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| ISSUE | SEVERITY | RESPONSE/REMEDIATION | RESPONSIBILITY |
| Salinity* | locally severe | revegetation of recharge areas with deep-rooted, high wateruse plants
fencing of watercourses and saline scalds revegetation around scalds |
landowner, greater community and government |
| Waterlogging | locally severe | fencing of waterlogged areas
drainage revegetation of recharge areas with deep-rooted, high wateruse plants |
landowner |
| Soil erosion* | by water - locally severe by wind - very little |
fencing of eroded areas
encouragement of ground cover by seeding pasture or planting native vegetation |
landowner, greater community and government |
| Soil acidity* | moderate | liming of pastures | landowner and greater community |
| Weeds* | locally severe | Woody weeds such as gorse, roses, broom are best controlled by
slashing and spraying.
Salvation jane (Patterson's curse) is best controlled by good pasture management and if necessary spray-grazing - spray with herbicide and then graze pasture to ground with shep, not cattle or horses Capeweed and annual grassy weeds all can be controlled by spraying or spray-grazing or spray-topping. |
landowner (by legislation) and local community |
| Stream degradation* | locally severe | fencing of watercourses, restricting animal access
revegetation of banks and removal of pest species such as willows rehabilitation of saline affected areas |
landowner, local community, wider community, government |
| Loss of biodiversity* | severe | fencing of remnant vegetation
replanting of native species |
landowner, local community, wider community, government |
| Pest animals* | moderate | rabbits - calicivirus has reduced rabbit numbers. Local
populations can be reduced by poisoning, ripping or dynamiting and
fumigation of warrens, and control of pest plants such as blackberry and
gorse. After rabbit control measures are put in place, fox and cat
control must occur.
foxes and wild dogs - coordinated baiting across local area. Fumigation of dens. cats - shooting and trapping |
landowner (by legislation), local community |
* - part of Upper Bremer local action plan (BBCGI 1999a). Italicised stakeholders are those identified as responsible for the major part of funding for remediation projects by the BBCGI in community consultation.
Action strategies:
The BBCG has put into place a number of strategies to help it attain its aims. It is based in the Mt Lofty Ranges Catchment Resource Centre (MLRCRC) in the town of Mt Barker, where locals and other interested parties can obtain information about the plan along with regional land and water management issues. In conjunction with the Mt Lofty soil conservation boards, using Natural Heritage Trust funds, the MLRCRC runs courses in land management for a variety of land use types, provides free land management advice for small property owners, runs field days and demonstration sites, and produces the "Small Talk" newsletter (see http://www.mlrcp.sa.gov.au/ for further information about programs offered by the MLRCRC). Pasture management is a focus of the program and a number of brochures can be obtained from the centre.
The BBCG has produced a number of booklets (such as those by Bradley examining weeds and eucalypt species present in the catchment) and pamphlets with information of interest to local land owners along with various kits such as the stream assessment kit, which gives information about measuring stream salinity and degradation and ways to remediate erosion and salinity. It has a timetable of research activities and monitoring continues of soil and water degradation issues. It co-ordinates funding applications for landcare groups and subcatchments, ensuring that funding is appropriate to the priorities of the local action plans for the subcatchments, and then helps implement on-ground works. Over $2.5 million in NHT funds were secured for the Mount Lofty Ranges in 1998/9, with over $1 million allocated to the MLRCP. The BBCG can apply for funding via Bushcare, Murray Darling, Landcare, the MLRCP and a number of other NHT-funded programs.
Education of absent land owners:
One of the greatest problems facing catchment-wide implementation of the local action plan is education of all community members. Not all property owners are on the property during business hours - the hobby/small farm owners are often non-resident or commute to Adelaide or local towns to work. They may not be able to attend the MLRCRC during working hours. This has required after hours visits to properties by extension officers, pamphlet drops, phone calls and other methods of contacting people who are not resident during the day. Farm planning and management courses, demonstration sites and on-farm visits have to be co-ordinated for weekends if they are to be attended by people who work off-property. The BBCG and MLRCRC have recognised information has to be made widely available for after hours and weekend access, no doubt as a result of its community consultation.
Other strategies:
The Mount Lofty Ranges Regional Revegetation Strategy is a new (2000) strategy released under the auspices of PIRSA, the MLRCP and the SRC. Its main focus is, obviously, the revegatation,
preferably by native vegetation, of areas of the Mount Lofty Ranges that suffer land and water degradation. The strategy is a wide-ranging examination of the vegetation issues found in the the Ranges, the options available to landholders, economic benefits of revegetation and means of implementing the strategy.
The Bremer Barker Catchment Plan is a document impressive in its range and ambition. It seeks to remediate the damage caused by past land management and prevent further land and water degradation. It has set in place a framework for action within the catchment.
The BBCG seems to have followed best practice guidelines in its construction and implementation of the local action plan. It has undertaken extensive community consultation, seeking to gain opinions form all parts of the community. It has broken the plan down into subcatchments so that it can best prioritise the responses needed to local problems and also so that local people feel that they are being listened to and that issues of importance to them are addressed. It involves local schools in the measurement of stream salinity and waterwatch-type programs.
In talking to local residents of the upper Bremer area, it seems that their main complaint is based on the limited local extension services currently offered. They would prefer to not have to travel far to attend field days or get information. Further education of landowners, particularly of small property owners, would be of great help in the implementation of the local action plan. During a visit to the area in August 2000, the writer found that many farmers seems to be unconcerned about the land and water degradation issues on their properties, if the lack of on-ground works are anything to go by. Despite limited time and resources, several local hobby farmers and small property owners were very interested in attacking land degradation issues, had undertaken various courses and participated in Landcare activities, and were enthusiastically engaged in revegetating various parts of their properties.
Most of the strategies employed by the BBCG to encourage local land owners to participate in revegetation and soil and water remediation activities are based on improving productivity, community goodwill, long term land values and aesthetics. Financial benefits of remediating problems with land and water have not been promoted as widely as they could be, possibly due to perceived negative impacts such as those associated with revegetating land that is productive to remediate land that is non-productive. Many landowners are not in a financial position to undertake major works. Revegetating reuires preparation of the land to be replanted, has a high initial cost, both pecuniary and temporal, and requires followup to ensure that weeds or poor rains have not reduced the numbers of plants. It takes a number of years for effects on watertables and salinity to be observed, although with good pasture management, improvements can be almost immediate. However, there are federal government tax breaks or rebates offered for Landcarers and these could be promoted more heavily. Other financial carrots could be offered - rebates on rates or heavily subsidised plants, fences, lime, etc, could be provided for those actively involved in improving the quality of their land.
Finally, to help new property owners, whether those intending to farm the land or those creating a 'rural living" base, an outreach program would be useful. This could be formed of local landcarers or the local extension officers or even a pamphlet drop giving the new landowners information about the area and the community and government groups available to help them with land management problems. This would have to be administered fairly carefully to avoid the perception of evangelicism.
The Squire farm is a triangular 85 hectare property near Harrogate in the Upper Bremer catchment ( figure three, highlighted pink triangle). There are indications that a small sawmill once operated by a small stream in the region of the lowest point in the property. The mill was most likely cutting the timber cut on the slopes above. The land was cleared its mountain gum and upland redgum woodlands some forty to fifty years ago (compare photo from 1949 and photo from 1966 ). The farm was then used for dairying, although the dairy was located off the property. The upper paddocks were used for potato growing by the previous owner but this venture was most unsuccessful as the soil and drainage were not suitable for potatoes.
The wedge-shaped property forms the headwaters of two to three small streams which merge about halfway down the property (figure five). Two dams on the property capture water from two of the streams. The property slopes considerably: the point of the wedge is to the north-west and forms one of two high points on the property, some 60m higher than the base of the wedge in the valley. The other high point is on the north-eastern side of the property and forms a rocky outcropping of sandstone with some remnant native vegetation, being native pastures and a scattering of shrubs such as hop bushes. Two dykes of quartzite/sandstone run across the property about one third and halfway down the slope. The land slopes down from these quite steeply. Soils are duplex and show signs of waterlogging, mainly in the valley and also uphill of the dykes. The A horizon ranges in depth from a few centimetres to about 20cm across the property.
The problem:
In 1990, the farm was bought by the Squire family who
intended to build a residence on the property and use it as an out of Adelaide
base. All members of the family work in Adelaide.
Along with buying a rural property, The Squires inherited a number of
problems related to the past use of the land. The land around the upper, larger
dam was showing signs of severe salting. For about 10 metres, the land to the
east up a gentle slope, was bare and little would grow upon it. White
encrustations were seen on the soil. The overflow from the dam was an eroded but
relatively stable channel with a rocky base. The lower dam also had a small
scald associated with it. Further up the slope from the small dam, to the
north, a salt scald was apparent (figure six), associated with groundwater flow
- tunnelling was clearly visible. The ground tended to be waterlogged in all but
the driest seasons (figure seven).
Figure
Six. Bare land associated with a salt scald north of the small
dam. April 1992.
Figure Seven.
Waterlogging of soil and scald near the small dam. April 1992.
Sea barley grass and cotula were the only plants that would grow in the area and even these did not colonise the worst affected areas. Barley and yorkshire fog grasses along with sedges marked the drainage line further up the slope (figure eight).
Figure Eight. Drainage line showing poor soil
condition indicated by presence of sedges, yorkshire fog grass and barley grass.
The quartzite dykes running across the property were lifting saline groundwater to the surface. At the bottom of the property, about a hectare was persistently waterlogged. Gorse (figure nine) and wild roses colonised the banks of the stream near the waterlogged area. Pattersons Curse also was found in the lower paddocks.
Figure Nine. Woody weeds in the lower paddock near the creek.
Rabbits were common in the rocky areas at the highest points of the property. Finally, there was a steep bank falling away from the proposed site for the residence
The response:
The Squires recognised that not all was well with
their property. They sought help from neighbours and the local Landcare group
and describe that their early experiences as involving a steep learning
curve. They chose to revegetate areas of the property that showed
problems.
The area around the salt scald near the small dam has been fenced off and revegetation works undertaken some eight years ago (figure ten).
Figure Ten.
Revegetation works in progress uphill of the small dam (looking up to the hill
that the girl is standing on in figure 6). 1994.
The steep area below the residence has has a plantation of gums planted to stabilise the bank. This woodlot will be used in the future for domestic consumption. The lower waterlogged area has had a variety of waterlogging tolerant trees planted in the mid 1990s and a surface drain dug in 1998 using Natural Heritage Trust funds. Landcare and Trees for Nature supplied plants for the revegetation works and the Squires now grow some of their own plants for revegetation. The Squires have spent many hours planting several hectares of trees to try to remediate the salting and waterlogging of their property. Landcare and NHT have supplied some funds for the restoration works, but the Squires have also invested their own money in the project. They do not care to reveal how much has been ploughed into their land. The recharge areas on the upper slopes have not been replanted - the Squires were unaware of the importance of increasing water use in these areas.
The present:
The Squires were part of a stream-monitoring group
for two years but have dropped out due to time constraints.
The property was used for grazing goats for five years but now little grazing occurs on the property. The Squires occasional let a paddock for sheep grazing in order to keep the pastures down. A small enclosure near the bottom of the property houses ostriches.
Few rabbits are found on the property thanks to calicivirus. Gorse and roses persist in the lower paddock near the creek.
The upper paddocks around the dams are showing some signs of recovering from waterlogging and salinisation. Grasses and reeds now grow all around the upper dam (figure eleven). The cause of the change is not readily apparent but may be associated with a change in water use by the pastures uphill of the dam. The property is not as heavily grazed as once it was and also, the surrounds of the dam are only infrequently damaged by hoofed animals.
Figure
Eleven. The upper dam showing vegetated banks. Note
the rocks exposed in the foreground. August 2000.
Barley grass and cotula have now colonised all but the very worst parts of the waterlogged area near the small dam. The bare salt scalded area now is only about two square metres of land (figure twelve), considerably down from what it was in 1990 .
Figure
Twelve. The scald north of the small dam. August
2000.
There is still evidence of subsurface tunnelling by groundwater flow (figure
thirteen)and after winter rainfall, the water table rises high enough to cause
ground water to pool (figure fourteen). Waterlogging is a persistent problem
affecting the growth of the gums planted nearby, particularly those closest to
the quartzite dyke, however the plantation is now well established (figure
fifteen).
Figure
Thirteen. Tunnelling is still evident in August 2000.
Figure
Fourteen. Waterlogging of the area north of the small dam.
August 2000.
Figure
Fifteen. Small dam plantation. August 2000.
The future:
A number of recommendations were made to the Squires
for future action. Further revegetation is planned for the property. The
Squires now recognise the value of replanting the recharge areas of their
property to try to lower the water table. This may reduce the waterlogging
experienced around the small dam. They would like to revegetate as much as of
the farm as possible but know that this will take a number of years at the
present rate. They do not work on the property full time and have limited time
to undertake major works, even with help from neighbours, local landcarers and
family. They are also considering direct seeding of the upper paddocks in the
recharge zone as this may be a cheaper way of revegetating the area.
Before they finalise any plans, however, the Squires will look at creating a whole farm plan so that they can target the areas of the property most in need of aid before revegetation and regeneration can occur. They intend to follow the guidleines set down by Fitzpatrick et al (1997) to identify problem areas by vegetation examination and simple tests of soil consistency, sodicity and salinity. They will also test for soil acidity to see if this is affecting remediation of the scalded area. They know where to find the Bremer Barker Catchment management centre and are aware that there are courses run for small property owners on weekends and outside working hours. The main constraints on completing such a course are time and budget. They are also considering getting professional soil tests done and tests of groundwater salinity in order to monitor changes associated with their revegetation activities.
The end result aimed for by the Squires - a healthy creek and healthy land.
Acknowledgements:
The Squire family for help, photos and information. The MLRCRC for technical data and many brochures. Nathan Hurst for help with computer and networking problems.
References:
BBCG. 1996. Catchment Plan and Catchment Manual.
BBCG. 1998. Water quality data collection program report 1997/1998.
BBCG. 1999a. Local Action Plan. Bremer Barker Catchment Group Inc.
BBCG. 1999b. Watercourse Report. A community guide to stream conditions in the Bremer Barker Catchment.
Ellis, MF. 2000. Mount Lofty Ranges Regional Revegetation Strategy. Primary Industry and Resources SA, Adelaide.
Fitzpatrick, R, J Cox and J Bourne. 1997. Managing waterlogged and saline catchments in the Mt Lofty Ranges, South Australia. CRC for Soil and Land Management.
Mills, D. 1996. The Bremer Valley - a place of woodland
beauty. in BBCG, Catchment Plan and Catchment Manual.
Useful websites:
Atlas of South Australia 1988. 2000. http://www.atlas.sa.gov.au/Atlas1988/index.html
Community Biodiversity Network. Regional Biodiversity Planning in South
Australia.
http://www.nccnsw.org.au/member/cbn/projects/LifeLines6.2/Bioreg_SA.html
Metropolitan Adelaide Development Program 1996-2000. Jan 1997. Chapter 9: Outer Metropolitan Area http://www.planning.sa.gov.au/metro_dev_prop/documents/emdp_sansmapserv/ html/MDPCH9.htm
Mount Lofty Catchment Management Program. Last updated Friday 22nd September 2000. http://www.mlrcp.sa.gov.au/
National Land and Water Resources Audit Australia. Audit themes. Implemention program 6. Mt Lofty Ranges. http://www.nlwra.gov.au/full/30_themes_and_projects/48_themes/6_capacity_for_change/ 01_implementation_project/mtlofty_project_abstract.html
National Dryland Salinity Program Fact sheet. Dryland Salinity in the Mt Lofty Ranges. Last modified March 2000. http://www.ndsp.gov.au/15_publications/10_fact_sheets/10_SA/_SA_fact_sheet_2.html
Natural Heritage Trust South Australia. http://www.landcaresa.org.au/NHT2.htm
Primary Industries and Resources SA Soil Conservation District Planning
website
http://www.pir.sa.gov.au/dhtml/ss/external.php?URL=http%3A%2F%2F
www.soil.pir.sa.gov.au&
Title=Soil%20Conservation%20District%20Planning&tempID=31
Other useful information:
BBCG. (undated) Stream Assessment Kit.
Jane Bradley. (undated booklet) Eucalyptus identification in the Bremer Barker Catchment.
Jane Bradley. (undated booklet) Weed identification in the Bremer Barker Catchment.
Liming for the Future. 1999. Lime acid soils to stay in business.
MLRCP. 1999. Mount Lofty Ranges Community Environment Groups.
MLRCP/EPA. (undated) Water Wise, managing your watercourse pamphlets
Mount Lofty Ranges Soil Conservation Boards (MLRSCB). 1999. Dairying in the Mt Lofty Ranges.
MLRSCB. (undated) Land capability in the Mt Lofty Ranges.
MLRSCB. (undated) Managing pastures on small porperties in the Mt Lofty Ranges
Murray Darling Basin Management Commission. 1999. Review of Cap
Implementation.
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