7.2 SCOPE AND ACTIONS
In order to avoid consequent release
of potentially highly polluting leachate, land-fills will have to be
operated with the full knowledge of the scientific and technical information,
and the civil engineering works that underpins
the controlled dumping and land-fill disposal of hazardous wastes. Consequently
it is necessary to consider the aspects outlined below.
7.2.1 Licensing Process
Establish a licensing procedure for producers
and dealers and for sites used. Under this, the site should posses a
valid planning permission which in turn should be based on criteria
for the prevention of danger to health, and the
pollution of soil and water. Conditions to be imposed in the licence
include:
extent of stripping and storage of
top-soil and sub- soil for later use to cover up;
types of materials to be accepted and the rate of filling;
the working hours for land-filling and restoration;
direction of tipping and extent of the working face;
keeping records of all activities including deposition;
layering of waste and use of compaction equipment;
fencing and gates, site accommodation and provision
of services;
description of operational techniques to deal with particular wastes;
description of measures to deal with land and water pollution by leachate;
description of measures to deal with gas emissions and/or migration
of toxic agents from;
cover materials both intermediate and final;
progressive restoration plan; and,
monitoring.
The licence should reflect the statutory
requirements and these should be prepared after careful consultation
with
all stake-holders.
7.2.2 Inspection Process
Establish an inspectorate and in particular
the post of a HAZARDOUS WASTE INSPECTOR in NEMA as part of a specialised
environmental inspectorate with the following goal and duties:
Goal
To ensure that the standards of waste
disposal sites, licensing, operation, monitoring and enforcement are
adequate to protect health and the environment.
Duties
To examine on routine basic, the management
of waste at all its stages from the starting point to that of final
disposal by visiting facilities being used to handle, store, treat,
process, and dispose of such waste.
To investigate potential occurrences with a view to determine causes
and preventive solutions.
To advise waste disposal authorities on the execution of their duties.
To make recommendations with the object of ensuring that standards
of operation, site licensing, and enforcement are adequate to protect
health and the environment, that they are equitable and consistent across
the country.
To liaise with all Government institutions that have a role to play
in the field.
To publish an annual report.
7.2.3 Fundamental Statistics
Establish the fundamental statistics
by carrying out a study: on the total quantity of hazardous waste generated
in the country, its types and sources, its geographical distribution,
and its patterns of movement and disposal;
7.2.4 Registration Process
Establish a register of all facilities,
sites licensed or authorised to deal with wastes.
Such facilities include:
Landfill
Transfer Station
Storage
Incineration
Lagoon
Recovery
Treatment
Civic Amenity
Mineshaft
Sludge Land Farm
Reception Pit
Baling
Soakway
Solidification
Evaporation Pit
Each of these facilities should have
a record of the location and of waste deposits to it. Any unauthorised
tipping of waste and should therefore, be banned.
7.2.5 Institutional Responsibilities
Establish a functional hazardous waste
disposal unit located in the Town Planner's Office in each urban authority.
The duties of the waste dispersal unit include:
to undertake a waste survey in its
area and prepare a waste disposal plan;
to control disposal sites by the issue of site licences;
to ensure compliance with the site licence conditions; and,
to administer the requirements of the Environment Management Statute.
7.2.6 Site Selection
Ensure scientific site selection and
evaluation. Before licensing, it is essential for the operator to perform
a detailed site investigation so that soil and hydrological characteristics
are identified and consequently areas unsuitable for wastes are avoided
The important site parameters to be used include:
Land use
Hydrology (surface, subsurface)
Geology
Soil properties (physical, chemical, hydraulic)
Topography
Climate (wind, temperature, moisture)
7.2.7 Site Mapping
Ensure that a land-fill site is mapped
at a scale of 1 : 250 with 1 metre contour intervals. The map should
show:
the proposed fill area;
any burrow area;
access roads; and
drainage devises;
This should include any other information
which will show the planned development, operations and completion of
the land-fill.
7.2.8 Site Monitoring: Standards for
Monitoring Leachate
The performance of the land-fill in
holding waste has to be monitored at least once every 1 year.
Leachate monitoring should not be confined to the land-fill itself,
but should also take place outside the land-fill boundary.
Monitoring must continue beyond the closure of the land-fill, for
at least 5 years.
7.2.9 Site Closure
Site closure must be planned with detailed
considerations equal to site development and operation. The following
must be assured:
adequate supply of final cover and
top-soil;
elimination of residual leachate problems;
capping the site after refuse has been built to its final level to
prevent rain-water ingress and weathering;
landscaping; and,
planting of trees.