MINING FOR CLOSURE
19
Thus, while the costs of environmental manage-
ment are generally lower when measures are in-
corporated at the planning stage instead of retrofit-
ting and redesigning systems later in the life of the
mine, and whilst it is not easy to quantify the costs
of best environmental practice, such costs appear
reasonable. For miners, there are clear indications
that the up-front costs of incorporating best envi-
ronmental practice into a mining operation provide
long term gains for projects in terms of regulatory
performance and lower potential liabilities (Envi-
ronment Australia, 2002b).
Further, widespread adoption of best practice envi-
ronmental management techniques will translate
into long term gains for the industry through great-
er certainty for access to land and project approvals,
improved relationships with regulatory authorities,
acceptance by the community, and lower levels of
risk to the environment.
2.2.1
the business case
Until recent decades organisations involved in
mining were generally
not
interested in assuming
responsibility for the rehabilitation of lands affect-
ed by mining activities. Rehabilitation of mine sites
imposes costs upon the extractive industries that
in the past have generally not been internalised.
However, trends towards high (and higher) expec-
tations for environmental protection, reduced risk
to human health, and for inclusions of community
related considerations, have combined with com-
peting land use demands, increasing value of the
natural environment as recreational space, and in-
creased appreciation of functioning ecosystems as
the repository of valuable biological assets, provid-
ers of natural environmental services and for their
aesthetic appeal (Environment Australia, 2002b).
These trends have greatly changed the business
case for
best environmental practice in mining
and
Mining for Closure
practices as described in this
document. The activities embodied in
best environ-
mental practice mining
and
Mining for Closure
for
which the business case is outlined here, are also
discussed in more detail in later sections.
In this setting – that of increasing requirements
(or absolute requirements) for mine closure – a
range of business related benefits of effective mine
closure are described (Allen, Maurer, & Fainstein,
2001; ANZMEC MCA, 2000; Environment Aus-
tralia, 2002a; Robertson & Shaw, 1998; UNEP
WHO, 1998; van Zyl
et al
., 2002a; Van Zyl, 2000;
Warhurst & Noronha, 1999; WOM Geological As-
sociates, 2000). Importantly for mining organiza-
tions, these benefits evidence themselves both dur-
ing mining operations and at the end of mine life
and as such, they constitute far more than just cost
savings that can be achieved during the execution
of a task forced upon them.
Benefits (principally after Environment Australia,
2002a) include
inter alia
:
continual reduction of liabilities via optimiza-
tion of rehabilitation works undertaken dur-
ing the productive phase of mining operations
rather than deferral of costs to the end of the
project;
provision of a basis for estimating rehabilita-
tion costs prior to final closure so that suffi-
cient financial and material resources can be
set aside;
ongoing testing, assessment and feedback re-
garding the effectiveness of rehabilitation de-
signs and/or processes in a site specific fash-
ion during the active mine life;
increased efficiency in execution of work (e.g.
in reduction of double-handling for waste ma-
terials and topsoil);
possibilities to optimise mine planning for ef-
ficient resource extraction
and
return of eco-
system to a functional form;
reduced areas of land disturbance through use of
smaller waste landforms and mining paths, and
in some circumstances progressive backfilling;
identification of areas of high risk as priorities
for ongoing research and/or remediation;
the direct involvement of operations personnel
in achieving mine rehabilitation outcomes;
the involvement of key stakeholders (especial-
ly local communities) in setting priorities for
mine rehabilitation;
reduction of ongoing responsibilities for the
site and facilitation of timely relinquishment
of tenements and bond recovery;
reductions in impacts on local communities in
terms of environmental, social and economic
impacts of mine operations;
reduction of exposure to contingent liabilities
related to public safety and environmental
hazards and risks;
lower risk of regulatory non-compliances;
greater acceptance/less resistance from key
stakeholders (in particular local communities
and land owners),
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