State of the Environment

2001

Land Theme Report

Australia State of the Environment Report 2001 (Theme Report)
Prepared by: Ann Hamblin, Bureau of Rural Sciences, Authors
Published by CSIRO on behalf of the Department of the Environment and Heritage, 2001
ISBN 0 643 06748 5

Soil and land pollution (continued)

Condition (continued)

Progress in Integrated Pest Management and risk reduction in agricultural industries: case studies

Risk assessment

Today environmental impacts can only be estimated by consideration of the types of chemicals habitually used in rural industry relating to land use. CSIRO is trialling a Pesticide Impact Ranking Index (PIRI) (Kookana et al. unpubl.; see PIRI: Pesticides Impact Ranking Index) that has the potential to provide relative assessment of the potential impact of different chemicals used in rural industries.

PIRI: Pesticide Impact Ranking Index

PIRI assesses the environmental ranking of individual pesticides causing damage to waterways. It is an index, not a model. PIRI allows managers and farmers to assess which chemicals may migrate and harm water ecology, quality or aesthetics. The index is also able to rank which pesticide combinations (and therefore land uses) are most likely to put water assets at risk.

The value of the water body is assessed by a simple scoring system. The overall pesticide load is considered in relation to the area, application rates, toxicity and distance to water bodies. If the pesticides are mobile it estimates the transport distance for each chemical including spray drift, direct runoff, soil erosion and leaching to groundwater as separate pathways. It includes important factors such as droplet size, local soil type, slope, and rainfall, as well as the special properties of each chemical (such as oil or water solubility, and persistence). The overall impact is the sum of all these impacts within a particular land use.

Key environmental variables Key pesticide variables
Distance to water Pesticide's half-life
Erosion rate (rainfall intensity, slope, bare soil) Toxicity to algae, water fleas, fish
Amount of organic matter in soil Solubility in oil and water

Tests carried out show PIRI can predict which pesticides and land use combinations are likely to impact on the environment with over 80% reliability. The highest impact is likely to come from market gardens, cotton and fruit orchards. Field crops are less likely to have environmental impact, and grazed pastures and forests have a lower risk of impact.

Integrated Pest Management: cotton [L Indicator 6.11]

The collapse of the cotton industry in the Ord Irrigation Area in the 1970s, following the build-up of resistance to pesticides, was an object lesson to the cotton industry. Cotton communities remain concerned with insecticide risks and careful monitoring and control programs are in place across Australia. The industry and its research collaborators have worked to develop Integrated Resistance Management (IRM) and Integrated Pest Management (IPM) systems that are now widely practiced. Almost all the irrigated cotton in Australia is intensively 'bug checked' every 3-4 days. Insecticides are applied only after threshold numbers are reached, with more selective products used in preference to older broader-spectrum groups wherever possible. In addition, different insecticide groups are rotated in an attempt to manage insect resistance. The Australian Cotton Cooperative Research Centre has recently developed practical IPM guidelines. These include breeding varieties that are least attractive to insects, management of fertilisers, timing of irrigation and defoliation. While environmental audits undertaken for the cotton industry show good levels of compliance with such guidelines, episodes of pesticide contamination in beef, waterways or the atmosphere still occur, and present a significant risk to communities, trade and the environment.

Of the 400 000 to 500 000 hectares of cotton grown in Australia each season about 30% is now genetically modified 'Bt' (Ingard ) cotton. In the past three years there has been an average 42% reduction (ranging from 30% to 60%) in insecticidal spray used against cotton bollworm or 'heliothis' (Helicoverpa armigera) on Ingard cotton crops. This has resulted in 1.75 million litres less pesticide being used on such crops. The pesticides in question were mainly endosulfan, but carbamates, organophosphates and pyrethroids are also used (ACIL Consulting 2000). Other components of IPM include the fostering of conditions that encourage beneficial insects, such as foliar food sprays, and using alternatives to 'hard' chemicals such as foliar-Bt sprays, and trap crops grown alongside cotton.

The remaining 70% of conventional cotton crop still requires a total of 10 to 18 spray applications of herbicides, insecticides and fungicides each year. New transgenic crops may need from three to ten sprays of similar chemicals. (Holloway pers. comm., ACCRC 2000). However, research has indicated that the use of Bt cotton has caused changes in soil microbial populations (Gupta et al. 1998). This would suggest a more precautionary approach may be required in the use of these genetically modified crops.

Integrated Pest Management: horticultural crops [L Indicator 6.11]

Australia, and other western countries, now sell over 75% of fresh fruit and vegetables through supermarket retail chains. Sales depend on the product being attractive, unblemished and of a sufficiently regular size to attract consumers. In addition, consumers require that there is no health risk from pesticides.

Horticultural crops are often grown in small blocks, mostly under irrigation and close to settlements. The crops are very vulnerable to many pests and diseases. To control the full range of pests, diseases and weeds that would make the product unsaleable, most crops require around 20 to 30 sprays of all kinds per growing season. The adoption of IPM will normally reduces this by about 20%, but also reduces the off-site impacts by up to 50% (Juffs et al. 1999).

A recent study of tomato growers found that most processing-tomato growers, all of whom are located in Victoria, started to use IPM in 1995. By 1998, 89% of them had adopted the full range of IPM practices, principally because processing companies demanded certified product (Juffs et al. 1999). The same study found all fresh tomato growers in the Bowen region of Queensland had fully adopted IPM, and in the Bundaberg region, 95% of the tonnage was produced with restricted pesticide use, although only 77% of growers had adopted full IPM. Eighty percent of apple and pear growers have adopted some form of IPM in the past nine years. 20 to 30% of larger growers are in transition to a system of Integrated Fruit Management in which the whole farm or even the district is managed in the most sustainable manner currently possible (Agtrans Research 1999).

IPM in horticultural crops requires some or all of the following measures:

Additional, more sophisticated levels of IPM include:

GM crops

During the past five years genetically modified (GM) crops have become a commercial reality in certain industries and regions of the world, but their introduction has become a matter of great public debate.

Australia has taken a cautiously positive approach to the development of GM crops, with joint government and industry funded research and development in grains, horticulture, cotton, pasture legumes, sugarcane, and tree crops. Biosafety and ethical standards were regulated through the Genetic Modification Advisory Committee (GMAC) until 1999, when the Commonwealth government developed the Interim Office of the Gene Technology Regulator. Subsequently initiatives to improve community understanding and information on a wide range of biotechnology issues have been undertaken. These have included a consensus conference to obtain community views in 1999, and the establishment of Biotechnology Australia, a consortium of government science, technology and industry groups that aims to improve information and education on genetic modification technologies. The Council of Australian Governments (COAG) agreed to guidelines and legislation on labelling, use, and segregation management of GM crops in October 2000. At the time of writing the main points in these guidelines are:

The majority of broadacre GM crops being developed in Australia, and those that have been produced in other countries, and may be grown here, have been designed to withstand commonly-used herbicides. The intention is that the farmer can then use a herbicide to which the crop would normally be susceptible (such as a broadleaf herbicide used against Brassica species of weeds in a crop of canola, which is itself a Brassica). In the case of canola, naturally occurring herbicide resistant varieties have also been identified from conventional plant breeding selection procedures.

A few examples exist of crops that have been produced for improved quality (such as tomatoes with a higher proportion of solids), and market fashion (such as inserting 'blue' colour into non-blue flowers such as carnations and roses). There is intense research interest in such quality attributes as maintaining ripe fruit and vegetables without browning. Most of these transformations are possible with conventional breeding techniques but are less easy to protect by patent.

Implications

Irrigated cotton poses the highest environmental risk from pesticides in Australian agriculture, both because of the number of chemicals used and the frequency of use. Because of the very poor state of knowledge on total chemical usage, not only in agricultural industries, but across all sectors, the relative risks from the conventional and GM crop production systems are difficult to compare.

The issue of resistance to pesticides is a complex one. The early use of some pesticides was over-enthusiastic and profligate, and resistant populations have built up in many instances. As a result, Australia now possesses some of the most challenging examples of herbicide resistance known. Examples include the multiple-herbicide resistance displayed by weeds such as wild oats, capeweed and ryegrass (Lolium perenne). Such weed species frequently develop cross resistance to chemical groups to which the particular plant population has never had exposure, simply because it has had exposure to another chemical group. For example, exposure to sulfonyl ureas can lead to resistance to FOPS (the aryloxy phyonxyproprionate group) (Gill 1994).

While integrated pest, weed or disease management is the ideal solution to resistance, the examples given in this section demonstrate how challenging it is to implement such management across a whole district or industry. This is especially so when the pest, weed or disease is highly destructive, very widespread and where conventional plant breeding has not been able to confer resistance or competitive survival.