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9. Biological control <strong>of</strong> parthenium (Parthenium hysterophorus)<br />

Project dates<br />

May 2007 – June 2014<br />

Project leader<br />

Dr K. Dhileepan<br />

Ecosciences Precinct<br />

Tel: (07) 3255 4449<br />

Email: k.dhileepan@deedi.qld.gov.au<br />

Other staff in 2010–11<br />

Mariano Treviño and Kelli Pukallus<br />

Asad Shabbir and Ruey Toh (The<br />

University <strong>of</strong> Queensland PhD students)<br />

Objectives<br />

• Monitor the field persistence and<br />

abundance <strong>of</strong> parthenium biological<br />

control agents.<br />

• Evaluate the role <strong>of</strong> beneficial<br />

competitive plants to enhance the<br />

effectiveness <strong>of</strong> weed biological<br />

control agents.<br />

Rationale<br />

Parthenium (Parthenium hysterophorus)<br />

is a WONS and a Class 2 declared weed<br />

in Queensland. Biological control is one<br />

<strong>of</strong> the most effective and economically<br />

viable management options for this<br />

weed. Among the various biological<br />

control agents introduced against<br />

parthenium in Queensland, the summer<br />

rust (Puccinia xanthii var. partheniihysterophorae,<br />

previously reported<br />

as P. melampodii) is an agent suited<br />

to areas with hot and dry weather<br />

conditions. It was introduced from<br />

Mexico in 1999 and released at more<br />

than 50 infested sites in Queensland.<br />

The clear-wing moth (Carmenta ithacae),<br />

also native to Mexico, was released<br />

from 1998 to 2002. The stem-galling<br />

weevil (Conotrachelus albocinereus) from<br />

Argentina was released in Queensland<br />

from 1995 to 2000. Although all three<br />

agents have established in the field, their<br />

incidence and abundance in parthenium<br />

infestations in central and northern<br />

Queensland is not fully known.<br />

The role <strong>of</strong> competition from beneficial<br />

plants in managing parthenium is widely<br />

known. So far, however, no information<br />

is available on the potential role <strong>of</strong><br />

various native and introduced pasture<br />

plants in enhancing the effectiveness<br />

<strong>of</strong> parthenium biological control agents<br />

in Australia. Identification <strong>of</strong> beneficial<br />

plants exhibiting high competitive<br />

indices, in particular under changing<br />

climate—specifically elevated carbon<br />

dioxide (CO 2 )—would help to manage<br />

parthenium more effectively.<br />

Methods<br />

Biological control agent<br />

monitoring<br />

Parthenium sites in central and northern<br />

Queensland are monitored at the end<br />

<strong>of</strong> the parthenium growing season. At<br />

each site, we record the incidence and<br />

abundance <strong>of</strong> various biological control<br />

agents—the summer rust (P. xanthii var.<br />

parthenii-hysterophorae), the clearwing<br />

moth (C. ithacae) and the stemgalling<br />

weevil (C. albocinereus)—along<br />

with information on other established<br />

biological control agents and the<br />

abundance <strong>of</strong> parthenium.<br />

Biological control and competitive<br />

plants under elevated CO2 We conduct an experiment in controlledenvironment<br />

rooms to quantify the<br />

combined effect <strong>of</strong> a stem-galling<br />

biological control agent (Epiblema<br />

strenuana) and plant suppression<br />

by buffel grass (Cenchrus ciliaris)<br />

on parthenium’s vegetative and<br />

reproductive growth under ambient CO2<br />

levels <strong>of</strong> 380 parts per million by volume<br />

(ppmv) and under elevated CO2 levels<br />

(550 ppmv).<br />

Parthenium canopy architecture<br />

Parthenium canopy architecture is studied<br />

under three temperature (day/night<br />

22/15 °C, 27/20 °C, and 32/25 °C in thermal<br />

time 12/12 hours) and two CO2 (ambient<br />

and elevated) regimes in controlledenvironment<br />

rooms. Identical light<br />

(photoperiod 12 hours, ~ 250 μmol s –1 ) and<br />

relative humidity (65%) are maintained<br />

in all rooms. We track plant development<br />

from the ninth day after transplantation<br />

using three-dimensional digitising<br />

every third day with a sonic digitiser.<br />

The last measurement is made after<br />

about 550 growing degree days. From<br />

empirical data, we develop a virtual threedimensional<br />

canopy architecture model <strong>of</strong><br />

a parthenium plant using the modelling<br />

s<strong>of</strong>tware L-systems.<br />

Progress in 2010–11<br />

In central Queensland, we surveyed<br />

17 sites in March 2011. Surveys at three<br />

sites in northern Queensland were<br />

conducted in April 2011.<br />

Parthenium summer rust<br />

The summer rust was evident at all<br />

sites with parthenium infestations. The<br />

proportion <strong>of</strong> infected plants was high<br />

at all three sites in northern Queensland<br />

(Cardigan Station, Felspar and Plain<br />

Creek), but the proportion <strong>of</strong> leaves with<br />

rust infection remained low at all these<br />

sites (Figure 9.1). In central Queensland,<br />

parthenium was evident in only 7 <strong>of</strong><br />

the 17 sampling sites, but the summer<br />

rust was observed at all sites with<br />

parthenium infestations. The proportion<br />

<strong>of</strong> plants and leaves infected varied<br />

widely between sites (Figure 9.1).<br />

Parthenium clear-wing moth<br />

We have previously confirmed field<br />

establishment <strong>of</strong> the clear-wing moth at<br />

5 <strong>of</strong> the 13 release sites and 2 nearby nonrelease<br />

sites in central Queensland. In<br />

2011 the clear-wing moth was recovered<br />

from a non-release site near Carfax,<br />

confirming its continued persistence in<br />

the field. High summer rainfall resulting<br />

in flooding could have affected the rootboring<br />

larvae at many sites.<br />

Parthenium stem-galling weevil<br />

The stem-galling weevil was not<br />

recovered in any <strong>of</strong> the survey sites.<br />

Limited establishment <strong>of</strong> this agent<br />

could be due to the dominance <strong>of</strong> the<br />

stem-galling moth (E. strenuana) in all<br />

parthenium-infested areas. The stemgalling<br />

moth and the stem-galling<br />

weevil share a similar feeding niche.<br />

Part 1 Integrated weed management 21

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