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From
Wastage to Usage
An
Account of Chrome Recovery in Ethiopian Tanning Industry
Wondirad Seifu
Quality
Control Service Head, Awash Tannery, Addis Ababa, Ethiopia
May-December,
1997, Vol.2, No. 2, ESALIA (Eastern and S. Africa Leather Ind. Asso.)
Introduction
Like many
important discoveries, tanning was probably stumbled upon by historical
accident. With time, leather-making has become an important form of trade,
with knowledge of leather making having spread to many parts of the world.
The world’s leather industry of the mid-nineteenth
century was very similar to that of the 300 or 400 years earlier. Despite
the introduction of various alternative vegetable tanning materials, it
still took 3-10 days to produce a piece of leather in a conventional
tanning process. In addition to this, an immense amount of capital was
required to run a small tannery, making it difficult to meet the needs of
manufacturers.
Chrome drying beds, Sagana
Tannery, Kenya An alternative method to chrome recovery; but postponing of environmental
pollution and chrome wastage.
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It was against this background that chemists attempted to
introduce a process called chrome tanning, in order to mitigate the problem
faced by the tanning industry in particular, and the leather sector in
general.
In Ethiopia, the leather industry is the second biggest
export earner. However tanning processes are characterised by lack of waste
treatment or recycling procedures. Of the various forms of wastes,
pollutants include lime yard fleshing and trimmings, spent vegetable tans,
sulphide, chromium and salts.
Out of these wastes, chrome recovery has been proven as
viable, both economically and environmentally. In general, the exhaustion
rate of chrome tanning process varies between 60-70 percent, and as such
leaves at a minimum about 25 percent of chrome applied in the main tanning
bath. Chrome recovery process is aimed at addressing this problem.
Chrome
and the Tanning Industry
The history of industrial chrome tanning goes back to
1884, when Augustus carried out the first two-bath chrome tanning in the
USA. The introduction of this new tanning material can be regarded as a
“breakthrough” as it took the leather industry one step nearer to a 24 hour
work cycle, as opposed to the vegetable tanning process. However, the
innovation was resisted by the conservative leather industry, which still
saw itself as a craft than an industry.
Chrome ranks sixth in the quantity of deposits on
earth’s crust, fifteen in sea water, and fifteen in the human body. Roughly
estimated, the global consumption of chromium by the leather industry is
about 65,000 tonnes per year, which is about 0.5 percent of the total world
consumption. In principle, however, all chrome tanning materials could be
produced from chromium wastes of several galvanic and chemical industries.
The Ethiopian tanning industry at present time consumes
around 223 tonnes of chrome tanning material (as Cr2O3)
per year (see table) at the current level of net supply of raw hide and
skins for tanneries.
Minimum* Chrome Demand and its
Wastage
in the Ethiopian Tanning Industry
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Description
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Types of chrome
tanning
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Sheep skins
tanning
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Goat skins
tanning
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Hide tanning
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Raw hide and skins consumptions per year (pcs)
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7.26 m
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4.6 m
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1.00 m
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Conversion rate to tanned leather (% )
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20
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100
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100
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Average processing weight, kg/pcs (pelt weight)
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0.6
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0.93
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11.5
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Total processing weight (kg)
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871,200m
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4,278,000
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11,500,000
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Min. Chrome powder offer (%) as commercial chrome salt
on weight base ( Baychrome-A 21% Cr2O3)
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5.0
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5.0
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7.0
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Total chrome powder offer per year (kg)
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43,560
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213,900
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805,000
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Min. Wastage rate (%)
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25
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25
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25
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Total wastage
(kg)
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10,890
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53,475
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201,250
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*it is minimum because it does not include the chromium
consumed in re-chroming or retaining operation and also the amount of
chrome powder offer varies from factory to factory depending on the
technology and the requirements of the end products.
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Chrome
Tanning
Before chrome tanning process starts, animal skins are
subjected to preliminary cleaning and brought into acid media by pickling.
After this, the resulting pure collagen matrix, the main component of the
leather making, is hydrothermally stabilized by tanning with basic
sulphates of trivalent chromium. In the process, the active groups of the
tanning agent bind with the functional groups of the collagen, which gives
the leather adequate strength properties and resistance to various
biological and physical agents.
Unfortunately, despite more than a century experience
with chrome tanning and extensive research work, complete fixation of
chrome to the collagen fibre has not been achieved. This is due to the
affinity of the tanning material to collagen which is in turn governed by
the law of chemical thermo-dynamics. In addition to this, full replacement
with other tanning minerals has been found unsuccessful due to the inherent
characteristics of chrome tanned leather.
As a result of this, chrome tanning process is generally
rather inefficient, sometimes leaving more than 40% of the chrome in the
tanning bath. Even with the most sophisticated chrome-leather manufacturing
process, complete prevention of chromium discharge to the environment by
the leather industry is difficult. However, improvements are gained by
application of highly exhaustive chrome tanning materials.
The above holds true in Ethiopian tanning industry.
According to a study made in Awash Tannery, the fixation rate of chrome
tanning process varies between 60-75%. As such it leaves at a minimum, 25%
of the chromium applied in the tanning bath, ultimately goes to the
environment. Roughly, Ethiopian tanning industry discharges to the
environment every year, at least 56 tonnes of chromium in solution form,
and mixed with other organic and inorganic compounds.
Chrome
and the Environment
Increasingly, the leather industry is being confronted
with the challenge of improving the tanning process, in order to reduce the
amount of effluent discharge to the environment. Many countries have now
imposed limits on the chrome content of the effluent due to the assumed
toxicity nature of chromium.
The toxicity of chrome has been a widely debated issue, although
no general consensus has emerged among tanners, researchers and the
environmental authorities; however, the latter considered any metal,
including chrome as a potential pollutant to the environment. The toxicity
argument asserts that chrome at +3 oxidation state is neutral and stable,
and therefore largely harmless to the environment. However, its conversion
to +6 oxidation state is said to render it biologically active, and
therefore may affect biological organisms. However, a great deal of additional
data is needed in order to adequately establish the valancy, stability and mobility of Cr III in industry waste,
as well as to establish an alternative analytical procedure for the
determination of Cr VI in environmental samples.
In pursuit of a solution to minimize chrome discharge to
the environment, many alternatives have been tried; among these are the
“cost-conscious and responsible tanners’ deed” whose aim was to promote
complete utilization of chromium. This is regarded as both an economic proposition
as well as environmentally responsible measure.
Chrome
Recovery
The technology of chrome recovery is very simple
process. It starts with the collection of spent chromium liquor, and is
followed by separation of the chromium by adding appropriate alkali,
usually magnesium oxide, in order to precipitate the chromium as chromium
hydroxide. The rest of the process is explained by the words of Dr.
Lieselotte Ferikes as follows: “What
is going to happen to the precipitated chromium hydroxide? ...My answer is
to let it settle, drain and dissolve in a boiling sulphuric acid, creating
a regenerated solution... I acquired this procedure and have used it for
decades without problems. This procedure must, however, be accompanied by
careful analytical control.”
Conclusion
Leather being the second major export commodity in
Ethiopia, its importance to the economy is unquestionable. However, the
waste it generates deserves critical attention in both economic and
environmental terms. Latest developments in the chrome tanning provide
prospects for improving the exhaustion rate of chromium in the tanning
bath. Practically, the leather produced from 100% recovered chrome has
showed no difference as compared with normal chrome tanned leather.
Of the two methods currently available for chrome waste
treatment such as disposal after drying in drying beds and chrome recovery
after precipitation, the later has great advantage. Chrome disposal after
drying demands large areas for drying, is liable to produce strong odour and
is contagious on weather conditions. In a country like Ethiopia where
industrial land and foreign exchange are scarce, chrome recovery could
contribute to land savings and increase exchange earnings.
References
1.
Beeby K.J. The Wonderful Story
of Leather, The Leather Institute: London
2.
Thomson R.C., Journal of the Society of Leather
Technologists and Chemists, (1985)
3.
Thorstensen T C. Practical
Leather Technology, Robert E. Krieger Pub. Comp.; USA(1984)
4.
Luck Wolfhard, Journal of the
Society of Leather Technologists and Chemists, (1986)
5.
Langlains J. S, Journal of the Society of Leather
Technologists and Chemists, (1985)
6.
Wilson J.S, Journal of the
American Leather Chemists
Association(1990)
7.
Langerwerf J.A., Journal of the
Society of Leather Technologists and Chemists
8. Ruiland
F.H., Journal of the American Leather Chemists Association(1987)
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