ABSTRACT
This project, compared three different oxidizing agents in the
reduction of cyanide content of cassava wastewater in order to facilitate
cassava wastewater degradation. Analysis of Variance was used to verify if
there is a significant difference on their rates of reaction with cyanide. A
second test using the Scheffé law was carried out to further investigate which
of them reacts faster with cyanide if at all there is a significant difference
on rates of reaction of Sodium Hydroxide, Chlorine and Water with cyanide. Some
parameters like BOD5, Cyanide, COD and Coliform were analyzed also
to support the investigation. From the results of the analysis, it can be concluded
that Sodium Hydroxide (NaOH) is a better oxidizing agent for cassava wastewater
pre – treatment since it results in greater removal of BOD5.
TABLE OF
CONTENT PAGE
TITLE
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CERTIFICATION PAGE ..
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APPROVAL PAGE ..
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DEDICATION ..
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ACKNOWLEDGEMENT ..
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ABSTRACT
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TABLE OF CONTENTS ..
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LIST OF TABLES ..
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LIST OF FIGURES ..
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CHAPTER
ONE:
INTRODUCTION
1.0
INTRODUCTION ..
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1.1 Background Of The
Study
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1.1.1 Effects Of Cassava Toxic Chemicals On
Nigerians ..
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1.2 STATEMENT OF THE
PROBLEM
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1.3 SIGNIFICANCE OF STUDY
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1.4 OBJECTIVES OF STUDY
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1.5 SCOPE AND
LIMITATIONS
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CHAPTER TWO: LITERATURE REVIEW
2.0 LITERATURE
REVIEW
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2.1 GENERAL OVERVIEW OF
CASSAVA ..
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2.1.1 Varieties Of Cassava
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2.1.2 Climate, Soil Requirement And
Cultivation
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2.2 CASSAVA
PROCESSING ..
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2.2.1 Cassava Wastewater
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2.2.2 Characteristics Of Cassava
Wastewater
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2.3 TREATMENT OPTIONS FOR
CASSAVA WASTEWATER 12
2.3.1 Aerobic
Treatment
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2.3.2 Anaerobic Lagoon/Digestion
Treatment
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2.3.3 Aerated
Lagoon
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2.4 ODOUR IN FERMENTED
CASSAVA WASTE WATER
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2.4.1 Factors Affecting Odour
Development
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Methods Of Odour Removal
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2.4.3 Odour Measurements
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CYANIDE AND ITS
OCCURENCE
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2.5.1 Preparation Of
Cyanide
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2.5.2 Reactions
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2.5.3 Cyanide In Form Of Alkalis
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2.5.4 Toxicity And Effect Of Cyanide On
Health ..
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2.5.5 Case Of Cyanide Industry Accident
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2.5.6 Economic Importance Of
Cyanide
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2.5.7 Destruction Of Hydrogen Cyanide
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2.5.8 Harmful Effects Of Cyanide Liberated
From Linamarin
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2.5.9 Effect Of Cassava Processing On Cyanide
Level
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2.6 Analytical Methods And
Treatment Technology
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Methods of Data
Analysis
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2.7.1 Assumptions of Parametric Statistics
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2.7.2 Analysis Of Variance
(ANOVA)
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2.7.3 Dependent And Independent
Variables
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2.7.4
Limitations
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The Scheffé’s
Test
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2.8.1 Level Of Significance
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2.9 Regression
Analysis
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CHAPTER THREE: MATERIALS AND METHODOLOGY
3.0 MATERIALS AND
METHODOLOGY
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3.1 DATA COLLECTION
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3.2 METHOD OF
ANALYSIS ..
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LEVEL OF SIGNIFICANCE
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3.4 PRINCIPLES OF
ANOVA ..
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3.4.1 Steps For One – Way
ANOVA
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3.5 THE SCHEFFÉ’S
TEST
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3.6 SIMPLE REGRESSION
ANALYSIS
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CHAPTER FOUR: RESULTS AND DISCUSSION
4.0 RESULTS AND
DISCUSSION
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4.1 Presentation And
Discussion Of Laboratory Results
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4.2 Data Analysis And
Discussion Of Results
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4.3. Graph of K values for
Coliform
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CHAPTER FIVE: CONCLUSION / RECOMMENDATION
5.0 RECOMMENDATIONS AND
CONCLUSION
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CONCLUSION
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o RECOMMENDATION
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Reference
Appendix
A: Laboratory Results And Associated Graphs.
LIST OF TABLES
Table A: World’s production of
cassava
Table B: Production of cassava in
Nigeria
Table 1: Comparative Effects of
NaOH, Cl2 and H2O on Cyanide Removal Using
ANOVA ..
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Table 2: Comparing The Order
Of Significance Between The Group Means/ Effects of NaOH, Cl2 and
H2O on Cyanide level Using Scheffé’s
Test ..
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Table 3: Comparative Effects of NaOH
and Cl2 on BOD5 Level Using ANOVA
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Table 4: Comparing The Order Of
Significance BetweenThe Group Means/ Effects of NaOH and Cl2 BOD5 level
Using Scheffé’s Test ..
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Table 5: Comparative Effects of NaOH
and Cl2 on Coliform (MPN)Level Using ANOVA
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Table 6: Comparing The Order Of
Significance Between The Group Means/ Effects of NaOH and Cl2 on
Coliform (MPN) level Using Scheffé’s Test
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Table 7: Comparing The Effects Of
De – Ionized H2O And Cyanide In Cassava On COD Concentration Using
ANOVA
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Table 8: Comparing The Order Of
Significance Between The Group Means/Effects Of De – Ionized H2O And
Cyanide In Cassava On COD Concentration Using Scheffé’s
Test
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Tables 9 – 11 K – Values for BOD5, Cyanide,
Coliform
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LIST OF
FIGURES
Fig 1. Graph of K values for BOD5 ..
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Fig 2. Graph of K values for
Cyanide
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Fig 3. Graph of K values for Coliform
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CHAPTER ONE
1.0 INTRODUCTION
1.1 Background Of The Study
Wastewater is categorized according to the source of discharge
like domestic wastewater, industrial wastewater, sanitary wastewater etc. The
effluent from industries is known as industrial wastewater and is noticed in
all industries, leather industries, textile industries, paper industries,
chemical industries, steel industries (Chanlett, 1979). In 1961 approximately
69 percent of all industries discharged their wastes into municipal sewers and
most of these did not provide any treatment at all (Chanlett, 1979). Some
standard methods for sampling, analyzing, reporting and testing industrial
wastewater have been developed over the years by international bodies like the
American Society for Testing Materials (ASTM) committee. There are seven basic
categories of industrial wastewater use, namely steam generation, heat
transfer, solvent action, raw materials, nuclear energy and kinetic energy.
Wastewater treatment has posed a very pressing problem in both rural and urban
cities especially in our country Nigeria.
Owing to change in technology, population and mode of
living, the effects of various physical, chemical and biological factors on the
treatment of the wastewater has been deemed necessary to review. It is
equally pertinent to explore the effect of cyanide on the degradation of
cassava wastewater. Since cassava, together with its various associated
products, is the most widely used stable food in many parts of the country, much
waste is generated during cassava processing. The environmental effect of
the cassava wastewater therefore should be taken into account because a greater
part of the wastewater generated during the process will turn into domestic
waste while others will percolate into the soil. Cassava wastewater is an
inevitable substance released during cassava starch processing. They are either
a by – product of initial production process, or they arise when the cassava
tubes are indiscriminately discharged to a nearby water body. Of course, a
large percentage of African dwellers use cassava tubers as food when processed
in different forms depending on the specie. During cassava starch production,
large amounts of cyano – glycosides are released and hydrolyzed by plant borne
enzymes, leading to Cyanide concentration in the wastewater as high as 200mg/l.
If this cassava wastewater is not properly treated to eliminate the cyanide and
is discharged indiscriminately, an acute health condition can result due to the
toxicity of the cyanide. Thus, the treatment of the cassava wastewater has to
be efficiently done before discharging it to a nearby stream or river since
most communities in Africa (Nigeria in particular) produce large quantities of
cassava wastewater as a result of the use of the cassava for food.
Cyanide is a substance that is formed in combination with other
chemicals in the environment. It refers to the CN– anion
radical. Compound that release cyanide can be inorganic or organic in nature,
but the one present in cassava wastewater is free and organic in nature. Of
these compounds, the one people are most likely to come into contact with are:
Hydrogen cyanide, Sodium cyanide and Potassium cyanide. Hydrogen cyanide
is a colourless gas or liquid with a faint bitter almond odour. Sodium cyanides
and Potassium cyanide are both colourless solids that have a slight odour of
bitter almonds in damp air. Cyanide can be man – made or free naturally
occurring substance. They are found in a number of foods which includes:
cassava, sweet potatoes, yams, maize, millet, bamboo, sugarcane, peas and beans
as well as kernel of almond, lemon, lime, apple, pear, cherry, apricot, and
plum. Examples of cyanides levels measured in selected foods include:
0.001 to 0.45µg/g for say protein products, 1mg/l for cassava and 0.1 to 3mg/l
for lima beans. The presence of cyanide in food of plant origin has been
attributed to natural production within the plants and uptake from the
surrounding.
Free cyanide is found in cassava wastewater. During degradation
of cassava wastewater, the presence of this free Cyanide inhibits the
activities of micro – organisms that degrade cassava wastewater. Degradation of
cassava wastewater simply means the breaking down of cassava wastewater
into simpler molecule by micro – organisms such as pseudomonas. It can be
aerobic or anaerobic. Pseudoalaligenes breaks cyanide into carbondioxide and
ammonia, cyanide can also be broken down by oxidation into cyanate and nitrogen
by ozone.
1.1.1 Effects Of Cassava Toxic Chemicals On Nigerians
Although it was concluded that despite the pathological
conditions in Nigerian, cases of Tropical Ataxic Neuropathy(TAN) are similar to
those observed else where, it is not justifiable to assume that those represent
clinical variants of the same disease. Since, when a diet is poor, multiple
nutritional deficiencies usually occur together although one single factor many
exercise overriding influence in association with others that combines to
produce the final picture. TAN was observed to be prevalent in areas of intense
cultivation of cassava, high frequency of cassava consumption, and high
thiocyanate levels. The disease was rare among 1 – 10 years old, and although
it tended to run in some families, there was no evidence to indicate it was
genetically inherited. In one village, the average incidence was 3%, but was 8%
among those 50 – 60 years old. Goiter was observed to be 2% – 5% higher among
patient with TAN. It has been observed that certain local cassava preparation
such as purupuru may contain 50mg of cyanide per 3kg of product compared to a
lethal dose of 60mg. There is no inverse relationship observed between iodine
content of drinking water and incident of goiter in areas where TAN occurs. A
survey revealed a high correlation between intake of dry, smoked, unfermented
cassava and goiter incidence. Kwashiorkor among children is another condition
that may result form cassava dependency due to imbalance.
1.2 STATEMENT OF THE PROBLEM
As the activities of man undoubtedly results in the accumulation
of wastes, our concern therefore is to drastically reduce, treat and if
possible eliminate completely the danger imposed by the discharge of these
wastes. Pollution caused by cassava wastewater is a threat to life and need
urgent attention, if not properly treated before disposal. Cyanide in cassava
wastewater has ability to cause significant social disruption and demands
special attention to public health preservation. Exposure to high
concentrations of cyanide can cause death within seconds to minutes. Hence this
research on how to reduce or if possible eliminate completely, the danger
imposed by the discharge of this wastewater.