E-Waste in Zimbabwe and Zambia*
Fred Gweme1, Hasha Maringe2, Luka Ngoyi3, Gertjan van Stam1
Abstract
With the advent of Information and Communications Technology, the
issue of electronic waste rises in importance. E-waste comprises of
electronics/electrical goods no longer fit for their originally intended use
or that have reached their expiry date. Apart from the e-waste produced
by its e-consumption (mobile phones, computers), African countries are
on the receiving end of Western e-waste. Presently, Zimbabwe and
Zambia, despite being recipients of ICTs, do not have e-waste disposal
mechanisms of their own. This paper discusses e-waste in both countries
and indicates the measures that are being taken, or can be taken, to
combat it.
1
Science and Industrial Research and Development Centre (SIRDC), Harare,
Zimbabwe
2
ICT Association of Zimbabwe (ICTAZ), Mutare, Zimbabwe
3
University of Zambia, School of Engineering, Lusaka, Zambia
1
Introduction
With the advent of the mainstreaming of Information and
Communications Technology, issues pertaining how to handle e-waste
become pregnant. Worldwide, in the decade between 1994 and 2003,
about 500 million personal computers containing approximately 718,000
tonnes of lead, 1,363 tonnes of cadmium and 287 tonnes of mercury,
reached their end-of-life (Smith et al., 2006). It is estimated that global
e-waste generation is growing by about 40 million tonnes a year.
Electronic waste comprises of discarded electronics/electrical goods that
are not fit for their originally intended use or have reached their end of
life (Sansa-Otim et al., 2012). Apart from the e-waste produced by their
e-consumption (e.g. mobile phones and computers), countries in the
Global South are on the receiving end of e-waste from the Global North.
Therefore, the issue of e-waste is growing exponentially in Africa.
Most African countries lack the capacity to handle and recycle the
hazardous materials contained in e-waste. Furthermore, the common
practice of disposal of e- waste on dumpsites represents a source of
2
environmental pollution. Due to its toxicity, e-waste creates real health
hazards for the nearby communities (Gweme, 2015). The modalities of
e-waste problems are little known in Zimbabwe and Zambia.
There exist no minimum specifications for second-hand equipment in
the fields of Information and Communication Technologies. As a result,
second-hand computers received in Zambia and Zimbabwe are often not
fit for purpose. Even if second-hand electronic goods are usable, their
limited lifespan accelerates their descend into e-waste. Shipping of used
computers to African countries often represents dumping. Second-hand
computers, whether usable or not, often end up in the informal sectors of
the economy. Here computers sustain informal employment and a
livelihood. Due to its nature, the informal sectors are rather immune for
government policies and regulation.
As e-waste contains electronic components that contain valuable
metals, the extraction of these metals gets attention by the informal
sector. Subsequently, e-waste is mostly handled by unregistered,
unauthorised informal recyclers. Craftspersons in the informal sectors do
not necessary possess knowledge and skills on how to recover valuable
components in a safe manner. Poignant documentaries from Kenya and
3
Ghana show e-waste being burned to dispose of its encapsulating parts.
Burning puts lethal toxins such as lead, cadmium, beryllium and
brominate flame retardants into the air.
Zimbabwe and Zambia do not have government-approved e-waste
recyclers. There are no entities that are individually licensed to collect,
process and dispose of e-waste. Therefore, e-waste involves informal
recycling in a context of inadequate legislation and a continued lack of
awareness of the stakeholders.
The tantalising problems of e-waste
“Only a few countries in the developed world are able to scientifically
recycle or dispose the E-waste they generate. In other developed
countries only a fraction of the E-waste is properly recycled, the rest is
either incinerated or sent to landfills" which are solutions that cause
serious secondary problems. Worse still, a sizeable portion of the E-
waste generated in the developed world is exported to developing
countries where it is recycled or dumped without any concern for the
gross pollution that is being caused. It can be said that if the situation
4
vis-a-vis E-waste is posing a challenge in most developed countries, it is
alarmingly bad in the developing world." (Spiegel & Maystre, 1998).
Loopholes in the current Waste Electrical and Electronic Equipment
(WEEE) Directives allow the export of e-waste from so-called
developed to so-called developing countries (Schluep et al., 2011). 70%
of the collected WEEE ends up in unreported and largely unknown
destinations4. Spiegel and Maystre (1998) already saw that “altogether it
is roughly estimated that during the past few years, at least 250,000 tons
of e-waste per annum ‘illegally entered the ports of the five selected West
African countries ... This number is comparable to the total amount of e-
waste generated in small European countries such as Belgium or the
Netherlands, and equates to approximately 5% of all e-waste generated
in the European Union”. Wolfe and Baddeley (2012) state that “the size
and the complexity of the E-waste problem is increasing at much faster
rate than the efficacy of our strategies to contain it. This trend is not
likely to reverse soon and the only viable means to solve the problem is
to drastically reduce generation of waste”.
4
http://www.unep.org/gpwm/FocalAreas/E-WasteManagement/tabid/56458/Default.aspx
5
Progressive legislation regulating e-waste has been adopted at both
regional and international contexts. However, little is done to assist
African countries to come up with their national legislation or strategy
on dealing with e-waste. Most countries in Africa, like Zimbabwe and
Zambia, have ratified the international treaties on e-waste management
without transposing it into national law. As a result, regulatory efforts
and supervising efforts are fragmented. Therefore, the implementation
of international e-waste policies and legislations remains a challenge
since there is no national laws and regulations to support them.
Among the general challenges faced in Zambia and Zimbabwe are
the limited capacity and capability of responsible institutions, lack of
implementation of legal instruments, strained participation among
stakeholders, and lack of resources. As e-waste is mostly handled in
informal industries, there is no reliable data on the volume, costs, and
benefits. The United Nations Environment Programme published its e-
waste estimates in 2009 (Hayden, 2009). Virtually all electronic
equipment contains toxic materials that can be harmful to people and the
environment. A lot of this hazardous materials are found in the circuit
board, and it includes the lead found in the solder and the mercury that
is found in relays and switches (Allsopp et al., 2006). Other electronic
6
equipment like smartphones and laptops contain heavy metals like
cadmium, beryllium, hexavalent chromium or arsenic which have been
shown to build up in our bodies and the environment (UNEP, 2010).
Kumar (2013) explains how hazardous substances come free from e-
waste through
• the product itself when landfilled, for instance the lead in
circuit boards or Cathode Ray Tube (CRT) glass and
mercury in Liquid Crystal Display (LCD) backlights
• distraction in substandard processes, for instance dioxin
formation during burning of halogenated plastics or use of
smelting processes without suitable off-gas treatment
• the use of reagents in the recycling process, for instance
cyanide and other strong leaching acids, nitrogen oxides
(NOx) gas from leaching processes and mercury from
amalgamation
Due to its lack of structure, the issue of electronic waste disposal is
delicate to handle in Zambia and Zimbabwe, much like other countries
in the Global South (e.g. Kanda & Taye, 2011). Recycling and disposal
of e-waste is a risky undertaking, and the risks do go beyond the area
where recycling is being done due to the leakage of hazardous materials
such as mercury and lead from landfills and incinerator ashes (Spiegel
7
& Maystre, 1998). In the mean time, the ICT industry is affected by the
globalised phenomenon of consumerism and what one is called a ‘built
in obsolescence’ of equipment (Charisa, 2013; Chitotombe, 2013). The
life span of computers has dropped from six years in 1997 to just two
years in 2005, and mobile phones have a lifespan of even less than two
years. Hi-tech products like cell phones and computers are driving the
purchasing and discarding of products in a way unknown a generation
ago5. Subsequently, many equipment arriving in Africa can be
considered e-waste at its arrival. Wolfe and Baddeley (2012) noted “70%
of all imports to the five countries are used electronic equipment, with
30% of the used EEE imported being determined to be non-
functioning.”.
E-Waste in Zambia and Zimbabwe
Authorative guidances on the handling of e-waste are set in the Basel
Convention of 1989 and the Bamako Convention of 1994. These
conventions ban the trans-boundary movement of hazardous waste. In
many countries in the Global South, these treaties are not supported by
local legislation. Equipment ends up at dumping sites and landfills.
5
http://www.theguardian.com/technology/2006/nov/27/news.waste
8
Zimbabwe has no policy or legislation on e-waste. In general, the
Environmental Management Act (20:27) prohibits the discharge of
hazardous substances into the environment, but there is no specific
legislation regulating e-waste6. The Environmental Management
Agency (EMA) is drafting a document or strategy for the safe handling
and disposal of e-waste. Responding to questions from environmental
stakeholders during a seminar to mark Africa Environment Day, Clifford
Muzofa said that Harare was yet to come up with a way of disposing of
electronic waste: “It’s something that is new to us, and we do not have a
method of dealing with electronic waste. Except for hazardous
substances, the rest of our waste is dumped at Pomona and taken away
by scavengers."7
In Zambia, e-waste in handled by persons who do most of the repairing
and reusing of electronic equipment. Their simple processing of
electronic waste involves serious health and pollution risks. According
to the Zambia Environmental Management Agency (ZEMA), only a
small percentage of e-waste is being recycled. Sometimes, Zambia sends
6
http://www.thestandard.co.zw/2013/11/10/identifying-key-strategies-e-waste-zim/
7
http://www.thezimbabwean.co/news/zimbabwe/56816/no-plan-for-electronic-
waste.html
9
its electronic waste to South Africa for disposal. Even when taken to a
recycling centre, e-waste is usually not recycled, at least not in the ways
experts think of the term recycling. What happens in some case is that
the gadgets are just buried in heaps underground without regard for the
health of the environment and the people around that particular area. A
small percentage of e-waste is estimated to be sent to recyclers in Zambia
according to the extended product responsibility. The remainder is
mostly dumped or burned, either in informal landfills and makeshift
incinerators. These inappropriate disposal methods of electronic waste
fail to reclaim valuable materials or manage the toxic materials safely.
In fact, soil, water and air are being contaminated.
The Zambia Environmental Management Agency has formulated some
objectives to control the e-waste. These focus on the encouraging of
resource recovery recycling reclamation, direct re-use, or alternative
uses to promote environmentally sound disposal methods. The Extended
Product Responsibility (EPR) extends the responsibilities of the
manufacturers’, importers’ or distributors’ financial or physical
responsibility for a product from its initial stages to the postconsumer
stage. The EPR includes waste minimization programmes through
financial contributions to any fund that may have been established to
10
promote the minimization, recovery, re-use or recycling of waste.
Further, the EPR sustains awareness programmes to inform the public of
the impacts of e-waste emanating from the product on human health and
the environment and any other measures to reduce the potential
implications of the product on human health and the environment. Some
of the other EPR objectives are
• to minimise the generation of e-waste
• to maximise on the e-waste collection efficiency
• to reduce the volume of e-waste requiring disposal and maximise
the economic value of it.
Discussion
With the growing use of ICTs, the production and handling of e-
waste continues to expand. Given the fragmented realities, or general
lack of capacity to handle e-waste in Africa, efforts should focus how to
reduce the impact of e-waste. One such effort is Green Computing.
Green computing is the use of computers and related resources in an
environmentally responsible manner and to avoid disposal for toxic
chemicals.
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Obviously, Zimbabwe and Zambia should avoid taking e-waste from
the Global North.
Another approach is to solicit contributions from citizens as well as
the manufacturers and producers. The citizens or consumers can
contribute by making their preferable choice to buy those electronic
products which can be recycled or it can be reused, or choose those
which contains a less toxic chemicals.
Educational institutions could integrated Green Computing as a
compulsory subject, rather than an optional one. New ideas can be
solicited from students, based on Green IT fueling innovations that could
make products less hazardous. Institutions of higher learning can
incorporate the important issues of e-waste in their research agenda.
As technology importing countries, there is a need for relevant
authorities to ensure that the recycling process is taken into consideration
already at import and/or purchase (pricing) of electronic equipment. The
contemporary adagio ‘from cradle to cradle’ provides for a clear
challenge to sustainable the transformation of waste into material
12
resources. E-waste could sustain business activities that include provide
for
• take-back systems
• manual dismantling facilities
• local pre-processing activities
• sound end-processing activities.
Within African philosophy, ‘things’ (Nguni: Kintu) are also seen as
part o ‘life.’ Thus (e-)waste also is part of the life in communities. This
view contrasts with a deconstructed philosophy in the Global North,
where materials are seen as lifeless, and thus ready to be manipulated
and even discarded. In African philosophy, the whole process of
technology is to be inclusive (Mawere & van Stam, 2016). Thus
technology starts when it is discussed for the first time (during design)
and is taken as to exist from that life with humans up to the sublimation
of the physical/tangible form. In this line of thought, discarding of waste
is foreign, because waste is not recognised in such
atomised/disconnected/sequenced way, but ‘the remains’ are still part of
the relational aspects with things. In that sense, African philosophy can
provide a basis for a more holistic, integrated approach to e-waste. When
13
addressing e-waste from an African positionality, we could envision
more integrated views. These view can contrast with the neo-liberal
methods privatisation of the benefits and externalising of the cost
(pollution, waste).
Further, there is need for thorough understanding the local context
and economy and how it provides for incentives for informal collectors
of e-waste. When appropriately approached and incentivised, the
informal sector can collect e-waste for registered, and thus formal,
recycling services. Further, there should be the right incentives for
consumers to part with the electronic goods they no longer want - and
that are often hoarded at home - in exchange for new benefits.
At present, the international treaties and (draft) policies best function
as ‘sensitization', but not necessarily as ‘training' as there appears little
research to gain an understanding of the complex and diverse realities.
Therefore, apart from the ‘top down' approach, a ‘bottom up' approach
can be fostered, in which every country must come up with their e-waste
management strategy and policy which should feed into Regional ones.
At a global level, clearly defined standards and best practices could
14
be presented as examples from National and Regional Policies. The
Global Partnership for Waste Management (GPWM) should assist
developing countries with expertise and funding for the formulation of
National E-Waste Strategies and Policies. Efforts should also be made to
ensure that Regional and International Conferences and Workshops on
e-waste attract a fair representation with more participation from the
regions worst affected by e-waste. The role of Private Public
Partnerships (PPP) can be strengthened in tackling the e-waste
challenge. International Conventions should set deadlines for
submission of National Policies and Strategies on e-Waste Management
and encourage the development of national evidence basis.
Conclusion
In conclusion, the hazardous nature of e-waste is one of the rapidly
growing environmental problems of the world. The ever-increasing
amount of e-waste is exacerbated by a general the lack of awareness.
Unappropriate skills is deepening the problem.
Currently, the informal sector is involved with the crude dismantling
of electronic waste, as part of for their livelihood. They, their
communities, and the environment is at great risk; therefore there is an
15
urgent need to strategise to contain health hazards of e-waste handling
among these workers in Zambia and Zimbabwe.
For e-waste management a number technical solutions are available.
However, these florish only in the right regulatory environment. A
context appropriate hybrid management system can be developed, for
which there is much room for operational research and evaluation
studies.
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*
Gweme, F., Maringe, H., Ngoyi, L., & van Stam, G. (2016). E-Waste
in Zimbabwe and Zambia. In 1st Institute of Lifelong Learning
and Development Studies International Research Conference,
Chinhoyi University of Technology, 2-5 August 2016, Chinhoyi,
Zimbabwe.
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