<strong>in</strong>g further data from animal transfer studies was<br />

needed on feed<strong>in</strong>g <strong>of</strong> pulse fodders and forages.<br />

Risks to human health (non-food related) and the environment - Monitor<strong>in</strong>g <strong>of</strong><br />

adverse experiences from the use <strong>of</strong> agricultural products is undertaken by APVMA as<br />

a part <strong>of</strong> its performance report<strong>in</strong>g. Agriculture and veter<strong>in</strong>ary chemicals are<br />

excluded from the Australian Government’s regulatory scheme for <strong>in</strong>dustrial<br />

chemicals (NICNAS, the National Industrial <strong>Chemicals</strong> Notification and Assessment<br />

Scheme). Products that are the subject <strong>of</strong> m<strong>in</strong>or use permits <strong>in</strong>clud<strong>in</strong>g those secured<br />

through MUP are not specifically monitored other than through adverse experience<br />

report<strong>in</strong>g. APVMA (2010) reported that dur<strong>in</strong>g the calendar year 2009 the monitor<strong>in</strong>g<br />

did not lead to a major regulatory action aga<strong>in</strong>st any registered product. Underreport<strong>in</strong>g<br />

is considered likely. Some reports warranted actions to mitigate potential<br />

risks, <strong>in</strong>clud<strong>in</strong>g updat<strong>in</strong>g product labels.<br />

In relation to health risks, a survey (MacFarlane et al 2008) <strong>of</strong> Victorian farmers<br />

showed that poor use <strong>of</strong> personal protective equipment <strong>in</strong>dicated possible significant<br />

pesticide exposure. Tra<strong>in</strong><strong>in</strong>g was seen as an important <strong>in</strong>tervention for reduc<strong>in</strong>g<br />

farmers’ pesticide exposure. In summary the <strong>in</strong>formation on risks to human health<br />

and the environment is limited and does not provide any <strong>in</strong>formation on MUP<br />

impacts. The low level <strong>of</strong> <strong>in</strong>cidents is some <strong>in</strong>dication <strong>of</strong> low risk. However there<br />

may be risks not evident <strong>in</strong> the short term.<br />

Direct Project Outcomes (on farm)<br />

Although there were six projects, each was <strong>in</strong> the ma<strong>in</strong> a cont<strong>in</strong>uation <strong>of</strong> the work <strong>in</strong><br />

progress from the previous project and with a common purpose <strong>of</strong> fill<strong>in</strong>g priority<br />

gaps. Table 6 summarises outcomes and picks up the ma<strong>in</strong> ways the projects<br />

evolved over the period. The Table illustrates how each project expanded on the<br />

previous projects <strong>in</strong> their scope and evolved to meet chang<strong>in</strong>g circumstances <strong>in</strong> the<br />

regulatory environment. This section then concludes with more detail on outcomes<br />

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Agtrans Research Page 14

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