EVALUATION OF CHLORIDE USING EMBEDDED SYSTEM...

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EVALUATION OF CHLORIDE USING EMBEDDED SYSTEM BASED ANALYSER AND ARTIFICIAL NEURAL NETWORK COMPUTATION IN BIOLOGICAL AND ENVIRONMENTAL SAMPLES A THESIS SUBMITTED TO BHARATHIDASAN UNIVERSITY, TIRUCHIRAPPALLI FOR THE AWARD OF THE DEGREE OF DOCTOR OF PHILOSOPHY IN PHYSICS By R.VASUMATHI A.V.V.M SRI PUSHPAM COLLEGE (AUTONOMOUS) (AFFILIATED TO BHARATHIDASAN UNIVERSITY) POONDI – 613503 THANJAVUR DISTRICT TAMILNADU, INDIA AUGUST 2011

Transcript of EVALUATION OF CHLORIDE USING EMBEDDED SYSTEM...

EVALUATION OF CHLORIDE USING EMBEDDED SYSTEM BASED

ANALYSER AND ARTIFICIAL NEURAL NETWORK COMPUTATION IN

BIOLOGICAL AND ENVIRONMENTAL SAMPLES

A THESIS SUBMITTED TO

BHARATHIDASAN UNIVERSITY, TIRUCHIRAPPALLI

FOR THE AWARD OF THE DEGREE OF

DOCTOR OF PHILOSOPHY

IN

PHYSICS

By R.VASUMATHI

A.V.V.M SRI PUSHPAM COLLEGE (AUTONOMOUS) (AFFILIATED TO BHARATHIDASAN UNIVERSITY)

POONDI – 613503 THANJAVUR DISTRICT TAMILNADU, INDIA

AUGUST 2011

Dr. P. Neelamegam

Reader in Physics(Retd),

Department of Physics,

A.V.V.M Sri Pushpam College,

Poondi – 613 503,

Tamil Nadu, India.

CERTIFICATE

Certified that this thesis entitled “EVALUATION OF CHLORIDE

USING EMBEDDED SYSTEM BASED ANALYSER AND ARTIFICIAL

NEURAL NETWORK COMPUTATION IN BIOLOGICAL AND

ENVIRONMENTAL SAMPLES” is the bonafied work of Mrs. R.VASUMATHI

who carried out the research under my supervision. Certified further, that to the best of

my knowledge the contents of this thesis have not formed the basis for the award of any

degree, diploma, or other similar title of any University or Institution.

Poondi. (Dr.P.NEELAMEGAM)

Date: Research supervisor/Guide

CONTENTS Page No

Preface Acknowledgements List of publications CHAPTER – I INTRODUCTION 1-18

1.1 Chloride 1 1.1.1 Pivotal Roles of Chloride in human body 2 1.1.2 Sources of Chloride 2

1.2 Roles of Chloride in biological samples 3 1.3 Roles of Chloride in environmental samples 4

1.3.1 Soil Chloride importance in plants 4 1.3.2 Yield and quality response of Chloride 5 1.3.3 Sea water Chloride importance in marine organism 5 1.3.4 Chloride influence on corrosion 7

1.4 Embedded system 8 1.5 Artificial Neural Network 10 1.6 Scope of the research work 12 References 13

CHAPTER – II MICROCONTROLLERS AND ARTIFICIAL NEURAL NETWORK 19-56 2. Basic concept of Measurement 19

2.1.1 Microcontrollers 19 2.1.2 Microcontroller Peripherals 21 2.2 Microcontroller P89C668 25 2.21 Pin descriptions 28

2.3 Microcontroller PIC16F877 29 2.3.1 Pin descriptions 32 2.4 Microcontroller P89C51RD2 33 2.4.1 Pin descriptions 36 2.5 Microcontroller ATmega32 37 2.5.1 Pin descriptions 40

2.6 Microcontroller PSoC CY8C27443 41 2.6.1 Pin descriptions 43 2.7 Artificial Neural Network 45 2.7.1 Introduction 45 2.7.2 Transfer function 46 2.7.3 Training of Artificial Neural Networks 47 2.8 Back Propagation Algorithm 49 2.8.1 Derivation for Back propagation algorithm 49

2.9 Genetic Algorithm 53 References 55

CHAPTER – III MEASUREMENT AND ANALYSIS OF CHLORIDE IN BIOLOGICAL SAMPLES 57-88

3.1 Renal physiology 57 3.1.1 Colorimetry principle 58 3.1.2 Proportionality between color and concentration 58 3.1.3 Stability of the color and clarity of the solutions 59 3.1.4 Analytical studies of the Instrument system 59

3.2 Measurement of Chloride in human urine using Microcontroller P89C668 62

3.2.1 System Architecture 62 3.2.2 Instrumental 63 3.2.3 Software 64

3.3 Materials and Method 64 3.3.1 Principle of color complex 65 3.3.2 Reagents 65 3.3.3 Measurement 65

3.4 Results and Discussion 66 3.4.1 Clinical Significance 66 3.4.2 Statistical Analysis 67 3.4.3 Detection and quantification limits 67 3.4.4 Precision 67 3.4.5 Recovery 67 3.4.6 Linear regression analysis 68

3.5 Analysis of Chloride in pharmaceutical sample - Oral Rehydration Salts 76

3.5.1 Introduction 76 3.5.2 Electrolyte supplements 76

3.6 Instrumental 77 3.6.1 Description of the Microcontroller based system 77 3.6.2 Software 78

3.7 Materials and Method 78 3.7.1 Measurement 78 3.8 Results and Discussion 79

3.8.1 Linearity and sensitivity 79

3.8.2 Recovery 79

3.8.3 Linear Regression analysis 80

3.8.4 Statistical analysis 80

References 87

CHAPTER – IV PERFORMANCE AND ANALYSIS OF THREE EMBEDDED BASED BIO-ANALYSERS IN MEASURING SERUM CHLORIDE 89-118

4.1 Introduction 89 4.2 Circuit description of three embedded based bio-analysers 90

4.2.1 P89C668 Microcontroller based bio-analyser 90 4.2.2 Bio-analyser using microcontroller PIC16F877 91 4.2.3 PSoC CY8C27443 microcontroller based bio-analyser 92 4.2.4 Software 93

4.3 Materials and Method 93 4.3.1 Measurement 94 4.4 Results and Discussion 95 4.4.1 Linearity and sensitivity 96 4.4.2 Precision 96 4.4.3 Recovery 96 4.4.4 Linear regression analysis 97 4.4.5 Statistical analysis 97

4.4.6 Interferences 97 4.5 Conclusion 97

CHAPTER – V ELECTRICAL CONDUCTIVITY AS A SURROGATE FOR CHLORIDE DETERMINATION 119-140

5.1 Introduction 119 5.1.1 Electrical Conductivity as a surrogate

for Chloride concentration 120 5.2 Agricultural Soil 120 5.3 Design and development of Electrical Conductivity Measurement set up using Microcontroller Atmega32 121

5.3.1 Design of the measurement system 121 5.3.2 AC modified Wheatstone bridge network 122 5.3.3 Microcontroller and interfacing circuit 123 5.3.4 Software 123

5.4 Materials and Method 124 5.4.1 Sampling Field 124 5.4.2 Sample Collection 124 5.4.3 Sampling procedure 125 5.4.4 Measurement 125 5.4.5 Development of regression Model 126

5.5 Results and Discussion 126 5.5.1 Analytical performance of the system 127 5.5.2 Analysis of Chloride concentration at various locations and plants 127 References 140

CHAPTER – VI COMPUTATION OF CHLORIDE IN ENVIRONMENTAL SAMPLES 141-171

Prediction of Chloride in soil samples using Artificial Neural Network 141

6.1 Introduction 141

6.2 Soil sampling 142 6.3 Implementation of Neural Network 142

6.3.1 Training phase 142 6.3.2 Validation of the developed Neural Network 143 6.3.3 Testing phase 143

6.4 Results and discussion 144 6.5 Prediction of Chloride in sea water

using Artificial Neural Network 154 6.5.1 Selection of input parameters 154

6.6 Sampling field description 154

6.6.1 Measurement 154

6.7 Back propagation Neural Network training 155

6.7.1 Genetic Algorithm based Back propagation Neural Network Training 155

6.7.2 Validation and testing pattern 156 6.8 Results and Discussion 157

6.8.1 Adaptiveness of the model 157 6.8.2 Comparison between the results obtained using Genetic and Back propagation algorithm 158 6.8.3 As an effective tool 158 6.8.4 Chloride influence for aquatic organisms 158

6.9 Conclusion 160 References 171

CHAPTER – VII PREDICTION OF RATE OF CORROSION USING CHLORIDE CONCENTRATION IN MILD STEEL 172-191

7.1 Introduction 172 7.2 Experimental procedures 174 7.2.1 Materials 174 7.2.2 Method - Rate of Corrosion by Weight Loss measurement 174 7.3 Explicit Neural Network formulations for Rate of Corrosion 174 7.3.1 Training Pattern 175 7.3.2 Validation of the proposed NN model 175 7.3.3 Testing Pattern 175

7.4 Results and Discussion 176 7.4.1 Performance of the developed model 176 7.4.2 Effect of Chloride content 176 7.4.3 Effect of pH and temperature 176

7.5 Conclusion 177 References 191

SUMMARY OF THE PRESENT WORK AND SUGGESTIONS FOR

FUTURE WORK 192-195

PUBLICATIONS

PREFACE

Chloride is one of the most eminent electrolytes required for all living cells. It is

abundant in nature and plays a vital role in biological and environmental samples. In

biological consideration, Chloride electrolyte is 70% of the body’s total negative ion

content, which is maintaining a proper balance of fluids inside and outside of human

body cells. It has a pivotal role in renal function, neurophysiology and nutrition. While

considering the environment, it influences greatly soil and sea water. Soil Chloride has

high degree of impact on plant growth and is readily taken up by the roots. It is essential

to the proper function of the plants stomatal openings and photosynthesis. It diminishes

the fungal infections of plants. Sea water contains naturally occurring Chloride which is

essential to the aquatic organisms that live there. In ocean, higher Chloride concentrations

can reduce the toxicity of Nitrite to aquatic life. In negative aspects, Chloride causes

corrosion on materials (Stainless steel, Mild steel and Concrete structures) which

produces cracks, blow holes and finally reduces the life span.

Because of the vital role of Chloride in biological and environmental samples, it

is aimed to perform the analytical studies by less expensive way. Previous research works

have suggested that the analytical method using embedded system to measure Chloride

anion in biological samples is very few. The computation of Chloride using Artificial

Neural Network (ANN) is also less compared to that of other analytical studies. Hence,

the research work is mainly focused on the evaluation of Chloride using the designed and

developed low cost embedded system in biological samples and computation of Chloride

using neural network in environmental samples.

This research report consists of seven chapters.

Chapter I explains the need for measuring Chloride electrolyte in biological and

environmental samples. It also delivers the various techniques used to measure the

Chloride electrolyte in various samples.

Chapter II presents the features of different microcontrollers used in this research

work. It also describes Artificial Neural Network and various algorithms, learning rules

related to the neural network.

Chapter III consists of the design and development of biomedical Analyser using

microcontroller P89C668 (Philips) to measure the human urinary Chloride and the

obtained results are analysed. The effect of hyperchloremia and hypochloremia are

discussed based on the results. The design and development of microcontroller

P89C51RD2 based instrument to find the concentration of Chloride in Oral Rehydration

Salts is also presented in this chapter. The recovery values of added Chloride ranged

from 98.13% to 99.15% with an average recovery of 98.42%, which indicates the

suitability of the designed instrument for bulk drugs and assay tests.

Chapter IV presents the design and implementation of Chloride analyzer to

measure Chloride in serum using the microcontrollers, (i) P89C668 (Philips) with

external peripherals, (ii) PIC16F877 (Microchip) with built in ADC, (iii) PSoC

(Programmable System on Chip- which integrates all the peripherals) - CY8C27443

(Cypress) with built in ADC, MUX, PGA etc. A comparative study has been made based

on the performance of three biomedical analysers using three microcontrollers. The

power consumption, processing time and analytical parameters of three embedded based

bio-analysers have been evaluated.

Chapter V explains the Electrical Conductivity measurement as a surrogate for

Chloride concentration measurement. The development of ATmega32 (Atmel)

microcontroller based Electrical Conductivity measurement set up has been explained.

The obtained results are compared with the EL1CO CM 180 conductivity meter to check

the accuracy of the designed instrument, which gives a correlation coefficient of R =0.98.

It is observed that the range of Electrical Conductivity of soil samples are varied from 45

to 109 mS/cm and the Chloride concentration is maximum at Ramarmadam, (1010 ppm)

and minimum at Kattuthottam (140 ppm), Tamilnadu, South India.

Chapter VI deals the Artificial Neural Network (ANN) with Back Propagation

Algorithm (BPA) to compute the Chloride concentration in soil samples. ANN has also

been used to compute the Chloride concentration in sea water samples using back

propagation algorithm neural network and Genetic Algorithm (GA) based back

propagation neural network. The training pattern consists of temperature (15 to 45° C),

pH (8.1 to 9.3) and Electrical Conductivity (25 to 34 mS/cm) as input parameters and

Chloride concentration as output parameter. The adaptiveness is checked for various

seasonal conditions by varying the input parameters.

Chapter VII presents the negative effect of Chloride concentration which induces

corrosion that reduces the life span of the materials. It explains the corrosion behavior of

mild steel in hydro chloric acid by weight loss measurements method is explained. The

rate of corrosion of mild steel at various aqueous environments by varying Chloride ion

concentration (HCl acid - 0.1N to 0.75 N), pH (0.12 to 1) and temperature (290K to

333K) is modeled by means of Artificial Neural Network is also presented in this chapter.

The summary of the present work along with the suggestions for the future

work are given in brief.

ACKNOWLEDGMENTS

I am deeply indebted to my Research Advisor, Dr.P.Neelamegam for his

guidance and kind encouragement throughout the course of my research work. His keen

interest and support are pivotal to the successful completion of my research.

I wish to thank Shriman.K. Thulasi Ayya Vandayar, Secretary and

Correspondent, A.V.V.M. Sri Pushpam College (Automonous), Poondi, Thanjavur.

I want to thank Dr.S.Chinnaian, Principal, A.V.V.M. Sri Pushpam College

(Automonous), Poondi, Thanjavur.

I owe my gratitude to Dr. A. Thayumanavan, Dean of Sciences and

Dr.P.Philominathan, Head of the Department and staff members, Department of

Physics, A.V.V.M. Sri Pushpam College (Automonous), Poondi, Thanjavur.

I wish to express my sincere thanks to the Doctoral committee members of my

research work, Dr.A. Venkatesan, Assistant professor, Department of Physics, Nehru

Memorial College, Puthanampatti and Dr.R. Radhakrishnan, Assistant professor,

Department of Physics, Jamal Mohamed College, Tiruchirappalli for all the fruitful

discussions and suggestions during the various stages of the work carried out.

I extend my sincere thanks to Dr.A.Rajendran, Assistant professor, Department

of Physics, Nehru Memorial College, Puthanampatti and Mr.R.Raghunathan,

Mr.K.Murugananthan and Mr.A.Jamaludeen for their constant interaction and

support.

I also deliver my heartfelt thanks to Mrs. N.Azhagusavithri and Mr.N.

Keerthivasan for giving a constant support during my research work.

Finally, I would like to express my thanks to my husband Mr.S.Sriram and my kid

S.Sree Krishniga for being my strength through the entire journey.

R.VASUMATHI

List of Publications

Papers Published in International Journals

1. Development of bio-analyzer for the determination of urinary Chloride –

R. Vasumathi, P. Neelamegam – Sensors & Transducers, 119, (8), 2010.

2. ATmega32 microcontroller based Conductivity measurement system as a

surrogate for Chloride estimation of soil samples - P. Neelamegam, R. Vasumathi

- Instrument and Experimental Techniques, Springer publications, No 6, 2010.

3. Measuring Chloride in serum using single Programmable System on Chip

(PSoC), P. Neelamegam, R. Vasumathi – Instrument and Experimental Techniques,

Springer publications, No 3, 2011.

4. Colorimetric determination of Chloride ion in Oral Rehydration Salts using

microcontroller P89C51RD2 - P. Neelamegam, R. Vasumathi – International Journal

of Pharmacy and Pharmaceutical Sciences, Vol 3, (2), 2011.

Papers Communicated to the Journals

1. Artificial Neural Network as a prediction tool for mild steel corrosion -

Communicated to International Journal of Pure and Applied Chemistry.

2. Prediction of Chloride in sea water of Tamil Nadu, India - Communicated to

Australian Journal of Basic and Applied Sciences.

Conference Attended/ paper presented

1. Paper presented in “National workshop on thin film preparation and

Characterisation techniques for energy conversion” 22-26th Nov 2004. Alagappa

University, karaikudi 630 003.

2. Poster presentation in “National symposium on instrumentation”

Cochin University of Science and Technology, Cochin. Nov 30th – Dec 2nd 2005.

3. Paper presented in “National conference on intelligent instrumentation”,

Department on Instrumentation Technology of Dayananda Sagar College of

Engineering, Bangalore. 7-8thApril 2006.

4. Paper presented in “5th International conference on trends in industrial

measurements and automation”, NIT, Trichy.Jan 4th-6th, 2007.

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CHAPTER I

INTRODUCTION

Chloride is a vital mineral required for both human and animal life. All the living

things require a subtle and complex electrolyte balance between the intracellular and

extra cellular milieu. In particular, the maintenance of precise osmotic gradients of

electrolytes is important. Such gradients affect and regulate the hydration of the body,

blood pH, and are critical for nerve and muscle function. Various mechanisms exist in

living species that keep the concentrations of different electrolytes under tight control.

Both muscle tissue and neurons are considered electric tissues of the body. Muscles and

neurons are activated by electrolyte activity between the extra-cellular fluid or interstitial

fluid, and intra-cellular fluid. Electrolytes may enter or leave the cell membrane through

specialized protein structures embedded in the plasma membrane called ion channels.

Electrolytes are ions which are having electric charge. Positively charged ions are called

cations. Negatively charged ions are called anions. In physiology, the primary ions of

electrolytes are Sodium(Na+), Potassium (K+), Calcium (Ca2+), Magnesium (Mg2+),

Chloride (Cl−), Hydrogen phosphate (HPO42−), and Hydrogen carbonate (HCO3

−).

Among these, Chloride anion is an essential electrolyte for all living and nonliving

things. This chapter presents the roles of Chloride in biological and environmental

samples and the literature survey for the previous research work carried out is also

discussed.

1.1 Chloride

Chloride is a major mineral nutrient that occurs primarily in body fluids. It is a

prominent negatively charged ion of the blood, where it represents 70 percent of the

body’s total negative ion content. On average, an adult human body contains

approximately 115 grams of Chloride, making up about 0.15 percent of total body weight

[1]. The suggested amount of Chloride intake ranges from 750 to 900 milligrams (mg)

per day, based on the fact that total obligatory loss of Chloride in the average person is

close to 530 mg per day.

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As the principal negatively charged ion in the body, Chloride serves as one of the

main electrolytes of the body. Chloride, in addition to Potassium and Sodium, assists in

the conduction of electrical impulses when dissolved in bodily water. Potassium and

Sodium become positive ions as they lose an electron when dissolved, and Chloride

becomes a negative ion as it gains an electron when dissolved. A positive ion is always

accompanied by a negative ion; hence there is close relationship between Sodium,

Potassium, and Chloride. Electrolytes are distributed throughout all body fluids including

the blood, lymph, and the fluid inside and outside cells [2]. The negative charge of

Chloride balances against the positive charges of Sodium and Potassium ions in order to

maintain serum osmolarity.

1.1.1 Pivotal roles of Chloride in human body

In addition to its functions as an electrolyte, Chloride combines with hydrogen in

the stomach to make hydrochloric acid—a powerful digestive enzyme responsible for the

breakdown of proteins, the absorption of other metallic minerals, and activation of

intrinsic factor, which, in turn, absorbs vitamin B12. Chloride is specially transported into

the gastric lumen, in exchange for another negatively charged electrolyte (bicarbonate) in

order to maintain electrical neutrality across the stomach membrane. After utilization in

hydrochloric acid, some Chloride is reabsorbed by the intestine, back into the

bloodstream where it is required for maintenance of extra cellular fluid volume [2]. For

Chloride is both actively and passively absorbed by the body, depending on the

current metabolic demands. A constant exchange of Chloride and bicarbonate between

red blood cells and the plasma helps govern pH balance and transport carbon dioxide, a

waste product of respiration, from the body. With Sodium and Potassium, Chloride works

in the nervous system to aid in the transport of electrical impulses throughout the body, as

movement of negatively charged Chloride into the cell propagates the nervous electrical

potential. Deficiency of Chloride results in a life threatening condition known as

alkalosis, in which the blood becomes overly alkaline.

1.1.2 Sources of Chloride

Healthier sources of Chloride include kelp (seaweed), ionic trace minerals, olives,

rye, tomatoes, lettuce, celery, beef liver, breads, salmon (canned), veal liver, cheese,

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vegetables (canned), chicken liver, clams, dried beef, eggs, frankfurters, olives (green),

milk, oysters, peanut butter, table salt, tomato juice and turkey liver [3].

1.2 Roles of Chloride in biological samples

Measurement of urinary Chloride is most useful in the differential diagnosis of

persistent metabolic alkalosis [4]. Metabolic alkalosis can be classified as Chloride

responsive or resistant. Chloride responsive alkalosis is due to loss of hydrogen ion and

Chloride containing extra-cellular fluid, such as occurs with vomiting, nasogastric suction

and diuretic therapy. Chloride resistant alkalosis results from excessive secretion of

mineralcorticoid hormones, which causes bicarbonate reabsorption. The most common

causes are hyperaldosteroism, Cushing's syndrome, exogenous steroid administration,

licorice ingestion and alkali ingestion. The reference range for a 24 hour human urine

collection is 20-250 mmol/day.

The serum Chloride value is a concentration measurement (e.g., the amount of

Chloride/liter of plasma water). Therefore, the serum Chloride concentration can be

elevated above the normal range (98 - 108 mmol/l)—hyperchloremia—either by the

addition of excess Chloride to the Extra Cellular Fluid (ECF) compartment or by the loss

of water from this compartment, and vice versa. The serum Chloride concentration can be

reduced below the normal range—hypochloremia—by the loss of Chloride from the ECF

or the addition of water to this compartment. This means that one cannot evaluate total

body Chloride stores from the serum Chloride concentration. Clinical parameters must be

used in conjunction with serum Chloride values to assess the significance of

hypochloremia or hyperchloremia.

Hypochloremia is due to total body Chloride depletion through, extrarenal,

inadequate NaCl intake, losses of gastrointestinal fluids, vomiting, nasogastric suction,

small bowel fistulas, burns, renal, diuretic abusers, salt-losing nephropathy, interstitial

nephritis, adrenal insufficiency, increased effective circulatory blood volume, drugs and

nicotine.

Conditions associated with Hyperchloremia are fever, hyper metabolic states

increased ambient room temperature, inadequate water intake, loss of thirst perception

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renal losses, central diabetes insipidus, nephrogenic diabetes insiuidos, early renal failure

and primary hyperparathyroidism.

1.3 Roles of chloride in environmental samples

1.3.1 Soil Chloride importance in plants

One of the Chloride influenced environmental samples is soil. Soil is defined as a

thin layer of earth's crust which serves as a natural medium for growth of plants. They

serve as a reservoir of nutrients and water for crops, provide mechanical anchorage and

favourable tilth. The components of soil are mineral matter, organic matter, water and air,

the proportions of which vary and which together form a system for plant growth. The

soil Chloride is readily taken up by the plants. The effect of Chloride, soil fertility and

plant nutrition on plant diseases has been the subject of numerous investigations over the

past two-decades.

Chloride is a nutrient which is important for plant growth. In the mid-1800's

Totingham, 1919 [5] reported that barley top dressed with NaCl (common table salt) is

helpful in stiffening straw and that Chloride is the active ingredient in this fertilizer. The

essentiality of Chloride for plant growth is confirmed during the 1950's. Broyer et al

(1954) [6] is generally considered to be the first study to demonstrate a requirement for

Chloride in higher plants. Growing Marglobe tomato plants in a hydroponic culture

depleted of Chloride, they found growth (dry matter production) is retarded up to 65%

compared to plants receiving adequate Chloride. Deficient plants resumed satisfactory

growth after Chloride is added to the nutrient solutions, or injected into the plants via a

hypodermic needle. Deficiency symptoms are characterized by wilting of leaflets in the

early stages, followed by chlorosis, bronzing, and necrosis in areas proximal to the

wilting. Following this initial study, Chloride requirement are demonstrated in number of

other plant species, including alfalfa, barley, bean, buckwheat, cabbage, carrot, corn,

lettuce, potato, squash, and sugarbeet (Ulrich and Ohki,1956; Johnson et al., 1957;

Ozanne, 1958; Gausman et al., 1958) [7, 8, 9, 10].

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1.3.2 Yield and quality response of Chloride

Chloride deficiencies in plants generally occur in inland soils (Fixen, 1987) [11].

Substantial responses to Chloride containing fertilizers have been reported for different

crops in many parts of the world; e.g.,Coconut (Von Uexkull and Sanders, 1986) [12],

Corn (Heckman, 1995) [13], Kiwifruit (Smith et al., 1987) [14], Oil palm (Von Uexkull,

1990) [15], Potato (Gausman et al., 1958a) [16], Spring wheat and Barley (Fixen et al.,

1986; Engel et al., 1994) [17, 18], Tobacco (Li et al., 1994) [19], and sugarbeet (Zhou

and Zhang, 1992) [20]. Typical symptoms of Chloride deficiency include wilting of

leaves, curling of leaflets, bronzing and chlorosis similar to those seen with Mn

deficiency and severe inhibition of root growth (Ozanne et al., 1957 [21]; Smith et al.,

1987) [14].

The concentration range of Chloride deficiency in plants varies between 0.13 and

5.7 mg/g for spinach and sugarbeet respectively. In wheat, the Chloride concentration of

leaf tissue at heading is a good predictor of the response to Chloride fertilization (Engel

et al., 1998) [22]; the critical range is between 1.5 and 4 mg/g above which no further

response is expected.

In pot experiments, positive responses to Chloride at 100-200mg/kg soil are

reported for white potato, peanut, tomato and at 100-1600mg/kg soil for sugarbeet (Jing

et al., 1992) [23]. On a sandy loam soil, Chloride applications of up to 400kg/ha yielded

500- 1500kg/ha more corn gain than is obtained in the control (Heckman, 1995) [13].

Grain yields of corn are correlated positively with increases in Chloride concentrations in

the leaf ears. Yields of sugarcane fertilized with Ammonium Chloride exceeded or

equaled those of Ammonium Sulfate at 67-225 kg N/ha (about 170- 570 kg Cl/ ha) (Veda

Narayanan, 1990) [24].

1.3.3 Sea water Chloride importance in marine organism

“Life is evolved from water”[25]. The ocean holds all of the Chloride that we

need. Chloride is an essential element for aquatic and terrestrial biota, representing the

main extra-cellular anion in animals. Although Chloride is an essential element for

maintaining normal physiological functions in all aquatic organisms, elevated or

fluctuating concentrations of this substance can be detrimental. More specifically,

exposure to elevated levels of Chloride in water can disrupt osmoregulation in aquatic

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organisms leading to impaired survival, growth, and/or reproduction. Because excess

Chloride is most frequently actively excreted from animal tissues via the kidneys or

equivalent renal organs to achieve osmoregulatory balance, the bioaccumulation potential

of Chloride is low.

Since 1977 Nitrite toxicity has been known to depend greatly on the salinity of the

water in which the Nitrite exposure took place (Crawford and Allen, 1977) [26].

Mortality in seawater occurred at Nitrite concentrations 50 to 100 times higher than in

fresh water (Crawford and Allen, 1977) [26]. The effect of Chloride on the toxicity of

Nitrite is now known to be so great that experiments in which Chloride concentrations are

not documented are of very low value because they cannot be meaningfully compared

with the results of other studies. According to Eifac (1984) [27] recommendation, it is

very important to monitor the Chloride-Nitrate ratio in aquaculture. The ratio of 17 and 8

is recommended for salmon and rough fish, respectively. In the case of Nile tilapia

(Oreochromis niloticus) health impairment without symptoms of toxicity, the ratios

ranged between 50 and 150 (Svobodova et al., 2005a) [28]. The experiments conducted

on rainbow trout and fathead minnow (Pimephales promelas) showed that the

relationship between Nitrite toxicity and Chloride concentration is linear (Russo and

Thurston, 1977; Palachek and Tomasso, 1984b; McConnell, 1985) [29, 30, 31]. Machova

et al. (2004) [32] also proved the linear relationship between lethal concentration and

Chloride concentration in water for ornamental fish (Poecilia reticulate). The most

sensitive species benefit from Chloride addition to the least extent although the benefit is

large even for sensitive fish (Lewis and Morris, 1986) [33].

Nitrite has an affinity for the active Chloride uptake mechanism by Chloride cells

in the gills (Maetz, 1971) [34]. Chloride cells excrete ammonia or H+ ions for Na+ ions

and bicarbonate (HCO3-) for Chloride ions (Love, 1980) [35]. Nitrite has affinity to

Chloride/ HCO3- exchanging. Part of Chloride demand is replaced by Nitrite when it is in

water. Fish with higher speed of Chloride uptake by gills (rainbow trout, perch, pike) are

more sensitive to Nitrites then fish with lower speed of Chloride uptake (eel, common

carp, tench) (Williams and Eddy, 1986) [36]. The competition between Chloride and

Nitrite ions transport across the gill membrane explains because the higher concentration

of Chloride protects fish against toxic impact of nitrite (Jensen, 2003) [37]. The positive

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effect of Chloride for fish tolerance to Nitrites has been demonstrated in other studies in

fish (Svobodova et al., 1987; Hilmy, 1987; Atwood et al., 2001; Huertas et al., 2002;

Tavares and Boyd, 2003; Fuller et al., 2003) [38, 39, 40, 41, 42, 43] and for crayfish

(Jeberg and Jensen, 1994; Beitinger and Huey, 1981) [44, 45].

1.3.4 Chloride influence on Corrosion

In negative aspects, Chloride causes corrosion on steels and concrete. The

research field on evaluation of Chloride diffusion in concrete is growing with

consideration for diffusion, permeation [46] and binding capacity of Chloride ions [47,

48]. Recently, numerical techniques covering Chloride diffusion in partially saturated

condition [49], Chloride behavior in concrete with early-age cracking [50], and micro

structures formation modeling in high performance concrete [51, 52] are proposed based

on behavior in early-age concrete considering hydration and micro pore structure. The

most significant environmental condition which influences the pitting corrosion behavior

of austenitic stainless steels is the Chloride ion concentration to initiate corrosion-induced

deterioration [53]. Chloride ion causes local destruction of the passive film leading to

localised corrosion.

Since the Chloride electrolyte plays a vital role in biological and environmental

samples, measurement of Chloride is necessary. Classical research lines in the sensors

field have pursued the achievement of ever more selective devices towards a particular

chemical species, and at the same time sensitive to its lower concentrations. Several

analytical methods are available to estimate the Chloride concentration in various

samples.

From the Literature survey, it is observed that the various analytical methods used

for the determination of Chloride in biological sample of blood are iodometric procedure

(Geoffrey Arthur, D and Earl Judson King, 1936) [54], Potentiometry ISE (A. Scheipers

et al., 2001) [55], in serum are Direct potentiometry method (M. Panteghini et al., 1986)

[56], Rayleigh light scattering technique (Jing wen Chen et al., 2007) [57], Colorimetry

method (R.G. Schoenfeld et al.,) [58], Enzymatic assay method (Toehihlro Ono et al.,

1988) [59], Chloride ion selective electrode method (G. Dimeski and AE. Clague, 2004,

W.Hubl et al., 1994) [60, 61], Apple computer (Paul J.Taylor and Rosalie A. Bouska,

1988) [62], Cyclic voltametry (Kensuke Arai, 1996) [63], Flow injection analysis (S.

8

Alegret et al., 1988) [64], Optical sensors (Huber Christial et al., 2003) [65] in another

biological sample of urine are colorimetry (Katsuhiko Yokoi, 2002, Wilbur L. Reimers

and Robert M. Zollinger, 1951) [66, 67], Potentiometric method (P.H. Anderson, 1952)

[68], Screen printed silver strip sensor (2009) [69], in sweat by Electrochemical method

(Javier Gonzalo Ruiza et al., 2009) [70] and so on.

Considering the environmental sample of soil, the Chloride concentration is

determined using Electrical Conductivity measurement which can be used as a surrogate

for Chloride concentration (Hamid Zare Abyaneh et al.,2005) [71]. The measurement of

Electrical Conductivity has been made by four point probe method (Makoto Ishikawa et

al., 2006, S.P.S. Badwal et al., 1991) [72, 73], Analog interface (Diego Ramirez Munoz

and Silvia Casans Berga., 2005) [74], Microcontroller AT89C55WD (A. Rajendran and

P.Neelamegam., 2004) [75], Conducting sensors (X.Li et al., 2002) [76], Optimal

frequency range in aqueous solutions (Ferrara L. Callegaro and F. Durbiano, 2000) [77].

The effect of Chloride application in soil and influence on plants (Hiroyuki

Hattori et al., 2006, Karin wiggler et al., 2004) [78, 79], Effect of soil Chloride on

Cadmium concentration in sunflower kernels (Yin Ming Li et al., 1994) [80], on yield

quality of strawberry fruits (Mahmood Esna Ashari and Mansour Gholami, 2010) [81],

on wheat (Dr. W.M. Stewart, 2002, W.A. Norvell et al., 2000) [82, 83] have been

investigated.

From the Literature survey very few works have been done using embedded

system to perform the analytical studies which consists of Microcontroller, having many

peripherals on chip that reduces the cost, size and increases the reliability and

performance.

1.4 EMBEDDED SYSTEM

Modern analytical instruments generally employ one or more sophisticated

electronic devices such as op- amp, integrated circuits, ADC, DAC, counters,

microprocessors and computers. An embedded system is some combination of hardware

and software, either fixed in capability or programmable, that is specifically designed for

a particular function. Industrial machines, automobiles, medical equipment, cameras,

household appliances, airplanes, vending machines and toys (as well as the more obvious

cellular phone and PDA) are among the myriad possible hosts of an embedded system.

9

Embedded systems are controlled by one or more main processing cores that are typically

either microcontrollers or digital signal processors (DSP) [84]. The key characteristic,

however, is being dedicated to handle a particular task, which may require very powerful

processors. Since the embedded system is dedicated to specific tasks, design engineers

can optimize it to reduce the size and cost of the product and increase the reliability and

performance.

Physically, embedded systems range from portable devices such as digital

watches and MP3 players, to large stationary installations like traffic lights, factory

controllers, or the systems controlling nuclear power plants. Complexity varies from low,

with a single microcontroller chip, to very high with multiple units, peripherals and

networks mounted inside a large chassis or enclosure. Home automation uses wired- and

wireless-networking that can be used to control lights, climate, security, audio/visual,

surveillance, etc., all of which use embedded devices for sensing and controlling.

Characteristics

1. Embedded Systems are designed to do some specific task, rather than be a general

purpose computer for multiple tasks.

2. Embedded Systems are not always separate devices. Most often they are

physically built-in to the devices they control.

3. The software written for embedded systems is often called firmware, and is stored

in read-only memory or Flash memory chips rather than a disk drive. It often runs

with limited computer hardware resources: small or no keyboard, screen, and little

memory.

4. Safety: No harm to be caused.

5. Security: Confidential and authentic communication. Even perfectly designed

systems can fail if the assumptions about the workload and possible errors turn

out to be wrong.

6. Must be efficient:

Energy efficient

Code-size efficient (especially for systems on a chip)

Run-time efficient

10

Weight efficient

Cost efficient

7. Dedicated towards a certain application. Knowledge about behavior at design

time can be used to minimize resources and to maximize robustness.

8. Dedicated user interface. (No mouse, keyboard and screen)

9. Many embedded system must meet real-time constraints.

10. Frequently connected to physical environment through sensors and actuators.

1.5 ARTIFICIAL NEURAL NETWORK

In recent years, Artificial Neural Networks (ANNs) have been used successfully

in various fields like biology, Engineering, pattern recognition, financial analysis and so

on, because of their merits such as self learning, self adapting, good robustness and

capability of dealing with non- linear problems. The parallel and distributed structure of

Neural Networks along with their capabilities of generalization, fault tolerance, adaptive

and associative performance, ability to perform dynamic and real time functions and their

limited requirement of software, ensure their appropriateness for many practical

environmental applications.

Artificial neural network technique is particularly suited for the problem that

involves non-linear interpolation [85]. The basic advantage of ANN is that it does not

need any mathematical model; an ANN learns from examples and recognizes patterns in

input–output data without need for any prior assumptions about their nature and

interrelations. Ability to learn by example makes neural networks flexible and powerful

[86]. Provision of data error tolerance [87] and built-in dynamism makes an ANN model

more attractive.

Artificial Neural Networks have been used in waste water quality monitoring

(Ayan Hore et al., 2008) [88], urban storm water quality prediction (Daniel B. May and

Muttucumaru Sivakumar 2009) [89], to predict the dielectric constant – water content

relationship (Magnus person et al., 2002) [90], to estimate of biological oxygen demand

(Emrah Dogan et al., 2007) [91], to model Nitrate concentration river (Suen . JP et al.,

2003) [92], to predict the water quality parameters of Axio river, Northern Greece

(Diamond Poulou et al., 2005) [93] and to predict COD in waste water (Azedine Charef

et al., 2000) [94].

11

Artificial Neural Networks have been applied to predict the Rate of Corrosion in

stainless steels of nuclear reactor (Hilde M.G. Smets et al., 1995) [95], Mild steel in

acidic media (Wanlin wang and Michael L.Free, 2000) [96], steel 3 in Chloride solution

(Kiselev V.D et al 2006) [97], AISI type 316 L stainless steel (K.V.S. Ramana et al.,

2009) [98], Steel in concrete (Parthiban Thirumalai et al., 2005) [99], Mild steel in 1N

H2SO4, ( S.Saratha and V.G. Vasudha, 2009) [100], Stainless steel type AISI 304 L

(Mandal Sumantra et al., 2009) [101], Austenic stainless steel (H.M.G Smets and W.F.L.

Bogaerts, 1992) [102].

Several studies of corrosion analyses have been made in Chloride media, like

corrosion behavior of mild steel in HCl (Ehterum A. Noor et al., 2008) [103], the

prevention of corrosion of carbon steel in Chloride containing solution (Ayse Tosun and

Mubeccel ergun, 2006) [104], Corrosion performance of reinforcing bars embedded in

concrete structures exposed to Chloride environments ( David Trejoa et al, 2005) [105],

Chloride induced corrosion on steels and concrete (Shahzma J. Jaffer, 2009, GK.Glass

and NR. Buenfeld, 2000, A. O. James et al., 2007) [106, 107, 108] have also been

analysed.

In the present research work, ANN is used to compute the Chloride

concentration in environmental samples of soil, sea water and rate of corrosion of mild

steel.

12

1.6 SCOPE OF THE RESEARCH WORK

The Research work is undertaken for the evaluation of Chloride using the

embedded system and computation of Chloride using neural network in biological and

environmental samples.

The objectives of the Research work

To develop a biomedical analyser using Microcontroller P89C668 for measuring

urinary Chloride.

To analyse the effects of elevated Chloride concentration (hyper chloremia) and

low Chloride concentration (hypo Chloremia) in human body using the measured

urinary Chloride concentration.

To measure Chloride in serum using Microcontrollers, P89C668 (Philips),

PIC16F877 (Microchip) and PSoC-CY8C27443 (Cypress).

To investigate the performances of different Microcontroller based Chloride

analysers.

To determine the Chloride concentration in Oral Rehydration Salts (ORS) - a

pharmaceutical sample, using Microcontroller P89C51RD2.

To check whether the value of Chloride in ORS is within the limit of World

Health Organisation (WHO) certified values.

To explore the Chloride concentration in agricultural soil using the developed

Electrical Conductivity measurement set up.

To study the soil Chloride and its effects on plant growth using the observed

results.

To compute Chloride concentration in soil samples using Artificial Neural

Network with back propagation algorithm.

To predict the concentration of Chloride in sea water using ANN with back

propagation algorithm and Genetic Algorithm based back propagation neural

network.

To compute the Rate of corrosion in mild steel using a three layered neural

network model.

To explain the effect of Chloride, effect of pH and temperature on mild steel

using the computed results.

13

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19

CHAPTER II

MICROCONTROLLERS AND ARTIFICIAL NEURAL NETWORK

This chapter explains the basic concept of measurement, microcontroller

architecture and various features of different Microcontrollers P89C668 (Philips),

PIC16F877 (Microchip), P89C51RD2 (Philips), ATmega32 (Atmel) and PSoC

CY8C27443 (Cypress) which are used to design the embedded based bio-analysers for

the study of Chloride in biological samples. It also explains the basics of Artificial Neural

Network, Back Propagation Algorithm and Genetic Algorithm which are employed in the

computation of Chloride in environmental samples.

2.1 Basic concept of Measurement

The measuring system can be considered to consist of three basic steps. (i) The

primary element that senses the quantity under measurement. (ii) The intermediated

means that modifies suitably the output of primary element and (iii) The end device that

renders for indication possible on a calibrated scale.

The primary element must sense and measure the quantity and sets the limit for

the subsequent finding or achievement. The accuracy of the measured value may be less

than the reality if handled by some intermediate systems. Whatever signal amplitude is

produced by a detector, it is processed in the processing module. After adequate

amplification, there is a decision to be taken about whether to carry out processing with

the signal still in analog form or to convert it to digital form by use of an A/D converter.

This conversion ordinarily given higher precision and accommodates to use

Microprocessors/ Microcontrollers/ Computers for further processing.

2.1.1 Microcontrollers

In this age of information technology it is hard to find a product around us that has

not been manufactured without the use of a computer in some form. While manufacturing

tools and processes are heavily dependent on computers for their control, smaller

appliances are more dependent on a smaller version of the computer. Termed as

microprocessors, these semiconductor devices are the heart of any computer. The

advances in microelectronics have led to the growth of single chip computers for a

variety of applications.

20

A microprocessor is a central processing unit fabricated on a silicon substrate. It is

the heart of every computer, laptop or server. The first portable embedded system built

using the Intel 4004 microprocessor was a calculator. Microprocessors are conventionally

programmed using assembly language. Assembly language refers to the list of

instructions provided to the microprocessor to perform arithmetic/logical operations on a

given set of data. Assembly language is usually converted to machine language, which

consists of binary numbers using software called the assembler. Based on the list of

machine language instructions, a microprocessor would perform the following

operations:

Arithmetic operations such as addition, subtraction, multiplication and division.

Logical operations like AND, OR, NOT, EXOR.

Transfer data between memory locations.

Decision control based on the results of the mathematical/logical operations.

The present trend in microprocessor architecture design is to implement 32 bit

ALU with in-built floating point math co-processors. Pipelined execution based on RISC

(Reduced Instruction Set Computer) architecture and special instructions based on CISC

(Complex Instruction Set Computer) designs are inter-mixed to deliver one billion

instructions per second. The availability of cache memory on the chip combined with

multi million transistors packed in silicon power the latest hand held computing

applications.

These microprocessors do not have built in memory, input or output functions

such as parallel ports or serial ports etc. They are optimized to provide only the raw

arithmetic and logic functions required by the operating system at the highest speed. All

other components required to make the computer such as memory, input/output ports,

serial, parallel, and mass storage are provided by external chips and devices. But a

Microcontroller contains its own memory, parallel ports, clock and very often a good

number of peripheral functions not found on a microprocessor.

A microcontroller consists of a microprocessor, memory and all input/output

peripherals on a single silicon chip. The microcontroller with software loaded in the

internal memory is commonly referred to as an embedded chip. An application such as

the cell phone implemented with the embedded chip as the heart of the system is termed

21

as an embedded system application. Figure 2.1 shows the block diagram of a

microcontroller.

The following features are usually included in the design for a microcontroller:

Arithmetic and logic unit

Memory for storing program

EEPROM memory for non-volatile data storage

RAM memory for storing variables and special function registers

Input-Output ports

Timers and counters

Analog to Digital converter

Circuits for reset, power up, serial programming, debugging

Instruction decoder and timing control unit

Serial communication port

The design for a microcontroller has evolved from the design of an embedded

system application using a microprocessor. In order to implement a small control system

with the microprocessor, peripherals such as timers, input ports, output ports and serial

communication driver hardware need to be interfaced. Over a period of time it has been

found that several control applications can be implemented with the same framework of

interfaces. With the advances in large scale integration of transistors, the microcontroller

evolved into its present form integrating these interfaces onto a single chip solution. But

all the microcontrollers will not have the same peripherals in it. Each one is from

different family and they have different peripherals with in it.

2.1.2 Microcontroller Peripherals

Read Only Memory (ROM): Read Only Memory (ROM) is a type of memory used to

permanently save the program being executed. The size of the program that can be

written depends on the size of this memory. ROM can be built in the microcontroller or

added as an external chip, which depends on the type of the microcontroller.

22

Random Access Memory (RAM): Random Access Memory (RAM) is a type of

memory used for temporary storing data and intermediate results created and used during

the operation of the microcontrollers.

Electrically Erasable Programmable ROM (EEPROM): The EEPROM is a special

type of memory not contained in all microcontrollers. Its contents may be changed during

program execution (similar to RAM), but remains permanently saved even after the loss

of power (similar to ROM).

Special Function Registers (SFR): Special function registers are part of RAM memory.

Their purpose is predefined by the manufacturer and cannot be changed therefore.

Program Counter: Program Counter is an engine running the program and points to the

memory address containing the next instruction to execute. After each instruction

execution, the value of the counter is incremented by 1.

Input/output ports (I/O Ports): In order to make the microcontroller useful, it is

necessary to connect it to peripheral devices. Each microcontroller has one or more

registers (called a port) connected to the microcontroller pins.

Oscillator: It is usually configured as to use quartz-crystal or ceramics resonator for

frequency stabilization. Accordingly, if the system uses quartz crystal with a frequency of

20MHz, the execution time of an instruction is not expected 50nS, but 200, 400 or even

800 nS, depending on the type of the microcontroller.

Timers/Counters: Timer is used to measure the time of the events. If the registers use

pulses coming from external source, then such a timer is turned into a counter.

Interrupt: In order to prevent the microcontroller from spending most of its time

endlessly checking for logic state on input pins and registers, an interrupt is generated. It

is the signal which informs the central processor that something attention worthy has

happened.

23

ADC: Analog to Digital converter is a device which converts the analog input into digital

number which is proportional to the magnitude of the analog input.

DAC: Digital to Analog converter is a device which converts a digital code to analog

signal.

PWM: Pulse Width Modulation is a commonly used technique for controlling power to

inertial electrical devices made practical by modern electronic power switches.

The demand from several industries for a variety of such interfaces with different

precision has resulted in several families of microcontrollers.

Accordingly there are 8 bit, 16 bit and 32 bit microcontrollers in the market today.

In addition to this there are several choices of packages starting from 6 pin

microcontrollers to around 156 pin implementations. The differentiation in the

microcontrollers would be in the presence of the number of I/O ports, availability of

multiple timers, precision of A/D converters and special functions like high speed serial

communications.

24

Figure 2.1 Block diagram of a Microcontroller

25

2.2 MICROCONTROLLER P89C668

Microcontroller P89C668 from ‘Philips’ is a single chip 8-Bit Microcontroller

manufactured in advanced CMOS process and is a derivative of the 80C51

microcontroller family. It contains a non-volatile 64 kbytes Flash program memory that is

both parallel programmable and serial In-System Programmable. It has the same

instruction set as the 80C51. It also has four 8-bit I/O ports, a multi-source, four-priority-

level, nested interrupt structure, an enhanced UART and on-chip oscillator and timing

circuits [1].

The microcontroller P89C668 has 80C51 Central Processing Unit, On-chip Flash

Program Memory and can be programmed by the end-user application (IAP) , Parallel

programmed with 87C51 compatible hardware interface to programmer, Speed up to 20

MHz with 6 clock cycles per machine cycle, Full static operation , RAM expandable

externally to 64 kbytes, 8 interrupt sources, Power control modes, Programmable clock

out and I2C serial interface.

The architecture of Microcontroller P89C668 is shown in figure 2.2.1. It

consists of Port0, Port1, Port2 and Port3, RAM, Register B, Accumulator, stack pointer,

ALU (Arithmetic and Logical Unit), PSW (Program Status Word), SFRs (Special

Function Registers), Timers, PCA (The Programmable Counter Array available on the

Microcontroller P89C668 is a special 16-bit Timer that has five 16-bit capture/compare

modules associated with it. Each of the modules can be programmed to operate in one of

four modes: rising and/or falling edge capture, software timer, high-speed output, or

pulse width modulator), Timing and control unit, Instruction register, Oscillator (XTAL1

and XTAL2 are the input and output, respectively, of an inverting amplifier. The pins can

be configured for use as an on-chip oscillator), program counter and Program Address

register.

The pin diagram of microcontroller P89C668 is shown in figure 2.2.2 and

their pin descriptions are explained in 2.2.1.

26

Figure 2.2.1 Architecture of Microcontroller P89C668

27

Figure 2.2.2 Pin diagram of Microcontroller P89C668

Pin Function Pin Function Pin Function

1 P1.5/CEX2 16 VSS 31 P0.6/AD6 2 P1.6/SCL 17 NIC* 32 P0.5/AD5 3 P1.7/SDA 18 P2.0/A8 33 P0.4/AD4 4 RST 19 P2.1/A9 34 P0.3/AD3 5 P3.0/RxD 20 P2.2/A10 35 P0.2/AD2 6 NIC* 21 P2.3/A11 36 P0.1/AD1 7 P3.1/TxD 22 P2.4/A12 37 P0.0/AD0 8 P3.2/INT0 23 P2.5/A13 38 VCC 9 P3.3/INT1 24 P2.6/A14 39 NIC* 10 P3.4/T0/CEX3 25 P2.7/A15 40 P1.0/T2 11 P3.5/T1/CEX4 26 PSEN 41 P1.1/T2EX 12 P3.6/WR 27 ALE 42 P1.2/ECI 13 P3.7/RD 28 NIC* 43 P1.3/CEX0 14 XTAL2 29 EA/VPP 44 P1.4/CEX1 15 XTAL1 30 P0.7/AD7

28

2.2.1 PIN DESCRIPTIONS

MNEMONIC

PIN NUMBER

NAME AND FUNCTION

VSS VCC P0.0–0.7 P1.0–P1.7 P2.0–P2.7 P3.0–P3.7 RST ALE PSEN

16 38 37–30 40–44, 1–3 40 41 42 43 44 1 2 3 18-25 5, 7–13 5 7 8 9 10 11 12 13 4 27 26

Ground: 0 V reference. Power Supply: This is the power supply voltage for normal, idle, and power-down operation. Port 0: Port 0 is an open-drain, bidirectional I/O port. Port 0 pins that have 1s written to them float and can be used as high-impedance inputs. Port 1: Port 1 is an 8-bit bidirectional I/O port with internal pull-ups on all pins except P1.6 and P1.7 which are open drain T2 (P1.0): Timer/Counter 2 external count input/Clockout T2EX (P1.1): Timer/Counter 2 Reload/Capture/Direction Con ECI (P1.2): External Clock Input to the PCA CEX0 (P1.3): Capture/Compare External I/O for PCA module 0 CEX1 (P1.4): Capture/Compare External I/O for PCA module 1 CEX2 (P1.5): Capture/Compare External I/O for PCA module 2 SCL (P1.6): I2C bus clock line (open drain) SDA (P1.7): I2C bus data line (open drain) Port 2: Port 2 is an 8-bit bidirectional I/O port with internal pull-ups. Port 2 pins that have 1s written to them are pulled high by the internal pull-ups and can be used as inputs. Port 3: Port 3 is an 8-bit bidirectional I/O port with internal pull-ups. Port 3 pins that have 1s written to them are pulled high by the internal pull-ups and can be used as inputs. RxD (P3.0): Serial input port TxD (P3.1): Serial output port INT0 (P3.2): External interrupt INT1 (P3.3): External interrupt CEX3/T0 (P3.4): Timer 0 external input; Capture/Compare External I/O for PCA module 3 CEX4/T1 (P3.5): Timer 1 external input; Capture/Compare External I/O for PCA module 4 WR (P3.6): External data memory write strobe RD (P3.7): External data memory read strobe Reset: A high on this pin for two machine cycles while the oscillator is running, resets the device. An internal diffused resistor to VSS permits a power-on reset using only an external capacitor to VCC. Address Latch Enable: Output pulse for latching the low byte of the address during an access to external memory. Program Store Enable: When executing code from the external program memory, PSEN is activated twice each machine cycle.

29

2.3 MICROCONTROLLER PIC16F877

The Microcontroller PIC16F877 from ‘Microchip’ is a low power, high

performance RISC CPU 8 bit microcontroller. Figure 2.3.1 shows the block diagram of

microcontroller PIC16F877. It consists of 8KW (Kilo Word) of flash programmable and

erasable memory together with 368 bytes of RAM. It has four I/O ports, Timer0(8 bit

timer/counter with 8bit prescaler), Timer1(16 bit timer/counter with prescaler), and

Timer2 (8 bit timer/counter with prescaler)two capture (capture is 16bit, maximum

resolution is12ns), compare (compare is 16 bit, maximum resolution is 200ns), PWM

modules (maximum resolution is 10 bit), synchronous serial port with SPI and I2C,

Universal synchronous asynchronous receiver, parallel slave port 8 bits wide, brown out

detection circuitry for brown out reset. It also consists of parallel ports, chip oscillator,

programmable code protection, 14 interrupt sources, 10 bit 8 channel A/D converter and

low power consumption [1].

The Microcontroller PIC16F877 has 100,000 erase/write cycle enhanced FLASH

program memory typical, 1,000,000 erase/write cycle data EEPROM memory typical,

Self-reprogrammable under software control, Fully static design, wide operating voltage

range (2 to 5.5v), commercial and industrial temperature ranges, Only 35 single word

instructions to learn, operating speed DC-20MHz clock input, DC-200ns instruction

cycle, In-circuit serial programming, Watchdog timer with its own on-chip RC oscillator

for reliable operation, Programmable code protection, Power saving SLEEP mode,

Selectable oscillator options and In-circuit debug via two pins.

The pin diagram of microcontroller PIC16F877 is shown in figure 2.3.2 and their

pin descriptions are explained in 2.3.1.

30

Figure 2.3.1 Block diagram of Microcontroller PIC16F877

31

Figure 2.3.2 Pin diagram of Microcontroller PIC16F877

32

2.3.1 PIN DESCRIPTIONS

Pin# Pin Name Description

1 ~MCLR 2 RA0/AN0 PORTA.0 /Analog Channel 0 3 RA1/AN1 PORTA.1 /Analog Channel 1 4 RA2/AN2 PORTA.2 /Analog Channel 2 5 RA3/AN3 PORTA.3 /Analog Channel 3 6 RA4/T0CK1 PORTA.4 / External Clock for Timer 0 7 RA5/AN4 PORTA.5 /Analog Channel 4 8 RE0/AN5 PORTE.0 /Analog Channel 5 9 RE1/AN6 PORTE.1 /Analog Channel 6 10 RE2/AN7 PORTE.2 /Analog Channel 7 11 Vdd +3 ~ +5V 12 Vss GND 13 OSC1/CLKIN Oscillator Connection /Clock In 14 OSC2/CLKOUT Oscillator Connection / Clock Out 15 RC0/T1CK1 PORTC.0 /External Clock for Timer 1 16 RC1/CCP2 PORTC.1 /CCP2 17 RC2/CCP1 PORTC.2 /CCP1 18 RC3/SCK/SCL PORTC.3 /SCK(for SPI)/SCL(for I2C) 19 RD0 PORTD.0 20 RD1 PORTD.1 21 RD2 PORTD.2 22 RD3 PORTD.3 23 RC4/SDI/SDA PORTC.4/SDI(for SPI)/SDA(for I2C) 24 RC5/SDO PORTC.5 /SDO (for SPI) 25 RC6/TX PORTC.6 /TX (for Serial Com.) 26 RC7/RX PORTC.7 /RX (for Serial Com.) 27 RD4 PORTD.4 28 RD5 PORTD.5 29 RD6 PORTD.6 30 RD7 PORTD.7 31 Vss GND 32 Vdd +3 V ~ +5 V 33 RB0/INT PORTB.0/External Interrupt 34 RB1 PORTB.1 35 RB2/PGM PORTB.2 /Programming Input 36 RB3 PORTB.3 37 RB4 PORTB.4 38 RB5 PORTB.5 39 RB6/PGC PORTB.6 /Debugger/ICSP 40 RB7/PGD PORTB.7 /Debugger/ICSP

33

2.4 MICROCONTROLLER P89C51RD2

A Single-Chip 8-Bit Microcontroller P89C51RD2 from ‘Philips’ is

manufactured in advanced CMOS process. Figure 2.4.1 shows the block diagram of

microcontroller. It contains a non-volatile 64kB Flash program memory that is both

parallel programmable and serial In-System and In-Application Programmable. In-

System Programming (ISP) allows the user to download new code while the

microcontroller sits in the application. In-Application Programming (IAP) means that the

microcontroller fetches new program code and reprograms itself while in the system.

This allows for remote programming over a modem link. The instruction set is 100%

compatible with the 80C51 instruction set. It also has four 8-bit I/O ports, three 16-bit

timer/event counters, a multi-source, four-priority-level, nested interrupt structure, an

enhanced UART and on-chip oscillator and timing circuits [1]. Boot ROM contains low

level flash programming routines for downloading via the UART, can be programmed by

the end-user application (IAP), 6 clocks per machine cycle operation (standard), 12

clocks per machine cycle operation (optional), Speed up to 20 MHz with 6 clock cycles

per machine cycle (40 MHz equivalent performance); up to 33 MHz with 12 clocks per

machine cycle, Fully static operation, Power control modes, Programmable clock out,

Second DPTR register, synchronous port reset, Low EMI (inhibit ALE) and

Programmable Counter Array (PCA) [1]. Figure 2.4.2 shows the pin diagram of

Microcontroller P89C51RD2 and their pin descriptions are given in 2.4.1.

34

Figure 2.4.1 Block diagram of Microcontroller P89C51RD2

35

Figure 2.4.2 Pin diagram of Microcontroller P89C51RD2

36

2.4.1 PIN DESCRIPTIONS MNEMONIC

PIN NUMBER

NAME AND FUNCTION

VSS VCC P0.0–0.7

P1.0–P1.7

P2.0–P2.7

P3.0–P 3.7

RST ALE

PSEN

EA/VPP

XTAL1 XTAL2

20 40 39–32

1–8 1 2 3 4 5 6 7 8 21–28 10–17 10 11 12 13 14 15 16 17 9 30 29 31 19 18

Ground: 0 V reference. Power Supply: This is the power supply voltage for normal, idle, and power-downoperation. Port 0: Port 0 is an open-drain, bidirectional I/O port. Port 0 is also the multiplexed low-order address and data bus during accesses to external program and data memory. Port 1: Port 1 is an 8-bit bidirectional I/O port with internal pull-ups on all pins except P1.6 and P1.7 which are open drain. As inputs, port 1 pins that are externally pulled low will source current because of the internal pull-ups. (See DC Electrical Characteristics: IIL). T2 (P1.0): Timer/Counter 2 external count input/Clockout (see ProgrammableClock-Out) T2EX (P1.1): Timer/Counter 2 Reload/Capture/Direction ECI (P1.2): External Clock Input to the PCA CEX0 (P1.3): Capture/Compare External I/O for PCA CEX1 (P1.4): Capture/Compare External I/O for PCA CEX2 (P1.5): Capture/Compare External I/O for PCA CEX2 (P1.5): Capture/Compare External I/O for PCA CEX3 (P1.6): Capture/Compare External I/O for PCA Port 2: Port 2 is an 8-bit bidirectional I/O port with internal pull-ups. As inputs, port 2 pins that are externally being pulled low will source current because of the internal pull-ups. (See DC Electrical Characteristics: IIL). Port 3: Port 3 is an 8-bit bidirectional I/O port with internal pull-ups. As inputs, port 3 pins that are externally being pulled low will source current because of the pull-ups. RxD (P3.0): Serial input port TxD (P3.1): Serial output port INT0 (P3.2): External interrupt INT1 (P3.3): External interrupt T0 (P3.4): Timer 0 external input T1 (P3.5): Timer 1 external input WR (P3.6): External data memory write strobe RD (P3.7): External data memory read strobe Reset: A high on this pin for two machine cycles while the oscillator is running, resets the device. In normal operation, ALE is emitted twice every machine cycle, and can be used for external timing or clocking. Note that one. ALE can be disabled by setting SFR auxiliary.0. With this bit set, ALE will be active only during a MOVX instruction. Program Store Enable: The read strobe to external program memory. When executing code from the external program memory, PSEN is activated twice each machine cycle. External Access Enable/Programming Supply Voltage: EA must be externally held low to enable the device to fetch code from external program memory locations. Crystal 1: Input to the inverting oscillator amplifier Crystal 2: Output from the inverting oscillator amplifier.

37

2.5 MICROCONTROLLER ATmega32

ATmega32 Microcontroller from ‘Atmel’ company is a high-performance, Low-

power AVR® 8-bit Microcontroller. The block diagram of microcontroller is shown in

figure 2.5.1. It has advanced RISC architecture, 31 Powerful Instructions, Most Single-

clock Cycle Execution,32 x 8 General Purpose, Working Registers, Fully Static

Operation, up to 16 MIPS Throughput at 16 MHz, On-chip 2-cycle Multiplier, High

Endurance Non-volatile Memory segments,32K Bytes of In-System Self-programmable

Flash program memory,1024 Bytes EEPROM, 2K Byte Internal SRAM [1]. It consists of

32 K Bytes in System Programmable Flash, one 16-bit Timer/ Counter and two 8-bit

Timer/ Counter, an eight Channel 10 bit ADC, 32 programmable I/O lines in four I/O

ports (Port A, Port B, Port C and Port D) and 2k Bytes of SRAM [1]. It has high

endurance non-volatile memory segments, In-System Programming by On-chip boot

program, True Read-While-Write Operation, JTAG Interface, On-chip analog

comparator, power-on reset and programmable brown-out detection, 40-pin PDIP, 44-

lead TQFP, and 44-pad QFN/MLF.

Figure 2.5.2 shows the pin diagram of Microcontroller ATmega32 and their pin

functions are explained in 2.5.1.

38

Figure 2.5.1 Block diagram of ATmega32

39

Figure 2.5.2 Pin diagram of Microcontroller ATmega32

40

2.5.1 PIN DESCRIPTIONS

VCC: Digital supply voltage.

GND: Ground.

Port A (PA7-PA0): Port A serves as the analog inputs to the A/D Converter. Port A also

serves as an 8-bit bi-directional I/O port, if the A/D Converter is not used. The Port A

output buffers have symmetrical drive characteristics with both high sink and source

capability.

Port B (PB7-PB0): Port B is an 8-bit bi-directional I/O port with internal pull-up

resistors (selected for each bit). The Port B output buffers have symmetrical drive

characteristics with both high sink and source capability.

Port C (PC7-PC0): Port C is an 8-bit bi-directional I/O port with internal pull-up

resistors (selected for each bit). The Port C output buffers have symmetrical drive

characteristics with both high sink and source capability. PC5 (TDI), PC3(TMS) and

PC2(TCK) will be activated even if a reset occurs. The TD0 pin is tri-stated unless TAP

states that shift out data are entered.

Port D (PD7-PD0): Port D is an 8-bit bi-directional I/O port with internal pull-up

resistors (selected for each bit). The Port D output buffers have symmetrical drive

characteristics with both high sink and source capability.

RESET:. A low level on this pin for longer than the minimum pulse length will generate

a reset, even if the clock is not running.

XTAL1: Input to the inverting Oscillator amplifier and input to the internal clock

operating circuit.

XTAL2: Output from the inverting Oscillator amplifier.

AVCC: It is the supply voltage pin for Port A and the A/D Converter. It should be

externally connected to VCC, even if the ADC is not used. If the ADC is used, it should

be connected to VCC through a low-pass filter.

AREF: It is the analog reference pin for the A/D Converter.

41

2.6 MICROCONTROLLER PSoC CY8C27443

Microcontroller PSoC (Programmable System on Chip) CY8C27443 from

‘Cypress’ consists of many mixed signal array with on-chip controller device. Figure

2.6.1 shows the block diagram of microcontroller ATmega32. It is a low cost single chip

programmable device with powerful Harvard Architecture processor. It has low power,

high speed, operating voltages down to 1.0V using On-chip Switch Mode Pump (SMP),

industrial temperature range: -40°C to +85° and 3.0 to 5.25V operating voltage. The 12

Rail-to-Rail analog PSoC blocks provides 14-Bit ADCs, 9-Bit DACs, Programmable

Gain Amplifiers (PGA) and Programmable Filters and Comparators. The 8 digital PSoC

blocks have 8- to 32-Bit Timers, Counters, PWMs, CRC and PRS Modules, 2 Full-

Duplex UARTs, Multiple SPI Masters or Slaves and Connectable to all GPIO Pins. The

precision, programmable clocking of PSoC has internal 2.5% 24/48 MHz Oscillator and

24/48 MHz with Optional 32 kHz Crystal. The flexible On-chip memory of PSoC has

16K flash program storage 50,000 Erase/ Write Cycles, 256 Bytes SRAM data storage

and In-System Serial Programming. Additional system resources of PSoC are I2C Slave,

Master, and Multi-Master to 400 kHz, Watchdog and Sleep Timers and User-

Configurable low voltage detection.

The PSoC consists of digital systems comprising of digital blocks and analog

systems comprising of analog blocks. Using the development tools, library elements can

be configured to provide analog functions (from Analog blocks), such as Programmable

Gain amplifiers, filters, ADCs with exceptionally low noise, input leakage and voltage

offset, DACs, comparators, Modulators, Correlators and Peak detectors. Digital

functions such as timers, counters, PWMs, SPI and UARTs can be configured from the

digital blocks of Digital systems. There is no other microcontroller that has

programmable voltage, instrumentational, inverting, and non-inverting amplifiers.

Hardware generators of pseudorandom and CRC code, as well as analog modulators, are

unique to PSoC families [1]. Figure 2.6.2 shows the pin diagram of Microcontroller PSoC

CY8C27443 and their pin functions are given in 2.6.1.

42

Figure 2.6.1 Block diagram of Microcontroller PSoC CY8C27443

43

Figure 2.6.2 Pin diagram of Microcontroller PSoC CY8C27443

44

2.6.1 CY8C27443 28-Pin PSoC Device Pin Pin Description No. Name 1 P0[7] Analog column mux input. 2 P0[5] Analog column mux input and column output. 3 P0[3] Analog column mux input and column output. 4 P0[1] Analog column mux input. 5 P2[7] 6 P2[5] 7 P2[3] Direct switched capacitor block input. 8 P2[1] Direct switched capacitor block input. 9 SMP Switch Mode Pump (SMP) 10 P1[7] I2C Serial Clock (SCL) 11 P1[5] I2C Serial Data (SDA) 12 P1[3] 13 P1[1] Crystal Input (XTALin), I2C Serial Clock (SCL) 14 Vss Ground connection. 15 P1[0] Crystal Output (XTALout), I2C Serial Data(SDA) 16 P1[2] 17 P1[4] Optional External Clock Input (EXTCLK) 18 P1[6] 19 Input XRES Active high external reset with internal pull down. 20 P2[0] Direct switched capacitor block input. 21 P2[2] Direct switched capacitor block input. 22 P2[4] External Analog Ground (AGND) 23 P2[6] External Voltage Reference (VRef) 24 P0[0] Analog column mux input. 25 P0[2] Analog column mux input and column output. 26 P0[4] Analog column mux input and column output. 27 I P0[6] Analog column mux input. 28 Vdd Supply voltage.

45

2.7 ARTIFICIAL NEURAL NETWORK

2.7.1 Introduction

Neural networks are being applied to an increasing large number of real world

problems. The human brain consists of about ten billion neurons and a neuron is, on

average, connected to several thousand other neurons. By way of these connections,

neurons both send and receive varying quantities of energy. One very important feature

of neurons is that they don't react immediately to the reception of energy. Instead, they

sum their received energies, and they send their own quantities of energy to other neurons

only when this sum has reached a certain critical threshold. The brain learns by adjusting

the number and strength of these connections. This biological fact is sufficiently powerful

to serve as a model for the neural net. The primary advantage of neural network is that

they can solve problems that are too complex for conventional technologies; problems

that do not have an algorithmic solution or for which an algorithmic solution is too

complex to be defined. In algorithmic approach, the computer follows a set of

instructions in order to solve a problem. Unless the specific steps that the computer needs

to follow are known, the computer cannot solve the problem. That restricts the problem

solving capability of conventional computers to problems that we already understand and

know how to solve. The versatility of the problems [2 - 5] in which Artificial Neural

Networks have been used are yielding promising results. ANN implementations have

been widely used over the last years on such applications as aerospace,

telecommunications [6], robotics [7], image processing [7, 8], applied mathematics [9,

10], financial analysis [11], intrusion detection systems and others.

The architecture of ANN (Figure 2.7) generally consists of three layers. An input

layer with input neurons, where the data are introduced, the hidden layer with hidden

neurons, where the data are processed and the output layer with output neurons, where

the results for the given inputs are produced. It also consists of weights between neurons,

a transfer function that controls the generation of output in a neuron, and learning laws

that define the relative importance of weights for input to a neuron [12]. Each neuron

receives a signal from the neurons in the previous layer, and each of those signals is

multiplied by a separate weight value. The weighted inputs are summed, and passed

46

through a transfer function which scales the output to a fixed range of values. The output

of the limiter is then broadcast to all of the neurons in the next layer. So, to use the

network to solve a problem, we apply the input values to the inputs of the first layer,

allow the signals to propagate through the network, and read the output values.

Figure 2.7 Architecture of Neural Network

2.7.2 Transfer Function

The behavior of an ANN depends on both the weights and the input – output

function (transfer function) that is specified for the units.

This function typically falls into one of three categories:

Linear: For linear units, the output activity is proportional to the total weighted output.

Threshold: For threshold unit, the output is set at one of two levels, depending on

whether the total input is greater than or less than some threshold value.

Sigmoid: For sigmoid units, the output varies continuously but not linearly as the input

changes. Sigmoid units bear a greater resemblance to real neurons than linear or

threshold units, but all three must be considered rough approximations.

47

2.7.3 Training of Artificial Neural Networks

A neural network has to be configured such that the application of a set of

inputs produces (either 'direct' or via a relaxation process) the desired set of outputs.

Various methods to set the strengths of the connections exist. One way is to set the

weights explicitly, using a priori knowledge. Another way is to 'train' the neural network

by feeding it teaching patterns and letting it change its weights according to some

learning rule.

We can categorise the learning situations in two distinct sorts. These are:

Supervised learning or Associative learning (Figure 2.8) in which the network is trained

by providing it with input and matching output patterns. These input-output pairs can be

provided by an external teacher, or by the system which contains the neural network

(self-supervised).

Figure 2.8 Training of Neural Network with supervised learning algorithm

Unsupervised learning or Self-organisation in which an (output) unit is trained to

respond to clusters of pattern within the input. In this paradigm the system is supposed to

discover statistically salient features of the input population. Unlike the supervised

48

learning paradigm, there is no a priori set of categories into which the patterns are to be

classified; rather the system must develop its own representation of the input stimuli.

Reinforcement Learning is another type of learning may be considered as an

intermediate form of the above two types of learning. Here the learning machine does

some action on the environment and gets a feedback response from the environment. The

learning system grades its action good (rewarding) or bad (punishable) based on the

environmental response and accordingly adjusts its parameters. Generally, parameter

adjustment is continued until an equilibrium state occurs, following which there will be

no more changes in its parameters. The self organizing neural learning may be

categorized under this type of learning.

Once the relationship between the input pattern and prediction is “learned”, an

expert system might be constructed around the neural network to provide a frame work

for the rules necessary to deduce the final prediction from the “interpreted” pattern. For

example the output from a neural network is numerical, not textural. These numbers need

to be translated into ‘n’ predictions. The rule based expert system provides for

incorporation of the rules needed to interpret the numerical output so as to present the

final predictions in a readily usable form.

Learning during the training stage consists of modifying the values of the synaptic

weights between neurons in such a way that ANN’s output confirms to the targets

suggested by the specific problem. Learning rules are the algorithms according to which

ANNs are trained. Unless the correlation between input data and desired outputs is high,

ANN will not converge [13]. Combining ANN architectures with different learning

schemes, results in a variety of ANN systems.

The neural network model having the steps of database collection, training of the

neural network which includes the choice of architecture, training functions, training

algorithm and parameters of the network; testing of the trained network and using the

network for prediction.

49

2.8 Back propagation algorithm (BPA)

The standard back propagation algorithm is the most thoroughly investigated

Artificial Neural Network algorithm. The success of this algorithm is solving large scale

problems critically depends on user specified learning rate and momentum parameters

and, there are no standard guideline for choosing these parameters.

When the training pattern is given, the network produces some output based on

the current state of it’s synaptic weights. This output is compared to the known output,

and a mean squared error is calculated. The error value is then ‘back propagated’ through

the network and small changes are made to the weights in each layer. The weight

changes are calculated to reduce the error signal. The cycle is repeated until the desired

output is reached. The learning process, or training, forms the interconnection between

neurons and is accomplished by known inputs and outputs, and presenting these to the

ANN in some ordered manner. Due to the interconnection, signals are sent from the

input layer to the output layer through the hidden layer. The intensity of the transmitted

signal is determined by the weight of the interconnections. It is used to properly obtain

the model by iteratively adjusting the values of interconnections between the neurons

while the sum of squared residuals between calculated and expected values are

minimized [14, 15]. The BPA is a supervised learning algorithm that aims at reducing

overall system error to a minimum.

2.8.1 Derivation for Back Propagation Algorithm

1. Propagates inputs forward in the usual way

All outputs are computed using sigmoid there holding of the inner product of the

corresponding weight and input vectors.

All outputs at stage n are connected to all the inputs at stage n+1.

2. Propagates the errors backwards by apportioning them to each unit according to the

amount of error.

Let, xj = Input vector for unit j (xji = ith input to the jth unit)

wj =Weight vector for unit j (wji = weight on xji)

zj = wj .xj , the weighted sum of inputs for unit j.

50

oj = Output of unit j. [oj = (zj)]

tj = target for unit ]

Downstream (j) = set of units whose immediate inputs include the outputs of j.

Outputs = set of output units in the final year.

To update the output for each training, let us consider the error can be denoted by E.

Now we have to calculate the value of for each input weight wji regardless of

where in the network unit j is located

= .

= ji

Furthermore, is the same regardless of which input weight of unit j we are trying to

update so we denote this quantity by δj

Consider the case when j outputs.

We know

Since the outputs of all units k j are independent of wji, we can drop the summation and

consider just the contribution to E by j.

δ j = =

=

51

=

=

=

Thus,

Now consider the case when j is a hidden unit Like before, we make the following two

important observations.

1. For each unit K downstream from j, zK is a function of zj

2. The contribution to error by all units l in the same layer as j is independent of

wji

We want to calculate for each input weight wji for each hidden unit j. Note that

wji influences just zj which influences Oj which influences zk downstream (j)

each of which influence E. So we can write,

Again note that all the terms except in the above product are the same regardless of

which input weight of unit j we are trying to update.

Like before, we denote this common quantity by j . Also note that

, , .

52

Substituting,

Thus,

Formal statement of the algorithm:

Back propagation (training examples, ,ni, nn , no).

Each training example in of the form < x, t >where x is the target vector.

rate (e.g. 0.05) ni nh, no, are number of input, hidden and output

nodes respectively. Input from unit I to unit j is denoted xji and its weight is denoted by

wji

Create a network with ni inputs, nh hidden units, and no output units.

Initialize all the weights to small random values (e.g.9 between – 0.05 and 0.05).

Until termination condition is met, Do.

For each training example < x, t >, Do

1. Input the instance x and compute the output ou of every unit.

2. For each output unit k, calculate

3. For each hidden limit h. calculate

53

4. Update each network weight wji as follows:

2.9 Genetic Algorithm

Genetic algorithms (GAs) are search algorithms based on the mechanics of

natural selection and genetics as observed in the biological world [16]. They use both

direction (``survival of the fittest'') and randomisation to robustly explore a function.

Importantly, to implement a genetic algorithm it is not even necessary to know the form

of the function; just its output for a given set of inputs (Figure 2.9).

Once a neural network model has been created, it is frequently desirable to use

the model backwards and identify sets of input variables which result in a desired output

value. The large numbers of variables and non-linear nature of many materials models

can make finding an optimal set of input variables difficult.

Figure 2.9 Genetic algorithm with inputs and output

Evolution - using genetic algorithms

To start with, it is necessary to encode the parameter set for a model into a

chromosome, Xi. This is a way of expressing the information that allows for various

54

forms of mutation to occur in the parameter set, and consists of a set of genes, [xi1, xi2,

xi3, xi4, ...]. This set of genes, when given to the model as inputs, will give the output fi.

The chromosomes are then ranked according to a fitness factor, Fi, describing how well

they perform relative to expectation and each other. The chromosomes are then allowed

to breed (with likelihood proportional to fitness) and mutate. In practice, evolution occurs

in two ways - crossover and random variation [17, 18]. In this example, mutation would

be represented by flipping a randomly chosen bit. In a neural network optimisation GA,

mutation would involve a small variation - plus or minus - in a randomly chosen gene.

To summarise, the procedures are:

1. Convert the chromosomes to a set of neural network inputs by combining them

with the fixed inputs.

2. Make predictions on each set of inputs, and convert the predictions and

uncertainties to fitnesses.

3. Rank the chromosomes by fitness.

4. Preserve the best chromosome (elitism).

5. Create new chromosomes by uniform crossover.

6. Create one new chromosome at random (within appropriate limits for each gene).

7. Mutate one randomly chosen gene in the entire population by adding or

subtracting a small amount (1% of the training database range for that input). If

the mutation makes the gene non-physical (less than zero in this case), set it to a

default physical value (zero in this case).

8. Return to (1) with the new population.

This Genetic Algorithm is used for the selection of Input nodes to get the best

predicted output.

55

References

1. www.datasheet.com.

2. Dayhoff J., DeLeo J., Cancer Supplement, 91- 8 (2001), 1615-1635.

3. Nayak R., Jain L., Ting B., Proc. 1st Asian-Pacific Congr. Computational Mechanics,

(2001), 887-892.

4. Perantonis S.J., Ampazis N., Varoufakis S., Antoniou G., Neural Processing Lett.,

l.- 7(1998), 5–14.

5. Huang D.S., Ma S.D., J. Intelligent Syst., 9(1999), 1–38.

6. Murillo-Fuentes J.J., González-Serrano F.J., Proc. of the IEEE Int. Conf. on

Acoustics, Speech, and Signal Processing (ICASSP’99). V(1999), 2575-2578.

7. Carnimeo L., Proceedings of the 3rd WSEAS Int.Conf. on Neural Network and

Applications, (2002), 107-111.

8. Rowley H., Baluja S., Kanade T., IEEE Transactions on Pattern Analysis and Machine

Intelligence, 20-1(1998), 23 – 38.

9. Kinderman L., Lewandowski A., Protzel P., Proc. Neural Information Processing,

ICONIP’01, 2(2001), 1075–1078.

10. Huang D.S., IEEE Transactions on Neural Networks, 15-2(2004), 477 – 491.

11. Papadourakis G.M., Spanoudakis G., Gotsiass A., Proceedings of 1st International

Workshop Neural Networks in the Capital Markets, (1993).

12. Suen, J.P., Eheart J.W., Asce M., Journal of Wat. Res. Plan. And Man, 129(2003),

505-510.

13. Anderson D., McNeil G., Kaman Science Corporation, (1992).

14. Kartalopoulos, S.V, Understanding Neural Networks and Fuzzy Logic- Basic

Concepts and Applications, Prentice Hall, New Delhi, ( 2000).

15. Ramana K.V.S, Anitha T., Sumantra Mandal, Kaliappan S., Shaikh H., Sivaprasad

P.V., Dayal R.K., Khatak H.S., Materials and design, 30(2009), 3770-3775.

16. Goldberg D.E., Genetic algorithms in search, optimisation, and machine learning.

Addison Wesley, 1989.

56

17. Shah I., Tensile Properties of Austenitic Stainless Steel, I. Shah, M.Phil. Thesis,

University of Cambridge. (2002)

18. Delorme A., Genetic Algorithm for Optimization of Mechanical Properties,

Technical report, University of Cambridge.(2003)

57

CHAPTER III

MEASUREMENT AND ANALYSIS OF CHLORIDE IN BIOLOGICAL

SAMPLES

This chapter presents the basic principle, design and development of

microcontroller P89C668 based bio-analyser to measure Chloride concentration in human

urine samples. The performance of the developed instrument is investigated by analytical

parameters and the results obtained which includes high (hyperchloremia) and low urine

chloride (hypochloremia) is also discussed. This chapter also explains the measurement

of concentration of Chloride in pharmaceutical sample of Oral Rehydration Salts using

the microcontroller P89C51RD2 based Chloride analyzer. The results are verified with

the WHO (World Health Organisation) certified values and it is found that the values are

well agree with the charted values.

3.1 Renal Physiology

Urine is a liquid product of the body that is secreted by the kidneys by a process

called urination and excreted through the urethra. Cellular metabolism generates

numerous waste compounds, many rich in nitrogen that require elimination from the

bloodstream. This waste is eventually expelled from the body in a process known as

micturition, the primary method for excreting water-soluble chemicals from the body.

These chemicals can be detected and analysed by urinalysis. Amniotic fluid is closely

related to urine, and can be analyzed by amniocentesis. A typical nephron, the functional

unit of the kidney is composed of a capillary bed for filtration, called the glomerulus and

tubule segments located in the cortex and medulla of the kidney. Chloride is both actively

and passively transported in various segments of the tubules. The kidneys are responsible

for the maintenance of total body Chloride balance. Several studies have suggested that

the Chloride ion may play a more active and independent role in renal function,

neurophysiology and nutrition. Body Chloride concentrations are regulated by excretions,

primarily via the kidneys [1, 2]. Normal urine density or specific gravity values vary

between 1.003–1.035 (g cm−3) and any deviations may be associated with urinary

58

disorders [3]. The presence of specific clinical disorders can affect the ability of the

kidneys to maintain Chloride balance. The result is hyperchloremia or hypochloremia.

Colorimetry is one of the simplest and best techniques, which is widely used for

the clinical routine assays compare to that of other analytical methods. It requires the

maintenance, portable and allows on-site testing. The amount of sample required is small.

If a unit cell is utilized through which light is passed, it is generally simple, little in size

and low in cost. Sample testing in the laboratory can take minutes to hours for sample

preparation testing to be run, but colorimetry using hand-held devices can take minutes or

even seconds to run. Hence, an attempt is made to develop a simple, accurate and low

cost embedded based bio-medical analyser based on colorimetry principle.

3.1.1 Colorimetry principle

According to this principle, a colorimeter measures the intensity of light shining

through a coloured solution compared to the intensity of light passing into the solution.

A detector measures the transmittance (T) (% of light passing through) of the solution.

This is mathematically converted to absorbance (A= -log 10 T). The absorbance is

directly proportional to the concentration (Beer-Lambert law) [4, 5]. Beer’s law describes

that the plot of absorbance ‘A’ against concentration, a straight line passing through the

origin should be obtained. The presence of small amount of colorless electrolytes, which

do not react chemically with the colored components, normally does not affect the light

absorption.

3.1.2 Proportionality between color and concentration

For, colorimeters, it is important that color intensity should increase linearly with

concentration of the compound to be determined. This is not necessary for photoelectric

colorimeters or spectrophotometers. Since, a calibration curve may be constructed

relating the instrumental reading of the color with the concentration of the solution. It is

desirable that the system follows Beer’s law even when photoelectric colorimeters are

used.

59

3.1.3 Stability of the color and clarity of the solutions

The color produced must be stable so as to allow accurate readings to be taken.

The periods over which maximum absorbance remains constant must be long enough for

precise measurement to be made. The solution must be free from precipitate if

comparison is to be made with a clear standard. Turbidity scatters as well as absorbs the

light.

3.1.4 Analytical studies of the Instrument system

The following parameters are the important analytical factors to be considered for

the instrument analytical performance.

(i) Accuracy and precision

The accuracy and precision of colorimetric method instrument set up depends on

three major factors.

a) Instrumental limitations

b) Chemical variables

c) Operator’s skill

Instrumental limitations are often determined by the quality of the instruments,

optical, mechanical and electronic systems. Chemical variables are determined by purity

of standards, reagents and reaction rates. These factors are usually determined by the

methodology chosen for the analysis. Under ideal conditions it is possible to achieve

relative standard deviations in concentrations as low as about 0.5%, which enables the

determination of micro quantities of components.

The precision of colorimetric method also depends on concentration of the

determinant. Visual methods generally give results with a precision of 1-10%. The

precision of the method is of course, higher and varies from 0.5 – 2% under suitable

measuring conditions.

Precision describes the reproducibility of results where accuracy denotes the

nearness of a measurement to its accepted value. The precision attainable is a function of

the absorbance measured. The error observed is, as expected very large on lower side of

concentrations. When intensely colored solutions are measured, only an insignificant

part of the radiation is transmitted and on logarithmic absorbance scale the gradations are

so close that the reading error is very high.

60

Precision is conveniently expressed in terms of the average deviation from the

mean or in terms of standard deviation. The standard deviation is the most reliable

estimate of the indeterminate uncertainty. When the standard deviation turns out to be

approximately proportional to the amount present in the formation on the precision can

be expressed in percent by using the coefficient of variation. Mathematical equation for

the coefficient of variation is

C.V = S × 100 / x

Where s – standard deviation

x - Arithmetic mean of a series of measurement.

(ii) Detection Limit

Detection limit is the smallest concentration of a solution of an element that can

be detected with 95% certainty [6, 7]. This is the quantity of the element that gives a

reading equal to twice. The standard deviation of a series of any least ten determinations

taken with solutions of concentrations are close to the level of the blank. Several

approaches for determining the detection limit are possible, depending on whether the

procedure is a non – instrumental or instrumental. Based on the standard deviation of the

bland samples and the slope of the calibration curve of the analyte, the detection limit (D)

may be expressed as:

D = 3.3σ / S

Where σ – standard deviation of the reagent blank.

S- Slope of the calibration curve.

The slope S may be estimated from the calibration curve of the analyte. The estimate of

σ may be measured based on the standard deviation of the reagent blank.

(iii) Comparison of the Results

The comparison of the values obtained from a set of results with either a) the true

value or b) other sets of data makes it possible to determine whether the analytical

procedure has been accurate and / or precise, or if it is superior to another method. There

are two common methods for comparing results: i) t- Test [8, 9] and ii) the variance test

[F-test].

61

(a) t- Test: t- test is used to compare the mean from a sample with some standard values

and to express some level of confidence in the significance of the comparison [9]. It is

also used to test the difference between the means of the two sets of data.

(b) F- test: F – Test is used to compare the precisions of two sets of data of two different

analytical methods are calculated from the following equations [8, 9].

F= SA2 / SB

2

The larger value of S is always used as the numerator so that the value of F is

always greater than unity. The value obtained for F is then checked for its significance

against values in the F- table calculated from the F-distribution [8, 9] corresponding to

the numbers of degrees of freedom for the two sets of data

(iv) Linear regression analysis

Linear Regression Analysis attempts to model the relationship between two

variables by fitting a linear equation that closely fits a collection of data points. All the

points fall into the linear range, and there is sufficient precision in the data to continue

with the linearity study. There will be no outliner for the data sets. The strength of the

linear association between two variables is quantified by the correlation coefficient. The

regression line equation arrived is,

y - y = bxy ( x – x )

Where bxy = r (σx / σy ); x and y are data sets.

x and y are mean of the σx and σy are standard Deviation of the data sets.

(v) Recovery

Recovery is the test performed to check the reproducibility of the instrument. It is

performed by adding the known concentration solution with the known concentration

sample. The resultant concentration should be the addition of those two concentration

values.

(vi) Quantification limit

The quantification limit is generally determined by the analysis of samples with

known concentrations of analyte with those of blank samples and by establishing the

minimum level at which the analyte can be quantified with acceptable accuracy and

precision [10, 11]. Based on the standard deviation of the blank samples and the slope of

the calibration curve of the analyte, the quantification limit (QL) may be expressed as:

62

QL = 10 σ / S

Where σ – the standard deviation of the reagent blank

S – the slope of the calibration curve.

The slope S may be estimated from the calibration curve of the analyte. The estimate of

σ may be measured based on the standard deviation of the reagent blank.

3.2 Measurement of Chloride in human urine using Microcontroller P89C668

3.2.1 System Architecture

The functional block diagram of Microcontroller based Instrument set up to

measure and analyse urinary Chloride with different blocks is shown in figure 3.1. Light

Emitting Diodes (LEDs) as quasi monochromatic light source have been used for

absorbance measurements. Block 1 represents Green LED, which acts as an illumination

source with a dominant wavelength of 480nm. It optically illuminates the sample solution

to measure the Chloride concentration. The photo detection assembly is well insulated

from outer light. Block 2 indicates the sample holder to hold the solutions of blank,

standard, and sample solution tube with a diameter of 1cm. Block 3 is a Photo Diode

GASPG1124 used to detect the amount of light falling on the sample, which acts as a

photo detector. This ideal detector has the characteristics of long term stability, short

response and high sensitivity to allow the detection of low level radiant energy [12]. The

output signals are fed to op-amp LM108 which is kept in Block 4. The LM108 is a

precision operational amplifier from National semiconductor having maximum input bias

current of 3.0 nA, Offset current less than 400 pA and supply current of only 300 μA.

The temperature sensor LM35D kept in Block 5 is a precision semiconductor temperature

sensor giving an output of 10mV per degree centigrade. It is capable of measuring

temperature between +2°C and +100°C. The output is proportional to degree centigrade.

It has low current drain and low self-heating. Block 6 indicates the multiplexer CD4051

to receive the signals from the op-amp and the temperature sensor. Block 7 is heater

controller to control and maintain temperature at 37°C for the incubation of sample. ADC

MCP3201 is represented by the Block 8 to convert Analog to Digital values [13]. IC

MCP3201 is a successive approximation type 12 bit serial A/D converter compatible with

the SPI protocol, sample rate of 100ksps at clock rate of 1.6 MHz and operates over

63

broad voltage range of 2.7-5.5 V. The Microcontroller P89C668, which is kept in Block

9, reads data from ADC for processing. Block 10 represents the keypad to give data for

processing and to compute the Chloride concentration. Block 11 is LCD, used to display

the output of microcontroller (Chloride concentration in Urine samples) [14]. The data

are transmitted from the microcontroller to the computer represented by Block 13 via

RS232 denoted by Block 12.

3.2.2 Instrumental

The microcontroller P89C668 and interfacing circuit to measure urinary Chloride

is shown in figure 3.3. Signal conditioning circuit which is used to isolate, convert and to

amplify the transducer signals is shown in figure 3.2. The photo diode used as a sensor is

connected to the input of op-amp LM108 to measure the amount of light absorbed by the

sample. The current output signal from the photo diode is converted to voltage. The

voltage output of op-amp is connected to the pin 13 of multiplexer CD4051. The

temperature sensor LM35D used to measure the temperature of the sample is connected

to the pin 14 of CD4051 (figure 3.2). The multiplexer (pin 3) is connected to pin 2 of

ADC MCP3201, to convert analog signals to 12 bit digital value. The pin 10 (A) and 11

(B) of multiplexer are connected to pin 18 (P2.0) and 19 (P2.1) of Microcontroller

P89C668 to select either temperature or absorbance of solution. The ADC is interfaced

with pin 42, 43, 44 of Microcontroller P89C668 to convert analog voltage into

corresponding digital values for processing and to compute urinary Chloride

concentration. The heater controller circuit is connected to pin 23 (P2.5) of

microcontroller and it is implemented with opto isolator (IC MOC3041), Triac

(GDA40AT6), to control and maintain the Temperature of sample at 37ºC. A special zero

crossing detector circuit in the optocoupler ensures that the connected triac is only

triggered when the alternating mains voltage goes through zero. During zero crossing

time, commands are given to the heater circuit to switch on/off. Hence, the desired

temperature is achieved. The opto isolator IC MOC3041 (Global suppliers of opto

electronic solutions) has a reverse leakage current of 10 μA, forward voltage of 1.5v and

LED triggering current of 30mA. The triac BTA126 has on-state RMS current of 40

amps and storage temperature range of -40 to 125 ºC. A keypad is interfaced with Port2

64

of the microcontroller as shown in figure 3.3. The LCD is interfaced to display the

results. The data lines (D7 to D0), RS (Register Select) and EN (Enable) of LCD are

connected with Port 0 and Port 3 of microcontroller as shown in figure 3.3. Data from

microcontroller is transferred to PC for further processing through the TXD and RXD

lines of the microcontroller by interfacing RS232 peripheral to achieve the necessary

level shifting for communication between PC and microcontroller. After the power on

reset the program will be executed from memory address 0000 onwards. A 24C16

EEPROM (Electrically Erasable Programmable Read Only Memory) of 16k bit is

interfaced with microcontroller to store the patient i.d and test result (Chloride

concentration). The 24C16 features a low power standby mode which is enabled, upon

power-up and after the receipt of the STOP bit and the completion of any internal

operations. It is a low cost and low voltage 2 wire serial EEPROM. The SCL (Serial

Clock Line) is connected to pin 2 and the SDA (Serial Data Line) is connected to pin 3 of

the microcontroller so that the data can be transmitted and received.

3.2.3 Software

Using C language, software is developed to configure the serial and parallel port to

read data from keyboard, to initialize LCD, to initialize timer1 interrupt, to initialize

enable interrupt, to select light intensity or temperature using multiplexer, to start A/D

conversion, to receive 12 bit data from A/D converter for temperature and light intensity,

to measure and control the temperature for incubation, to measure the voltages for blank,

standard, and sample solutions, to compute absorbance and hence concentration, to store

the data, and to display user information and the results (Keil software is used for the

development of programs). The flowchart for performing the above tasks is shown in

figure 3.4.

3.3 Materials and Method

Samples are collected from the patients whose urinary Chloride has to be

measured. Urine specimen is collected in a container without preservative. The samples

are maintained at 37°C temperature. The solution of blank, standard and sample are

prepared to measure the concentration of electrolyte.

65

3.3.1 Principle of color complex

Chloride is mixed with a solution of undissociated mercuric thiocyanate, the

Chloride preferentially combines with the mercury to form mercuric Chloride. The

thiocyanate that is released combines with ferric ions present in the reagent to form ferric

thiocyanate, which can be measured spectrophotometrically. The mercuric nitrate binds a

fixed amount of Chloride ion and therefore makes them unavailable for reaction with

mercuric thiocyanate. Only the Chloride present in excess of that bound by the mercury

from mercuric nitrate is reacted with mercuric thiocyanate and produced a color complex

(red ferric thiocyanate) that absorbs light at 480 nm. According to Beer-Lambert’s law,

the intensity of the color produced is directly proportional to the Chloride concentration.

[15].

2Cl- + Hg(SCN)2 HgCl2 + 2SCN- (1)

3SCN- +Fe +++ 4Fe (SCN)++ + (2)

3.3.2 Reagents

Two reagents R1 and R2 are used in this method. The reagent R1 consists of

mercuric thiocyanate (2m mol/l), ferric nitrate (20m mol/l) and nitric acid (29m mol/l).

The reagent R2 is Chloride standard solution [16, 17]. All the solutions are prepared in a

well cleaned dried test tube of same diameter. Blank solution is prepared by mixing 1 ml

of reagent R1 with 10 µl of distilled water. To prepare standard, 1 ml of reagent R1 is

added with 10 µl of standard (R2). For sample preparation, 1 ml of reagent R1 is added

with 10 µl of urine sample. The above solutions are thoroughly mixed and left for

incubation for 5 min at 37 ° C, before the absorbance is measured at 480nm.

3.3.3 Measurement

The test tube labeled blank is placed in a sample holder and the measured voltage

is noted as Vo. By holding the standard solution test tube in a sample holder, the voltage

Vstd is taken. To find the absorbance of sample solution, the sample solution is placed in

a sample holder and voltage measured is noted as Vt. The concentration of urinary

Chloride is determined using the formula,

Concentration of Chloride ion = log (Vo/Vt) / log (Vo/Vstd) x 100 (3)

66

Where, log (Vo/Vt) = Absorbance of sample, log (Vo/Vstd) =Absorbance of standard

100 is the concentration of standard Chloride.

The concentrations of urinary Chloride measurements are made for 40 urine

samples using the developed instrument. The same urine samples are tested using the

commercial clinical analyser. The absorbance of sample solution is measured and

repeated for five times to check the reproducibility.

3.4 Results and Discussion

The performance of the Microcontroller P89C668 based electrolyte bio-analyser

using colorimetry principle is investigated by comparing its results with the results

obtained by other clinical analyser (ST 100 analyser) which is given in table 3.1. It can

be seen that there is no obvious difference between the results obtained by two analysers.

3.4.1 Clinical Significance

The normal range of urinary excretion is 20 to 250 milliequivalents per day

(mEq/day). [18]. From table 3.1, it is observed that for patient i.d No, 20, 35 and 39, they

are suffered by hyperchloremia (Increased Chloride levels). This is because of

adrenocortical insufficiency, increased salt intake, inflammation of the kidney that results

in salt loss and Production of an unusually large amount of urine. It is evident that they

are suffered by vomiting (or nasogastric suction), diuretic therapy, or diarrhea due to a

villous adenoma. In this setting, the most likely diagnosis is surreptitious vomiting or

diuretic therapy or one of the causes of mineralocorticoid excess (such as primary

hyperaldosteronism) [19]. The first two disorders induce effective volume depletion,

whereas hyperaldosteronism is usually associated with mild volume expansion due to the

stimulatory effect of aldosterone on sodium reabsorption. It is noted that the drugs that

increases the level of Chloride in the urine are corticosteroids and diuretics (patient i.d

20). It is observed that there are no patients suffered from hypochloremia and it may due

to that the people are taking food regularly with adequate amount of Chloride in their

(NaCl – table salt) daily diet.

67

3.4.2 Statistical Analysis

Statistical analysis is carried out for the results obtained from the developed

instrument to check the accuracy of the instrument. The table 3.2 represents the statistical

reports for the developed instrument and the commercial clinical analyser. It is noted that

the values of standard deviation, mean value, median value, mean dev, Co-efficient of

variation and standard error of Co-efficient of variation for the designed analyser is close

to the clinical analyser. The less residual between the two analysers confirms the

accuracy of the microcontroller based instrumentation set up.

3.4.3 Detection and quantification limits

The detection and quantification limits are calculated as sb + 3s, where sb is the

average signal of blank solutions and s is the standard deviation. For the wavelength of

480nm, the absorbance change of 0.1119 typically corresponds to Chloride concentration

of 30 m mol/l of the sample solution, which gave the sensitivity of the electrolyte bio-

analyser. As the absorbance increases the Chloride concentration also increases, which

shows the linearity of the instrument up to 300 m mol/l.

3.4.4 Precision

To determine the reproducibility and accuracy of the instrument run to run and

within run tests are investigated. Run-to-run precision is obtained by assaying

commercial human control serum AccutrolTM Normal (Sigma – certified value – 102

mmol/l) gave the results of Mean 104.4, S.D. 4.0, C.V (%) 3.3 and elevated results for a

period of thirty (30) days produced the results of Mean 91.7, S.D.3.8, C.V(%)4.1. Within

run precision is obtained by assaying control normal serum twenty (20) times having

Mean 86.9 (104.4), S.D. 1.3 (4.0), C.V. (%) 1.0(3.3).

3.4.5 Recovery

To determine the feasibility of the developed instrument recovery test is

performed in pooled serum by the addition of known amount of Sodium Chloride

solution. Recovery of Chloride added to pool human urine is given in table 3.3. Pooled

urine is diluted approximately two-fold with distilled water. To 0.5ml of diluted urine,

various amounts of 0.1N Sodium Chloride (NaCl) solutions are added to bring the total

Chloride concentration within normal range. Using the developed instrument the

68

recovery values of added Chloride ranged from 98.1% to 99.3% with an average recovery

of 98.65%, which indicates the suitability of the designed instrument for biomedical tests.

3.4.6 Linear regression analysis

Linear regression analysis attempts to model the relationship between two

variables by fitting a linear equation that closely fits a collection of data points. Figure

3.5 shows a linear regression between the designed electrolyte bio-analyser and the

commercial clinical analyser which is used to determine the correlation between the two

instruments. The value of slope 0.97 and the intercept 5.2 (close to ideality) indicated

that the developed instrumentation system is well correlated with the clinical analyzer.

The correlation coefficient between the two method is R=0.99. The implemented

instrument is well suited to determine the concentration of Chloride in urine sample.

69

Table 3.1

Urinary Chloride Concentration (m mol/day)

S.No of

patients

By

developed

instrument

By

clinical

analyzer

S.No of

patients

By developed

instrument

By clinical

analyser

1

2

3

4

5

6

7

8

9

10

11

12

13

14

15

16

17

18

19

20

102.79

106.55

96.85

82.99

108.58

111.15

120.43

150.12

92.81

130.86

180.14

120.52

200.11

104.09

98.71

182.35

123.53

156.18

230.28

260.92

105

103

101

92

110

120

128

162

102

142

193

134

194

110

92

176

133

142

225

258

21

22

23

24

25

26

27

28

29

30

31

32

33

34

35

36

37

38

39

40

89.42

156.62

186.87

96.23

145.78

210.45

232.98

88.32

154.84

190.17

100.74

98.15

101.36

115.64

290.85

210.92

84.74

168.12

301.56

142.28

95

144

190

95

140

218

225

85

158

182

93

105

108

111

292

202

78

172

305

152

70

Table 3.2

Statistical Reports for the two analysers

Variable Mean Value

Median Value

Mean Deviation

Coeff of Variance

SE of Coeff of Variation

Sample Std Deviation

Developed Instrument Clinical analyzer

145.75 149.05

127.19

137

44.28 45.46

37.47 37.53

4.18 4.19

54.61 55.94

Table 3.3

Recovery of added Chloride from pooled urine Chloride (mmol/day)

S.No In pooled

Serum

Added Total

Content

Total

Determined

Difference Recovery %

1. 82 40 122 120 2.0 98.3

2. 86 45 131 130 1.0 99.2

3. 90 50 140 138 2.0 98.5

4. 96 55 151 150 1.0 99.3

5. 104 55 159 156 3.0 98.1

71

Figure 3.1 Block diagram of Microcontroller P89C668 based Bio-analyser

72

Figure 3.2 Signal conditioning circuit of the developed Bio-analyser

73

Figure 3.3 Microcontroller and interfacing circuit for the developed Bio-analyser

74

Figure 3.4 Flow chart

75

Figure 3.5 Linear regression between the Microcontroller P89C668 based developed

instrument and clinical analyser

76

3.5 Analysis of Chloride in pharmaceutical sample- Oral Rehydration Salts

3.5.1 Introduction

The human body needs various kinds of salts to be healthy and to function

normally. Serious salt imbalances occur with dehydration, may lead to heart and nervous

system problems that, unless they are rapidly resolved, can result in a medical

emergency. Dehydration is a major cause of electrolyte imbalance in human beings

which occurs whenever water is lost from the body. When fluids are lost, electrolytes in

those fluids are lost too, increasing the risk of electrolyte imbalance. Dehydration can be

caused by heavy exercise, especially in hot weather, severe vomiting and diarrhea. Large

amounts of water and many electrolytes that would normally be absorbed in the intestines

are lost with diarrhea and vomiting. Dehydration is a real threat to children, especially

infants and toddlers. Small children with diarrhea can become seriously dehydrated in

less than one day. Infants can become dehydrated within hours, and Severe burns. Parents

should be alert to dehydration caused by illness or athletic activity and begin oral fluid

and electrolyte replacement therapy immediately. Athletes and trainers know that the

body loses salt through sweat and that it's important to replace it. Hence, many athletes

drink sports drinks that contain salts before, during and after exercise to minimize things

like muscle cramps that are associated with salt imbalance.

3.5.2 Electrolyte supplements

Most people get all the electrolytes from a normal diet. Short-term therapy often

quickly restores electrolyte balances. Persons suffering from dehydration are recovered

by the electrolyte replacement supplements by prescription which can be given by mouth

or intravenously under supervision of a physician [21, 22, 23, 24].

The Dietary supplements are popular among athletes who participate in endurance

sports which can be in the form of tablets and powders. Some also contain herbs and

flavorings. They are regulated by the United States Food and Drug Administration (FDA)

as dietary supplements. Electrolyte replacements for children are Pedialyte, Naturalyte, or

77

Rehydralyte and are available in supermarkets and pharmacies. Children should not be

given sports drinks for vomiting and diarrhea.

Medicinal rehydration sachets and drinks are available to replace the key

electrolyte ions lost during diarrhea and other gastro-intestinal distresses. The science of

Oral Rehydration Salts (ORS) is advanced when Phillips and colleagues determined the

composition of fluid lost in diarrhea [24, 25]. Oral rehydration therapy is proposed as a

viable alternative for cholera in areas of the world with short supplies of intra-venous

fluids and needles forcing clinicians to deliver oral solutions to those with cholera. This

reduced mortality rates to only 3% compared to 30% of those treated in other camps with

intravenous fluids. Based on this evidence, WHO and UNICEF recommended a single

standard ORS formula for all ages. There are lot of brands of ORS therapy is available in

local pharmacy. The accurate analysis of minerals in drugs is very important in

medications.

Hence, a study is undertaken to analyse Chloride in ORS therapy using a

Microcontroller P89C51RD2 and the results are compared with the other analytical

technique (Ion Selective Electrode method).

3.6 Instrumental

3.6.1 Description of the Microcontroller based system

The Microcontroller P89C51RD2 and interfacing circuit is shown in figure 3.6.

The output signals from photodiode are connected to the input of op-amp LM108 (Figure

3.2) for current to voltage conversion and for amplification. The output of op-amp is

connected to the pin 35 of ADC 7109 through 1 MΩ resistance to convert analog to

digital value. ADC 7109 is a low power integrated device providing high accuracy, low

drift and dual slope integrator with 12 bits parallel outputs. The lower and higher bytes

of ADC 7109 are interfaced with port 2 and Port 0 of Microcontroller P89C51RD2 as

shown in figure for computing Chloride concentration. LBEN and HBEN which are used

to select lower and higher byte are connected to pin 36 and 37 of microcontroller. The

RUN and STATUS pins of ADC are connected to 38 and 39 of microcontroller. The pin

29 of ADC 7109 generates the internal reference voltage. A tap from preset is given to

78

pin 36 of ADC 7109, the reference input pin. By adjusting this preset it is possible to get

a full scale, which means that inputs between –4 and +4 can be converted. A reset switch

is provided at pin 9 of the microcontroller, so that the program can be executed from

0000 after the power is switched on. A two row Alphanumeric LCD is interfaced to Port

1 to display the measured concentration of Chloride.

3.6.2 Software

Fully dedicated Software for the data acquisition and computing the Chloride

concentration in different ORS samples is developed in C and assembly language and

linked to the application program. The structure of the software is elaborated as

flowchart in figure 3.7. Software for the implemented system is written to initialize LCD,

to start ADC (Analog to Digital conversion), to check EOC (End of Conversion) to read

lower byte enabling LBEN signal, to read higher byte enabling HBEN signal, to measure

the readings for blank, standard, and sample, to compute absorbance and Chloride

concentration, to display the result in the LCD and to get data from the keyboard.

3.7 Materials and Method

Oral Rehydration Salts of six different brands are collected from local

pharmaceuticals in Thanjavur, Tamil Nadu, South India. The samples of ORS are

dissolved in 1L of deionized water without any precipitation. The colorimetry principle is

used for the measurement of absorbance and concentration of Chloride electrolyte

The principle and the reagent used to measure Chloride in ORS are same as 3.3.1

and 3.3.2. The sample is prepared by adding 1 ml of reagent R1 with 10 µl of prepared

ORS sample.

3.7.1 Measurement

The prepared solutions of blank, standard and sample are placed in sample holder

to measure the voltages of blank, standard and sample. The absorbance and hence

Chloride concentration is determined using the formula (3) in 3.3.3. The concentration of

Chloride for six different brands of ORS samples is made using the developed

instrument. The same samples are tested using the Chloride Ion Selective Electrode

(ISE). The absorbance of sample solution is measured and repeated for five times to

check the reproducibility.

79

3.8 Results and Discussion

The Microcontroller P89C51RD2 based Instrument set up to measure the

concentration by colorimetry method in ORS samples is designed and developed. The

table 3.4 shows the readings for blank and standard of Chloride reagent. The measured

readings of absorbance and concentration of Chloride in different ORS samples are given

in table 3.5. The table 3.6 gives the concentration of Chloride measured using the

developed instrument and ISE method in different ORS samples. The concentration of

Chloride is varied from (61.87-64 mmol/l). The certified concentration of Chloride in

ORS is 65mmol/l [26]. It is found that the range is well within the safe limits and also it

is observed that there is no significant difference between the concentration values of

different samples, which depicts that they are prepared by following the ORS formula

given by W.H.O. The people who have suffered by dehydration having symptoms like

dry mouth, loss of body weight greater than 10%, extreme thirst, sunken eyes, no tears

when crying, decreased urination, fussiness, weakness, skin that stayed compressed and

pinched should have the habit of in taking ORS to avoid some chronic condition. The

dosage of ORS depends on age and severity of dehydration. The dosage for infants and

children is 1-2 litres over a period of 24 hours. For adults it differs from 2-4 litres over a

period of 24 hours.

3.8.1 Linearity and Sensitivity

As the absorbance increases the Chloride concentration also increases, which

shows the good fit of colorimetry principle. To check the linearity of the developed

instrument set up various samples having different Chloride concentration have been

measured at the wavelength of 480nm. The absorbance change of 0.1 typically

corresponds to Chloride concentration of 42 m mol/l of the sample solution, which gave

the sensitivity of the developed Instrument.

3.8.2 Recovery

To test the feasibility of the procedure and instrument, the recovery of the

developed Instrument is studied by the standard addition method. To 0.5ml of ORS

sample, various amounts of 0.1N Sodium Chloride (NaCl) solutions are added to bring

the total Chloride concentration within normal range. The table 3.7 shows the recovery

80

values of added Chloride ranged from 98.13% to 99.15% with an average recovery of

98.42%, which indicates the suitability of the designed instrument for bulk drugs and

assay tests.

3.8.3 Linear regression analysis

Linear regression is plotted for the results obtained using designed Instrument and

the ISE method which is shown in figure 3.8. The strength of the linear association

between two variables is quantified by the correlation coefficient. The regression line

equation arrived is y = 0.92X+4.43, the value of slope and the intercept indicated that

the developed instrumentation system is well suited to determine the Chloride in ORS

samples. The correlation coefficient R=0.99 (n=6), shows that the designed instrument

is well correlated with the Chloride ISE method.

3.8.4 Statistical Analysis

The statistical reports of Chloride electrolyte in different brands of ORS samples is

given in table 3.8. It is noted from the table that the mean value 63.30 and median value

63.43 are also within the safe limits. The data reported in this study refers that the

concentration levels of electrolytes are fairly within the recommended levels, which

confirms the pharmaceutical integrity. There is no considerable difference between the

results obtained (Mean value, Std Err of Mean value, Median value, Std Err of Median

value, S.D, Std Err of S.D, Mean Deviation, Coefficient of Variation, Std Err of Coeff of

Variation) using the designed instrument and the ISE method which corroborates the

validity of the implemented instrument set up. The accuracy of the microcontroller based

instrument is confirmed by the less residual between the two methods.

81

Table 3.4

Voltage of blank and standard

S.No Blank Vo (mV) Standard (mV) 1

0.22

0.32

Table 3.5

Absorbance and concentration of Chloride in Oral Rehydration Powder

S.No Types of

sample Sample

(VT) Absorbance Chloride

Concentration m mol/l

1 ORS 1 0.175 0.099 61.87 2 ORS 2 0.174 0.101 63.12 3 ORS 3 0.174 0.101 63.12 4 ORS 4 0.173 0.104 64 5 ORS 5 0.173 0.104 64 6 ORS 5 0.175 0.099 61.8

82

Table 3.6

Comparison of results obtained using the developed instrument and Chloride ISE

Table 3.7

Recovery of added Chloride from ORS Chloride (mmol/l)

S.No In ORS sample

Added Total

Content

Total

DeterminedDifference

Recover %

1. 62 40 102 100.5 1.5 98.52

2. 62 45 107 105 2.0 98.13

3. 63 50 113 111 2.0 98.23

4. 63 55 118 117 1.0 99.15

5. 63 45 108 107 1.0 98.07

Chloride concentration (m mol/l) Sample id Developed

Instrument Chloride ISE

ORS 1 61.87 62 ORS 2 63.12 63 ORS 3 63.12 63 ORS 4 64 64 ORS 5 64 64 ORS 6 61.87 63

83

Table 3.8

Statistical analysis for the data arrived using developed instrument and the ISE

Variables Developed Instrument Chloride ISE

Mean 62.99 63.16

Std err of mean 0.356 0.280

Median 63.12 63

Std err of median 0.445 0.350

S.D 0.873 0.687

Std err of S.D 0.252 0.187

Mean deviation 0.751 0.555

Coefficient of variation 1.38 1.08

S.E of Coeff of Variation 0.400 0.314

84

Figure 3.6 Microcontroller P89C51RD2 and interfacing circuit

85

Figure 3.7 Flow chart

86

Figure 3.8 Linear regression between the developed instrument and the Chloride

Ion Selective Electrode

87

References

1. Weast R.C., 3 ed: CRC handbook of Chemistry and Physics 67th ed Boca Raton

FL CRC press (1986).

2. Kuleita T.A., Pediatrics, 78(1986), 714-5.

3. Narins R.G., Emmett M., Medicine., 50(1980), 161–87.

4. Wolfbeis O.S., Fiber Optic Chemical Sensors and Biosensors Analytical Chemistry,

72(2000), 81-89.

5. Rakow N.A., Suslick K.S.A., Nature, 406(2000), 710-712.

6. Green J.M., Anal.Chem., News& features, (1996), 305.

7. Renger B., Jehle H., FisherM., Funk W., J.Planar Chrom., (1995), 269.

8. Skoog D.A., West D.M., Holler F.J., Fundamentals of Analytical chemistry,

Saunders college publishing, Philadelph1ia, 7th Edn., (1996).

9. Jeffery G.H., Bassett J., Mehdham J., Denney R.C., Vogel’s Text book of

quantitative chemical analysis, 6th Edn., (2000).

10. Vessman J, J. Pharm. Biomed. Anal., 14(1996), 867.

11. Marr D., Horvoth P., Clark B.J., Fell A.F., Anal Proceed., 23(1986), 254.

12. Cooper W.D., Electronic Instrumentation and Measurement techniques, Practice hall

of India private Ltd, New Delhi.(1987).

13. Wobschall D., In Circuit design for Electronic Instrumentation -Analog and Digital

devices from sensor to display, Second edition, McGraw-Hill Book Company, NY,

(1987), 367-368.

14. Morvis Alan S., Principles of Measurement and Instrumentation, New York. (1988).

15. De Jong E.B., Goldschmidt H.M., Van Alphen A.C. , Loog J.A., Clin Chem, 26-8

(1980),1233-1234.

16. Yokoi K., Biol Trace Elem Res., 85-1(2002), 87-94.

17. Feldkamp, J Chem Clin Biochem., 12(1974), 146-150.

18. Bishop M. L., Clinical Chemistry: Principles, Procedures, Correlations

(4th ed.). Philadelphia, PA: Lippincott Williams & Wilkins. (2000).

19. Rose B.D., Post T.W., Clinical Physiology of Acid-Base and Electrolyte Disorders,

5th ed, McGraw-Hill, New York, (2001), 565-567.

20. Kotchen T., Hypertension, 45(2005), 849–850.

88

21. Armon K., Stephenson T., MacFaul R., Arch Dis Child., 85(2001), 132-142.

22. Lieberman S., Bruning N., The Real Vitamin & Mineral Book, Avery Publishing,

Garden City, NY, (1990), 91-181.

23. Harrison H.E., Pediatr Clin North Am, 1(1954),335-348.

24. Phillips R.A., Ann Rev Med, 19(1968),69-80.

25. Hirschhorn N., Greenough W.B., III., Cholera. Sci Amer., 225(1971),15-21.

26. World Health Organization. Oral Rehydration Salts (ORS), A new reduced

Osmolarity formulation (Version current at September 12 (2006)).

119

CHAPTER V

ELECTRICAL CONDUCTIVITY AS A SURROGATE FOR CHLORIDE

DETERMINATION

This chapter presents the design and development of Microcontroller

ATmega32 based Instrument set up to determine the Electrical Conductivity in soil

samples. The Electrical Conductivity of the soil samples measured by the implemented

embedded based Electrical Conductivity instrument is comparable with that of the

commercial instrument (ELICO CM 180). Since, Electrical Conductivity can be used as

a surrogate for Chloride concentration measurement, a linear regression model is

developed between Electrical Conductivity and Chloride concentration of soil samples.

The Chloride concentration of the soil samples collected at various samples and their

plant cultivation is also discussed.

5.1 Introduction

Electrical conductivity is an inherent property of most materials, and ranges from

extremely conductive materials like metals to very non-conductive materials like plastics

or glass. In metals, the electrical current is carried by electrons, while in water it is

carried by charged ions. In both cases, the conductivity is determined by the number of

charge carriers, how fast they move and how much charge each one carries. Conductivity

(G), the inverse of resistivity (R) is determined from the voltage and current values

according to Ohm's law. Using Ohm’s Law, V= iR and knowing conductivity G=

(1/R)*k, where k=cell constant =length (d, spacing between two electrodes)/area of

electrodes then G can be determined as G= (1/R)*k = (i/V)*k. When resistance is

measured in ohms, conductance is measured in siemens (formerly known as a mho).

Since 1 siemens is a very large unit, aqueous samples are commonly measured in micro

siemens μS. Metals are extremely conductive because electrons move almost with the

speed of light, while in water ions move much slower and the conductivity is much

lower. Raising the temperature makes water less viscous and the ions can move faster.

Because the ions are of different sizes and carry different amounts of water with them as

they move, the temperature effect is different for each ion.

120

5.1.1 Electrical Conductivity as a surrogate for Chloride concentration

Electrical Conductivity (EC) is usually a representation of salinity and it can

be measured with a simple device. Chloride ion is an important element among dissolved

solids which can limit plant growth, decrease yields and reduce quality of drinking water.

Chloride is highly soluble and remains in the soil solution, while other ions such as

sulphate and bicarbonate combine with calcium and magnesium, are present, to form

calcium sulphate and calcium carbonate, which are sparingly soluble compounds.

Chloride concentration typically is measured by titration of aqueous samples using

standard AgNO3

solution. Chloride analysis thus is time consuming and expensive,

compared to EC measurement which is fast and inexpensive (Hajrasuliha, S et al) [1].

Since Chloride is a major constitute of saline waters and soils and it directly affects EC, a

close correlation between EC and Chloride can be obtained. Maas et al., [2] suggested

that if Chloride is the predominant anion in a soil solution, the Chloride concentration in

molm-3

would be approximately equal to 10 times the EC

measured in dSm-1

.

Observations of Chloride concentration and Electrical Conductivity delivered the

possibility of a generelised empirical relationship between these two factors. Therefore it

is conceivable that the Chloride concentration can simply be estimated from Electrical

Conductivity measurement. The concept of computation of Chloride concentration is, to

correlate Electrical Conductivity with the Chloride Concentration of the soil samples

using regression model, which validates Electrical Conductivity as a surrogate for

Chloride estimation.

5.2 Agricultural soil

All soils contain some water soluble salts which include essential nutrients for

plant growth. When the level of water soluble salts exceeds a certain level, harmful

effects on plant growth occur. A soil with excess total soluble salts is referred to as a

saline soil. The influence that a certain level of soluble salt will have on crop growth

depends upon several factors such as climatic condition, soil texture, distribution of salt

in the profile, salt composition and plant species ( Milne, R.A et al) [3]. The areal extent

and depth of a salt problem is usually irregular. Soil sampling on a grid system may be

necessary to map the extent of the problem. Soluble salts are most commonly detected by

measuring the soil solution’s ability to conduct an electric current, referred to as

121

Electrical Conductivity. The common unit of measurement for EC has been mmhos/cm.

The official international unit of measurement is siemen/ m (S/m). One mmhos/cm is

equal to 0.1S/m or 1.0 ds/m.

5.3 Design and development of Electrical Conductivity measurement set up using

Microcontroller Atmega32

Soil Chloride analysis has been conducted primarily for the purpose of salinity

and irrigation management. Presently, it has become highly advantageous to carry out

information processing and control using microcontroller. It is also a well known fact that

the microcontroller system can offer high accuracy and high speed response. Hence, these

reasons infuse a strong motivation for the design and implementation of the automatic

measurement system based on microcontroller. An embedded systems controlled by

microcontrollers consist of not only a digital part, used for control and data processing,

but also an analog part mostly used for adjustment of input signals e.g. from sensors. In

this experimental study, to decrease the test cost, it is proposed to use ATmega32

microcontroller mounted in the system and the developed system is used for in-situ

measurement of the conductivity.

5.3.1 Design of the measurement system

The block diagram of microcontroller based Electrical Conductivity measurement

set up is shown in figure 5.1. The conductivity cell made up of platinum which is used to

measure the conductivity of the samples is kept in Block 1. The cell constant (K) is

related to the physical characteristics of the measuring cell. K is defined for two flat,

parallel measuring electrodes as the electrode separation distance (d) divided by the

electrode area (A). Thus, for a 1 cm cube of liquid, K = d/A = 1 cm–1. Its determination is

much more convenient by calibration with pattern solutions (Braunstein et al.,) [4].

Polarizing the conductance cell by an external DC potential VDC produces some

undesirable effects (double-layer capacitance, electrolysis, ohmic resistance and

electrolytic saturation). On the other hand, it is proved that the electrolytic saturation is

reduced considerably if the AC polarization frequency is high enough. Hence, a fixed

sinusoidal excitation voltage of 1V is applied to the bridge. The Conductivity cell is

connected to one arm of a modified Wheatstone’s bridge network. The Block 2 consists

of precision rectifier to rectify the output of Bridge network. Block 3 represents the

122

temperature sensor Chromel alumel thermocouple to measure the temperature of the

sample. The effect of temperature is important when an electric conductivity of a liquid

or solution must be done. A solution at a higher temperature will present higher quantity

of ions dissociated, therefore the concentration of electric charges will raise and as a

consequence, conductivity will be higher. On the contrary, the same solution at low

temperature will have a low conductivity due to the low quantity of ions present, which

results in lower electric conductivity. From an application point of view, conductivity is

given at a certain temperature, which has been stated as a reference to better compare the

measurements at different times and locations. This temperature is usually 25°C. Block 4

indicates keypad to give input data to the Microcontroller for processing. Block 5 consists

of ATmega32 microcontroller from Atmel company, is a low power, high performance 8

bit AVR microcontroller. Block 6 is a four rows twenty characters LCD (Liquid Crystal

Display) from Hitachi, to display the experimental results. Block 7 consists of MAX232

(dual RS232 transmitter/receiver interface), which is used to communicate with PC kept

in Block 8.

5.3.2 AC modified Wheatstone bridge network

A modified AC Wheatstone bridge network is shown in figure 5.2. The most

accurate methods of measurement of unknown impedance are the bridge methods, whose

accuracy is basically limited only by the accuracy of the known values of the various

elements constituting the bridge. A modified approach of the balancing techniques of AC

Wheatstone’s bridge network has been reported to achieve high accuracy in

measurement. In the developed Instrument, two high gain operational amplifiers

(CA3041) IC1 and IC2 are connected with the bridge network with the non-inverting

terminal connected to the ground circuit. The bridge output nodal points B and D almost

at the same potentials with respect to the ground and hence the effect of stray capacitance

that will exist between them and also between them and ground is assumed to be

minimized. Since, B and D are at virtual ground, the sinusoidal supply voltage,

V= V sin ωt, the current through the bridge impedances are Z1, Z2, Z3 and Z4

respectively. The output voltage of the circuit is [5]

Vo= Rf [Z2Z3 – Z1 Z2] V (1)

123

At balance condition of the bridge, Vo=0 which is identical with the conventional bridge

network. The conductivity cell is connected instead of Z3. The conductivity of a sample

is determined by,

Vo= Bridge output Voltage, Vi= input excitation voltage, Z1, Z2, Z4=known resistances,

Rf =Feed back resistance and Gc = Conductivity of a sample.

The output of the Amplifier IC2 is given to input of the precision rectifier constructed

with operational amplifiers IC3 and IC4 as shown in Figure 5.2.

5.3.3 Microcontroller and interfacing circuit

The circuit diagram of the Microcontroller based instrumentation set up to

measure the Electrical Conductivity of the sample is shown in figure 5.3. In the designed

circuit, the output from the modified Wheatstone’s bridge network (figure 5.2) is given to

pin 38 (ADC 2) of microcontroller. The Thermocouple which is used to measure the

temperature of the sample is connected to pin 39 (ADC 1) of Port A. The signal

generated by the junction of the thermocouple due to thermal changes is fed to an

amplifier circuit specially designed for very low signal amplification as shown in figure

5.4 (Temperature measurement). The output signal is amplified to a suitable level by

using an instrumentation amplifier read by the microcontroller through A/D converter. A

semiconductor temperature sensor AD590 is used to simulate a reference junction

(Neelamegam et al., 1992) [6]. A crystal oscillator of 8MHz is connected between pin 12

and 13 of microcontroller as shown in figure 5.3. Three keys are connected to PC0, PC1,

and PC2 Port C. A four rows twenty characters LCD is connected with Port D, to display

the measured data and the computed results. MAX232 (dual RS232 transmitter/receiver

interface) is connected with pin 14 and 15 of Port D to transmit/ receive data from PC.

5.3.4 Software

Software is developed in C and assembly language to initialize LCD, to start

ADC, to check End of Conversion, to read 10bits of data from ADC, to measure the

temperature, to compute Conductivity, to compute Chloride concentration using

124

regression model, to display the results in LCD and to send data to PC for further

processing. The flowchart for performing the above tasks is shown in figure 5.5.

5.4 Materials and Method

5.4.1 Sampling Field

Soil samples are collected from thirty paddy field sites originated from

Thanjavur- Nagapattinam Delta districts, TN, South India, where rice is the main crop of

several agricultural products (Figure 5.6). The field chosen is located on the eastern coast

of TN, between 9o 50’ and 11o 25’ of the north latitude and 78o 45’ and 70o 25’ of the

East. The samples are collected at every 3 kms from Thanjavur to Nagapattinam over

90kms, during the major cropping season of spring-summer (March- June), which

produces about 56% of the Nations total production.

5.4.2 Sample Collection

Sampling areas of paddy fields are selected by avoiding tracks, drainage lines,

sheep camp, or influences other than effluent irrigation. During collection, the size of the

sample (Volume or weight), identification of sample (unique labeling), special packaging

and storage are noted. After collection of the samples, they are air-dried to remove

moisture. Samples are commonly collected from the soil surface or from boreholes

drilled with a hollow stem auger equipped with a split-spoon or core barrel sampler. The

sample is placed in a mixing bowl and organic matter such as roots discarded. Rock and

gravel larger than small pebbles are commonly removed. Homogenize the sample by

thoroughly mixing it prior to weighing or placement in a sample jar (if laboratory

analysis is to be performed). To the extent possible the material placed in a sample jar for

laboratory analysis should be as much like the sample selected for field determination. In

addition coordinate with the analytical laboratory to ascertain if they have a standard

protocol for selection of small volume samples (e.g. a maximum size of pebbles in the

sample).

5.4.3 Sampling procedure

The collected soil samples are assigned a number, transferred to a paper bag,

and then placed in a metal tray. These samples are dried overnight in a cabinet equipped

with a heating element and an exhaust fan to remove moisture. The temperature in the

cabinet does not exceed 36oC in order to approximate air drying conditions. Samples are

125

crushed with a mechanical grinder equipped with porcelain mortar and stainless steel 10

mm mesh sieve to remove larger clods and unwanted debris. Since the material from the

particle sizing 2mm and smaller are most important in making an inventory of the

mineral constituents of the soil and in evaluating EC, the sample is crushed again and the

particles sizing 2mm and less than 2mm are sieved using 2mm mesh. The sample is

prepared as given below to measure the conductivity. Three 10 gram scoops of soil and

30 ml of deionized water are taken in a large test tube and shaken well for 30 min to get

1:1 suspension of soil sample. After initial shaking, the suspension is allowed to stand,

with intermittent shaking for 30 minutes [7]. The supernatant solution is then filtered and

it is used for the measurement of Electrical Conductivity.

5.4.4 Measurement

To measure the Electrical conductivity of the sample, the conductivity cell is

connected at one arm of the modified AC Wheatstone bridge and selecting the resistance

value Z1 (100 Ω or 1 kΩ), Z2 (1 kΩ), and Z4 (1 kΩ). A fixed sinusoidal excitation

voltage of 1V with frequency 1 KHz is applied to the bridge. For the calibration of the

instrument, the known concentrations of NaCl are prepared and the Conductivity is

measured before using the Soil samples. The solution is maintained at 25° C. Initially, the

Conductivity cell is kept in the solution of NaCl having concentration of 0.1N, and the

Electrical Conductivity is measured using the developed Instrument. Then the probe is

washed with deionised water and the Electrical Conductivity for various concentrations

of NaCl (0.2N, 0.3N, 0.4N and 0.5N) is measured using the microcontroller based

instrument. The calibration curve is drawn between NaCl concentrations versus

Conductivity (figure 5.7). Then, the conductivity cell is immersed in the prepared soil

sample and the measurements are made for Electrical Conductivity. A graph is drawn

between soil samples and their corresponding Electrical Conductivity as shown in Figure

5.8. At the same time, Chloride concentration of the prepared soil samples is determined

using the titration method for the development of regression model.

5.4.5 Development of regression Model

Regression analysis is the statistical technique that identifies the relationship

between two or more variables. The technique is used to find the equation to evaluate the

relation between the two and to predict the unknown value from the developed equation.

126

A simple regression analysis can show that the relations between an independent variable

X and a dependent variable Y is linear, using the simple linear regression equation.

Y= a + mX (where a is an intercept and m is a slope).

The Chloride concentration of the sample is strongly related to the Electrical

Conductivity of the sample, a relation between them is evaluated using linear regression

model (using software ULTIMACALC). It can be seen that from the figure 5.9, as the

Chloride concentration increases the Electrical Conductivity of the soil sample also

increases. The regression line equation is arrived by using the following statistical

equation,

y - y = b xy ( x- x )

where b xy = r ( x / y ).

The regression line equation y = -517.80+14.02x is obtained for that line, using the above

relation. The concentration of Chloride for the soil sample can be determined if the

conductivity of the soil sample is known. The correlation coefficient between the

Electrical Conductivity and the Chloride concentration is R= 0.96 (n=30) which enables

the value of Electrical Conductivity can be used as a surrogate for Chloride estimation.

A regression line also drawn between the Electrical Conductivity measured using

the developed instrument and the commercially available ELICO CM 180 instrument to

check the correlations between the two, which is shown in figure 5.10. The regression

line equation arrived is y= 5.85 + 0.94x, and correlation coefficient R = 0.97 (n=30).

127

5.5 Results and Discussion

The developed microcontroller based instrument is used to measure the

Conductivity of the soil samples. The empirical relationship between the Electrical

Conductivity and the Chloride concentration has been developed using linear regression

model to determine the Chloride concentration of the sample. The performance of the

designed instrument is investigated by comparing the results with the standard instrument

(ELICO CM 180).

5.5.1 Analytical performance of the system

The calibration curve is obtained by plotting the concentration of Chloride against

the Electrical Conductivity of prepared NaCl Solutions at various concentrations as

shown in figure 5.7. The reproducibility of the instrument is tested by taking five

replicate readings for soil sample and it is found to agree well within the limits. The

statistical analysis is made for the results obtained using the developed instrument and the

standard instrument to compare the relative accuracies in average Electrical Conductivity

for soil samples. The values (n=30) of Mean=72.06, Median value=62, Standard

Deviation= 20.45, Coefficient of Variation =28.38 and Standard Error of Coefficient of

variation= 3.66 for the Conductivity measured using the designed instrument and for the

standard one, the values of mean=73.83, Median value=64, S.D=19.69, Coeff of

Variation= 26.68 and Std Err of Coeff of variation= 3.44 which shows that there is no

significant difference between the two methods. The accuracy of the developed

instrument is confirmed by the absence of large exceptional errors which allows the

suitability of microcontroller based instrument for Electrical Conductivity measurement.

5.5.1 Analysis of Chloride concentration at various locations and plants

In this study, it is observed (Figure 5.8) that the range of Electrical Conductivity

of soil samples varies from 45mS/cm to 109mS/cm and the Chloride concentration

(Figure 5.11) is maximum at Ramarmadam (1010 ppm) and minimum at Kattuthottam

(140ppm). It is also to be noted that all the collected paddy field soil samples are having

the Chloride concentration within the maximum tolerable limit (1050 ppm).

The concentration of Chloride varies from 140ppm to 210ppm for the particular

places like Kattuthottam (140ppm), Pulavarnatham (210ppm), Athanur (210ppm),

Needamangalam (210ppm), and Kilerium (175ppm). It is observed from the literature

128

survey (Jing et al., 1992) [8], that the places having Chloride concentration from

100ppm-200ppm are suitable for the cultivation of white potato, peanut, tomato and

sugarcane. Hence, the research report suggests that the above places are suitable for the

cultivation of the above plants with other necessary minerals.

The Chloride concentrations are ranged from 820ppm to 1010ppm for the places

like Aandipalayam (985ppm), Kurukkathi (930ppm), Koothanur (820ppm), Kilvelur

(860ppm), Aazhiyur (980ppm), Ramarmadam (1010ppm), Sikkal (965ppm) and

Nagapattinam (985ppm). These places are suitable for paddy field which is confirmed by

the literature survey (Zhu, Q.S., and Yu,B.S,1991)[9]. It is also observed that the above

places are already cultivating rice only. Hence, it is concluded that the Chloride

concentration is also very important for the paddy growth in addition to other necessary

minerals (rice).

Tomatoes are sensitive to salinity. The test has been conducted to know the effect

of Chloride on tomato plant which is planted at Thanjavur (Tamil Nadu, South India)

having deep, loamy, well-drained soil. The value of soil pH is about 6.2 to 6.8 and the

direct sun light on plant is around 6 hours. The test is performed on the plant during the

ripening stage of tomato fruit. It is observed that irrigating tomato plant with 1N of NaCl

once in a day for the period of 1 month (1.09.2010 to 30.09.2010) increases the total

soluble solids rather than the normal irrigation.

Chloride plays a vital role in stomatal movement in the palm. It is observed that

healthy coconut palms along seashores (Nagapattinam, Tamil Nadu, South India)

Chloride at a concentration of 7-10mg/g DM in their foliage. The optimal Chloride

concentration is usually in the range of 3.8 to 6.4 mg/g.

An embedded based Electrical Conductivity measurement set up has been

designed and developed and a regression model is developed between Conductivity and

Chloride concentration of soil samples. The Chloride concentration of soil samples at

various locations is measured and their plant cultivation is also discussed.

129

Figure 5.1 Block diagram of Microcontroller ATmega32 based Electrical

Conductivity instrument set up.

130

Figure 5.2 AC modified Wheatstone’s bridge network with precision rectifier

131

Figure 5.3 Microcontroller ATmega32 and interfacing circuit

132

Figure 5.4 Temperature measurement circuit

133

Figure 5.5 Flowchart

134

Figure 5.6 Site map

135

Figure 5.7 Electrical Conductivity measured for known concentration of NaCl

Solution using developed instrument.

136

Figure 5.8 Graph drawn between collected soil samples versus Electrical

conductivity

137

Figure 5.9 Linear regression drawn between Electrical Conductivity versus

Chloride concentration

138

Figure 5.10 Linear regression for Electrical Conductivity of the soil samples drawn

between the developed instrument and standard instrument.

139

Figure 5.11 Graph drawn between collected soil samples versus Chloride

concentration

140

References 1. Hajrasuliha S., Cassel D. K., Rezainejad Y., 49(1991), 117-127.

2. Maas E. V., Chloride and crop production. (Eds.: T.L. Jackson). Potash and

Phosphate Institute. Atlanta, GA, (1986), 4-20.

3. Milne R.A, E.Rapp, Soil salinity and drainage problems, Canada

Dept. of Agric, Ottawa, (1968), 1314

4. Braunstein J., Robbins G.D., Journal of Chemical Education, 48 -1 (1981), 52–59.

5. Rajendran A., Neelamegam P., Measurement, 35(2004), 59–63.

6. Neelamegam P., Padmanabhan K., Selvasekarapandian S., Meas. Sci. Technol,

3(1992) 581.

7. Recommended Chemical Soil Test Procedures for the North Central Region,

North Central Regional Publication No. 221. NDSU Bull. No. 499, (1988).

8. Jing A.S., Guo B.C., Zhang X.Y., Chin.J.Soil Sci, 33(6) (1992), 257-259.

9. Zhu Q.S., Yu B.S., Wubei Agric. Sci. 5(1991), 22-26. (Chinese)

119

CHAPTER V

ELECTRICAL CONDUCTIVITY AS A SURROGATE FOR CHLORIDE

DETERMINATION

This chapter presents the design and development of Microcontroller

ATmega32 based Instrument set up to determine the Electrical Conductivity in soil

samples. The Electrical Conductivity of the soil samples measured by the implemented

embedded based Electrical Conductivity instrument is comparable with that of the

commercial instrument (ELICO CM 180). Since, Electrical Conductivity can be used as

a surrogate for Chloride concentration measurement, a linear regression model is

developed between Electrical Conductivity and Chloride concentration of soil samples.

The Chloride concentration of the soil samples collected at various samples and their

plant cultivation is also discussed.

5.1 Introduction

Electrical conductivity is an inherent property of most materials, and ranges from

extremely conductive materials like metals to very non-conductive materials like plastics

or glass. In metals, the electrical current is carried by electrons, while in water it is

carried by charged ions. In both cases, the conductivity is determined by the number of

charge carriers, how fast they move and how much charge each one carries. Conductivity

(G), the inverse of resistivity (R) is determined from the voltage and current values

according to Ohm's law. Using Ohm’s Law, V= iR and knowing conductivity G=

(1/R)*k, where k=cell constant =length (d, spacing between two electrodes)/area of

electrodes then G can be determined as G= (1/R)*k = (i/V)*k. When resistance is

measured in ohms, conductance is measured in siemens (formerly known as a mho).

Since 1 siemens is a very large unit, aqueous samples are commonly measured in micro

siemens μS. Metals are extremely conductive because electrons move almost with the

speed of light, while in water ions move much slower and the conductivity is much

lower. Raising the temperature makes water less viscous and the ions can move faster.

Because the ions are of different sizes and carry different amounts of water with them as

they move, the temperature effect is different for each ion.

120

5.1.1 Electrical Conductivity as a surrogate for Chloride concentration

Electrical Conductivity (EC) is usually a representation of salinity and it can

be measured with a simple device. Chloride ion is an important element among dissolved

solids which can limit plant growth, decrease yields and reduce quality of drinking water.

Chloride is highly soluble and remains in the soil solution, while other ions such as

sulphate and bicarbonate combine with calcium and magnesium, are present, to form

calcium sulphate and calcium carbonate, which are sparingly soluble compounds.

Chloride concentration typically is measured by titration of aqueous samples using

standard AgNO3

solution. Chloride analysis thus is time consuming and expensive,

compared to EC measurement which is fast and inexpensive (Hajrasuliha, S et al) [1].

Since Chloride is a major constitute of saline waters and soils and it directly affects EC, a

close correlation between EC and Chloride can be obtained. Maas et al., [2] suggested

that if Chloride is the predominant anion in a soil solution, the Chloride concentration in

molm-3

would be approximately equal to 10 times the EC

measured in dSm-1

.

Observations of Chloride concentration and Electrical Conductivity delivered the

possibility of a generelised empirical relationship between these two factors. Therefore it

is conceivable that the Chloride concentration can simply be estimated from Electrical

Conductivity measurement. The concept of computation of Chloride concentration is, to

correlate Electrical Conductivity with the Chloride Concentration of the soil samples

using regression model, which validates Electrical Conductivity as a surrogate for

Chloride estimation.

5.2 Agricultural soil

All soils contain some water soluble salts which include essential nutrients for

plant growth. When the level of water soluble salts exceeds a certain level, harmful

effects on plant growth occur. A soil with excess total soluble salts is referred to as a

saline soil. The influence that a certain level of soluble salt will have on crop growth

depends upon several factors such as climatic condition, soil texture, distribution of salt

in the profile, salt composition and plant species ( Milne, R.A et al) [3]. The areal extent

and depth of a salt problem is usually irregular. Soil sampling on a grid system may be

necessary to map the extent of the problem. Soluble salts are most commonly detected by

measuring the soil solution’s ability to conduct an electric current, referred to as

121

Electrical Conductivity. The common unit of measurement for EC has been mmhos/cm.

The official international unit of measurement is siemen/ m (S/m). One mmhos/cm is

equal to 0.1S/m or 1.0 ds/m.

5.3 Design and development of Electrical Conductivity measurement set up using

Microcontroller Atmega32

Soil Chloride analysis has been conducted primarily for the purpose of salinity

and irrigation management. Presently, it has become highly advantageous to carry out

information processing and control using microcontroller. It is also a well known fact that

the microcontroller system can offer high accuracy and high speed response. Hence, these

reasons infuse a strong motivation for the design and implementation of the automatic

measurement system based on microcontroller. An embedded systems controlled by

microcontrollers consist of not only a digital part, used for control and data processing,

but also an analog part mostly used for adjustment of input signals e.g. from sensors. In

this experimental study, to decrease the test cost, it is proposed to use ATmega32

microcontroller mounted in the system and the developed system is used for in-situ

measurement of the conductivity.

5.3.1 Design of the measurement system

The block diagram of microcontroller based Electrical Conductivity measurement

set up is shown in figure 5.1. The conductivity cell made up of platinum which is used to

measure the conductivity of the samples is kept in Block 1. The cell constant (K) is

related to the physical characteristics of the measuring cell. K is defined for two flat,

parallel measuring electrodes as the electrode separation distance (d) divided by the

electrode area (A). Thus, for a 1 cm cube of liquid, K = d/A = 1 cm–1. Its determination is

much more convenient by calibration with pattern solutions (Braunstein et al.,) [4].

Polarizing the conductance cell by an external DC potential VDC produces some

undesirable effects (double-layer capacitance, electrolysis, ohmic resistance and

electrolytic saturation). On the other hand, it is proved that the electrolytic saturation is

reduced considerably if the AC polarization frequency is high enough. Hence, a fixed

sinusoidal excitation voltage of 1V is applied to the bridge. The Conductivity cell is

connected to one arm of a modified Wheatstone’s bridge network. The Block 2 consists

of precision rectifier to rectify the output of Bridge network. Block 3 represents the

122

temperature sensor Chromel alumel thermocouple to measure the temperature of the

sample. The effect of temperature is important when an electric conductivity of a liquid

or solution must be done. A solution at a higher temperature will present higher quantity

of ions dissociated, therefore the concentration of electric charges will raise and as a

consequence, conductivity will be higher. On the contrary, the same solution at low

temperature will have a low conductivity due to the low quantity of ions present, which

results in lower electric conductivity. From an application point of view, conductivity is

given at a certain temperature, which has been stated as a reference to better compare the

measurements at different times and locations. This temperature is usually 25°C. Block 4

indicates keypad to give input data to the Microcontroller for processing. Block 5 consists

of ATmega32 microcontroller from Atmel company, is a low power, high performance 8

bit AVR microcontroller. Block 6 is a four rows twenty characters LCD (Liquid Crystal

Display) from Hitachi, to display the experimental results. Block 7 consists of MAX232

(dual RS232 transmitter/receiver interface), which is used to communicate with PC kept

in Block 8.

5.3.2 AC modified Wheatstone bridge network

A modified AC Wheatstone bridge network is shown in figure 5.2. The most

accurate methods of measurement of unknown impedance are the bridge methods, whose

accuracy is basically limited only by the accuracy of the known values of the various

elements constituting the bridge. A modified approach of the balancing techniques of AC

Wheatstone’s bridge network has been reported to achieve high accuracy in

measurement. In the developed Instrument, two high gain operational amplifiers

(CA3041) IC1 and IC2 are connected with the bridge network with the non-inverting

terminal connected to the ground circuit. The bridge output nodal points B and D almost

at the same potentials with respect to the ground and hence the effect of stray capacitance

that will exist between them and also between them and ground is assumed to be

minimized. Since, B and D are at virtual ground, the sinusoidal supply voltage,

V= V sin ωt, the current through the bridge impedances are Z1, Z2, Z3 and Z4

respectively. The output voltage of the circuit is [5]

Vo= Rf [Z2Z3 – Z1 Z2] V (1)

123

At balance condition of the bridge, Vo=0 which is identical with the conventional bridge

network. The conductivity cell is connected instead of Z3. The conductivity of a sample

is determined by,

Vo= Bridge output Voltage, Vi= input excitation voltage, Z1, Z2, Z4=known resistances,

Rf =Feed back resistance and Gc = Conductivity of a sample.

The output of the Amplifier IC2 is given to input of the precision rectifier constructed

with operational amplifiers IC3 and IC4 as shown in Figure 5.2.

5.3.3 Microcontroller and interfacing circuit

The circuit diagram of the Microcontroller based instrumentation set up to

measure the Electrical Conductivity of the sample is shown in figure 5.3. In the designed

circuit, the output from the modified Wheatstone’s bridge network (figure 5.2) is given to

pin 38 (ADC 2) of microcontroller. The Thermocouple which is used to measure the

temperature of the sample is connected to pin 39 (ADC 1) of Port A. The signal

generated by the junction of the thermocouple due to thermal changes is fed to an

amplifier circuit specially designed for very low signal amplification as shown in figure

5.4 (Temperature measurement). The output signal is amplified to a suitable level by

using an instrumentation amplifier read by the microcontroller through A/D converter. A

semiconductor temperature sensor AD590 is used to simulate a reference junction

(Neelamegam et al., 1992) [6]. A crystal oscillator of 8MHz is connected between pin 12

and 13 of microcontroller as shown in figure 5.3. Three keys are connected to PC0, PC1,

and PC2 Port C. A four rows twenty characters LCD is connected with Port D, to display

the measured data and the computed results. MAX232 (dual RS232 transmitter/receiver

interface) is connected with pin 14 and 15 of Port D to transmit/ receive data from PC.

5.3.4 Software

Software is developed in C and assembly language to initialize LCD, to start

ADC, to check End of Conversion, to read 10bits of data from ADC, to measure the

temperature, to compute Conductivity, to compute Chloride concentration using

124

regression model, to display the results in LCD and to send data to PC for further

processing. The flowchart for performing the above tasks is shown in figure 5.5.

5.4 Materials and Method

5.4.1 Sampling Field

Soil samples are collected from thirty paddy field sites originated from

Thanjavur- Nagapattinam Delta districts, TN, South India, where rice is the main crop of

several agricultural products (Figure 5.6). The field chosen is located on the eastern coast

of TN, between 9o 50’ and 11o 25’ of the north latitude and 78o 45’ and 70o 25’ of the

East. The samples are collected at every 3 kms from Thanjavur to Nagapattinam over

90kms, during the major cropping season of spring-summer (March- June), which

produces about 56% of the Nations total production.

5.4.2 Sample Collection

Sampling areas of paddy fields are selected by avoiding tracks, drainage lines,

sheep camp, or influences other than effluent irrigation. During collection, the size of the

sample (Volume or weight), identification of sample (unique labeling), special packaging

and storage are noted. After collection of the samples, they are air-dried to remove

moisture. Samples are commonly collected from the soil surface or from boreholes

drilled with a hollow stem auger equipped with a split-spoon or core barrel sampler. The

sample is placed in a mixing bowl and organic matter such as roots discarded. Rock and

gravel larger than small pebbles are commonly removed. Homogenize the sample by

thoroughly mixing it prior to weighing or placement in a sample jar (if laboratory

analysis is to be performed). To the extent possible the material placed in a sample jar for

laboratory analysis should be as much like the sample selected for field determination. In

addition coordinate with the analytical laboratory to ascertain if they have a standard

protocol for selection of small volume samples (e.g. a maximum size of pebbles in the

sample).

5.4.3 Sampling procedure

The collected soil samples are assigned a number, transferred to a paper bag,

and then placed in a metal tray. These samples are dried overnight in a cabinet equipped

with a heating element and an exhaust fan to remove moisture. The temperature in the

cabinet does not exceed 36oC in order to approximate air drying conditions. Samples are

125

crushed with a mechanical grinder equipped with porcelain mortar and stainless steel 10

mm mesh sieve to remove larger clods and unwanted debris. Since the material from the

particle sizing 2mm and smaller are most important in making an inventory of the

mineral constituents of the soil and in evaluating EC, the sample is crushed again and the

particles sizing 2mm and less than 2mm are sieved using 2mm mesh. The sample is

prepared as given below to measure the conductivity. Three 10 gram scoops of soil and

30 ml of deionized water are taken in a large test tube and shaken well for 30 min to get

1:1 suspension of soil sample. After initial shaking, the suspension is allowed to stand,

with intermittent shaking for 30 minutes [7]. The supernatant solution is then filtered and

it is used for the measurement of Electrical Conductivity.

5.4.4 Measurement

To measure the Electrical conductivity of the sample, the conductivity cell is

connected at one arm of the modified AC Wheatstone bridge and selecting the resistance

value Z1 (100 Ω or 1 kΩ), Z2 (1 kΩ), and Z4 (1 kΩ). A fixed sinusoidal excitation

voltage of 1V with frequency 1 KHz is applied to the bridge. For the calibration of the

instrument, the known concentrations of NaCl are prepared and the Conductivity is

measured before using the Soil samples. The solution is maintained at 25° C. Initially, the

Conductivity cell is kept in the solution of NaCl having concentration of 0.1N, and the

Electrical Conductivity is measured using the developed Instrument. Then the probe is

washed with deionised water and the Electrical Conductivity for various concentrations

of NaCl (0.2N, 0.3N, 0.4N and 0.5N) is measured using the microcontroller based

instrument. The calibration curve is drawn between NaCl concentrations versus

Conductivity (figure 5.7). Then, the conductivity cell is immersed in the prepared soil

sample and the measurements are made for Electrical Conductivity. A graph is drawn

between soil samples and their corresponding Electrical Conductivity as shown in Figure

5.8. At the same time, Chloride concentration of the prepared soil samples is determined

using the titration method for the development of regression model.

5.4.5 Development of regression Model

Regression analysis is the statistical technique that identifies the relationship

between two or more variables. The technique is used to find the equation to evaluate the

relation between the two and to predict the unknown value from the developed equation.

126

A simple regression analysis can show that the relations between an independent variable

X and a dependent variable Y is linear, using the simple linear regression equation.

Y= a + mX (where a is an intercept and m is a slope).

The Chloride concentration of the sample is strongly related to the Electrical

Conductivity of the sample, a relation between them is evaluated using linear regression

model (using software ULTIMACALC). It can be seen that from the figure 5.9, as the

Chloride concentration increases the Electrical Conductivity of the soil sample also

increases. The regression line equation is arrived by using the following statistical

equation,

y - y = b xy ( x- x )

where b xy = r ( x / y ).

The regression line equation y = -517.80+14.02x is obtained for that line, using the above

relation. The concentration of Chloride for the soil sample can be determined if the

conductivity of the soil sample is known. The correlation coefficient between the

Electrical Conductivity and the Chloride concentration is R= 0.96 (n=30) which enables

the value of Electrical Conductivity can be used as a surrogate for Chloride estimation.

A regression line also drawn between the Electrical Conductivity measured using

the developed instrument and the commercially available ELICO CM 180 instrument to

check the correlations between the two, which is shown in figure 5.10. The regression

line equation arrived is y= 5.85 + 0.94x, and correlation coefficient R = 0.97 (n=30).

127

5.5 Results and Discussion

The developed microcontroller based instrument is used to measure the

Conductivity of the soil samples. The empirical relationship between the Electrical

Conductivity and the Chloride concentration has been developed using linear regression

model to determine the Chloride concentration of the sample. The performance of the

designed instrument is investigated by comparing the results with the standard instrument

(ELICO CM 180).

5.5.1 Analytical performance of the system

The calibration curve is obtained by plotting the concentration of Chloride against

the Electrical Conductivity of prepared NaCl Solutions at various concentrations as

shown in figure 5.7. The reproducibility of the instrument is tested by taking five

replicate readings for soil sample and it is found to agree well within the limits. The

statistical analysis is made for the results obtained using the developed instrument and the

standard instrument to compare the relative accuracies in average Electrical Conductivity

for soil samples. The values (n=30) of Mean=72.06, Median value=62, Standard

Deviation= 20.45, Coefficient of Variation =28.38 and Standard Error of Coefficient of

variation= 3.66 for the Conductivity measured using the designed instrument and for the

standard one, the values of mean=73.83, Median value=64, S.D=19.69, Coeff of

Variation= 26.68 and Std Err of Coeff of variation= 3.44 which shows that there is no

significant difference between the two methods. The accuracy of the developed

instrument is confirmed by the absence of large exceptional errors which allows the

suitability of microcontroller based instrument for Electrical Conductivity measurement.

5.5.1 Analysis of Chloride concentration at various locations and plants

In this study, it is observed (Figure 5.8) that the range of Electrical Conductivity

of soil samples varies from 45mS/cm to 109mS/cm and the Chloride concentration

(Figure 5.11) is maximum at Ramarmadam (1010 ppm) and minimum at Kattuthottam

(140ppm). It is also to be noted that all the collected paddy field soil samples are having

the Chloride concentration within the maximum tolerable limit (1050 ppm).

The concentration of Chloride varies from 140ppm to 210ppm for the particular

places like Kattuthottam (140ppm), Pulavarnatham (210ppm), Athanur (210ppm),

Needamangalam (210ppm), and Kilerium (175ppm). It is observed from the literature

128

survey (Jing et al., 1992) [8], that the places having Chloride concentration from

100ppm-200ppm are suitable for the cultivation of white potato, peanut, tomato and

sugarcane. Hence, the research report suggests that the above places are suitable for the

cultivation of the above plants with other necessary minerals.

The Chloride concentrations are ranged from 820ppm to 1010ppm for the places

like Aandipalayam (985ppm), Kurukkathi (930ppm), Koothanur (820ppm), Kilvelur

(860ppm), Aazhiyur (980ppm), Ramarmadam (1010ppm), Sikkal (965ppm) and

Nagapattinam (985ppm). These places are suitable for paddy field which is confirmed by

the literature survey (Zhu, Q.S., and Yu,B.S,1991)[9]. It is also observed that the above

places are already cultivating rice only. Hence, it is concluded that the Chloride

concentration is also very important for the paddy growth in addition to other necessary

minerals (rice).

Tomatoes are sensitive to salinity. The test has been conducted to know the effect

of Chloride on tomato plant which is planted at Thanjavur (Tamil Nadu, South India)

having deep, loamy, well-drained soil. The value of soil pH is about 6.2 to 6.8 and the

direct sun light on plant is around 6 hours. The test is performed on the plant during the

ripening stage of tomato fruit. It is observed that irrigating tomato plant with 1N of NaCl

once in a day for the period of 1 month (1.09.2010 to 30.09.2010) increases the total

soluble solids rather than the normal irrigation.

Chloride plays a vital role in stomatal movement in the palm. It is observed that

healthy coconut palms along seashores (Nagapattinam, Tamil Nadu, South India)

Chloride at a concentration of 7-10mg/g DM in their foliage. The optimal Chloride

concentration is usually in the range of 3.8 to 6.4 mg/g.

An embedded based Electrical Conductivity measurement set up has been

designed and developed and a regression model is developed between Conductivity and

Chloride concentration of soil samples. The Chloride concentration of soil samples at

various locations is measured and their plant cultivation is also discussed.

129

Figure 5.1 Block diagram of Microcontroller ATmega32 based Electrical

Conductivity instrument set up.

130

Figure 5.2 AC modified Wheatstone’s bridge network with precision rectifier

131

Figure 5.3 Microcontroller ATmega32 and interfacing circuit

132

Figure 5.4 Temperature measurement circuit

133

Figure 5.5 Flowchart

134

Figure 5.6 Site map

135

Figure 5.7 Electrical Conductivity measured for known concentration of NaCl

Solution using developed instrument.

136

Figure 5.8 Graph drawn between collected soil samples versus Electrical

conductivity

137

Figure 5.9 Linear regression drawn between Electrical Conductivity versus

Chloride concentration

138

Figure 5.10 Linear regression for Electrical Conductivity of the soil samples drawn

between the developed instrument and standard instrument.

139

Figure 5.11 Graph drawn between collected soil samples versus Chloride

concentration

140

References 1. Hajrasuliha S., Cassel D. K., Rezainejad Y., 49(1991), 117-127.

2. Maas E. V., Chloride and crop production. (Eds.: T.L. Jackson). Potash and

Phosphate Institute. Atlanta, GA, (1986), 4-20.

3. Milne R.A, E.Rapp, Soil salinity and drainage problems, Canada

Dept. of Agric, Ottawa, (1968), 1314

4. Braunstein J., Robbins G.D., Journal of Chemical Education, 48 -1 (1981), 52–59.

5. Rajendran A., Neelamegam P., Measurement, 35(2004), 59–63.

6. Neelamegam P., Padmanabhan K., Selvasekarapandian S., Meas. Sci. Technol,

3(1992) 581.

7. Recommended Chemical Soil Test Procedures for the North Central Region,

North Central Regional Publication No. 221. NDSU Bull. No. 499, (1988).

8. Jing A.S., Guo B.C., Zhang X.Y., Chin.J.Soil Sci, 33(6) (1992), 257-259.

9. Zhu Q.S., Yu B.S., Wubei Agric. Sci. 5(1991), 22-26. (Chinese)

141

CHAPTER VI

COMPUTATION OF CHLORIDE IN ENVIRONMENTAL SAMPLES

SOIL AND SEAWATER

This chapter presents the computation of Chloride in environmental samples of soil

and sea water using Artificial Neural Network. A three layered neural network is

employed for the computation of Chloride in environmental samples. Soil samples are

collected at thirty various places from Thanjavur to Nagapattinam, Tamil Nadu, South

India. In the prediction of soil Chloride, distance is used as an input parameter and

Chloride concentration is used as output parameter. Computation of Chloride in sea water

is made using Back Propagation Algorithm Neural Network and Genetic Algorithm

based Back Propagation Neural Network to identify the best technique that could

adequately predict the Chloride concentration to a desired accuracy. Sea water samples

are collected from Middle East coastal region of Tamil Nadu. Temperature, pH and

Electrical Conductivity are used as input parameters in the Chloride prediction system.

The adaptiveness is checked for various seasonal conditions by varying the input

parameters. The prediction accuracy is improved by using various numbers of hidden

neurons and training iterations.

Prediction of Chloride in Soil samples using Artificial Neural Network

6.1 Introduction

Neural Networks are among current Artificial Intelligence (AI) research areas of

interest to the environmental studies. In order to obtain an ANN with the proper

modelling ability, a number of internal parameters that rule its training and operation

must be correctly configured. These are related to the ANN topology and to the learning

algorithm used for its training. In this study, neural network is trained to learn the

distance as input and Chloride concentration of soil samples as output vector by using the

back propagation algorithm. The output parameter (Chloride concentration) is measured

using titrimetry method to obtain the training data for neural network. After the training,

the validation is performed for verification and testing is done to compute the output

(Chloride concentration) of the soil samples using the trained neural network.

142

In this study, 30 soil samples are collected at every 3 kms from Thanjavur to

Nagapattinam, Tamil Nadu, South India. Out of thirty data set, twenty data set are used to

train the neural network and ten data set are used for testing the neural network model.

6.2 Soil sampling

The soil sample collection and the sampling have been done as per the procedure

given in Chapter V (5.4.2 and 5.4.3). The prepared soil samples are used to measure the

Chloride concentration. Using the standard titration method, the Chloride concentration is

measured for the collected samples. In this method, titrant solution of Silver Nitrate

(0.01N) and indicator of Potassium Chromate is used with the reddish brown color end

point.

Chloride in ppm = ml of titrant used x N x 35.46 x 1000 / ml of seawater sample. Where

N = Normality of titrant.

6.3 Implementation of neural network

Neural Network with back propagation algorithm is used to compute the Chloride

concentration of the soil samples. The architecture of ANN consists of three layers. The

input layer consists of one neuron (distance), six neurons in the hidden layer and one

neuron (Chloride concentration) in the output layer are used for the architecture. Twenty

data set are used as a training pattern.

6.3.1 Training phase

During the training, the signal from the input vector propagates through the

network layer till the output layer is reached. The output vector represents the predicted

output of the ANN and has a node for each variable that is being predicted. The task of

training the ANN is to find the most appropriate set of weights for each connection which

minimises the output error. All weighted inputs are summed at the neuron node and this

summed value is then passed to a transfer function. The back propagation algorithm

(BPA) or the generalized delta rule uses sigmoid activation function f(x) = 1/(1+e-x). The

BPA is a supervised learning algorithm that aims at reducing overall system error to a

minimum. In this learning procedure, an initial weight vectors w0 is updated,

143

Wij (t+1) = Wij (t) + η δj xi + α (Wij (t) - Wij (t-1)) (6.1)

Where, Wij (t) = connection weight from a node i in one layer at time t; xi = input or

output of the hidden node i; δj = error term for node j; η = learning rate factor; α =

momentum factor.

If j is an output node, then, δj = yj (1- yj) (dj - yj)

where, dj – desired output of node j; yj – actual output.

If j is hidden node, the computation of error becomes, δj = xj (1- xj) Σ δk Wj k

where, k is summed over all nodes in the layer above node j.

The learning rate parameter took the value of 0.03 and the training pattern data is

given in table 6.1. Prior to the execution of the training process of neural network, the

input and output parameters were normalized in order to acquire accurate results.

6.3.2 Validation of the developed neural network

In this part of the study, the trained network model is used to compute the

concentration of Chloride for the input parameter. For this 10 distances are randomly

selected from the trained pattern and their soil Chloride concentrations are computed as

seen in table 6.2. To demonstrate the generalization capability of the model, the statistical

test results of validation data set are given in table 6.3. It is observed that there is a

significantly high compromise between the experimental and the proposed model

indicating the powerful performance of NN.

6.3.3 Testing Phase

Once the neural network is trained, testing is required to check the effectiveness or

accuracy of the network. During the testing (external validation), the NN model is used to

compute the Chloride concentration of soil samples, which are not involved in training

pattern. The results are given in table 6.4 and the performance of the network on this test

set is in good agreement with the measured results. The statistical results of the test data

set are given in table 6.5. Hence, it is confirmed that the neural network is properly

trained.

144

6.4 Results and Discussion

The predictability of the developed model has been quantified in terms of

correlation coefficient (R). The correlation between experiments and predicted results for

both the validation and test dataset has been shown by regression analysis in figure 6.1

and 6.2 respectively. It could be observed that a very good correlation between

experimental and predicted data set is obtained. No scattering in the data points could be

observed through out the whole data range, which shows the excellent predictability of

the model.

The table 6.6 gives the parameters of the designed neural network which is used to

predict the concentration of Chloride in soil samples. One hidden layer is found to be

adequate for the present problem. Neurons in the hidden layer are varied from 3 to 9.

Neurons more than 9 are not tried in order to avoid overfitting. The performance of the

model at different hidden neurons is shown in table 6.7. It could be observed that ANN

model with 6 hidden neurons produced best performance and is considered to be the

optimal configuration for the present problem.

Optimum number of neurons in the hidden layer plays a vital role in the Root

Mean Square Error (RMSE). Selection of neuron number based on the criteria of a

minimum divergence of training and test data during training curves and the lowest value

for RMSE of the test data. The RMS error for the neuron number in the hidden layer is

plotted in figure 6.3. From the figure, low RMS errors are observed if the neuron

numbers are six in the hidden layer. When this number exceeds, high RMS errors are

observed. More the RMS error, the predicted outputs are far away from the true or

measured value. Hence, six neurons are chosen in the hidden layer to reduce the RMS

error. This network needs 10,000 iterations to reach RMS error of 0.005 of the training

data, 0.003 for validation and 0.006 for the test data respectively.

The table 6.3 and 6.5 compares the statistical reports of the validation and testing

pattern computed using the neural network with that of measured results. The values of

Mean (±0.3), Standard error of mean (±0.05), Median (±0.25), Standard error of Median

(±0.05), Mean Deviation (±2.5), Standard Deviation (±4), Standard error of Standard

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Deviation (±0.1), Coefficient of Variation (±0.1) and Standard error of Coefficient of

Variation (±0.02) of the predicted results are very close to the values of the measured

results.

Table 6.1 Training pattern for soil Chloride computation

Distance

(km)

Soil Chloride

concentration

(ppm)

3 140

6 280

9 210

12 280

15 560

18 385

21 245

24 280

27 315

30 210

33 210

36 175

39 315

42 245

45 350

48 385

51 490

54 280

57 560

60 280

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Table 6.2 Validation data – Comparison between computed and measured results

Distance

(km)

Computed Chloride

concentration (ppm)

Measured Chloride

concentration (ppm)

9 208 210

15 557 560

21 242 245

24 279 280

30 208 210

39 311 315

42 242 245

48 384 385

51 486 490

57 557 560

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Table 6.3 Statistical reports of validation data set and measured results

Variables Validation Measured

Std.Dev 132.47 132.81

Std.Err of Std.Dev 29.62 29.69

mean value 347.4 350

Std.Err of Mean 41.89 42

median value 295 297.5

Std.Err. of Median 52.36 52.5

Mean Dev 118.88 119

Co-eff of variation 38.13 37.94

S.E of Co-eff of variation 8.52 8.48

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Table 6.4 Testing pattern – Comparison between computed and measured results

Distance

(km)

Computed Chloride

concentration (ppm)

Measured Chloride

concentration (ppm)

63 581 585

66 674 680

69 982 985

72 923 930

75 812 820

78 854 860

81 977 980

84 1002 1010

87 961 965

90 982 985

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Table 6.5 Statistical reports of testing data set and measured results

Table 6.6 Parameters used for the designed neural network

Variables Testing Measured

Std.Dev 137.97 137.73

Std.Err of Std.Dev 30.85 30.79

mean value 874.8 880

Std.Err of Mean 43.63 43.55

median value 942 947.5

Std.Err. of Median 54.54 54.44

Mean Dev 115.64 115

Co-eff of variation 15.77 15.65

S.E of Co-eff of

variation

3.52 3.49

Parameters Developed NN model

Topology 1- 6-1

Algorithm Back Propagation

Transfer function Sigmoid Activation

Epochs 10000

Validation Testing

RMSE 0.003 0.006

Correlation cofeeicient

(R)

0.99 0.98

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Table 6.7 Hidden neurons versus accuracy of the predicted results

Topology Accuracy of the

predicted results

(%)

1 – 3 - 1 97.5

1 – 4 – 1 97.9

1 – 5 – 1 98.3

1 – 6 – 1 99.1

1 – 7 – 1 98.9

1 – 8 – 1 98.2

1 – 9 - 1 97.8

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Figure 6.1 Linear regression between the validation results and measured results

152

Figure 6.2 Linear regression between the testing results and measured results

153

Figure 6.3 RMSE value for 1-6 neurons in hidden layer

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6.5 Prediction of Chloride in sea water using Artificial Neural Network

6. 5.1 Selection of input parameters

Two of the most important properties of sea water are temperature and salinity,

which have a major influence on ocean currents and behavior. Since Chloride is a major

constitute of saline water, and it directly affects Electrical conductivity, a close

correlation between the Electrical Conductivity and Chloride concentration is obtained

[1, 2]. Along with the physical parameters of temperature and Electrical conductivity, pH

has an important role in water quality measurements. To validate salinity, in this study,

the estimation of Chloride concentration in seawater is done, and it is computed with the

help of three physico- chemical parameters using Artificial Neural Network as a

prediction tool.

6.6 Sampling field description

The experimental site chosen is located at Manora (Thanjavur District) – Mimisal

(Pudukkottai District), Middle East coastal region, Tamil Nadu, South India (Figure 6.4).

The average temperature over the year varies from 26°c to 35°c and rainfall of 279mm. It

has a dry climate, with a long frost-free period and relatively high summer temperatures.

The water samples are collected at every 2kms from Manora over 100kms to Mimisal.

6.6.1 Measurement

The seawater samples are collected at the located sites and packed in an air

tightens PVC bags. To carry out the known input and output for training the neural

network model, measurements of pH and temperature are made in- situ using HI96107

(HANNA instruments) and thermometer respectively for the samples. To monitor the pH

value of seawater samples, the pH probe is calibrated using distilled water for all the

samples. After calibration, the probe is dipped into the sample and then the value is

taken. The Electrical Conductivity of the samples is measured using conductivity meter

(ELICO CM 180) and it is reported in terms of milli siemens per centimeter (mS/cm).

The Chloride concentration for the samples is measured using standard method of

titration.

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6.7 Back propagation neural network training

In this study, the neural network model with back propagation algorithm is used

to predict the concentration of Chloride. It has three input neurons, one output neuron and

hidden layer with five neurons. In the data used, pH varied from 8.1 to 9.3, the

temperature lies between 28ºC to 30ºC while the EC took the values of 25mS/cm to 34

mS/cm.

The back propagation algorithm uses sigmoid activation function f(x) = 1/(1+e-x).

The training is achieved using the equation 6.1 and the training pattern data is given in

table 6.8. Before the training of the neural network, the input and output parameters are

normalized. The transference functions used within each neuron layer were preset as

sigmoidal and linear for the hidden and output layers, in that order.

6.7.1 Genetic Algorithm based back propagation neural network training

Genetic algorithm based back propagation neural network offer good

generalization ability although it is difficult to determine the optimal network

configuration and network parameters. The architecture of GA based BPNN consists of

input layer with three neurons (pH, temperature, Conductivity), hidden layer with five

neurons and output layer with one neuron.

Genetic Algorithms (GAs) are search algorithms based on the mechanics of the

natural selection process (biological evolution) [3, 4]. During each temporal increment

(called a generation), the structures in the current population are rated for their

effectiveness as domain solutions, and on the basis of these evaluations, a new population

of candidate solutions is formed using specific genetic operators such as reproduction,

crossover, and mutation. The most basic concept is that the strong tend to adapt and

survive while the weak tend to die out. That is, optimization is based on evolution, and

the "Survival of the fittest" concept. GAs has the ability to create an initial population of

feasible solutions, and then recombine them in a way to guide their search toonly the

most promising areas of the state space. Each feasible solution is encoded as a

chromosome (string) also called a genotype, and each chromosome is given a measure of

fitness via fitness (evaluation or objective) function [5, 6]. In this method, the Neuro

156

solution software is used for the training and is done by selecting GA search for the input

parameters.

The various learning rules used to train the neural networks are Conjugate

Gradient method, Deltabardelta method, Momentum and Levenberg Marquadt method.

The data in Table 6.8 is trained using the above learning rule to find the better, which

reduces the error. In the case of conjugate gradient method the input gets diverged which

resulted in large error. The network when trained using delta bar delta and Levenberg

method converged quickly not able to result in minimum error. The only leaning rule,

which got converged quickly and resulted in minimum error, is momentum and hence

this is used to find the Chloride concentration. An iterative search for the optimum

learning rate and momentum is done in table 6.10. A suitable learning rate and

momentum factor can prevent the network from being trapped in local minimum error

surface. From table 6.10 the best learning rate and momentum are found to be 0.6 and

0.7 respectively with a hidden layer for various numbers of epochs.

6.7.2 Validation and testing pattern

The (internal) validation process is used to internally evaluate the fitness degree,

and it is used to stop training if the sum of residuals for this set, increases. This

precaution is aimed to prevent over fitting, and so, to accomplish good generalisation

ability, that is, good prediction ability for points not participating in training. In this

validation process, the trained network model is used to compute the concentration of

Chloride for the known input parameters. In table 6.9 (validation data), the input

parameters (pH, temperature, Electrical conductivity) for the seawater samples and their

Chloride concentration computed by the two models are compared with the measured

results. It is found that the computed results agree with the conventional method

(Titration), which shows the efficiency of the Artificial Neural Network model. During

the Testing (external validation), these simulated models are used to compute the

Chloride concentration of seawater samples, which are not involved in training pattern.

These results are plotted in a graph (Figure 6.5 - Testing pattern for 20 samples using GA

based BPNN vs Measured and Figure 6.6 - Testing pattern for 20 samples using BPA NN

versus Measured) with the measured results. The prediction method developed using

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Genetic Algorithm based Back propagation Neural Network is well suited for the

Chloride estimation of seawater and the prediction accuracy is proved with the help of

statistical studies.

6.8 Results and Discussion

The table 6.8 gives the Input and output data for thirty samples of sea water which

are used for training pattern. Table 6.9 gives the cross validation set of data where the

trained data are internally tested to check the ability of producing the output data. It is

found that the Chloride concentration computed using GA based BPNN method is in

good agreement with the measured results than that of BPA NN method. The testing

patterns of Chloride concentration of 20 seawater samples using the developed models

are shown in figure 6.5 and 6.6. It can be seen that there is no obvious difference

between those the predicted and measured results for GA based back propagation neural

Network.

6.8.1 Adaptiveness of the model

To check the adaptiveness of the model for various seasonal conditions, the

Chloride concentration is computed at various input parameters. The temperature input is

varied from 15° C to 45° C and the corresponding changes in pH and Electrical

conductivity are monitored by the use of probes. The Concentration also measured at

that particular variation in the inputs. As the temperature increases the Electrical

Conductivity and relatively Chloride Concentration also increases. But there is no

considerable variation is observed in the value of pH for the sample. It has to be noted

that during summer season (when the temperature is high) the concentration of Chloride

increases relatively with the Electrical conductivity and the reverse is observed during

winter season (when the temperature is low). The predicted Chloride concentrations for

various temperatures using the two methods are shown in figure 6.7 and figure 6.8. The

corresponding variation in Electrical conductivity is also plotted in figure 6.9 and Figure

6.10 for these methods. The continuous line (predicted) in the graph matched with the

dotted line (measured) for the method using GA based BPNN than that of Back

propagation Neural Network.

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6.8.2 Comparison between the results obtained using Genetic and Back propagation

algorithm

The table 6.11 compares the statistical reports of the testing pattern computed

using two models with that of measured results. The values of statistical parameters for

the GA based BP NN Method approaches the conventional method than the other

Method. The linear regression equation between the predicted and measured for GA

based back propagation Neural Network gave the slope of 1.07 and intercept of -1205 for

testing and for another model 1.07 and -1075. The Genetic Algorithm based BPNN well

correlated R= 0.98 (n=20) with that of the conventionally measured Chloride

Concentration than that of another model R= 0.85.

6.8.3 As an Effective Tool

The ANN method is a good prediction tool for the estimation of Chloride

concentration in seawater samples over the other methods like Chloride ISE, titrations,

and Ion chromatography which are time consuming and expensive. ISEs are accurate

when recently calibrated, but are sensitive to drift, and are not ideal for field monitoring.

Titrimetry methods can generate hazardous wastes that require proper disposal. Ion

Chromatography is an accurate laboratory method, but cannot produce real time data

needed for rapid decisions in the field. Using NN model, estimation of Chloride

concentration offers several advantages over currently available Chloride analysis

methods. This model provides more robust data sets for long-term projects such as salt-

water intrusion studies of coastal aquifers, salinity studies, salt marsh studies and coastal

wet lands monitoring projects.

6.8.4 Chloride Influence for aquatic organisms

Chloride concentration of sea water collected at various places varies from

14,000 to 16,900 ppm. It is maximum at Kattumavadi (Pudukkottai, Tamil nadu, South

India) and minimum at Mimisal (Pudukkottai, Tamil Nadu, South India). Chloride is a

common component of waters and is beneficial to fish in maintaining their osmotic

balance. In commercial fish production Chloride is often added to waters to obtain a

159

minimum concentration of 60 mg/l. This is done because fish are susceptible to “brown

blood” disease caused by excess Nitrite in the water. A ratio of Chloride to Nitrite of 10:

1 reduces Nitrite poisoning. High Chloride levels are a concern only if the water is also

used to irrigate sensitive land based crops.

Eels plasma Chloride ion concentration is easy to measure and is often used as an

indication of osmoregulatory status, on the assumption that it is proportional to total ionic

concentration. The plasma Sodium concentration minus Chloride concentration

difference is often used as a rough approximation to calculate strong ion difference (SID).

The gram positive, aerobic, moderately halophilic bacterium Halobacillus halophilus

(marine organism) is challenged in its environment by frequently changing salt

concentrations. H.halophilus is shown to be the first prokaryote that is dependent on

Chloride for growth. In a search for the biological function of Chloride in this prokaryote

different Chloride dependent processes are identified, which suggests a more general role

for Chloride in the metabolism of H. halophilus. In addition to growth, endospore

germination, activation of transport of the compatible solute glycine betaine, motility and

flagulum production has been identified as Chloride dependent processes. These very

different functions of Chloride suggest a more general role for Chloride in the physiology

of H.halophilus such as involvement in regulatory processes or interaction with the

environment.

The transformation from salt stressed halo tolerant organism to moderate

halophile was accompanied by the change of an inducible stress regulon to a constitute

regulon strictly required for growth; gene expression and protein production can now

occur optimally only at “high” salt concentrations, which results in the strict salt

dependence of growth. If the salt concentration falls below a certain threshold, then

growth is impaired due to the lack of gene expression.

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6.9 Conclusion

The neural network with back propagation algorithm is designed to compute

Chloride concentration in soil samples which are collected from Thanjavur to

Nagapattinam, Tamil Nadu, South India. The accuracy of the computed results is

confirmed by the comparison of statistical reports between the measured data and the

computed data. The soil salinity can be determined using the soil Chloride concentration

and it is used for the plantation and cultivation of proper crops, vegetables and fruits.

The Electrical Conductivity, pH, temperature are measured and the data are used

for training the neural networks (GA based BPNN and BPA NN). From the trained neural

network, the Chloride concentration of sea water samples of Middle East coastal region,

Tamil Nadu, South India is computed. It is observed that the Genetic algorithm based

back propagation neural network method tracked the experimental data very closely than

back propagation algorithm to estimate the Chloride concentration. The performance of

the network is obviously dependent on the quality and completeness of data provided for

system training. Using Chlorinity, it is easy to determine the salinity of the seawater,

which took great effect on ocean environmental monitoring system. It is observed that,

BPA NN learning is very fast, but the accuracy is inadequate. Whereas, GA based BPNN

iteration took long time compared to that of BPA, but the accuracy is good enough

having the learning rate of 0.6 and momentum of 0.7 layer for 30 000 epochs.

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Table 6.8 Training pattern of 30 samples for GA based BPNN method and BPA NN

method

Sample

i.d

pH T

(° C)

EC

(mS/cm)

Cl- Con

(ppm)

Sample

i.d

pH T

(° C)

EC

(mS/cm)

Cl- Con

(ppm)

1 8.1 30 30 15744 16 8.8 30 30 16173

2 8.6 28 29 15035 17 9.0 30 30 15957

3 8.8 30 28 16311 18 9.0 30 30 15937

4 8.6 30 30 16382 19 9.0 30 30 16453

5 8.8 30 32 16666 20 8.8 30 28 15531

6 8.8 30 29 16169 21 8.9 30 29 15460

7 8.8 30 31 15957 22 9.3 28 29 16098

8 9.0 30 31 15531 23 9.2 28 29 15247

9 9.2 30 33 15460 24 9.1 28 30 16670

10 9.2 30 33 15389 25 9.1 28 28 16878

11 8.6 30 28 15673 26 9.1 28 29 15460

12 8.7 30 34 16169 27 9.1 28 29 15035

13 8.7 28 28 16453 28 9.1 28 27 14983

14 8.8 28 28 16595 29 9.1 28 26 14751

15 8.8 28 29 16524 30 9.0 28 25 14254

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Table 6.9 Validation (Internal) using GA based BPNN method and BPA NN method

Chloride Concentration (ppm) Input Parameters Sample

i.d

pH T(° C) EC

(mS/cm)

Measured Using GA

based BPNN

method

Using

BPA NN

method

3 8.8 30 28 16311 16248 15981

7 8.8 30 31 15957 15906 16356

14 8.8 28 28 16595 16515 16466

17 9.0 30 30 15957 16099 16126

23 9.2 28 29 15247 15167 15223

29 9.1 28 26 14751 14758 14862

Table 6.10 Hidden Layer with various learning rates and epochs for GA based

BPNN

Hidden Layer S.No

Learning rate Momentum

Epochs Error

Percentage

1 1 0.7 1,000 27.8

2 0.4 0.7 20,000 24.4

3 0.4 0.7 30,000 2.7

4 0.5 0.7 30,000 3.5

5 0.3 0.7 30,000 2

6 0.4 0.7 30,000 0.5

7 0.5 0.7 30,000 0.47

8 0.6 0.7 30,000 0.37

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Table 6.11 Statistical Results of the computed data (Testing) for 20 samples

Parameters Measured GA based BPNN

Method

BPA NN Method

Mean Value 16059 15961 15861

Std Err of Mean 145.22 143.53 136.66

Median Value 16204.5 16079.5 16112.5

Std Err of Median 181.52 179.42 170.83

Mean Dev 503.805 473.8 500.82

S. D 649.44 641.91 611.19

Std err of S.D 102.68 101.49 96.63

Co-eff of Variation 4.04 4.02 3.85

S.E of Co-eff of Var 0.639 0.635 0.609

164

Figure 6.4 Site map for sampling field

165

Figure 6.5 Testing pattern for 20 samples using GA based BPNN vs Measured

12500

13000

13500

14000

14500

15000

15500

16000

16500

17000

17500

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20

No of Samples

Chl

orid

e C

once

ntra

tion(

ppm

)

Computed

Measured

166

Figure 6.6 Testing pattern for 20 samples using BPA NN versus Measured

12500

13000

13500

14000

14500

15000

15500

16000

16500

17000

17500

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20

No of Samples

Chl

orid

e C

once

ntra

tion(

ppm

)

Computed

Measured

167

Figure 6.7 Prediction of Chloride concentration for various temperatures using GA

based BPNN method (Sample id: 5)

168

Figure 6.8 Prediction of Chloride concentration for various temperatures using BPA

NN method (Sample id: 5)

169

Figure 6.9 Prediction of Chloride concentration for various Electrical Conductivity

using GA based BPNN method (Sample id: 5)

170

Figure 6.10 Prediction of Chloride concentration for various Electrical Conductivity

using BPA NN method (Sample id: 5)

171

References

1. Cristina Windsor, Rob Mooney, Verifying the use of specific conductance

as a surrogate for Chloride in seawater marices. Naples, Florida, USA, June (2008).

2. Hamid Zare Abyaneh, Nazemi A.H., Neyshabori M.R., Mohammadi K.,

Majzoobi G.H., Tarim bilimleri dergisi, , 11-1(2005), 110-114.

3. Asif Ullah Khan T. K., Bandopadhyaya , Sudhir Sharma, IJCSNS International

Journal of Computer Science and Network Security, 8-7(2008).

4. Diamonto poulou M.J., Antonopoulos V.Z., Papamichail D.M., European water,

11-12(2005), 55-62.

5. Whitley, A Genetic Algorithm Tutorial, Technical report CS, Dept of Comp Sci,

Colorado State University, (1993), 93-103.

6. Azedine Charef, Antoine Ghauch, Patrick Baussand, Michel Martin-Bouyer,

Measurement , 28 (2000), 219-224.

172

CHAPTER VII

PREDICTION OF RATE OF CORROSION IN MILD STEEL

In this chapter, the negative effect of Chloride which causes corrosion on the

surface of steels is explained. The corrosion behavior of mild steel in hydrochloric acid is

investigated by the use of Weight loss measurement method. A neural network with back

propagation algorithm is employed to compute the Rate of Corrosion for mild steel at

various aqueous environments (pH, temperature, Chloride concentration). Fifty data set

are used for training, validation and testing of neural network. The effect of pH,

temperature and Chloride concentration on corrosion also discussed.

7.1 Introduction

The corrosion of metals remains a world-wide scientific problem as it affects the

metallurgical, chemical and oil-industries. The increasing interest in the manufacture of

hydrochloric acid has created the need for obtaining information on the corrosion

resistance of mild steel to hydrochloric acid attack [1, 2]. Mild steel corrosion in acid

solution has been effectively controlled by the use of organic substances containing

nitrogen, oxygen, or sulphur in the conjugated system as inhibitors [2-4].

Mild steel finds application in many industries due to its easy availability, ease of

fabrication, low cost and good tensile strength besides various other desirable properties.

It suffers from severe corrosion when it comes in contact with acid solutions during acid

cleaning, transportation of acid, de-scaling, storage of acids and other chemical

processes. The heavy loss of metal as a result of its contact with acids can be minimized

to a great extent by the use of corrosion inhibitors. Hydrochloric acid is the most difficult

of the common acids to handle from the standpoints of corrosion and materials of

constructions. Extreme care is required in the selection of materials to handle the acid by

itself, even in relatively dilute concentrations or in process solutions containing

appreciable amount of hydrochloric acid. This acid is very corrosive to most of the

common metals and alloys. Metals are exposed to the action of acids in many different

ways and for many different reasons. Processes in which acids play a very important part

are [4], Acids pickling, industrial acid cleaning and oil well acidizing in order to

173

stimulate of oil well. One of the most commonly used acids in today’s industrialized

world is hydrochloric acid HCl, where some of its applications include chemical cleaning

and processing, acid treatment of oil wells and other applications.

Corrosion by Chloride can occur by the following ways: (i) Chlorides are held

to pass through the protective oxide film, which exists on the steel surface in a high pH

environment, hence, depassivating the steel (ii) adsorption of Chlorides on the steel

surface and thus promoting the hydration of metal ions and facilitating depassivation and

(iii) it is supposed that Chlorides are able to compete with hydroxyl ions for the ferrous

ions produced by corrosion process. The effect of temperature on a chemical reaction is

of practical and theoretical important. Like most chemical reactions, the rate of corrosion

of iron and steel increases with temperature especially in media in which evolution of

hydrogen a companies corrosion, e.g. during corrosion of steel in acids. With increasing

temperature, the contribution of Chloride increases but the effect of hydrogen decreases

due to its increased mobility in the ferrite matrix. The most significant environmental

conditions, which influence the corrosion behavior of steels, are the Chloride ion

concentration, temperature and pH. Reliable prediction of the Rate of corrosion behavior

is the fundamental step towards effective control of Corrosion.

Artificial Neural Network (ANN) technique [5] is suited for the problem that

involves non linear interpolation. Ability to learn by example makes neural network

flexible and powerful [6]. In recent past, ANN has been successfully applied to model

various corrosion behaviors [7-10]. A neural network model using back propagation

algorithm has been used to predict the Rate of corrosion of mild steel with three input

neurons of pH, temperature and Chloride concentration. Out of Fifty data set, thirty data

set of Rate of corrosion of mild steel (by Weight Loss measurement) has been taken for

training set. Nine data set are used for validation from the training pattern. Twenty data

set is used for testing pattern. A good correlation between experimental and predicted

data is obtained, which shows a high prediction capability of neural network.

174

7.2 Experimental procedures

7.2.1 Materials

Mild Steel specimens are cut to size of 5 x 1 cm from mild steel sheets having the

percentage composition: Fe = 99.686, Ni =0.013, Cr=0.043, S=0.014, P=0.009, Si=0.007,

Mn=0.196 and C = 0.017. The surfaces of specimens are polished with emery papers

ranging from 110 to 410 grades. The hydrochloric acid with various concentrations of

0.1N, 0.15N, 0.2N, 0.25N, 0.3N, 0.35N, 0.4N, 0.5N and 0.75N with pH from 0.12 to 1

are prepared. All the solutions are prepared with AR grade chemicals in double distilled

water.

7.2.2 Method- Rate of corrosion by Weight loss measurement

Weight loss measurements are performed as per American Society for Testing

and Materials (ASTM) method [11] to determine the Rate of corrosion. The polished

mild steels are initially weighed in an electronic balance. After that the specimens are

suspended with the help of thread and glass rod in 100 ml beaker containing hydrochloric

acid having concentration range from 0.1N to 0.75N with pH (0.12-1) at different

temperature varied from 290K to 333K. The specimens are removed after 4 hours

exposure period. They are dried and reweighed to determine the Rate of corrosion.

Rate of corrosion (mmpy) = Density of mild steel x loss in weight (mg) x time (h)

Area of mild steel (cm2)

Density of mild steel = 87.6

Loss in weight = Final weight (mg) – Initial weight (mg)

Time (h) = 4 hours; Area of mild steel = 5 x 1 cm

7.3 Explicit Neural Network formulation for Rate of Corrosion

The neural network architecture that proved able to solve the problem has three

input neurons, one output neuron and one hidden layer with ten processing elements

(neurons). In the input data used, the temperature lies in the interval of 290K to 333k, the

Chloride concentration ranges from 0.1N to 0.75N while the pH values are in the range of

0.12 to 1. The Rate of corrosion calculated from weight loss measurements method is

used as output parameter. The input – output neuron architecture is shown in figure 7.1.

Out of 50 data set, 30 data set are used to train the NN while the remaining is used for

testing. Since test data set are not used for training, it essentially verified the ability of

175

any ANN model to associate and generalize a true physical response, which is unknown

to the network.

7.3.1 Training pattern

Before the execution of the training process of neural network, the input and

output parameters were normalized in the range of (-0.95; 0.95) via in order to acquire

accurate results. The generalized delta rule uses sigmoid activation function f(x) = 1/

(1+e-x). The learning is achieved through the equation 6.1 (Chapter VI). The training

pattern is given in table 7.1.

The error between computed results and expected results are decreased with

increasing epochs and training for learning is finished within a target convergence. One

hidden layer is found to be adequate for the present problem. Neurons in the hidden layer

more than 12 are not tried in order to avoid overfitting. It could be observed that ANN

model with 10 hidden neurons produced best performance and is considered to be the

optimal configuration for the present problem. An iterative search for the optimum

learning rate and epochs is done in table 7.2. A suitable learning rate can prevent the

network from being trapped in local minimum error surface. From table 7.2, the best

learning rate is found to be 0.6 with a hidden layer for 30,000 epochs.

7.3.2 Validation of the proposed NN model

In this part of the study, the developed NN model is verified through the relevant

data obtained from experimental. For this, 9 data are selected randomly from the trained

data (Table 7.1) as seen in table 7.3. Then, these data are evaluated using the developed

model. To demonstrate the robustness and generalization capability of the model, the

statistical test results of validation data set are also given in table 7.4. It is observed that

there is a significantly high compromise between the experimental and the developed

model indicating the powerful performance of NN Model.

7.3.3 Testing pattern

To make sure that the network has not just memorized the training data but really

extracted the general features of the problem, new test data which are not included in the

training set, are presented to the NN. If the performance of the network on this test data

set is satisfactory, the network can be assumed properly trained and is ready to be used.

During the testing (external validation), the simulated model is used to compute the Rate

176

of corrosion of mild steel samples for various pH and Chloride Concentration at the

temperatures of 318K and 333K, which are not involved in training pattern. These results

are plotted in a linear regression pattern (Computed versus Experimental Results) which

is shown in figure 7.2 and figure 7.3 for the temperatures 318K and 333K respectively.

7.4 Results and Discussion

7.4.1 Performance of the developed model

A high prediction capability is achieved for testing data set even though it is not

employed in the training of the NN. The overall performances of validation data set and

testing data set are evaluated via mean absolute percentage error and the correlation

coefficient R which is shown in table 7.5. As seen in table 7.5, high correlation

coefficient 0.99 is achieved for both validation and testing data sets. Moreover the model

provided highly reasonable mean absolute percentage errors 1% and 2% for the

validation and testing data sets respectively. The results of testing phase in figure 7.2 and

7.3 indicated that the NN appears to have a high generalization capability between the

input variables and the output response.

7.4.2 Effect of Chloride content

Weight loss measurement has been used in the present study to determine the Rate

of corrosion. The variation of corrosion rate of mild steel with Chloride ion

concentration in acidic environment is shown in figure 7.4, which shows that Rate of

corrosion increases with increase in Chloride concentration at 290K temperature. It is

because of Chloride ions are highly aggressive for mild steel due to very high solubility

of iron Chloride. In this study, the range of Rate of corrosion varied from 1.396 mmpy to

507.91mmpy by varying Chloride concentration from 0.1N to 0.75N and temperature

from 290K to 333K. It has been suggested that corrosion occurred as a result of

adsorption of aggressive anions on film followed by penetration of this film under the

influence of an electrostatic field [12].

7.4.3 Effect of pH and temperature

Figure 7.5 shows the dependence of corrosion on the pH at 290K temperature. It

could be observed that the Rate of corrosion increases with decrease in pH. This strong

influence of pH on the Rate of corrosion of mild steel could be attributed to the result of

acceleration of Cathodic reaction due to high concentration of hydrogen ions.

177

Figure 7.6 shows that corrosion increases with increase in temperature (290K,

303K, 310K, 318K and 333K) at 0.75N Chloride concentration. The results indicate the

possibility of a temperature induced change in the mild steel surface. The defect

structure of semiconductor Fe-Cr-Ni alloys may change from p-type to n-type with

temperature. It has been argued that n-type films could be more susceptible to corrosion

initiation than p-type films due to the existence of oxygen vacancies. This may enhance

the transport of Chloride ions through the oxide lattice [13, 14]. It could be observed that

almost a linear relationship has been obtained between Rate of corrosion and

temperature. The gradient of the Rate of corrosion versus temperature curves varied

between 1.39 Mmpy to 507 mmpy over the whole range of Chloride concentration and

pH. The combined influence of Chloride concentration and pH on Rate of corrosion at

the temperatures 290K, 303K and 310K is shown in figure 7.7, figure 7.8 and figure 7.9

respectively. It could be observed that the Rate of corrosion increases with the decrease

in pH, and increase in Chloride concentration.

The above analysis suggests that the developed ANN model can efficiently

simulate the intricate inter relationship between the Rate of corrosion and various

environmental parameters viz. Chloride concentration, pH and temperature. The model

in turn would help to predict the Rate of corrosion of mild steel as a function of the above

environmental parameters with a high degree of accuracy and reliability.

7.5 Conclusion

Mild Steel is subjected to Weight loss measurement tests in various aqueous

environments by varying Chloride concentration (0.1N to 0.75N), pH (0.12 to 1) and

temperature 290K to 333K. A three layer neural network model with back propagation

algorithm is employed to predict the Rate of corrosion of mild steel with three input

parameters (pH, Chloride Concentration and Temperature). The developed model is fast

and is able to produce an output that has minimum error. On modeling with neural

network, a good correlation between experimental and predicted data is obtained. The

correlation coefficient of the validation and test data is 0.998 and 0.99 respectively,

which reflects the excellent predictability of the model. Besides, it is seen that by

increasing Chloride concentration and temperature and decreasing pH are found to

increase the Rate of corrosion.

178

Table 7.1 Input and output data base of training set

Temperature

(K)

pH Chloride

concentration (N)

Rate of corrosion

(mmpy)

1 0.1 1.39 290

0.82 0.15 1.54

0.69 0.2 1.78

0.60 0.25 1.92

0.52 0.3 2.12

0.45 0.35 2.24

0.39 0.4 2.39

0.34 0.45 2.46

0.30 0.5 2.52

0.12 0.75 3.86

1 0.1 2.56 303

0.82 0.15 2.71

0.69 0.2 2.89

0.60 0.25 3.18

0.52 0.3 3.34

0.45 0.35 3.51

0.39 0.4 3.72

0.34 0.45 4.08

0.30 0.5 4.27

0.12 0.75 6.46

1 0.1 63.74 310

0.82 0.15 78.23

0.69 0.2 85.56

0.60 0.25 93.87

0.52 0.3 116.52

0.45 0.35 125.86

0.39 0.4 138.29

179

0.34 0.45 146.48

0.30 0.5 152.32

0.12 0.75 225.18

Table 7.2 Hidden Layer with various learning rates and epochs for BPA NN method

Learning Rate Epochs Error

Percentage

1 1,000 24.8

0.4 20,000 21.4

0.5 30,000 3.7

0.5 30,000 1.5

0.3 30,000 3

0.4 30,000 0.5

0.5 30,000 0.46

0.6 30,000 0.33

180

Table 7.3 Validation set of the developed NN model

Rate of Corrosion (mmpy) Temperature (K)

pH Chloride Concentration (N) By

Experimental By Neural Network

290 0.60 0.25 1.92 1.98

0.12 0.75 3.86 3.78

0.34 0.45 2.46 2.16

303 0.69 0.2 2.89 2.83

0.39 0.4 3.72 3.66

0.30 0.5 4.27 4.47

310 1 0.1 63.74 63.66

0.52 0.3 116.52 115.91

0.45 0.5 152.32 151.87

Table 7.4 Statistical results for the validation data set

Statistical parameters Experimental results Neural network results

Mean 39.07 38.92

Std Err of Mean 18.31 18.25

Median 3.86 3.78

Std Err of Median 22.89 22.81

Std Dev 54.93 54.75

Std Err of Std Dev 12.94 12.90

Mean Deviation 47.85 47.70

Coeff of Variation 140.58 140.66

S.E of Coeff of Variation 33.13 33.15

181

Table 7.5 Performance of the NN model

Parameters Validation Test set

Error% 1% 2%

R 0.99 0.99

Slope - 0.991 at 318K 0.995 at 333K

Intercept - 2.66 at 318K 0.818 at 333K

182

Figure 7.1 Input – Output neuron architecture

183

Figure 7.2 Predicted Rate of Corrosion from the Neural Network versus

Experimental results at 318K

184

Figure 7.3 Predicted Rate of Corrosion from the Neural Network versus

Experimental results at 333K

185

Figure 7.4 Variation of Rate of Corrosion with Chloride concentration at 290K

0

0.5

1

1.5

2

2.5

3

0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5

Chloride Concentration (N)

Rat

e of

Cor

rosi

on (

mm

py)

186

Figure 7.5 Variation of Rate of Corrosion with pH at 290K

0

0.5

1

1.5

2

2.5

3

1 0.82 0.69 0.6 0.52 0.45 0.39 0.34 0.3

pH

Rat

e of

Cor

rosi

on (

mm

py)

187

Figure 7.6 Variation of Rate of Corrosion with Temperature at 0.75N

0

100

200

300

400

500

600

290 303 310 318 333

Temperature

Rea

te o

f C

orro

sion

(m

mpy

)

188

Figure 7.7 Combined influence of pH and Chloride concentration on Rate of

Corrosion at 290K

189

Figure 7.8 Combined influence of pH and Chloride concentration on Rate of

Corrosion at 303K

190

Figure 7.9 Combined influence of pH and Chloride concentration on Rate of

Corrosion at 310K

191

References

1. Abiola O. K., Oforka N. C., Corrosion Science and Engineering, 3(2002), 1.

2. Noor E. A., Corrosion Science, 47(2005), 33

3. Langrenee M., Mernari B., Bauanis M., Traisnel M., Bertiss F., Corrosion Science,

44 (2002), 573.

4. Libin Tang, Xueming Li, Guannan Mu, Lin Li and Guangheng Liu, Applied Surf. Sci.,

253(2006), 2367-2372.

5. Sha W., Edwards K.L., Mater Design, 28(2007), 1747.

6.Yilmaz Muharrem, Metin Ertunc H., Mater Design, 28(2007),599.

7.Cottis R.A., Qing Li , Owen G., Gartland S.J., Helliwell I.A., Turega M., Mater Design,

20(1999),169.

8. Smets H.M.G., Bogaerts W.F.L., Mater Design, 13(1992), 149.

9. Malinov S., Sha W., Mater Sci Eng A, 365(2004), 202.

10.Parthiban Thirumalai, Ravi R., Parthiban G.T., Srinivasan S., Ramakrishnan K.R.,

Raghavan M., Corros Sci, 47(2005),625.

11. Saratha R., Vasudha V.G., E-Journal of Chemistry, 6-4(2009), 1003-1008,

12. Hoar T.P., Mears D., Rothwell G., Corros Sci, 5(1965), 279.

13. Manning P.E., Duquette D.J., Corros Sci, 20(1980), 597.

14. Bianchi G., Cerquetti A., Mazza F., Torchio S., International conference on localized

corrosion, (Stachie R.W., Brown B.F., Kruger J., Agrawal A. editors), NACE,

Houston TX, (1974)., 399.

192

SUMMARY, CONCLUSION AND SUGGESTIONS FOR FUTURE WORK

Summary and Conclusion

Measurement and analysis using embedded system is the ever-growing

phenomenon in the field of research and development. Advances in electronics

technology and innovative manufacturing processes have driven the semiconductor

industry towards extensive miniaturization and ever greater integration of chip design.

Embedded systems have three common principles: real-time performance, low power

consumption and low price (limited hardware). Embedded computers use chip

microprocessors (CMPs) to meet these expectations. The aim of this study is to explore

various ways to increase performance, as well as reducing resource usage and energy

consumption for embedded systems. In this thesis, a primary anion Chloride, an essential

electrolyte has been measured and analysed using the designed and developed

Microcontroller based bio-analyser. The biological and environmental samples are taken

for the Chloride measurement and analysis. The microcontroller P89C668 based bio-

analyser is used for the determination of Chloride in human urine samples. After

measurement using embedded system, the effect of hyperchloremia and hypochloremia

are discussed using the obtained results. An implementation of embedded based bio-

analyser (P89C51RD2) has been used to determine the Chloride concentration in

pharmaceutical sample of Oral Rehydration Salts (ORS) too. The results arrived are

compared with the other analytical technique (ISE) to confirm the accuracy of the

developed embedded based bio-analyser.

Designing high performance and low power embedded systems with various

constraints and limited resources has become an important research problem. Three

embedded based bio-analysers using three different microcontrollers (P89C668,

PIC16F877 and PSoC CY8C27443) are designed and developed and their performance is

studied. A comparative study has been done to find the high performance and low power

bio-analyser to measure serum Chloride. The Microcontroller P89C668 (Philips) with

external Amplifier (LM108), Analog to Digital converter (MCP3202), the

microcontroller PIC16F877 (Microchip) with external Amplifier (LF353) and built – in

193

Multiplexer and Analog to Digital Converter and the microcontroller PSoC CY8C27443

(Cypress) with built in Amplifier, Multiplexer and Analog to Digital converter are the

three different microcontrollers which are taken for the comparative study. The accuracy

of the developed embedded based bio-analysers is analysed by evaluating various

analytical parameters (linearity, sensitivity, precision, recovery, statistical analysis). In

addition to the various features of the microcontrollers their power consumption and their

processing time (speed) also compared. From the comparative study, it is found that the

power consumption is less for PSoC (CY8C27443) (recent breakthrough in technology)

based bio-analyser because of built-in digital and analog peripherals. PIC16F877 based

bio-analyser consumes more power than the other two bio-analysers. The power

consumption of P89C668 based bio-analyser is slightly higher than that of PSoC based

bio-analyer. Considering the processing time, it is high for PSoC which means less speed

bio-analyser comparing with that of the other two. But the processing time is less (high

speed) for PIC16F877 based bio-analyser. For P89C668 based bio-analyser the

processing time is slightly higher than that of PIC16F877 based bio-analyser.

The designed Instruments are user friendly, economic, sensitive, reliable and easy

to adaptive for the measurement of Chloride in samples. The implemented system is

employed for the measurement of Chloride on laboratory standard with 96% confidence

level.

Electrical conductivity can be used as a surrogate for the Chloride concentration

determination. Hence, a linear regression model is developed correlating Electrical

conductivity and Chloride concentration. In this case, soil sample is taken for the

determination of Chloride which played an important role in the plant growth. Linear

regression model is developed by collecting 30 soil samples at every 3 kms from

Thanjavur to Nagapattinam over 90kms. The Electrical Conductivity is measured by

using ATmega32 microcontroller based instrument set up. The results obtained are

verified with the commercial instrument. The Chloride concentration can be determined

using the linear regression equation. The Chloride concentration of soil samples at

various places and their plant growth are discussed. The Electrical Conductivity

determination has replaced the tedious Chemical methods for the Chloride determination

and can be easily handled by irrigators and farm managers.

194

The Artificial Neural Network technology is a robust Artificial Intelligence

technology that can handle Non-linear problems. In this research work ANN is used for

the computation of Chloride in environmental samples. The proposed ANN implements a

Multilayer perceptron architecture featuring an input layer, hidden layer and output layer.

In order to find the optimum topology of the ANN model, several parameters have been

changed during the training process including the number of hidden layers, number of

neurons, learning factor, and number of training iterations. The Neural Network is trained

with the data is verified by performing validation and testing. The results of the testing

pattern are compared with the measured (conventional method) results. The predicted

results and the measured results have clearly demonstrated that ANNs are not only

promising but also an acceptable approach for the prediction of Chloride in samples.

ANNs have been used for the prediction of Chloride in environmental samples of soil and

sea water. In the case of soil samples, 30 samples are collected at every 3 kms from

Thanjavur to Nagapattinam over 90kms. The ANN architecture consists of one neuron in

Input layer, 6 neurons in hidden layer and one neuron in output layer. ANN computation

with distance as input parameter and Chloride concentration as output parameter. It is

found that ANN model with 6 neurons in the hidden layer produced the best performance

and is considered to be the optimal configuration for the prediction of Chloride in soil

samples. This network needs 10,000 iterations to reach RMS Error of 0.005 for the

training data and 0.006 for the test data respectively.

In the case of sea water samples, pH, Electrical Conductivity and Temperature are

used as input parameters and Chloride concentration as output parameter. The sea water

samples are collected at every 2kms from Manora (Thanjavur District) over 100kms to

Mimisal (Pudukkottai District), Middle East coastal region, Tamil Nadu, South India.

The NN is trained with Genetic Algorithm based Back propagation Neural Network and

Back Propagation algorithm. The prediction using GA based BPNN is well suited for the

Computation of Chloride in sea water. The adaptiveness of the model is checked by

varying the input parameters. As the temperature increases Electrical Conductivity and

relatively Chloride concentration also increases. But there is no considerable variation is

observed in the value of pH of the sample. Statistical studies and Linear regression

analysis are performed to confirm the accuracy of the predicted results.

195

Considering the negative aspects of Chloride, it causes corrosion on materials. In

this study, the corrosion effect on Mild steel is observed. For that, the corrosion behavior

of mild steel in Hydro Chloric Acid is investigated by weight loss method. The Rate of

corrosion is computed for the Input parameters of Chloride concentration, pH and

Temperature. ANN with BPA is used for the prediction of rate of corrosion. Effect of

Chloride concentration, Effect of pH and temperature are also discussed. The correlation

coefficient of validation and test data is 0.99 and 0.98 reflects the excellent predictability

of the NN model.

Suggestions for future work

In future, the developed bio-analyser can be used to measure other cations of

Sodium, Potassium, Calcium and Magnesium by changing the source and reagent. It is

also aimed that the developed instrument can be used to determine the cation and anion in

all biomedical samples like plasma, blood, sweat and Cerebro spinal fluid (CSF) etc as an

in-situ measurement system. The sensitivity of the instrument can be increased by using

higher ADC. In the case of Neural Network computation, the number of input data can

be increased for training to improve the prediction accuracy. The learning time can be

reduced by using various learning algorithms. Further, it is also decided that the

developed Neural Network can be used to compute the analyte concentration over wide

area of the country.

Sensors & Transducers Journal, Vol. 119, Issue 8, August 2010, pp. 142-150

142

SSSeeennnsssooorrrsss &&& TTTrrraaannnsssddduuuccceeerrrsssISSN 1726-5479© 2010 by IFSA

http://www.sensorsportal.com

Development of Bio-analyzer for the Determinationof Urinary Chloride

1R. Vasumathi , 2*P. Neelamegam 1Department of Physics, A.V.V .M Sri Pushpam College,

Poondi, Thanjavur, Tamilnadu India, 613503 2*Department of Electronics and Instrumentation Engineering, SASTRA University,

Thanjavur, Tamilnadu, India*E-mail: [email protected]

Received: 5 March 2010 /Accepted: 17 August 2010 /Published: 31 August 2010

Abstract: A high performance Microcontroller P89C668 based Biomedical Analyzer to measure the Urinary Chloride Concentration is designed and developed. The implemented system incorporates light source, Photodiode GASPG1104, Sample holder, LCD for displaying patient test results and key board for executing functions. The details of the interfacing circuit and the software to compute the concentration of Chloride ion is explained in this paper. To determine the run to run precision of the implemented system, human control serum AccutrolTM Normal (Sigma) is analyzed and the Chloride concentration is found to be 10 4± mmol/l (mean ± SD, n=5), which closes to the certified value. Goodrecovery results are obtained with the range of 98 % to 99 %. The results obtained using the designed instrument is in agreement with those obtained by the clinical analyzer. The sensitivity and linearity of the microcontroller based instrument are high enough to determine the concentration of Chloride ion without any significant interference. Copyright © 2010 IFSA.

Keywords: Chloride ion, Colorimetry, Bio-analyzer, Urine sample.

1. Introduction

Chloride is an essential electrolyte for human which occurs primarily in body fluids. This anion is specially transported into the gastric lumen, in exchange for another negatively charged electrolyte (bicarbonate) in order to maintain electrical neutrality across the stomach membrane. After utilization in hydrochloric acid, some Chloride ion is reabsorbed by the intestine, back into the blood stream

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where it is required for maintenance of extra cellular fluid volume [1]. Since, Chloride is a highly mobile ion that easily crosses cell membranes and is involved in maintaining proper osmotic pressure, water balance and acid–base balance. Several studies have suggested that the Chloride ion may play a more active and independent role in renal function, neurophysiology and nutrition. Body Chloride concentrations are regulated by excretions, primarily via the kidneys [2, 3]. Assessing the urinary composition is an important aid in the diagnostic evaluation of metabolic alkalosis.

Over the years, numerous analytical methods for Chloride in a variety of samples have been developed. Such as Ion Chromatography [4, 5], near infrared Spectrometry [6], Spectroscopy [7], Ion Selective electrode method [8], turbidimetric method [9] and so on. Among these methods, the turbidimetric method was popular and regarded relatively reliable for the quantification of Chloride. Although it often provided very accurate results, it suffered from the long experimental time, lower sensitivity, and complexity. Partly, because of lower sensitivity, few of the above methods were applied to determine Chloride in biological systems. The ISE is currently used in Chloride analysis in Biological samples. Nevertheless, these methods suffered from the drawbacks of time consuming, expensive and inapplicability to low Chloride containing samples. Colorimetry is one of the simplest and best techniques which have been used for the clinical routine assays. Hence, an inexpensive, simple and accurate Microcontroller P89C668 based Instrument has been designed and developed to measure the absorbance and hence the concentration of Chloride in Serum samples, with the results comparable with a commercial Clinical analyzer.

2. Instrumental

The signal conditioning circuit of the P89C668 microcontroller based instrumentation system is shown in Fig. 1, which measures the concentration of Chloride ion based on colorimetry principle.

According to this principle, a colorimeter measures the intensity of light shining through a coloured solution compared to the intensity of light passing into the solution. A detector measures the transmittance (T) (% of light passing through) of the solution and it is mathematically converted to absorbance (A= -log 10 T). The absorbance is directly proportional to the concentration (Beer-Lambert law) [10, 11]. The developed instrumentation system incorporated with Green LED (480 nm) as the source for measuring Chloride ion concentration. The photo detection assembly is well insulated from outer light. It has a sample holder to hold the solutions like blank, standard and sample test tubes. A photo diode of GASPG 1124 is used to detect the amount of light falling on the sample. The output signals are fed to OP-AMP CA3041, which is connected to the pin 13 of multiplexer CD4051. The temperature sensor LM35D is connected to the pin 14 of CD4051 (Fig. 1). The LM35D is a precision semiconductor temperature sensor giving an output of 10mV per degree centigrade. It is capable of measuring temperature between +2 °C and +100 °C. The output is proportional to degree centigrade. It has low current drain and low self-heating. The multiplexer (pin 3) is connected to ADC MCP3201 through pin 2, to convert analog signals to digital value [12]. IC MCP3201 is a successive approximation type 12 bit serial A/D converter compatible with the SPI protocol, sample rate of 100ksps at clock rate of 1.6 MHz and operates over broad voltage range of 2.7-5.5 V. The pin 10 (A) and 11 (B) of multiplexer are connected to pin 18 (P2.0) and 19 (P2.1) of Microcontroller P89C668 to select either temperature measurement or concentration measurement. The ADC is interfaced with pin 42, 43, 44 of Microcontroller P89C668 for computing urinary Chloride concentration. The microcontroller P89C668 is a quad flat package (44pins) 8 bit controller which has four I/O ports and three 16bit timer/counters. The data lines of LCD display is interfaced with Port 0 of Microcontroller. RD and WR of the Microcontroller are connected to LCD as shown in Fig. 2.

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Fig. 1. Signal conditioning circuit.

Fig. 2. Microcontroller and interfacing circuit.

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Data from Microcontroller is transferred to PC through the serial port of the Microcontroller by interfacing ICL232. A reset switch is provided so that the program is executed from 0000 after the power is switched on. A 24C16 EEPROM is interfaced with Microcontroller to store the patient i.d and test result (Chloride concentration). The 24C16 features a low power standby mode which is enabled, upon power-up and after the receipt of the STOP bit and the completion of any internal operations. It is a low cost and low voltage 2 wire serial EEPROM. The SCL (Serial Clock Line) is connected to pin 2 and the SDA (Serial Data Line) is connected to pin 3 of the Microcontroller.

2.1. Software

Software is developed in C, to initialize LCD, to start ADC conversion, to check EOC, to read 12 bit data signals, to measure and maintain temperature using ISR, to measure readings for blank, standard, and sample, to compute absorbance and concentration, to display the result in LCD and to get the data from the key board and to send data to PC for further processing. The implementation of the above tasks is given in the flowchart (Fig. 3).

Fig. 3. Flowchart.

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3. Materials and Methods

Samples are collected from the patients whose urinary Chloride has to be measured. The samples are maintained at room temperature. To measure the concentration of electrolyte, the solution of blank, standard and sample are prepared.

3.1. Materials

Chloride ion in acidic environment in presence of ferric nitrate forms a colored complex with mercuric thiocyanate. According to colorimetry principle, the intensity of the developed colour is proportional to the Chloride ion concentration in the sample [13].

2Cl- + Hg(SCN)2 AgCl2 + 2SCN-

SCN- +Fe +++ Fe(SCN)++

Two reagents R1 and R2 are used in this method. The reagent R1 consists of Mercuric thiocyanate (2m mol/l), Ferric Nitrate (20m mol/l) and Nitric acid (29m mol/l). The reagent R2 is Chloride standard solution [14, 15]. All the solutions are prepared in a well cleaned dried test tube of same diameter. Blank solution is prepared by mixing 1 ml of reagent R1 with 10 µl of distilled water. To prepare standard, 1 ml of reagent R1 is added with 10 µl of standard (R2). For sample preparation, 1 ml of reagent R1 is added with 10 µl of urine sample. The above solutions are thoroughly mixed and left for incubation for 5 min at 37 ° C, before the absorbance is measured at 480 nm.

3.2. Measurement

The test tube labeled blank is placed in a sample holder and the measured voltage is noted as Vo. By holding the standard solution test tube in a sample holder, the voltage Vstd is taken. To find the absorbance of sample solution, the sample solution is placed in a sample holder and voltage measured is noted as Vt. The concentration of urinary Chloride is determined using the formula,

Concentration of Chloride ion = log (Vo/Vt) / log (Vo/Vstd) x 100,

where, log (Vo/Vt) = Absorbance of sample, log (Vo/Vstd) =Absorbance of standard 100 is the concentration of standard Chloride.

The concentrations of urinary Chloride measurements are made for 40 urine samples using the developed instrument. The same urine samples are tested using the commercial clinical analyser. The absorbance of sample solution is measured and repeated for five times to check the reproducibility.

4. Results and Discussions

The performance of the Microcontroller P89C668 based electrolyte bio-analyser using colorimetry principle is investigated by comparing its results with the results obtained by other clinical analyser which is given in Table 1. It can be seen that there is no obvious difference between the results obtained by two methods.

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Table 1. Urinary Chloride Concentration (m mol/day).

S. No of patients

By developed instrument

By clinical analyzer

S. No of patients

By developed instrument

By clinical analyser

1 102.79 105 21 89.42 95 2 106.55 103 22 156.62 144 3 96.85 101 23 186.87 190 4 82.99 92 24 96.23 95 5 108.58 110 25 145.78 140 6 111.15 120 26 210.45 218 7 120.43 128 27 232.98 225 8 150.12 162 28 88.32 85 9 92.81 102 29 154.84 158

10 130.86 142 30 190.17 182 11 180.14 193 31 100.74 93 12 120.52 134 32 98.15 105 13 200.11 194 33 101.36 108 14 104.09 110 34 115.64 111 15 98.71 92 35 290.85 292 16 182.35 176 36 210.92 202 17 123.53 133 37 84.74 78 18 156.18 142 38 168.12 172 19 230.28 225 39 301.56 305 20 260.92 258 40 142.28 152

4.1 .Statistical Analysis

The Table 2 represents the statistical reports for the two methods. It is noted that the values of std. dev, mean value, median value, mean dev, Co-eff of variation and S.E of Co-eff of variation for the designed analyzer is close to the clinical analyzer [12]. The less residual between the two methods confirms the accuracy of the microcontroller based instrumentation set up.

Table 2. Statistical Reports for the two methods.

Variable MeanValue

MedianValue

MeanDeviation

Coeff. of Variance

SE of Coeff. of Variation

Sample Std. Deviation

DevelopedInstrument 145.75 127.19 44.28 37.47 4.18 54.61

Clinicalanalyzer 149.05 137 45.46 37.53 4.19 55.94

4.2. Detection and Quantification Limits

The detection and quantification limits are calculated as sb + 3 s, where sb is the average signal of blank solutions and s is the standard deviation. For the wavelength of 480 nm, the Absorbance change of 0.1119 typically corresponds to Chloride concentration of 68.81 m mol/l of the sample solution, which gave the sensitivity of the electrolyte bio-analyser. As the absorbance increases the Chloride concentration also increases, which shows the linearity of the instrument up to 300 m mol/l.

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4.3. Precision

Run-to-run precision is obtained by assaying commercial human control serum AccutrolTM Normal (Sigma) gave the results of Mean 104.4, S.D. 4.0, C.V (%) 3.3 and elevated results for a period of thirty (30) days produced the results of Mean 91.7, S.D. 3.8, C.V (%) 4.1. Within Run precision is obtained by assaying control Normal serum twenty (20) times having Mean 86.9 (104.4), S.D. 1.3 (4.0), C.V. (%) 1.0 (3.3).

4.4. Recovery

Recovery of Chloride added to pool human Urine is given in Table 3. Pooled Urine is diluted approximately two-fold with distilled water. To 0.5 ml of diluted Urine, various amounts of 0.1 N Sodium Chloride (NaCl) solutions are added to bring the total Chloride concentration within normal range. Using the developed Instrument the recovery values of added Chloride ranged from 98.1% to 99.3 % with an average recovery of 98.65 %, which indicates the suitability of the designed instrument for biomedical tests.

Table 3. Recovery of added Chloride from pooled Urine Chloride (mmol/day).

S. No In pooled Serum Added Total

ContentTotal

Determined Difference Recovery%

1. 82 40 122 120 2.0 98.3 2. 86 45 131 130 1.0 99.2 3. 90 50 140 138 2.0 98.5 4. 96 55 151 150 1.0 99.3 5. 104 55 159 156 3.0 98.1

4.5. Linear Regression Analysis

Linear regression analysis attempts to model the relationship between two variables by fitting a linear equation that closely fits a collection of data points. Fig. 4 shows a linear regression between the designed electrolyte bio-analyser and the commercial clinical analyser which is used to determine the correlation between the two methods. The value of slope 0.97 and the intercept 5.2 (close to ideality) indicated that the developed instrumentation system is well correlated with the clinical analyzer. The correlation coefficient between the two method is r2=0.99. The implemented method is well suited to determine the concentration of Chloride in Urine sample.

5. Conclusion

An inexpensive Electrolyte Bio-analyser has been fabricated using Microcontroller P89C688 to measure the Chloride concentration of urine. The developed system is a user friendly one, as no special training is required to use it. Normal spectrophotometers have optical lenses and filter which makes the system clumsy and difficult to use, as incandescent lamps are used as light sources, it generates lot of heat and consumes more power. All these problems are rectified in this system. Since the implemented instrument is based on colorimetry principle, any of the branded reagents which are available in local pharmaceuticals can be used. The designed instrument can be used to measure the Chloride concentration of other biological samples like serum, blood, plasma, CSF and also to measure the concentration of Sodium and Potassium by changing the source.

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Fig. 4. Linear regression between the developed instrument and clinical analyzer.

References

[1]. Wesson L. G., Physiology of the human kidney, New York Rune and Stratton, 1969, pp. 591. [2]. Weast R C, CRC handbook of Chemistry and Physics, 67th ed, CRC Press, Boca Raton, FL, 1986. [3]. Kuleita T A, Neurologic behavioral syndrome associated with ingestion of Chloride deficient infant

formula, Pediatrics, 78, 1986, pp. 714-715. [4]. J. B. Xiao, Determination of nine components in Bayer liquors by high performance ion Chromatography

with conductivity detector, Journal of the Chilean Chemical Society, Vol. 51, 2006, pp. 964-967. [5]. H. Cao and J. B. Xiao, Analysis of anions in alkaline solutions by ion Chromatography after solid phase

extraction, Annali di Chimica, Vol. 97, 2007, pp. 49-58. [6]. R. H. Wu and X. G Shao, Application of near infra red spextra in the determination of water soluble

Chloride ion in plant samples, Spectroscopy and Spectral Analysis, Vol. 26, 2006, pp. 617-619. [7]. M. Philippi, H. S. dos Santos, A. O. Martins, C. M. N. Azevedo, and M. Pires, Alternative

spectrophotometric method for standardization of Chloride solutions, Analytica Chimica Acta, Vol. 585, 2007, pp. 361-365.

[8]. T. V. Shishkanova, D. Sykora, J. L. Sessler, and V. Kral, Potentiometric response and mechanism of anionic recognition of heterocalixarene based ion selective electrodes, Analytica Chimica Acta, Vol. 587, 2007, pp. 247-253.

[9]. R. B. R. Mesquita, S. M. V. Fernandes, and A. O. S. S. Rangel, Turbidimetric determination of Chloride in different types of water using a single sequential injection analysis system, Environmental Monitoring,Vol. 4, 2002, pp. 458-461.

[10]. Wolfbeis O S, Fiber Optic Chemical Sensors and Biosensors Analytical Chemistry, 72, 2000, pp. 81-89. [11]. Rakow N A, Suslick K S A, Colorimetric sensor array for odor for Visualisation, Nature 406, 2000,

pp. 710-712. [12]. Wobschall D, In Circuit design for Electronic Instrumentation -Analog and Digital devices from sensor to

display, Second edition, McGraw-Hill Book Company, NY, 1987, pp. 367-368. [13]. De Jong, E B, Goldschmidt H M, Van Alphen A C, Loog J A, An improved automated method for serum

chloride, Clin Chem., 26, 8, 1980, pp. 1233-1234.

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[14]. Yokoi K, Colorimetric determination of chloride in biological samples by using mercuric nitrate and diphenylcarbazone, Biol Trace Elem Res, 85, 1, 2002, pp. 87-94.

[15]. Feldkamp et al, J Clin Chem Clin Biochem, 12, 1974, pp. 146-150.

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1 1. INTRODUCTION

Electrical conductivity is a general indicator ofwater quality, especially a function of the amount ofdissolved salt, and can be used to monitor processes inthe wastewater treatment that causes changes in totalsalt concentration and thus changes the conductivity.Recently different circuits have been presented tomeasure conductivity, from the application point ofview. In [1] a circuit model is presented whichresponds to the electric behavior in conductivity frequency. In [2] an analog interface is presented whichprovides good accurate results but with a fourelectrode cell. In [3] an electronic conditioning circuit,based on a variant of Wheatstone bridge is presentedwith the help of a digital processing stage based on amicrocontroller.

In the present work, option is provided for the conductivity temperature compensation by software orthe user can measure the conductivity by keeping thesample at a desired temperature for the analysis ofconductivity variation with temperature. The conductivity of a solution is proportional to its ion concentration, and if Chloride is the predominant anion in a soilsolution, the Chloride concentration in m mole wouldbe approximately equal to 10 times the electrical conductivity measured in dS/m [4, 5]. In this experimental study, we use the ATmega32 microcontrollermounted in the system, to correlate electrical conduc

1 The article is published in the original.

tivity with the Chloride concentration of the soil samples using regression model.

2. EXPERIMENTAL

2.1. Design of the Measurement System

The Block diagram of microcontroller based electrical conductivity measurement set up is shown inFig. 1. The conductivity cell made up of platinum isused to measure the conductivity of the samples is keptin Block 1. The cell constant is determined conveniently by calibration with pattern solutions [6].

Polarizing the conductance cell by an external DCpotential produces some undesirable effects (doublelayer capacitance, electrolysis, ohmic resistance andelectrolytic saturation). On the other hand, it is provedthat the electrolytic saturation is reduced considerablyif the AC polarization frequency is high enough. Practical values are (1–5 kHz) although those values mustnot be high in excess because it would appear the effectof the capacitance in parallel with the electrolyticsolution itself [7]. Hence, a fixed sinusoidal excitationvoltage of 1 V is applied to the bridge.

The conductivity cell is connected to one arm of amodified Wheatstone’s bridge network. The Block 2consists of precision rectifier to rectify the output ofbridge network. Block 3 represents the temperaturesensor LM35D to measure the temperature of thesample. Output of this sensor calibrated directly toCelsius does not require any external calibration. The

PHYSICAL INSTRUMENTS FOR ECOLOGY, MEDICINE, AND BIOLOGY

ATMEGA32 Microcontroller Based Conductivity Measurement System for Chloride Estimation of Soil Samples1

P. Neelamegama and R. Vasumathib

a Department of Electronic and Instrumentation Engineering, SASTRA University, Tanjore, Tamil Nadu, Indiab PG and Research Department of Physics, AVVM Sri Pushpam College, Poondi, Tanjore, Tamilnadu, 613503, India

email: [email protected] October 26, 2009

Abstract—This paper presents the development of an inexpensive and portable microcontroller based instrument set up to measure the electrical conductivity of the soil samples and hence to determine the Chlorideconcentration using empirical relation between the two parameters. A dedicated ATmega32 microcontrollerand its associated peripherals are employed to measure electrical conductivity and temperature. A special feature of the designed Instrument is that the conductivity temperature compensation can be achieved by software or the user can maintain the sample at desired temperatures by using the temperature controller.An empirical relationship between Chloride concentration and electrical conductivity of soil samples hasbeen developed using Linear Regression Model, which gave a Correlation Coefficient of R = 0.95 (n = 20),Slope = 14.95 and Intercept = –563.9. The obtained results are compared with the EL1CO CM 180 conductivity meter to check the accuracy of the designed instrument, which gives a correlation coefficient of R =0.98 (n = 20).

DOI: 10.1134/S0020441210040214

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effect of temperature is important when an electricconductivity of a liquid or solution must be done.

Block 4 indicates keypad to give input data to themicrocontroller for processing. Block 5 consists ofATmega32 microcontroller from Atmel company. It isa low power, high performance 8bit AVR microcontroller with 32 Kbyte in System Programmable Flash,one 16bit Timer/ Counter and two 8bitTimer/Counter, an eight channel 10bit ADC [8], 32programmable I/O lines in four I/O ports and 2 Kbyteof SRAM. Temperature controller kept in the Block 6is used to keep the sample at a desired temperature.Block 7 is a four rows twenty characters LCD (LiquidCrystal Display) from Hitachi, to display the experimental results. Block 8 consists of MAX232 (dualRS232 transmitter/receiver interface), which is usedto communicate with PC kept in Block 9.

2.2. AC Modified Wheatstone’s Bridge Network

A modified AC Wheatstone bridge network isshown in Fig. 2. In the developed instrument, two highgain operational amplifiers (CA3041) IC1 and IC2 areconnected with the bridge network with the non

inverting terminal connected to the ground circuit.The bridge output nodal points B and D almost at thesame potentials with respect to the ground and hencethe effect of stray capacitance that will exist betweenthem and also between them and ground is assumed tobe minimized. Since, B and D are at virtual ground,the sinusoidal supply voltage, V = Vsinωt, the currentthrough the bridge impedances are Z1, Z2, Z3 and Z4respectively. The output voltage of the circuit is [3]

Vo = Rf(Z2Z3 – Z1Z2]V.

At balance condition of the bridge, Vo = 0 which isidentical with the conventional bridge network. Theconductivity cell is connected instead of Z3. The conductivity of a sample is determined by

1/Z3 = Gc = (Z1Z4/RiVi + VoZ1Z4/Z2)–1,

where Vo —bridge output voltage, Vi —input excitation voltage, Z1, Z2, Z4 —known resistances, Rf —feedback resistance and Gc —conductivity of a sample.

The output of the amplifier IC2 is given to input ofthe precision rectifier constructed with operationalamplifiers IC3 and IC4 as shown in Fig. 2.

1Conductivity

cell

2PrecisionRectifier

3LM35D

6Temperature

controller

5Micro

controller

4Keypad

7LCD

8MAX232

9PC

Fig. 1. Block diagram of microcontroller based electrical conductivity instrumentation set up.

ACinput

Z1

I1

Z2

I2

Z4

I4

Z3

I3

С

D

IС1

IС2

3

2

6

3

2

6

3

2

6

3

2

6

D1

D2

IС3 IС4

Rf R1

ВR2 R3 R4

R5

to pin 38 of MC

Fig. 2. AC modified Wheatstone’s bridge network with precision rectifier. (IC1 – IC4) CA3041.

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ATMEGA32 MICROCONTROLLER BASED CONDUCTIVITY MEASUREMENT SYSTEM 593

2.3. Microcontroller and Interfacing Circuit

The circuit diagram of the microcontroller basedinstrumentation set up to measure the electrical conductivity of the sample is shown in Fig. 3. In this circuit, the output from the modified Wheatstone’sbridge network is given to pin 38 (ADC2) of microcontroller. The temperature sensor LM35D is connected to pin 39 (ADC1) of Port A. A crystal oscillatorof 8 MHz is connected between pin 12 and 13 ofmicrocontroller as shown in Fig. 3. Three keys areconnected to PC0, PC1, and PC2 Port C. A four rowstwenty characters LCD is connected with Port D, todisplay the measured data and the computed results.

The temperature controller built with optocouplertransistor and heater coil with battery (12 V, 7 A h),Exide power safe, ShinKobe Electric machinery Co.Ltd, Japan, and other associated components is alsoshown in Fig. 3. An opto transistor MCT2E is used toisolate temperature controller section from the microcontroller circuit. The opto coupler is activated/deactivated through the transistor BC547, which is connected to PA7 of microcontroller. By proper commands from the microcontroller, heater is switchedON/OFF to maintain the temperature of the sampleat desired temperature. MAX232 (dual RS232 transmitter/receiver interface) is connected with pin 14 and15 of Port D to transmit/receive data from PC.

2.4. Software

Software is developed in C and assembly languageto initialize LCD, to compute conductivity temperature compensation by software, to keep the sample atdesired temperature using temperature controller, tostart ADC conversion, to check End of conversion, toread 10 bit of data from ADC, to measure the temperature, to control the temperature, to compute conductivity, to compute Chloride concentration usingregression model, to display the results in LCD, and tosend data to PC for further processing.

3. SOIL SAMPLING

3.1. Field Description

Soil samples are collected from twenty paddy fieldsites originated from ThanjavurThiruvarur Delta districts, TN, South India, where rice is the main crop ofseveral agricultural products. The samples are collected at every 3 km from Thanjavur to Thiruvarur over60 km, during the major cropping season of springsummer (March–June), which produces about 56%of the National total production.

+5 V

+5 V

+12 V +5 V

+5 V

+5 V

1

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40

39

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22

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LM35D

VCC

R

R

R

R

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Q

D

1

2

5

4

MCT2E

BDX33C

BC547

Heater coil

op

to t

ran

sist

or

O/P from AC Wheatstone’s bridge

ATmega32

PA0/ADC0

PA1/ADC1

PA2/ADC2

PA3/ADC3

PA4/ADC4

PA5/ADC5

PA6/ADC6

PA7/ADC7

PB0/T0

PB1/T1

PB2/AIN0

PB3/AIN1

PB4/SS

PB5/MOSI

PB6/MISO

PB7/SCK

RESET

XTAL1

XTAL2

AREF

AVCC

AGND

PC0/SCL

PC1/SDA

PC2/TCK

PC3/TMS

PC4/TD0

PC5/TD1

PC6/TOSC1

PC7/TOSC2

PD0/RXD

PD1/TXD

PD2/INT0

PD3/INT1

PD4/OC1B

PD5/OC1A

PD6/ICP1

PD7/OC2

Key p

ad

MAX232PC

LCD

D4

D5

D6

D7

RS

ENR/W

GND

11

C

X

Fig. 3. Microcontroller and interfacing circuit.

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3.2. Soil Sample Collection

Sampling areas of paddy fields are selected byavoiding tracks, drainage lines, sheep camp, or influences other than effluent irrigation. During collection,the size of the sample (volume or weight), identification of sample (unique labeling), special packagingand storage are noted. After collection of the samples,they are airdried to remove moisture.

3.3. Sampling Procedure

The collected soil samples are dried overnight in acabinet equipped with a heating element and anexhaust fan to remove moisture. The temperature inthe cabinet does not exceed 36°C in order to approximate airdrying conditions. Samples are crushed with amechanical grinder equipped with porcelain mortarand stainless steel 10 mm mesh sieve to remove largerclods and unwanted debris. Since the material fromthe particle sizing 2 mm and smaller are most important in making an inventory of the mineral constituents of the soil and in evaluating EC, the sample iscrushed again and the particles sizing 2 mm and lessthan 2 mm are sieved using 2 mm mesh. The sample isprepared as given below to measure the conductivity.Three 10 g scoops of soil and 30 ml of deionized waterare taken in a large test tube and shaken well for 30 minto get 1:1 suspension of soil sample. After initial shaking, the suspension is allowed to stand, with intermittent shaking for 30 min [9]. The supernatant solutionis then filtered and it is used for the measurement ofelectrical conductivity.

3.4. Measurement

To measure the electrical conductivity of the sample, the conductivity cell is connected at one arm ofthe modified AC Wheatstone bridge and selecting theresistance value Z1 (100 Ohm or 1 kOhm), Z2

(1 kOhm), and Z4 (1 kOhm). A fixed sinusoidal excitation voltage of 1 V with frequency 1 kHz is applied tothe bridge. For the calibration of the instrument, theknown concentrations of NaCl are prepared and theconductivity is measured before using the soil samples.The solution is maintained at 25°C by means of temperature controller. Initially, the conductivity cell isimmersed into the solution of NaCl having concentration of 0.1N, and the electrical conductivity is measured. Then the probe is washed with deionised waterand the electrical conductivity for various concentrations 0.2N, 0.3N, 0.4N and 0.5N are measured. Then,the conductivity cell is immersed in the prepared soilsample and the measurements are made for electricalconductivity. The Chloride concentration of the prepared soil samples is determined using the titrationmethod for the development of regression model.

3.5. Development of Regression Model

The Chloride concentration of the sample isstrongly related to the electrical conductivity of thesample, a relation between them is evaluated using linear regression model (using software ULTIMACALC).

The regression line equation y = –563.9 + 14.95x isobtained and it is used by the microcontroller to compute Chloride concentration of the soil. The correlation coefficient between the electrical conductivityand the Chloride concentration is R = 0.95 (n = 20).

4. RESULTS AND DISCUSSION

The developed microcontroller based instrument isused to measure the conductivity of the soil samples.The empirical relationship between the electrical conductivity and the Chloride concentration has beendeveloped using linear regression model to determinethe Chloride concentration of the sample. The performance of the designed instrument is investigated bycomparing the results with the standard instrument(ELICO CM 180).

The calibration curve is obtained by plotting theconcentration of Chloride against the electrical conductivity of prepared NaCl solutions at various concentrations as shown in Fig. 4. From the figure, it isobserved that the developed instrument shows the linearity between the Chloride concentration and theelectrical conductivity. The regression line betweenthe electrical conductivity measured for soil samplesusing the developed instrument and the commerciallyavailable ELICO CM 180 instrument is: y = –1.10 +1.07x, and the correlation coefficient for this line isR = 0.98 (n = 20). The reproducibility of the instrument is tested by taking five replicate readings for soilsample and it is found to agree well within the limits.

In this study, it is observed that the range of electrical conductivity of soil samples are varied from 45 to74 mS/cm and the Chloride concentration is maxi

30

25

20

15

10

5

00.1 0.2 0.3 0.4 0.5

NaCl Concentration, N

Electrical Conductivity, mS/cm

Fig. 4. Electrical conductivity measured for known concentration of NaCl solution using developed instrument.

INSTRUMENTS AND EXPERIMENTAL TECHNIQUES Vol. 53 No. 4 2010

ATMEGA32 MICROCONTROLLER BASED CONDUCTIVITY MEASUREMENT SYSTEM 595

mum at Ammaiyappan (560 ppm) and minimum atKattuthottam (140 ppm). It is also to be noted that allthe collected paddy field soil samples are having theChloride concentration within the maximum tolerable limit (1050 ppm).

5. CONCLUSIONS

ATmega32 microcontroller based instrumentationsystem has been developed to compute Chloride concentration of the soil samples using electrical conductivity. The design allows an efficient and easy solutionto the thermal compensation needed in this type ofmeasurements. This system is a portable one and canbe easily handled by irrigators and farm managers. Theelectrical conductivity determination has replaced thetedious chemical methods for the Chloride determination. The results are comparable with the valuesreported using the standard method.

REFERENCES

1. Ferrara, E., Callegaro, L., and Durbiano, F., OptimalFrequency Range for the Measurement of AC Conduc

tivity in Aqueous Solutions, Proc. 17th IEEE Instrumentation and Measurement Technology Conference,Baltimore, 2000.

2. Li, X. and Meijer, G.C.M., A LowCost and AccurateInterface for Conductivity Sensors, Proc. 19th IEEEInstrumentation and Measurement Technology Conference, Anchorage, AK, USA, 2002.

3. Rajendran, A. and Neelamegam, P., Measurement,2004, vol. 35, p. 59.

4. Abyaneh, H.Z., Nazemi, A.H., Neyshabori, M.R.,et al., Tarim Bilimleri Dergisi, 2005, vol. 11, no. 1,p. 110.

5. Hajrasuliha, S., Cassel, D.K., and Rezainejad, Y., Geoderma, 1991, vol. 49, p. 117.

6. Braunstein, J., Robbins, G.D., J. of Chemical Education, 1981, vol. 48, no. 1, p. 52.

7. Gopel, W., Hesse, J., and Zemel, J.N., Eds., Sensors. AComprehensive Survey, Chemical and Biochemical Sensors, part I, vol. 2, Weinheim: VCH, 1991.

8. ATmega32 Microcontroller data sheet [www.atmel.com].

9. Recommended Chemical Soil Test Procedures for theNorth Central Region. North Central Regional Publication, no. 221, NDSVBull., 1988, no. 499.

ISSN 00204412, Instruments and Experimental Techniques, 2011, Vol. 54, No. 2, pp. 262–267. © Pleiades Publishing, Ltd., 2011.

262

1 1. INTRODUCTION

Chloride is an essential electrolyte for human,which occurs primarily in body fluids. This anion isspecially transported into the gastric lumen, inexchange for another negatively charged electrolyte(bicarbonate) in order to maintain electrical neutralityacross the stomach membrane. After utilization inhydrochloric acid, some chloride ion is reabsorbed bythe intestine, back into the blood stream where it isrequired for maintenance of extra cellular fluid volume [1]. A constant exchange of chloride and bicarbonate between red blood cells and the plasma helpsgovern pH balance and transport carbon dioxide, awaste product of respiration from the body.

Since, chloride is a highly mobile ion that easilycrosses cell membranes and is involved in maintainingproper osmotic pressure, water balance and acidbasebalance. Several studies have suggested that the chloride ion may play a more active and independent rolein renal function, neurophysiology and nutrition. Lowserum chloride values are found with extensive burns,excessive vomiting, intestinal obstruction, nephritis,metabolic acidosis, and in addisonian crisis. Elevatedserum chloride values seen in dehydration, hyperventilation, congestive heart valve, and prostatic or othertypes of urinary obstruction [2]. The clinical significance of tests for chloride in the serum are importantin the diagnosis and treatment of patients sufferingfrom hypertension, renal failure or impairment, car

1 The article is published in the original.

diac distress, disorientation, dehydration, nausea anddiarrhea.

Plasma or serum chloride is routinely assayed by aclinical chloride ion meter that uses a chloride ionselective electrode [3], or by cyclic voltametry [4].Because of the difficulty in tuning of the chloridemeter that is usually specialized for human serum orplasma in clinical laboratories, determination of urinary chloride is based on titration methods using thereaction between chloride and silver ions [5]. There isdifficulty in judging the correct end point, especiallyfor the silver nitrate method. The coulometric titrationsolved this problem but requires the special instrumentation [6].

Colorimetry is one of the simplest and best techniques, which have been used for the clinical routineassays. Hence, there is a need to develop a simple,accurate and inexpensive biomedical analyzer basedon colorimetry principle.

Modern embedded measurement and control systems incorporate a microcontroller as the principalcomponent. As well as the microcontroller, an embedded control system frequently uses external chips suchas peripheral device controllers and analog chips forprocessing input analog signals.

The new generation of reconfigurable PSoC controllers, which integrates all the above components,will become the dominant system architecture for themajority of microbased designs, by employingadvanced lithography and FLASHbased programming technology. A single PSoC device can integrate

PHYSICAL INSTRUMENTS FOR ECOLOGY,MEDICINE, AND BIOLOGY

Measuring Chloride in Serum Using Single Programmable System on Chip (PSoC)1

P. Neelamegama and R. Vasumathib

a Department of Electronics and Instrumentation Engineering, SASTRA University, Thanjavur, Tamil Nadu, Indiaemail: [email protected]

b Department of Physics, AVVM Sri Pushpam College, Poondi, Thanjavur, Tamil Nadu, India, 613503Received July 21, 2010

Abstract—PSoC devices are dynamically reconfigurable, versatile programming, lowpower consumptionand multiple interfacing, which motivates the design of portable and inexpensive instruments. The chlorideanalyzer is built around a cypress CY8C27443 PSoC with its analog and digital blocks, which is typically anembedded system, and it is configured for the measurement of chloride in serum. The principle of chloridemeasurement is based on colorimetry with LED as illuminating source and photodiode GASPG1104 as alight sensor. The run to run precision of the implemented system is determined by analysing human controlserum AccutrolTM Normal (Sigma) and the chloride concentration is found to be 104 ± 4 mmol/l (mean ±SD, n = 5), which is close to the certified value. This system has been used successfully for the routine assayof biomedical samples, with the results in good agreement with values obtained by the commercial clinicalanalyzer at 95% of confidence level.

DOI: 10.1134/S0020441211010258

INSTRUMENTS AND EXPERIMENTAL TECHNIQUES Vol. 54 No. 2 2011

MEASURING CHLORIDE IN SERUM USING SINGLE PROGRAMMABLE SYSTEM 263

as many as 100 peripheral functions with a microcontroller [7]; saving customers design time, board space,power consumption. Using the development tools,library elements can be configured to provide analogfunctions (from analog blocks), such as programmablegain amplifiers, filters, ADCs with exceptionally lownoise, input leakage and voltage offset, DACs, comparators, etc. Digital functions such as timers,counters, PWMs, SPI, and UARTs can be configuredfrom the digital blocks of digital systems.

Due to the flexibility of configuration (peripheralfeatures), low power and other advantages of PSoC, itis selected for the design of biomedical analyzer todetermine the chloride concentration in serum. Thisinstrument has been applied to measure the absorbance and hence the concentration of chloride inserum samples, with the results comparable with acommercial clinical analyzer.

2. INSTRUMENTATION

2.1. Design of the Implemented System

The design scheme of the implemented system isshown in Fig. 1. Block 1 represents the Green LED,which acts as an illumination source with a dominantwavelength of 480 nm. Block 2 indicates the sampleholder to hold the blank, standard, and sample solution tube with a diameter of 1 cm. Block 3 is a photodiode GASPG1124 used to detect the amount oftransmitted intensity of the sample. The temperaturesensor LM35D kept in block 4 is a precision semiconductor temperature sensor giving an output of 10 mVper degree centigrade. It is capable of measuring temperature between 2°C and 100°C. The output signalsare fed to the CY8C27443 microcontroller for signalamplification. After that the analog signals are converted into digital signals to compute absorbance andhence concentration of chloride.

Block 5 represents the microcontroller PSoCCY8C27443 [8]. It’s analog system is composed ofconfigurable blocks as programmable gain amplifiers(PGA) up to 4, with gain up to 48x and instrumentation amplifiers up to 2, with selectable gain up to 93x,analog to digital converters up to 4, with 6 to 14 bit res

olution, filters with 2, 4, 6, and 8 pole band pass, lowpass and notch, digital to analog converters with 6 to9 bit resolution and comparators up to 4, with 16selectable thresholds. It has configurable digital blocksof timers (8 to 32 bit), counters (8 to 32 bit), PWMs(8 to 32 bit). SPI slave and master up to 2, and 8 bitUART with selectable parity up to 2. It also contains16 KB of flash memory, 256 bytes of SRAM, an 8 × 8multiplier with 32bit accumulator, power and sleepmonitoring circuits, and hardware I2C communications.

A keypad denoted by block 6 is used to give inputdata to the microcontroller. Block 7 is LCD, a two rowalphanumeric display, which is used to displayPatient’s ID number, measured data and the results.The data are transmitted from the microcontroller tothe computer represented by block 9 via RS232denoted by block 8.

2.2. Description of the Microcontroller Based System

The microcontroller PSoC CY8C27443 and interfacing circuit of the developed instrument system,based on colorimetry principle is shown in Fig. 2. Herea colorimeter measures the intensity of light shiningthrough a coloured solution compared to the intensityof light passing into the solution. A detector measuresthe transmittance T (% of light passing through) of thesolution. This is mathematically converted to absor

bance (A = – ) and the absorbance is directlyproportional to the concentration (Beer–Lambertlaw). The photo detection assembly is well insulatedfrom outer light and the output signals are detected byphoto diode of GASPG1124.

The analog blocks in CY8C27443 are configured asprogrammable gain amplifier and ADC for the processing of analog signals (Fig. 3). The output signalsfrom the photodiode sensor are fed to analog inputP0(7) as shown in Fig. 2. The two stages of programmable gain amplifier (PGA) are used for amplifyingthe light sensor’s signals. The configured 12 bit dualADC is used for converting analog signals to digitalquantities.

The temperature sensor LM35D is connected topin P0(3), the other input for the 12 bit dual ADC of

Tlog

1LED

2Sampleholder

3Photodiode

4LM35D

5Micro

controller

6Key pad

7LCD

8RS232

9PC

Fig. 1. Block diagram of the implemented biomedical analyzer.

264

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NEELAMEGAM, VASUMATHI

microcontroller (Fig. 2). The temperature controllercircuit is implemented with PWM (pulse width modulation), Opto isolator (IC MOC3021), and TRIAC(BT136), to control and maintain the temperature ofsample at 37°C for incubation. The IC MOC3021 isused to isolate low voltage section from high voltagesection.

The data lines of LCD are interfaced with port 2(Fig. 2) of microcontroller to display the patient IDnumber, user information, and results. A digital blockin the microcontroller is configured as UART forRS232 interface to transmit/receive data from the PC.

2.3. Software

In the present work, software is developed in C, toconfigure analog and digital blocks as peripherals, to

initialize LCD, to start ADC, to read 12 bit data signals, to measure and maintain temperature, to measure voltages for blank, standard, and sample, to compute absorbance and concentration, to display theresult in LCD, to get the data from the keyboard andto send data to PC for further processing. The implementation of the above tasks is given in the flowchart(Fig. 4).

3. MATERIALS AND METHOD

Serum samples are collected from the patients andare separated from the blood clot soon after drawing.Grossly hemolyzed serum should not be used, as it willcreate falsely decreased values. The collected serumsamples are stored at room temperature. The colorimetry principle is used for the measurement of absorbance and concentration of chloride electrolyte.

3.1. Principle

Chloride ions form a soluble, nonionized compound, with mercuric ions and will displace thiocyanate ions from nonionized mercuric thiocyanate. Thereleased thiocyanate ions react with ferric ions to forma color complex that absorbs light at 480 nm. According to Beer–Lambert’s law, the intensity of the colorproduced is directly proportional to the chloride concentration [9]

2Cl– + Hg(SCN)2 HgCl2 + 2SCN–,

3SCN– + Fe+++ 4Fe(SCN)+++.

FuseHeater

coll

ACInput TRIAC

Photodiac

R2

D

R1

P0(1)

P0(3)

P0(7)Photodiode

LM35D

1

4

CY8C27443

GND

VCC

28

+5 V

14

16

12

20

21

7

22

23

5

18

17

Key padP1(2)

P1(3)

P2(0)

P1(6)P1(4) RS232 PC

D7

D6

D5

D4

RS

EN

P2(2)

P2(3)

P2(4)

P2(6)

P2(7)

LCD

Fig. 2. Microcontroller and interfacing circuit.

Photodiode

LM35D

PSoC internal blocks

PGAMUX

PGA

12 bit dualADC

Fig. 3. Internal blocks of PSoC.

INSTRUMENTS AND EXPERIMENTAL TECHNIQUES Vol. 54 No. 2 2011

MEASURING CHLORIDE IN SERUM USING SINGLE PROGRAMMABLE SYSTEM 265

3.2. Reagents

Two reagents R1 and R2 are used in this measurement system. The reagent R1 consists of mercuricthiocyanate (2 mmol/l), ferric nitrate (20 mmol/l),and nitric acid (29 mmol/l). The reagent R2 is chloride standard solution (NaCl 100 mmol/l). Blanksolution is prepared by mixing 1 ml of reagent R1 with10 μl of distilled water. To prepare standard, 1 ml ofreagent R1 is added with 10 μl of standard (R2).For sample preparation, 1 ml of reagent R1 is addedwith 10 μl of serum sample. The above solutions arethoroughly mixed and left for incubation for 5 min at37°C, before the absorbance is measured at 480 nm.

3.3. Measurement

The designed instrument is used to measure theblank, standard and sample voltages and to computeabsorbance and concentration. The test tube labeledblank is placed in a sample holder and the measuredvoltage is V0. By holding the standard solution test tubein a sample holder, the voltage Vstd is read by themicrocontroller. The sample solution is placed in asample holder and voltage measured as Vtest. The con

centration of serum chloride is computed using theformula:

Concentration of chloride ion = log(V0/Vtest)/log(Vo/Vstd) × 100,

where log(V0/Vtest) is the absorbance of sample,log(V0/Vstd) is the absorbance of standard, and 100 isthe concentration of standard chloride.

The concentrations of serum chloride measurements are made for 20 patient’s sample using thedeveloped instrument. The same samples are testedusing the commercial clinical analyzer. The absorbance of sample solution is measured and repeated forfive times to check the reproducibility. Chloride is stable in serum for one day at room temperature, up toone week at refrigerator temperature and for threemonths frozen when stored as tightly capped.

4. RESULTS AND DISCUSSION

The absorption curve of the ferric thiocyanatecomplex formed is shown in Fig. 5. Since the curve hasa rather broad peak, the color can be read over a widespectral range. A wavelength of 480 nm is used in the

Start

IST

Imitalise port

Call IST

Measure and store V0using ADC

Measure and store Vstdusing ADC

Measure and store Vtestusing ADC

Read ST

Read MT

On

Yes

No

IsST = MT

Off

End

Display concentration

Clorideconcentration

(mmol/l)=

Abs of blank/Abs of testAbs of blank/Abs of std

× 100

ST = set temperatureMT = measure temperature

Fig. 4. Flowchart.

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NEELAMEGAM, VASUMATHI

developed analyzer. However, any wavelength chosenbetween 450 and 480 nm gave satisfactory results.This is an advantage for laboratories using photometers with fixed filter systems.

The concentration of nitric acid (HNO3) in thecolor reagent has a marked effect on color development. When HNO3 is added to give a concentrationabove 0.25 N, proteins in the specimen are precipitated. A nitric acid concentration of approximately0.03 N gave optimum conditions for the determination of physiologic serum chloride levels.

4.1. Linearity and Sensitivity

To check the linearity of the designed instrument,different types of serum sample ranging between 90–150 mmol/l have been used. The absorbance increaseswith the chloride concentration, and shows the linearity of the instrument up to 150 mmol/l. For the wavelength of 480 nm, the absorbance change of 0.001 typically corresponds to chloride concentration of 0.25mmol/l, which gave the sensitivity of the analyzer.

4.2. Precision

Runtorun precision is obtained by assaying commercial human control serum AccutrolTM normal(Sigma) gave the results of mean 104.4, S.D. 4.0,C.V (%) 3.3 and elevated results for a period of thirty(30) days produced the results of mean 91.7, S.D. 3.8,C.V (%) 4.1. Within run precision is obtained by assaying control normal serum twenty (20) times havingmean 86.9 (104.4), S.D. 1.3 (4.0), C.V (%) 1.0 (3.3).

4.3. Recovery

To measure the recovery of chloride, pooled serumis diluted approximately twofold with distilled water.To 0.5 ml of diluted Serum, various amounts of 0.1 NSodium chloride (NaCl) solutions are added to bringthe total chloride concentration within normal range.Using the developed instrument the recovery values ofadded chloride ranged from 99.4 to 97.5% with anaverage recovery of 98.44%, this indicates the suitability of the designed instrument for biomedical tests.

4.4. Interferences

No significant interferences are observed with theexception of bromide and fluoride and they can causefalsely elevated chloride values. Bromide at 10 and20 mmol/l produced positive bias of 20 and42 mmol/l, respectively, for chloride measurements.However, the assays can be directly performed on rawbiological samples, i.e., in the presence of lipid, protein and minerals such as magnesium, iron and zincwithout any pretreatment. Lipemic and/or icteric serado not interfere in the reaction.

4.5. Linear Regression Analysis

To examine the accuracy of the developed instrument, linear regression is performed and tested for theresults obtained using designed biomedical analyzerand the other clinical analyzer. All the samples fall intothe linear range, and there is sufficient precision in thedata to continue with the linearity study. There is nooutlier in the data sets. The strength of the linear association between two variables is quantified by the correlation coefficient. The regression line equationarrived is,

y = 0.95x + 4.6,the value of slope m = 0.95 (close to ideality) and theintercept c = 4.6 indicated that the developed instrumentation system is well suited to determine the chloride in serum. The correlation coefficient R = 0.95(n = 20), shows that the present method is well correlated with the clinical analyzer.

4.6. Statistical Analysis

The performance of the PSoC based biomedicalanalyzer using colorimetry principle is investigated bycomparing its results with the results obtained by otherclinical analyzer. There is no obvious differencebetween the results obtained by two Instruments. Thetable represents the statistical reports for the resultsarrived using the developed instrument and the commercial clinical analyzer. It is noted that the values ofStandard deviation, standard error of standard deviation, mean value, standard error of mean, medianvalue. Standard error of mean, mean deviation, coef

400 420 440 460 480 500 520 540Wavelength, nm

0.40

0.35

0.30

0.25

0.20

0.15

0.10

Absorbance

Fig. 5. Absorption curve.

INSTRUMENTS AND EXPERIMENTAL TECHNIQUES Vol. 54 No. 2 2011

MEASURING CHLORIDE IN SERUM USING SINGLE PROGRAMMABLE SYSTEM 267

ficient of variation and standard error of coefficient ofvariation for the designed analyzer is close to the clinical analyzer.

5. CONCLUSION

A rapid, precise, and inexpensive programmablesystem on chip based biomedical analyzer has beenfabricated to measure the chloride concentration inserum. The PSoC design increases flexibility of configuration of peripherals, lower part count, and provides in system performance improvement, designsecurity, and field upgrades. The developed Instrument is sensitive and suitable for determining chlorideconcentration in serum and it is a user friendly one, asno special training is required to use it. Usual spectrophotometers have optical lenses and filter, whichmakes the system clumsy, and difficult to use, asincandescent lamps are used as light sources, it gener

ates lot of heat and consumes more power. All theseproblems are rectified in this PSoC based system andit can be used as an alternative to the commercial clinical analyzer. The instrument can be used to measurethe chloride concentration of other biological sampleslike serum, blood, plasma and cerebro spinal fluid bychanging reagents. Since, the method of measuringchloride in serum is based on colorimetry principle,any of the branded reagents, which are available inlocal pharmaceuticals, can be used. Comparing thepresent results on analytical performance with that ofother clinical analyzer, the developed Instrument givescompatible analytical results in all approaches.

REFERENCES

1. Wesson, L.G., Physiology of the Human Kidney, NewYork and London: Grune and Stratton, 1969, p. 591.

2. Tietz, N.W. and Saunders, W.B., Fundamentals of Clinical Chemistry, Philadelphia: PA, 1976, p. 897.

3. Külpmann, W.R., J. Clin. Chem. Clin. Biochem., 1989,vol. 27, p. 815.

4. Arai, K., Kusu, F., Noguchi, N., Takamura, K., andOsawa, H., Anal. Biochem., 1996, vol. 240, p. 109.

5. Annino, J.S., Chloride in Clinical Chemistry. Principleand Procedures, Little, Brown, Boston, 1964, pp. 98–104.

6. Scott, M.G., Heusel, J.W., LeGrys, V.A., and SiggaardAndersen, O., Electrolytes and Blood Gases, in Textbookof Clinical Chemistry, C.A. Burtis and E.R. Ashwood,Eds., Philadelphia: W.B. Saunders Company, 1999,pp. 1056–1092.

7. Sidek, O., Omar, M.G., Edin, H., et al., Eur. J. Sci.Res., 2009, vol. 33, no. 2, p. 249.

8. www. C Y8C27443.com

9. De Jong, E.B., Goldschmidt, H.M., van Alphen, A.C.,and Loog, J.A., Clin. Chem., 1980, vol. 26, no. 8,p. 1233.

Statistical analysis for the data arrived using developed instrument and the clinical analyzer

Variables Developed instrument

Clinicalanalyzer

Standard deviation 5.07 5.40

Standard error of standard deviation

0.82 0.85

Mean value 100.84 100.5

Standard error of mean 1.16 1.20

Median value 101 100.5

Standard error of median 1.45 1.51

Mean deviation 4.37 4.5

Coefficient of variation 5.02 5.38

Standard error of coefficient of variation

0.81 0.85

Research Article

COLORIMETRIC DETERMINATION OF CHLORIDE ION IN ORAL REHYDRATION SALTS USING MICROCONTROLLER P89C51RD2

P. NEELAMEGAMa, R. VASUMATHIb aDepartment of Electronic and Instrumentation Engineering, SASTRA University, Tanjore, Tamilnadu, India, b PG and Research

Department of Physics, AVVM Sri Pushpam College, Poondi, Tanjore, Tamilnadu, India ­613503

Received: 01 Nov 2010, Revised and Accepted: 01 Dec 2010

ABSTRACT

A simple, precise and inexpensive Microcontroller P89C51RD2 based Instrument set up has been designed, developed and validated to find the Concentration of Chloride ion concentration in Oral Rehydration Salts (ORS). The present method is based on the quantitative reduction of thiocyanate ions by Chloride ions by means of Colorimetry principle. Hardware and software are developed for implementing the absorbance measurement and to calculate the Chloride concentration. There is statistically no significant difference between the results obtained with the developed Instrument and the Chloride Ion Selective Electrode (ISE). It is found that the Concentration of Chloride is well within that of World Health Organisation (WHO) certified values. The Correlation coefficient r= 0.99 (n=6) is obtained between the developed instrument and the Ion Selective Electrode method. The sensitivity and the precision are high enough to determine the concentration of Chloride ion without any significant interference. The developed Instrument could be routinely used for the determination of Chloride ion in bulk drugs.

Keywords: Chloride, Dehydration, ORS, drugs, Microcontroller P89C51RD2.

INTRODUCTION

Dehydration is one of the most common problems of infancy and early childhood. They are affected by dehydration during prolonged vomiting, diarrhea and in cases of some diuretic medications. Because vital body fluids and minerals are lost during the above illness. These fluids and minerals contain electrolytes. They must be replaced quickly in order to prevent dehydration. Dehydration affects the body’s electrolyte balance. Electrolytes give your body the electrical support necessary1 for your heart, muscles and nervous system to work properly. When electrolytes are out of balance many organs cannot function properly, and lead to life threatening condition. Chloride is the main extracellular anion. With Sodium it accounts for most of the osmotic pressure of plasma and contributes to maintenance of electroneutrality. Chloride ions are ingested with food and absorbed in the intestinal track. It absorbs minerals and vitamin B12, enables normal muscle contraction2, relaxation and nerve impulse transmission. Decreased levels of Chloride (Hypochloremia) occur with any disorder. It occurs with prolonged vomiting or gastric suction, chronic diarrhea, emphysema or other chronic lung disease. In order to Rehydrate, Doctors recommend ORS therapy immediately.

The modern era of oral replacement of fluid and electrolytes in pediatric diarrheas had its beginnings in reports from Baltimore using Sodium, Potassium, Chloride and lactate to replace losses in infantile diarrheas in the 1950’s with subsequent addition of sugar to spare protein3. The science of ORS is advanced when Phillips and colleagues determined the composition of fluid lost in diarrhea4, 5. Oral Rehydration Therapy is proposed as a viable alternative for cholera in areas of the world with short supplies of intra‐venous fluids and needles forcing clinicians to deliver oral solutions to those with cholera. This reduced mortality rates to only 3% compared to 30% of those treated in other camps with intravenous fluids. Based on this evidence, WHO and UNICEF recommended a single standard ORS formula for all ages. There are lot of brands of ORS therapy is available in local pharmacy. The accurate analysis of minerals in drugs is very important in medications.

Over the years, numerous analytical methods for Chloride in a variety of samples have been developed, such as Ion Chromatography6, 7, Spectroscopy8, Ion Selective Electrode (ISE) method9, Turbidimetric method10, and so on. Ion Chromatography is an accurate laboratory method, but cannot produce real time data needed for rapid decisions in the field. Spectroscopy is one of the tedious methods. ISEs are accurate when recently calibrated, but are sensitive to drift, fouling and are not ideal for field monitoring. Turbidimetric is popular and regarded relatively reliable for

quantification of Chloride. But it suffered from long experimental time, lower sensitivity and complexity. Hence, there is a need for an analytical tool to quantitate the Chloride ion concentration in an inexpensive way.

Moreover, low cost but powerful Microcontrollers are used in many types of portable and hand held Instruments. These electronic circuits can be programmed with the measurement algorithms and the calibration function needed for full instrument operation with the numeric result appearing on a screen at the end of the measurement process. Their internal memory, versatility of programming, possibility of multiple interfaces and low power function make it possible to design the system with high accuracy and high speed response.

In the present method, a Microcontroller P89C51RD2 based Instrument set up has been designed and developed with colorimetric principle to measure the absorbance and hence to determine the Concentration of Chloride in ORS samples, with the results comparable to the other analytical technique (Ion Selective Electrode method).

INSTRUMENTAL

Design scheme of the implemented system

The functional block diagram of Microcontroller based Instrument set up is displayed with a clear depiction of its different blocks is shown in figure 1.

LEDs have been widely studied and applied to this kind of Instruments as monochromatic light source and solid state photo detectors are used for absorbance measurements. The Block A in Figure 1 consists of Green LED with a wavelength of 480nm to optically illuminate the sample solution to measure the Chloride concentration. Block B represents sample holder, which is used to hold the Blank, Standard and Sample solutions. A photo diode (GASPG 1124) is used to detect the amount of light falling on the sample, which acts as a photo detector represented, by a Block C. This ideal detector has the characteristics of long term stability, Short response and high sensitivity to allow the detection of low level radiant energy11. Block D consists of OP‐AMP, which acts as an instrumentation amplifier that amplifies the weak signal. The output of instrumentation amplifier is connected to the 12 bit A/D converter, which is in Block E. The Microcontroller P89C51RD2, which is kept in Block F, reads data from ADC for processing. Block G represents the keypad to give data for processing and to compute the Chloride concentration. Block H represents LCD, which is used to display the output of Microcontroller (Chloride concentration in ORS samples)12.

International Journal of Pharmacy and Pharmaceutical Sciences

ISSN- 0975-1491 Vol 3, Suppl 2, 2011

Neelamegam et al. Int J Pharm Pharm Sci, Vol 3, Suppl 2, 2011, 72­77

73

Fig. 1: Design of the implemented system

Fig. 2: Microcontroller and interfacing circuit

Description of the microcontroller based system

The Microcontroller and interfacing circuit is shown in Figure 2, which measures the concentration of Chloride ion based on colorimetry principle.

According to this principle, the absorbance of light (which passes through the colored solution) is proportional to the concentration of the ion. The Instrument system is incorporated with the Green LED source. A photodiode GASPG1124 is used as a sensor to detect the amount of light and convert into current. The output current of

Neelamegam et al. Int J Pharm Pharm Sci, Vol 3, Suppl 2, 2011, 72­77

74

photo detector is converted into voltage by an operational amplifier. The output of OP‐AMP is connected to the pin 35 of ADC 7109 through 1 MΩ resistance to convert analog to digital value. The lower and higher bytes of ADC 7109 are interfaced with port 0 of Microcontroller. The pin 29 of ADC 7109 generates the internal reference voltage. The Microcontroller P89C51RD2 contains a non‐volatile 64KB flash program memory and 1 K bytes of RAM. It has four 8 bit I/O ports, three 16‐bit timer/counters, a multi‐source four‐priority‐level, nested interrupt structure, an enhanced UART and on‐chip oscillator and timing circuits13. A reset switch is provided at pin 9, so that the program can be executed from 0000 after the power is switched on. A tap from preset is given to pin 36 of ADC 7109, the reference input pin. By adjusting this preset it is possible to get a full scale, which means that inputs between –4 and

+4 can be converted. A two row Alphanumeric LCD is interfaced to port 0 to display the measured concentration of Chloride.

Software

Fully dedicated Software for the data acquisition and computing the Chloride concentration in different ORS samples is developed in C and assembly language and linked to the application program. The structure of the software is elaborated as flowchart in Figure 3. Digital conversion), to check EOC (End of Conversion) to read lower byte enabling LBEN signal, to read higher byte enabling HBEN signal, to measure the readings for blank, standard, and sample, to compute absorbance and Chloride concentration, to display the result in the LCD and to get data from the keyboard.

Fig. 3: Flow chart

Software for the implemented system is written to initialize LCD, to start ADC (Analog to It is observed that the minimum time for data acquisition and computation is 0.6 s, taking into account the implemented algorithm.

MATERIALS AND METHODS

Oral Rehydration Salts of six different brands are collected from local pharmaceuticals in Tanjore, Tamil Nadu, South India. The samples of ORS are dissolved in 1L of deionized water without any precipitation. Since the samples are colorless, there is no need to add any chemical reagent to remove the color. The colorimetry

principle is used for the measurement of absorbance and concentration of Chloride electrolyte

Principle

The Chloride reagent is based on the method of Zall, Fisher and Garner14. When Chloride is mixed with a solution of undissociated mercuric thiocyanate, the Chloride preferentially combines with the mercury to form mercuric Chloride. The thiocyanate that is released combines with ferric ions present in the reagent to form ferric thiocyanate, which can be measured spectrophotometrically. The procedure is very sensitive and needs to be reduced for routine

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clinical applications by the addition of mercuric nitrate. The mercuric nitrate binds a fixed amount of Chloride ion and therefore makes them unavailable for reaction with mercuric thiocyanate. Only the Chloride present in excess of that bound by the mercury from mercuric nitrate is reacted with mercuric thiocyanate and produced the red ferric thiocyanate.

2Cl‐ + Hg(SCN)2 HgCl2 + 2SCN‐

3SCN‐ +Fe +++ 4Fe (SCN)++ +

Reagents

In this measurement system, two reagents R1 and R2 are used. The reagent R1 consists of Mercuric thiocyanate (2mmol/l), Ferric Nitrate (20mmol/l) and Nitric acid (29mmol/l). The reagent R2 is Chloride standard solution (NaCl of 100 mmol/l). All the solutions are prepared in a well cleaned dried test tube of same diameter. Blank solution is prepared by mixing 1 ml of reagent R1 with 10 µl of distilled water. For the preparation of standard solution, 1 ml of reagent R1 is added with 10 µl of standard (R2). The sample is prepared by adding 1 ml of reagent R1 with 10 µl of prepared ORS sample.

Measurement

The designed Instrument is used to measure the blank, Standard and sample voltages and to compute absorbance and concentration of Chloride. The test tube labeled blank is placed in a sample holder and the measured voltage is Vo. By holding the standard solution test tube in a sample holder, the voltage Vstd is read by the Microcontroller. The sample solution is placed in a sample holder

and voltage measured as Vt. The concentration of Chloride is computed using the formula,

Concentration of Chloride ion = log (Vo/Vt) / log (Vo/Vstd) x 100

Where, log (Vo/Vt) = Absorbance of sample, log (Vo/Vstd) =Absorbance of standard

100 = Concentration of standard Chloride.

The concentration of Chloride for six different brands of ORS samples is made using the developed instrument. The same samples are tested using the Chloride Ion Selective Electrode (ISE). The absorbance of sample solution is measured and repeated for five times to check the reproducibility.

RESULTS AND DISCUSSION

This study reveals the development of Microcontroller based Instrument set up to measure the concentration by colorimetry method in ORS samples. The Table 1 shows the readings for blank and standard of Chloride reagent.

Table 1: Voltage of blank and standard

S.No Blank Vo (mV) Standard (mV)

1 0.22 0.32

The measured readings of absorbance and concentration of Chloride in different ORS samples are given in Table 2.

The Table 3 gives the concentration of Chloride measured using the developed instrument and ISE method in different ORS samples.

Table 2: Absorbance and concentration of chloride in oral rehydration powder

S.No Types of sample Sample (VT) Absorption Chloride concentration m mol/l

1 ORS 1 0.175 0.099 61.87 2 ORS 2 0.174 0.101 63.12 3 ORS 3 0.174 0.101 63.124 ORS 4 0.173 0.104 645 ORS 5 0.173 0.104 64 6 ORS 5 0.175 0.099 61.8

Table 3: Comparison of results obtained using the developed instrument and chloride ISE

Sample id Chloride concentration (m mol/l) Developed instrument Chloride ISE

ORS 1 61.87 62 ORS 2 63.12 63 ORS 3 63.12 63 ORS 4 64 64 ORS 5 64 64 ORS 6 61.87 63

The concentration of Chloride is varied from (61.87‐64 mmol/l). The Certified Concentration of Chloride in ORS is 65mmol/l15. It is found that the range is well within the safe limits and also it is observed that there is no significant difference between the concentration values of different samples, which depicts that they are prepared by following the ORS formula given by W.H.O. The people who have suffered by dehydration having symptoms like dry mouth, loss of body weight greater than 10%, extreme thirst, sunken eyes, no tears when crying, decreased urination, fussiness, weakness, skin that stayed compressed and pinched should have the habit of in taking ORS to avoid some chronic condition. The dosage of ORS depends on age and severity of dehydration. Generally, for infants and children 1‐2 litres over a period of 24 hours. For Adults it differs from 2‐4 litres over a period of 24 hours.

Linearity and sensitivity

As the absorbance increases the Chloride concentration also increases, which shows the good fit of colorimetry principle. To

check the linearity of the developed instrument set up various samples having different Chloride concentration have been measured at the wavelength of 480nm. The Absorbance change of 0.1 typically corresponds to Chloride concentration of 42 m mol/l of the sample solution, which gave the sensitivity of the developed Instrument.

Recovery

To test the feasibility of the procedure and instrument, the recovery of the developed Instrument is studied by the standard addition method. Because the samples may produce some interference during the color development. To 0.5ml of ORS sample, various amounts of 0.1N Sodium Chloride (NaCl) solutions are added to bring the total Chloride concentration within normal range. The Table 4 shows the recovery values of added Chloride ranged from 98.13% to 99.15% with an average recovery of 98.42%, which indicates the suitability of the designed instrument for bulk drugs and assay tests.

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Table 4: Recovery of added chloride from ORS chloride (mmol/l)

S.No In ORS sample Added Total content

Total determined

Difference Recover %

1. 62 40 102 100.5 1.5 98.52 2. 62 45 107 105 2.0 98.13 3. 63 50 113 111 2.0 98.234. 63 55 118 117 1.0 99.155. 63 45 108 107 1.0 98.07

Fig. 4: Linear regression between the developed instrument and the chloride ISE

Linear regression analysis

Linear regression is plotted for the results obtained using designed Instrument and the ISE method which is shown in Figure 4.

Linear regression analysis attempts to model the relationship between two variables by fitting a linear equation that closely fits a collection of data points. All the samples fall into the linear range, and there is sufficient precision in the data to continue with the linearity study. There is no outlier in the data sets. The strength of the linear association between two variables is quantified by the

correlation coefficient. The Regression line equation arrived is y = 0.92X+4.43, the value of slope and the intercept (closes to ideality) indicated that the developed instrumentation system is well suited to determine the Chloride in ORS samples. The Correlation Coefficient R=0.99 (n=6), shows that the designed Instrument is well correlated with the Chloride ISE method.

Statistical analysis

The Statistical reports of Chloride electrolyte in different brands of ORS samples is given in Table 5.

Table 5: Statistical analysis for the data arrived using developed instrument and the ise

Variables Developed instrument Chloride ISE Mean 62.99 63.16 Std err of mean 0.356 0.280 Median 63.12 63Std err of median 0.445 0.350 S.D 0.873 0.687 Std err of S.D 0.252 0.187 Mean deviation 0.751 0.555Coefficient of variation 1.38 1.08S.E of Coeff of Variation 0.400 0.314

It is noted from the table that the mean value 63.30 and median value 63.43 are also within the safe limits. The data reported in this study refers that the concentration levels of electrolytes are fairly within the recommended levels, which confirms the pharmaceutical integrity. There is no considerable difference between the results obtained (Mean value, Standard Error of Mean value, Median value, Standard Error of Median value, Standard Deviation, Standard Error of Standard Deviation, Mean Deviation, Coefficient of Variation, Standard Error of Coefficient of Variation) using the designed Instrument and the ISE method which corroborates the validity of the implemented Instrument set up. The accuracy of the Microcontroller based Instrument is confirmed by the less residual between the two methods.

CONCLUSION

The instrument fabricated has been used to measure the concentration of Chloride electrolyte, which uses the colorimetry principle. The implemented system requires simple and low cost

electronics component. Normal spectrophotometers have optical lenses and filter, which makes the system clumsy, and difficult to use, as incandescent lamps are used as light sources, it generates lot of heat and consumes more power. All these problems are rectified in this developed Instrument and it does not require any programming expertise. The measurement system is tested with different samples to check the reproducibility. The application of this Instrument for the determination of Chloride in ORS is very important, due to the high levels of production in the world where these therapies contain considerable amounts of this ion. The same instrument can be used to measure the other analytes like Sodium and Potassium in bulk drugs by changing the light sources.

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