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Sustainability Report 2015 79

The proposed Stockman Project is located in the high alpine

region of East Gippsland, Victoria, within the State Forest

area and with tenements bordering the National Park. The

project area contains steep topography ranging in elevation

from 600–1,200 metres above sea level. It straddles a

surface water divide that includes the headwaters of

the Tambo River, which flows south to the ecologically

important Gippsland Lakes on the south coast, and part

of the Goulbourn-Murray system to the north-east, which

has significant ecological, urban water supply and farmland

irrigation values. It is therefore critical that the project be

operated to minimise water use, and to protect ecological

values of the catchments in which it is located.

Because of the location high in the watersheds,

establishing large dedicated project water supply dams is

neither practical nor likely to be approved under Victorian

law. The very low permeability or ‘hydrogeologically-tight’

ground at site means that reliable groundwater supplies

are unlikely to be present. Therefore, during development

of the project, a number of other water supply options

were examined including extraction from:

distant rivers

distant commercial water supply dams

dedicated offsite borefields (which would need to be

developed).

In conjunction with this work, close attention was also

paid to minimising water use by the project, and to

capturing and reusing as much process water as possible

– given that 80% or more of water use is for ore crushing

and processing, discharged in tailings disposal, and is

potentially recoverable.

Detailed water balance modelling was carried out during

the project design work. This aimed at closely defining the

differing site water quantity and quality requirements, and

how they could be could be best met, while also meeting

project environmental management objectives. This work

demonstrated that almost all of the project’s water supply

requirements and environmental management targets

could be met by:

storing rain falling directly on the project’s processing

plant site (runoff from which potentially could be

contaminated from plant operations),

storing rain falling on the proposed tailings dam pond

and immediate surrounds (which would mix with

recycled process water)

storing water sourced from other small onsite sources

incorporating various levels of water treatment

maximising recycling of tailings water. That is, the early

estimate of ‘offsite’ water requirements (i.e. sources

from distant rivers, borefields etc.) of some 350 MLpa

could be reduced to almost nil.

As the main inputs to the site water balance model are

rainfall, which varies year-to-year, as well as within longer

time horizon patterns and trends, the modelling was

probabilistic i.e. it used statistical records to predict the

probability of a certain rainfall occurring in a particular year.

The output from many model ‘runs’ established confidence

levels of a particular outcome, such as water available from

the onsite sources in the median, or most likely, year (50th

percentile of the output values). This allowed testing of the

difference between median and wet and dry years, and the

planning implications for those years.

Overall, the modelling results showed that, with a modest

increase in site storage capacity, natural fluctuations in

input could be mitigated and the construction of significant

external ‘redundancy’ infrastructure could be avoided.

CASE STUDY:

WATER USE EFFICIENCY

This outcome had a triple bottom line benefit:

environmental

- no clearing of vegetation for

construction plus reduced energy use for pumping

social

- no groundwater water use in potential

competition with other users

economic

- no expensive infrastructure “insurance”

construction that may never be needed.

The headwaters of the Tambo River between the Currawong and Wilga deposits showing the steep topography

ENVIRONMENTAL IMPACT