• Pecan nuts: these agronomic conditions also promote the production of high quality, counter-
seasonal pecan nuts. Commercial pecan cultivation in Argentina has grown exponentially
in recent years, which in the medium term will make Argentina one of the world’s top three
producers of this nut and the world’s leading exporter of high value-added pecan-based products
(Frusso 2013).
• Wheat: On the other hand, wheat is one of the most widely grown cereals in the world. In
Argentina, around 15.5 million tons of wheat are produced annually. Seventy-five per cent is
exported and approximately 4.6 million tons are milled to produce 3.4 million tons of flour.
As by-products of this process, approximately 500,000 tons of bran and germ are extracted
annually and used almost entirely for animal feed (Apro et al. 2004).
• Banana: Banana cultivation is the most prominent of Argentina’s tropical crops, with an annual
production ranging from 180,000 to 205,000 tons, with bananas being the most consumed fruit
in Argentina with an annual per capita average of 12 kg (Molina et al. 2015).
• Moringa oleifera: Moringa oleifera, a shrubby plant native to India, is little known in
South America, although it is now abundant throughout the tropics. It is a hardy species that
requires little horticultural attention and grows rapidly, recognized for its nutritional and
medicinal characteristics, as well as being used in some water purification processes (Folkard
and Sutherland 1996). Different parts of the plant are usable raw materials, the leaves, the
undeveloped pods and seeds. Obtaining products and by-products generates around 80% by
crop weight of waste, the husks during dehulling the seed or the green stalks are discarded
during the obtaining of the leaf for infusions use. Currently, in Argentina there is a growing
wave of Moringa cultivation with a large generation of new products that in the short term will
result in a large amount of waste to be disposed of.
The waste from the agri-food industry proposed in this work will be used as biosorbents to
study the retention of metal ions from aqueous effluents. In the case of liquid effluents, the aim
is to reach the polluting discharge levels required by local legislation, considering industries such
as tanning or electroplating. In the case of solid effluents, the goal is to achieve eco-friendly final
disposal.
The design of the Reactor App software were intended to simplify the calculations and to
give as a result the volume of the continuous reactor to be used in a first approximation from data
obtained with few tests carried out on batch reactors. In this way, a first scale-up can be carried out
in a simplified way. As a second objective, Reactor App aims to facilitate the processing of the data
derived from the continuous tests.
3.2 Initial Considerations
The total adsorption capacity (mg adsorbate/g adsorbent) was calculated by Eq. 3.1 and the removal
percentage (%R) by Eq. 3.2 (Boeykens et al. 2017):
(C0 – Cf)
q0 =
V
Eq. 3.1
m
(C0 – Cf)
%R =
Eq. 3.2
C0
where, q
–1
a (mg g ) is the adsorption capacity, C
0 (mg L–1) is the P or Crinitial concentration, Cf is the
P or Cr final concentration (after adsorption), m (g) is the adsorbent mass and V (L) is the volume
of adsorption solution.
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Bioremediation for Sustainable Environmental Cleanup