Many longtime landholders in the local district (not just in the areas that were burnt in 2009) have noticed the emergence of Fleabane (Conzya Sp.) as a dominant weed in areas, especially on roadsides and open areas. A common comment goes something along the lines of “I have never seen this weed before but now it is popping up everywhere” There are three species of this weed that are closely related. The most common one in this district seems to be Tall Fleabane – Conyza sumatrensis, which can grow up to 2m high. Unlike the closely related Flax-leaf Fleabane – Conzya bonariensis, which has multiple branches from the base, it has one main stem from the base with branches containing flower heads at the top of the stem.
Fleabane like many weeds is most likely to take hold in areas where there is bare soil or disturbance and less competition from other plants. The best way to control it is to prevent it seeding, as well as trying to maintain a thick ground cover of more desirable species. This could be done by hand pulling or herbicide for larger infestations, Some sources say that one Fleabane plant can produce over 100,000 seeds. It is a member of the Asteraceae (Daisy) family and like most species in that family the seeds are light and fluffy and can spread a long way when carried by the wind.
Flower head (inflorescence) of Tall Fleabane (Conzya sumatrensis) each plant can produce many thousands of wind-blown seeds.
Conzya sumatrensis – Tall Fleabane, Growing in an open disturbed site. Note the singe stem from base, with the branched flower-heads.
Conzya sumatrensis – Tall Fleabane, Showing a leafy new branch.
Masses of Fleabane (Conzya sp.) in this disturbed area between a roadside and a logging Coupe.
Conzya sumatrensis – Tall Fleabane, Showing the hairy stems.
If you are keen to get a better idea of what species are native to the area, one great resource that is now available is the Atlas of Living Australia. You can search any area and it will come up with a whole heap of information about what has been found. It is focused on all biodiversity so it covers a whole range of flora and fauna including fungi and fish and it doesn’t just come up with lists, it also includes links to photo galleries and other information about each species. If you are really keen the site also gives you the opportunity to upload your own species records. You can find the atlas via the following link http://www.ala.org.au
If you are wanting to restore native vegetation, you can save a lot of expense and wasted effort by working with nature as much as possible. Different sites will require different actions to get the desired results. The following examples show some of the different possibilities for action.
The overstorey trees in this gully, (mainly Blue Gums) are regenerating strongly, There are also plenty of understorey plants including various species of native daisy bushes coming back.The main threat to the site is destruction of the recovering vegetation by stock and weed invasion by transforming weeds. Some annual weeds such as Thistles are very common here now but as the trees and understorey grow back they will be shaded out. The real threat is weeds that will potentially outcompete the native plants and reduce the quality of the habitat for animals, in this case Blackberries are the main issue and a high priority should be to establish a plan for their control. There should be no need for any replanting of vegetation, because it should all be able to recover naturally, in order for this to happen the main priority should be to ensure that a good quality fence is built to keep stock away from this sensitive area.
The site above is a completely different story. This area is on an exposed west-facing ridge, it is steep, erosion prone and unproductive so the landholder has wisely decided to re-vegetate it.There are virtually no native species found on this site and given its position in the landscape and the history of grazing, in the near future there is not likely to be any appear on their own . This site needs a long process of rehabilitation it first needs to be fenced out from stock then planted with as many species as possible from its original vegetation type, so that it can eventually become a diverse and valuable habitat for native species. Ongoing control of high threat weeds will need to continue, especially in the first few years after planting to ensure that they do not get a stranglehold on the site and restrict the growth and development of the new plantings.
The above site along a small creek is in a degraded condition with a cover of exotic grasses and weeds and some dead trees present. On a positive note the site does have some surviving overstorey trees as well as some thickets of native understorey present. Again the first priority for this site will be to fence it out from stock. This will give any regenerating trees a much better chance of survival and allow the understorey to spread. Also again weed control of high threat weeds is a high priority. Once fenced is site can be monitored for the appearance of regenerating native plants that may come from seed stored in the soil, blown in by the wind, washed down the gully or dropped on the ground via birds. If regeneration is not occurring you may have to consider other control measures. Rabbits or other browsing animals could be killing new seedlings, you could build a rabbit proof area on the site to see if that makes a difference. Or perhaps thick grass is stopping germination, you could spray an area with herbicide or scalp off some topsoil to see if that helped trigger new plants to sprout. If all else fails you may go back and resort to planting out the open areas of the site with tube-stock.
The site above is quite a difficult one, It is steep, highly exposed and has poor soil. It formerly had pines growing on it before the fires. It has been sprayed for Blackberry but there are still plenty of Blackberry canes re-sprouting and other weeds such as Variegated Thistle covering the site. the other side of the ridge does have some native scrub growing on it which could provide a source of seed, but it also harbours plenty of Swamp Wallabies which will be keen to eat any newly planted seedlings. Turning this site back to native vegetation will probably be a slow process. One strategy may be to fence the site out from stock and replant the site with overstorey eucalypt and wattle species. The site is likely to be too exposed and weedy for understorey plants to survive. If a canopy can eventually be achieved (maybe up to 10 years later), Shade and protection will provide a better opportunity for understorey and a greater diversity of plants to be established.
This site above is typical of many in the Strzelecki Ranges. It is a very steep slope that was cleared for farming, although hindsight tells us that this was a bad mistake. Since given up for agriculture this gully has seen species such as Blackwood and Silver Wattle come back via soil stored seeds and root suckers, and daisy bushes blow in via their wind-blown seeds. The Eucalyptus overstorey however has disappeared, with no hope of natural replacement. The answer is to once again fence out the site from any stock that may be keen enough to wander down into the gully. Attempts to establish carefully selected Eucalyptus species can then be attempted, this will not be simple as Swamp Wallabies are again sure to be common at this site. One common (but expensive and labour intensive) option is to install mesh wire guards at least 1.2m tall around any plantings to allow them to grow above the height at which Wallabies can graze them). Another issue on this site is the large established Pine trees, Pinus radiata, the simplest way of dealing with the Pines may be to poison them.If they are allowed to persist they will reduce the habitat value of the site and regularly drop seed and produce new wildlings.
This last site on this post has seen a mass regeneration of some species after the fires. No stock on the site has seen thousands of seedlings emerge. The landholder is fencing, what is a very long gully, some areas of the gully have recovering remnants, other bits were formerly pasture with a thick carpet of new Wattles and other species coming up and other bits are bare. The uneven regeneration at this site means that planting may be necessary in some parts and not others. Carefully selection of species to plant is also necessary. There is no point wasting time and effort planting when thousands of plants of that species are already coming up on their own. Spots where overstorery trees are missing are probably the highest priority because unlike species that can be spread by wind-borne winged or fluffy seed or berries carried by birds Eucalyptus seed is only spread by release from its capsules.
When you are putting in the effort of planting you would naturally be intending that what you plant (as well as their descendents) will persist for many years. Research and experience have shown that there are many reasons why aiming to restore the original mix of species, that would have grown on the site prior to it being cleared is the best strategy. These plants are more likely to survive in the long term as they will be well adapted to the local soil and climate. The food and shelter that they provide will suit local wildlife and the risk of introducing plants that can become serious weeds will be minimised. eg. Cootamundra Wattle. Therefore it is an important part of any revegetation project to carefully select the species you with to plant.
In our focus area it is highly likely that the original vegetation of your planting site would be one of three vegetation types. Modelling of the landscape has been done across the region and tools have been produce to enable anyone to identify the what the likely original vegetation type or Ecological Vegetation Class (EVC) of any project site would have been. These tools are available online at sites such as http://www.dse.vic.gov.au/about-dse/interactive-maps or you can find this information by other means such as contacting the local Landcare Network or agencies such as the DSE. The following map shows a wide scale view of the original vegetation distribution for this area.
Once you have identified your EVC you can then download the corresponding list from the links below. These lists have been developed from local species records, to help you choose the most suitable species for re-vegetation on your site.
*Note that not all species listed are commercially available and/or not robust enough to be used in new plantings. But they have been included to provide more information about the original flora.
The key to protecting our unique Koala population and ensuring their long term future is to ensure that they have high quality habitat to live in. Koalas need to be able to find regular food and young need to be able to safely disperse to new areas and find breeding partners. The key things that the community can do is to protect existing habitat, this includes controlling weeds such as Blackberries that Koalas are unable to move through. Gullies and Riparian areas are particularly important areas for Koalas, especially in summer, because they are cooler and the leaves there have higher moisture content. The other thing to do is improve it by extending it and linking it to other suitable habitat nearby.
In the region Hancock Plantations (HVP) manage a large area of Koala habitat. They have strategies in place designed to better understand and protect the Koala populations and are open to working with community members on projects such as Koala habitat linkages. They have been involved in work to map the Koala habitat across the region on the land they manage. Studies have shown locally the preferred trees for Koalas are Mountain Grey Gum (Eucalyptus cypellocarpa), Blue Gum (Eucalyptus globulus) and Manna Gum (Eucalyptus viminalis), vegetation that is dominated by these species is classed as “Primary Koala Habitat“.
However all indigenous Eucalypt species in this district have been shown to provide Koala food and habitat. Mountain Ash (Eucalyptus regnans) forests as well as Yertchuk (E. consideniana), Messmate (E. obliqua) and Apple Box (Eucalyptus bridgesiana) are classed as “Secondary Species” so are still very important habitat areas.
Narrow Leaf Peppermint (E. radiata/croajingolensis) and Swamp Gum (E. ovata) are classed as supplementary species, and are also known to support Koalas.